Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left...

35

Transcript of Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left...

Page 1: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

i

Status of the Western Silvery Minnow(Hybognathus argyritis) in Alberta

Prepared forAlberta Sustainable Resource Development (SRD)

Alberta Conservation Association (ACA)

Prepared bySusan M Pollard

This report has been reviewed revised and edited prior to publicationIt is an SRDACA working document that will be revised and updated periodically

Alberta Wildlife Status Report No 47

January 2003

Published By

ii

Publication No T032ISBN 0-7785-2328-4 (Printed Edition)ISBN 0-7785-2329-2 (On-line Edition)

ISSN 1206-4912 (Printed Edition)ISSN 1499-4682 (On-line Edition)

Series Editors Sue Peters and Robin GutsellIllustrations Brian Huffman

Maps Jane Bailey

For copies of this reportvisit our web site at httpwww3govabcasrdfwriskspecies

and click on ldquoDetailed Statusrdquo

OR

ContactInformation Centre - Publications

Alberta EnvironmentAlberta Sustainable Resource DevelopmentFish and Wildlife Division

Main Floor Great West Life Building9920 - 108 Street

Edmonton Alberta Canada T5K 2M4

Telephone (780) 422-2079

OR

Information ServiceAlberta EnvironmentAlberta Sustainable Resource Development

100 3115 - 12 Street NECalgary Alberta Canada T2E 7J2

Telephone (403) 297-6424

This publication may be cited as

Alberta Sustainable Resource Development 2003 Status of the Western Silvery Minnow (Hybognathusargyritis) in Alberta Alberta Sustainable Resource Development Fish and Wildlife Division and AlbertaConservation Association Wildlife Status Report No 47 Edmonton AB 24 pp

iii

PREFACE

Every five years the Fish and Wildlife Division of Alberta Sustainable Resource Development reviewsthe status of wildlife species in Alberta These overviews which have been conducted in 1991 1996and 2000 assign individual species ldquoranksrdquo that reflect the perceived level of risk to populations thatoccur in the province Such designations are determined from extensive consultations with professionaland amateur biologists and from a variety of readily available sources of population data A primaryobjective of these reviews is to identify species that may be considered for more detailed statusdeterminations

The Alberta Wildlife Status Report Series is an extension of the general statusing exercises (1996 Statusof Alberta Wildlife The General Status of Alberta Wild Species 2000) and provides comprehensivecurrent summaries of the biological status of selected wildlife species in Alberta Priority is given tospecies that are potentially at risk in the province (ldquoAt Riskrdquo ldquoMay Be At Riskrdquo) that are of uncertainstatus (ldquoUndeterminedrdquo) or those considered to be at risk at a national level by the Committee on theStatus of Endangered Wildlife in Canada (COSEWIC)

Reports in this series are published and distributed by the Alberta Conservation Association and the Fishand Wildlife Division of Alberta Sustainable Resource Development They are intended to providedetailed and up-to-date information which will be useful to resource professionals for managing populationsof species and their habitats in the province The reports are also designed to provide current informationwhich will assist the Alberta Endangered Species Conservation Committee to identify species that maybe formally designated as ldquoEndangeredrdquo or ldquoThreatenedrdquo under Albertarsquos Wildlife Act To achieve thesegoals the reports have been authored andor reviewed by individuals with unique local expertise in thebiology and management of each species

iv

EXECUTIVE SUMMARY

The western silvery minnow (Hybognathus argyritis) is a small cyprinid fish found in large plains streamsof the Missouri and Mississippi river drainages in mid-west North America Although this species isrelatively common in many areas of the United States it is extremely rare in Alberta with a confirmedpresence only in the lower Milk River Very little is known regarding the biology of western silveryminnow and much of the information available is based on studies of other silvery minnow speciesAbundance of this species in the Milk River does not appear to have changed since it was first identifiedin Alberta in the 1960s However it is suspected that both the extent of distribution and abundance ofwestern silvery minnow within the Milk River may have been altered significantly prior to this time (in theearly 1900s) when the St Mary Canal was constructed to divert irrigation water from the St MaryRiver to the Milk River The combination of water removal for irrigation and extreme drought conditionshas probably had the greatest impact on the survival of the western silvery minnow in Alberta Elsewhereit is believed that habitat alterations particularly associated with irrigation are responsible for declines inthe abundance and distribution of western silvery minnow

The western silvery minnow is currently ranked as ldquoMay Be At Riskrdquo according to The General Statusof Alberta Wild Species 2000 Nationally it is listed by the Committee on the Status of EndangeredWildlife in Canada (COSEWIC) as ldquoThreatenedrdquo The extremely limited distribution and low numbersof western silvery minnow consistently encountered in the Milk River make this species extremely vulnerableto extirpation The combination of severe drought conditions the operation of the St Mary Canal andthe removal of water for irrigation left the lower Milk River both above and below the internationalborder completely dry except for a series of shallow isolated pools during the fall and winter of 20012002 Studies are underway to determine the present status of western silvery minnow in the Albertaportion of the lower Milk River (see Addendum)

v

ACKNOWLEDGEMENTS

I wish to acknowledge a number of people for their assistance in compiling information for this documentincluding Terry Clayton (Sustainable Resource Development Lethbridge Alberta) Sean Stash (USForest Service Glacier Ranger District Girdwood Alaska) Kent Gilge (Montana Fish Wildlife andParks Havre Montana) Wayne Roberts (Zoology Museum University of Alberta Edmonton Alberta)Dr Robert Campbell (Species Specialist Subcommittee Co-chair Committee on the Status of EndangeredWildlife in Canada Ottawa Ontario) Sue Peters (Alberta Conservation Association Edmonton Alberta)and Sue Cotterill (Sustainable Resource Development Edmonton Alberta) In particular special thanksgo to Terry Clayton for taking the time to show me the key western silvery minnow locations on the MilkRiver and providing excellent background information regarding the water and fisheries issues of southernAlberta as well as a useful review of the manuscript Thank you also to Mark Steinhilber (AlbertaProvincial Museum Edmonton Alberta) Sue Peters and Robin Gutsell (Sustainable ResourceDevelopment Edmonton Alberta) for their useful comments and reviews of the manuscript Thanks toJane Bailey (Ducks Unlimited Canada) for creating the distribution maps

Preparation of this report was funded by the Alberta Conservation Association and the Fish and WildlifeDivision of Alberta Sustainable Resource Development

vi

TABLE OF CONTENTS

PREFACE iii

EXECUTIVE SUMMARY iv

ACKNOWLEDGEMENTS v

INTRODUCTION 1

HABITAT 1

1 Features 12 Trends 3

CONSERVATION BIOLOGY 3

1 Species identification 32 Life history 43 Diet 44 MovementDispersal 4

DISTRIBUTION 5

1 Alberta 52 Other Areas 7

POPULATION SIZE AND TRENDS 9

1 Alberta 92 Other Areas 9

LIMITING FACTORS 9

1 Alberta 92 Other areas 11

STATUS DESIGNATIONS 12

1 Alberta 122 Other Areas 12

RECENT MANAGEMENT IN ALBERTA 12

SYNTHESIS 12

LITERATURE CITED 14

vii

LIST OF FIGURES

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b)Specific locations correspond to collection sites summarized in Appendix 3 6

Figure 2 The distribution of western silvery minnow in North America 8

LIST OF TABLES

Table 1 Comparison of western silvery minnow sample sizes and percent species composition oftotal catch from the lower Milk River mainstem and creek mouths over time 10

TABLE OF CONTENTS cont

APPENDIX 1 Glossary of terms 17

APPENDIX 2 Definitions of selected legal and protective designations 18

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta20

ADDENDUM Summary of data collected in fall 2002 22

1

See Appendix 1 for definitions of selected statusdesignations

INTRODUCTION

The western silvery minnow (Hybognathusargyritis Girard Girard 1857) is a small fish ofthe cyprinid (carp) family native to large plainsstreams of the Missouri and Mississippi riversystems in midwest North America In Canadathis speciesrsquo presence has been confirmed in onlyone river system the Milk River (Willock 1969aScott and Crossman 1973 Nelson and Paetz1992) which runs east through the grasslandsof southern Alberta before joining the MissouriRiver in Montana The Milk River is a uniqueriver in Alberta in that it is the only system inthe province that contributes to the Missouridrainage This attribute of the Milk Riverexplains the very limited range of some fishspecies in Alberta including western silveryminnow which is believed to originate from theMississippiMissouri glacial refugium (seeGlossary Appendix 1) In addition to theextremely limited distribution of the westernsilvery minnow in Alberta its abundance withinthe Milk River has remained extremely low sincefirst documented in 1961 (see Appendix 3)

There has been some suggestion that the westernsilvery minnow was considerably more commonbefore 1917 (Willock 1969b) It was at this timethat the irrigation canal from the St Mary Riverto the North Milk River was constructed inMontana resulting in increased turbidity levelsThis diversion of water into the North Milk Riverhas also resulted in much greater water volumesduring the summer that likely allowed thewestern silvery minnow greater upstream accessinto the Alberta portion of the Milk RiverHowever the combination of water removal forirrigation from the Milk River temporary orpremature canal closures and drought conditionssuch as those experienced in 2000-2001 hasresulted in extremely low water conditions fromsummer to late winter It is this combination offactors that likely limits the abundance anddistribution of western silvery minnow inAlberta

The western silvery minnow is currentlyconsidered ldquoMay Be At Riskrdquo according to TheGeneral Status of Alberta Wild Species 2000(Alberta Sustainable Resource Development2001) Nationally the Committee on the Statusof Endangered Wildlife in Canada (COSEWIC)listed western silvery minnow as ldquoThreatenedrdquoin 2001 Although this species is considerablymore abundant in the Milk River south of theinternational border in Montana other stateshave documented a significant decline or lossof populations The intent of this status reportis to provide a summary of relevant and currentinformation regarding the status of westernsilvery minnow in Alberta

HABITAT

1 Features - In general the western silveryminnow is found in backwaters and pools oflarge silty plains streams (Pflieger 1980) InOhio the western silvery minnow appeared tobe most abundant in areas with little or nocurrent where the water was rich inphytoplankton (small aquatic plant organisms)and the gravelly sandy muddy or debris-covered bottom was not covered in silt(Trautman 1957) Spawning was found to occuronly where the rate of bottom siltation was low(Trautman 1957) One early study of a closelyrelated species eastern silvery minnow (Hregius) found that spawners moved to heavilyvegetated backwaters in slower-moving reachesof streams (Raney 1939) Rearing of botheastern and western species occurs near quietinshore areas and tributary mouths where smallschools can be found (Raney 1939 RLampL1987)

The presence and abundance of western silveryminnow in the United States appears to bestrongly associated with a number of habitatfeatures including bottom type gradient andturbidity The western silvery minnow of the

2

lower Ohio-upper Mississippi Basin occurs inthe Mississippi River proper only below themouth of the Missouri River (Burr and Page1986) This section is a transitional area withincreased turbidity increased velocity shiftingsands and silty substrates providing suitablehabitat for H argyritis (Burr and Page 1986)These characteristics are also common in theMissouri River where H argyritis is commonto dominant throughout the system (Cross et al1986) In particular the lower Missouri Riverhas extreme fluctuations in water flowthroughout the year high silt loads and unstablestreambeds devoid of vegetation (Cross et al1986) Similar habitats characterize the lowerMilk River in Alberta

A number of fish species inventories have beenconducted on the Milk River in Alberta sincethe 1960s (Willock 1969b Clayton and Ash1980 RLampL 1987 2001 2002a b) Thesestudies all found western silvery minnow limitedto the lowest section of the Milk River mainstemwhere the river has been described as low-gradient and even-flowing with many backwaterareas and shallow flat and run habitats (seeGlossary Appendix 1) This section of the MilkRiver is distinct from upstream sections wherethe habitat features include more runs riffles andrapids (RLampL 2001) The middle and lowerMilk River in Alberta flows through easilyeroded shale formations resulting in a soft-bottomed riverbed and muddy highly turbidwaters in contrast to the more erosion-resistantsandstone formations upstream (Willock 1969b)In addition the lower section receives lessprecipitation and waters are considerablywarmer (Willock 1969b) Based on theminnowrsquos limited distribution in the lowersection of the Milk River Willock (1969b)concluded that this species was restricted toregions with warm silty water Given the lackof other refugia in the lower Milk River highturbidity provides the main source of cover forthe minnow The western silvery minnowappears to be restricted to mainstem waters inthe Milk River since no individuals were

captured in small tributaries in recent studies(RLampL 2001 2002b) these results support thoseof an earlier investigation by Willock (1969a)Absence in the tributaries studied may be due tothe intermittent nature of the streams surveyedparticularly considering the extreme droughtconditions such as those observed during theyears 2000-2001

A microhabitat analysis of the data collected in2000 and 2001 found that several habitat featuresfor western silvery minnow were similar amongthe collection sites (RLampL 2002b) Thesefeatures included relatively low water velocities(00-003 ms) low silt depths (00-010 m) anda high percentage of sand as substrate (95-100) Similar results were observed forwestern silvery minnow in the Milk River fromthe International Boundary Crossing to theFresno Reservoir in Montana although the meanvelocity was higher (15 ms) (Stash 2001)

The lower Milk River in Alberta appears tocontain abundant rearing and feeding habitat forthe western silver minnow (RLampL 2001) wherewith the exception of fall 2001 quiet waters withlow to moderate velocities are usually prevalent(RLampL 2002a) Similarly overwintering habitathas also been documented in the lower MilkRiver (Clayton and Ash 1980) althoughavailability is highly dependent on winter flowsOverwintering habitat is likely one of the majorlimiting factors for the silvery minnow in theMilk River With regards to spawning habitatrequirements areas rich in aquatic vegetationhave been listed as a key feature (Raney 1939Houston 1998a) However no aquaticvegetation is present in the lower Milk RiverInstead high waters during the spring result inflooded backwater areas where terrestrialvegetation is often present particularly near thecreek mouths and spawning minnows may usethese areas (T Clayton pers comm)

2 Trends - The greatest changes to westernsilvery minnow habitat in Alberta have beenassociated with irrigation In 1917 the St Mary

3

Canal was constructed in Montana to divertwater from the St Mary River to the North MilkRiver for irrigation purposes In most years thecanal diverts water from April to Septemberincreasing the water volume in the North MilkRiver and the Milk River proper Before theconstruction of the dam the Milk River wasprobably a typical small prairie stream possiblyintermittent in times of drought and generallyless turbid (Willock 1969b) The even-flowingwaters now observed in the lower Milk River inAlberta were probably mainly restricted todownstream of the international border beforethe dam was constructed (Willock 1969b) Thesignificant increase in water volume since thecanal went into use is believed to haveextensively altered the ecological regime of theMilk River (with the exception of the South MilkRiver fork) by shifting habitat types westwardinto the Alberta portion (Willock 1969b TClayton pers comm) The result has been thecreation of a more turbid higher-flow systemwith more potential western silvery minnowhabitat available in the lower section of the MilkRiver in Alberta However Willock (1969b)also states that historically western silveryminnow may actually have used the uppersections of the Milk River before theconstruction of the canal The increased flowsassociated with the canal resulted in greater bankerosion and higher quantities of silt possiblyleading to a rapid decline in the minnowrsquospopulation size in the upper sections

Since the construction of the St Mary Canal nomajor losses or changes in habitat have occurredRather the availability of habitat is highlyvariable from year to year and mainly dependenton adequate water flows particularly in the latesummer and fall and for overwintering Duringperiods of very low flows the western silveryminnow may experience temporary reductionsin available habitat and under extremeconditions such as those of fall and winter 20012002 temporary habitat fragmentation Theextent of the drought during this period was suchthat the lower section of the Milk River in

Alberta where most silvery minnows have beendocumented was reduced to a series of isolatedpools many of which were not deep enough tosupport overwintering fish (RLampL 2002a) Awinter survey of a subset of these pools did notfind any minnows present (RLampL 2002a)Furthermore south of the international borderthe Milk River was completely dry to the FresnoReservoir from September 2001 to February2002 and the reservoir was only at 4 of itscapacity (K Gilge pers comm)

A small number of western silvery minnows wassubsequently collected (July 2002) upstream ofthe section that was dry in fall 2001 (T Claytonpers comm) It may also be present in theFresno Reservoir but has not been confirmed bysurveys (K Gilge pers comm) Thereforelimited re-colonization potential from upstreamand downstream sections in the system existsbut the re-establishment of significant numbersin the lower Milk River may require severalyears Downstream of the Fresno Reservoir andassociated dam in Montana six more impassibledams upstream of the confluence (see GlossaryAppendix 1) with the Missouri River preventany broader dispersal of western silvery minnow(Stash 2001 K Gilge pers comm)

In summary while rearing and feeding habitatfor the western silvery minnow in Albertaappears to be abundant in most years theavailability of overwintering habitat may bequite limited in some years depending on waterflow conditions In particular the combinationof extreme drought conditions canal operationand water removal could severely reduce or eveneliminate winter refugia for the western silveryminnow in the lower Milk River

CONSERVATION BIOLOGY

1 Species Identification - The western silveryminnow is a small fish belonging to the cyprinid

See glossary in Appendix 1 for definitions of thefollowing terms used in this subsection total lengthfork length caudal peduncle and subterminal mouth

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 2: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

ii

Publication No T032ISBN 0-7785-2328-4 (Printed Edition)ISBN 0-7785-2329-2 (On-line Edition)

ISSN 1206-4912 (Printed Edition)ISSN 1499-4682 (On-line Edition)

Series Editors Sue Peters and Robin GutsellIllustrations Brian Huffman

Maps Jane Bailey

For copies of this reportvisit our web site at httpwww3govabcasrdfwriskspecies

and click on ldquoDetailed Statusrdquo

OR

ContactInformation Centre - Publications

Alberta EnvironmentAlberta Sustainable Resource DevelopmentFish and Wildlife Division

Main Floor Great West Life Building9920 - 108 Street

Edmonton Alberta Canada T5K 2M4

Telephone (780) 422-2079

OR

Information ServiceAlberta EnvironmentAlberta Sustainable Resource Development

100 3115 - 12 Street NECalgary Alberta Canada T2E 7J2

Telephone (403) 297-6424

This publication may be cited as

Alberta Sustainable Resource Development 2003 Status of the Western Silvery Minnow (Hybognathusargyritis) in Alberta Alberta Sustainable Resource Development Fish and Wildlife Division and AlbertaConservation Association Wildlife Status Report No 47 Edmonton AB 24 pp

iii

PREFACE

Every five years the Fish and Wildlife Division of Alberta Sustainable Resource Development reviewsthe status of wildlife species in Alberta These overviews which have been conducted in 1991 1996and 2000 assign individual species ldquoranksrdquo that reflect the perceived level of risk to populations thatoccur in the province Such designations are determined from extensive consultations with professionaland amateur biologists and from a variety of readily available sources of population data A primaryobjective of these reviews is to identify species that may be considered for more detailed statusdeterminations

The Alberta Wildlife Status Report Series is an extension of the general statusing exercises (1996 Statusof Alberta Wildlife The General Status of Alberta Wild Species 2000) and provides comprehensivecurrent summaries of the biological status of selected wildlife species in Alberta Priority is given tospecies that are potentially at risk in the province (ldquoAt Riskrdquo ldquoMay Be At Riskrdquo) that are of uncertainstatus (ldquoUndeterminedrdquo) or those considered to be at risk at a national level by the Committee on theStatus of Endangered Wildlife in Canada (COSEWIC)

Reports in this series are published and distributed by the Alberta Conservation Association and the Fishand Wildlife Division of Alberta Sustainable Resource Development They are intended to providedetailed and up-to-date information which will be useful to resource professionals for managing populationsof species and their habitats in the province The reports are also designed to provide current informationwhich will assist the Alberta Endangered Species Conservation Committee to identify species that maybe formally designated as ldquoEndangeredrdquo or ldquoThreatenedrdquo under Albertarsquos Wildlife Act To achieve thesegoals the reports have been authored andor reviewed by individuals with unique local expertise in thebiology and management of each species

iv

EXECUTIVE SUMMARY

The western silvery minnow (Hybognathus argyritis) is a small cyprinid fish found in large plains streamsof the Missouri and Mississippi river drainages in mid-west North America Although this species isrelatively common in many areas of the United States it is extremely rare in Alberta with a confirmedpresence only in the lower Milk River Very little is known regarding the biology of western silveryminnow and much of the information available is based on studies of other silvery minnow speciesAbundance of this species in the Milk River does not appear to have changed since it was first identifiedin Alberta in the 1960s However it is suspected that both the extent of distribution and abundance ofwestern silvery minnow within the Milk River may have been altered significantly prior to this time (in theearly 1900s) when the St Mary Canal was constructed to divert irrigation water from the St MaryRiver to the Milk River The combination of water removal for irrigation and extreme drought conditionshas probably had the greatest impact on the survival of the western silvery minnow in Alberta Elsewhereit is believed that habitat alterations particularly associated with irrigation are responsible for declines inthe abundance and distribution of western silvery minnow

The western silvery minnow is currently ranked as ldquoMay Be At Riskrdquo according to The General Statusof Alberta Wild Species 2000 Nationally it is listed by the Committee on the Status of EndangeredWildlife in Canada (COSEWIC) as ldquoThreatenedrdquo The extremely limited distribution and low numbersof western silvery minnow consistently encountered in the Milk River make this species extremely vulnerableto extirpation The combination of severe drought conditions the operation of the St Mary Canal andthe removal of water for irrigation left the lower Milk River both above and below the internationalborder completely dry except for a series of shallow isolated pools during the fall and winter of 20012002 Studies are underway to determine the present status of western silvery minnow in the Albertaportion of the lower Milk River (see Addendum)

v

ACKNOWLEDGEMENTS

I wish to acknowledge a number of people for their assistance in compiling information for this documentincluding Terry Clayton (Sustainable Resource Development Lethbridge Alberta) Sean Stash (USForest Service Glacier Ranger District Girdwood Alaska) Kent Gilge (Montana Fish Wildlife andParks Havre Montana) Wayne Roberts (Zoology Museum University of Alberta Edmonton Alberta)Dr Robert Campbell (Species Specialist Subcommittee Co-chair Committee on the Status of EndangeredWildlife in Canada Ottawa Ontario) Sue Peters (Alberta Conservation Association Edmonton Alberta)and Sue Cotterill (Sustainable Resource Development Edmonton Alberta) In particular special thanksgo to Terry Clayton for taking the time to show me the key western silvery minnow locations on the MilkRiver and providing excellent background information regarding the water and fisheries issues of southernAlberta as well as a useful review of the manuscript Thank you also to Mark Steinhilber (AlbertaProvincial Museum Edmonton Alberta) Sue Peters and Robin Gutsell (Sustainable ResourceDevelopment Edmonton Alberta) for their useful comments and reviews of the manuscript Thanks toJane Bailey (Ducks Unlimited Canada) for creating the distribution maps

Preparation of this report was funded by the Alberta Conservation Association and the Fish and WildlifeDivision of Alberta Sustainable Resource Development

vi

TABLE OF CONTENTS

PREFACE iii

EXECUTIVE SUMMARY iv

ACKNOWLEDGEMENTS v

INTRODUCTION 1

HABITAT 1

1 Features 12 Trends 3

CONSERVATION BIOLOGY 3

1 Species identification 32 Life history 43 Diet 44 MovementDispersal 4

DISTRIBUTION 5

1 Alberta 52 Other Areas 7

POPULATION SIZE AND TRENDS 9

1 Alberta 92 Other Areas 9

LIMITING FACTORS 9

1 Alberta 92 Other areas 11

STATUS DESIGNATIONS 12

1 Alberta 122 Other Areas 12

RECENT MANAGEMENT IN ALBERTA 12

SYNTHESIS 12

LITERATURE CITED 14

vii

LIST OF FIGURES

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b)Specific locations correspond to collection sites summarized in Appendix 3 6

Figure 2 The distribution of western silvery minnow in North America 8

LIST OF TABLES

Table 1 Comparison of western silvery minnow sample sizes and percent species composition oftotal catch from the lower Milk River mainstem and creek mouths over time 10

TABLE OF CONTENTS cont

APPENDIX 1 Glossary of terms 17

APPENDIX 2 Definitions of selected legal and protective designations 18

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta20

ADDENDUM Summary of data collected in fall 2002 22

1

See Appendix 1 for definitions of selected statusdesignations

INTRODUCTION

The western silvery minnow (Hybognathusargyritis Girard Girard 1857) is a small fish ofthe cyprinid (carp) family native to large plainsstreams of the Missouri and Mississippi riversystems in midwest North America In Canadathis speciesrsquo presence has been confirmed in onlyone river system the Milk River (Willock 1969aScott and Crossman 1973 Nelson and Paetz1992) which runs east through the grasslandsof southern Alberta before joining the MissouriRiver in Montana The Milk River is a uniqueriver in Alberta in that it is the only system inthe province that contributes to the Missouridrainage This attribute of the Milk Riverexplains the very limited range of some fishspecies in Alberta including western silveryminnow which is believed to originate from theMississippiMissouri glacial refugium (seeGlossary Appendix 1) In addition to theextremely limited distribution of the westernsilvery minnow in Alberta its abundance withinthe Milk River has remained extremely low sincefirst documented in 1961 (see Appendix 3)

There has been some suggestion that the westernsilvery minnow was considerably more commonbefore 1917 (Willock 1969b) It was at this timethat the irrigation canal from the St Mary Riverto the North Milk River was constructed inMontana resulting in increased turbidity levelsThis diversion of water into the North Milk Riverhas also resulted in much greater water volumesduring the summer that likely allowed thewestern silvery minnow greater upstream accessinto the Alberta portion of the Milk RiverHowever the combination of water removal forirrigation from the Milk River temporary orpremature canal closures and drought conditionssuch as those experienced in 2000-2001 hasresulted in extremely low water conditions fromsummer to late winter It is this combination offactors that likely limits the abundance anddistribution of western silvery minnow inAlberta

The western silvery minnow is currentlyconsidered ldquoMay Be At Riskrdquo according to TheGeneral Status of Alberta Wild Species 2000(Alberta Sustainable Resource Development2001) Nationally the Committee on the Statusof Endangered Wildlife in Canada (COSEWIC)listed western silvery minnow as ldquoThreatenedrdquoin 2001 Although this species is considerablymore abundant in the Milk River south of theinternational border in Montana other stateshave documented a significant decline or lossof populations The intent of this status reportis to provide a summary of relevant and currentinformation regarding the status of westernsilvery minnow in Alberta

HABITAT

1 Features - In general the western silveryminnow is found in backwaters and pools oflarge silty plains streams (Pflieger 1980) InOhio the western silvery minnow appeared tobe most abundant in areas with little or nocurrent where the water was rich inphytoplankton (small aquatic plant organisms)and the gravelly sandy muddy or debris-covered bottom was not covered in silt(Trautman 1957) Spawning was found to occuronly where the rate of bottom siltation was low(Trautman 1957) One early study of a closelyrelated species eastern silvery minnow (Hregius) found that spawners moved to heavilyvegetated backwaters in slower-moving reachesof streams (Raney 1939) Rearing of botheastern and western species occurs near quietinshore areas and tributary mouths where smallschools can be found (Raney 1939 RLampL1987)

The presence and abundance of western silveryminnow in the United States appears to bestrongly associated with a number of habitatfeatures including bottom type gradient andturbidity The western silvery minnow of the

2

lower Ohio-upper Mississippi Basin occurs inthe Mississippi River proper only below themouth of the Missouri River (Burr and Page1986) This section is a transitional area withincreased turbidity increased velocity shiftingsands and silty substrates providing suitablehabitat for H argyritis (Burr and Page 1986)These characteristics are also common in theMissouri River where H argyritis is commonto dominant throughout the system (Cross et al1986) In particular the lower Missouri Riverhas extreme fluctuations in water flowthroughout the year high silt loads and unstablestreambeds devoid of vegetation (Cross et al1986) Similar habitats characterize the lowerMilk River in Alberta

A number of fish species inventories have beenconducted on the Milk River in Alberta sincethe 1960s (Willock 1969b Clayton and Ash1980 RLampL 1987 2001 2002a b) Thesestudies all found western silvery minnow limitedto the lowest section of the Milk River mainstemwhere the river has been described as low-gradient and even-flowing with many backwaterareas and shallow flat and run habitats (seeGlossary Appendix 1) This section of the MilkRiver is distinct from upstream sections wherethe habitat features include more runs riffles andrapids (RLampL 2001) The middle and lowerMilk River in Alberta flows through easilyeroded shale formations resulting in a soft-bottomed riverbed and muddy highly turbidwaters in contrast to the more erosion-resistantsandstone formations upstream (Willock 1969b)In addition the lower section receives lessprecipitation and waters are considerablywarmer (Willock 1969b) Based on theminnowrsquos limited distribution in the lowersection of the Milk River Willock (1969b)concluded that this species was restricted toregions with warm silty water Given the lackof other refugia in the lower Milk River highturbidity provides the main source of cover forthe minnow The western silvery minnowappears to be restricted to mainstem waters inthe Milk River since no individuals were

captured in small tributaries in recent studies(RLampL 2001 2002b) these results support thoseof an earlier investigation by Willock (1969a)Absence in the tributaries studied may be due tothe intermittent nature of the streams surveyedparticularly considering the extreme droughtconditions such as those observed during theyears 2000-2001

A microhabitat analysis of the data collected in2000 and 2001 found that several habitat featuresfor western silvery minnow were similar amongthe collection sites (RLampL 2002b) Thesefeatures included relatively low water velocities(00-003 ms) low silt depths (00-010 m) anda high percentage of sand as substrate (95-100) Similar results were observed forwestern silvery minnow in the Milk River fromthe International Boundary Crossing to theFresno Reservoir in Montana although the meanvelocity was higher (15 ms) (Stash 2001)

The lower Milk River in Alberta appears tocontain abundant rearing and feeding habitat forthe western silver minnow (RLampL 2001) wherewith the exception of fall 2001 quiet waters withlow to moderate velocities are usually prevalent(RLampL 2002a) Similarly overwintering habitathas also been documented in the lower MilkRiver (Clayton and Ash 1980) althoughavailability is highly dependent on winter flowsOverwintering habitat is likely one of the majorlimiting factors for the silvery minnow in theMilk River With regards to spawning habitatrequirements areas rich in aquatic vegetationhave been listed as a key feature (Raney 1939Houston 1998a) However no aquaticvegetation is present in the lower Milk RiverInstead high waters during the spring result inflooded backwater areas where terrestrialvegetation is often present particularly near thecreek mouths and spawning minnows may usethese areas (T Clayton pers comm)

2 Trends - The greatest changes to westernsilvery minnow habitat in Alberta have beenassociated with irrigation In 1917 the St Mary

3

Canal was constructed in Montana to divertwater from the St Mary River to the North MilkRiver for irrigation purposes In most years thecanal diverts water from April to Septemberincreasing the water volume in the North MilkRiver and the Milk River proper Before theconstruction of the dam the Milk River wasprobably a typical small prairie stream possiblyintermittent in times of drought and generallyless turbid (Willock 1969b) The even-flowingwaters now observed in the lower Milk River inAlberta were probably mainly restricted todownstream of the international border beforethe dam was constructed (Willock 1969b) Thesignificant increase in water volume since thecanal went into use is believed to haveextensively altered the ecological regime of theMilk River (with the exception of the South MilkRiver fork) by shifting habitat types westwardinto the Alberta portion (Willock 1969b TClayton pers comm) The result has been thecreation of a more turbid higher-flow systemwith more potential western silvery minnowhabitat available in the lower section of the MilkRiver in Alberta However Willock (1969b)also states that historically western silveryminnow may actually have used the uppersections of the Milk River before theconstruction of the canal The increased flowsassociated with the canal resulted in greater bankerosion and higher quantities of silt possiblyleading to a rapid decline in the minnowrsquospopulation size in the upper sections

Since the construction of the St Mary Canal nomajor losses or changes in habitat have occurredRather the availability of habitat is highlyvariable from year to year and mainly dependenton adequate water flows particularly in the latesummer and fall and for overwintering Duringperiods of very low flows the western silveryminnow may experience temporary reductionsin available habitat and under extremeconditions such as those of fall and winter 20012002 temporary habitat fragmentation Theextent of the drought during this period was suchthat the lower section of the Milk River in

Alberta where most silvery minnows have beendocumented was reduced to a series of isolatedpools many of which were not deep enough tosupport overwintering fish (RLampL 2002a) Awinter survey of a subset of these pools did notfind any minnows present (RLampL 2002a)Furthermore south of the international borderthe Milk River was completely dry to the FresnoReservoir from September 2001 to February2002 and the reservoir was only at 4 of itscapacity (K Gilge pers comm)

A small number of western silvery minnows wassubsequently collected (July 2002) upstream ofthe section that was dry in fall 2001 (T Claytonpers comm) It may also be present in theFresno Reservoir but has not been confirmed bysurveys (K Gilge pers comm) Thereforelimited re-colonization potential from upstreamand downstream sections in the system existsbut the re-establishment of significant numbersin the lower Milk River may require severalyears Downstream of the Fresno Reservoir andassociated dam in Montana six more impassibledams upstream of the confluence (see GlossaryAppendix 1) with the Missouri River preventany broader dispersal of western silvery minnow(Stash 2001 K Gilge pers comm)

In summary while rearing and feeding habitatfor the western silvery minnow in Albertaappears to be abundant in most years theavailability of overwintering habitat may bequite limited in some years depending on waterflow conditions In particular the combinationof extreme drought conditions canal operationand water removal could severely reduce or eveneliminate winter refugia for the western silveryminnow in the lower Milk River

CONSERVATION BIOLOGY

1 Species Identification - The western silveryminnow is a small fish belonging to the cyprinid

See glossary in Appendix 1 for definitions of thefollowing terms used in this subsection total lengthfork length caudal peduncle and subterminal mouth

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 3: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

iii

PREFACE

Every five years the Fish and Wildlife Division of Alberta Sustainable Resource Development reviewsthe status of wildlife species in Alberta These overviews which have been conducted in 1991 1996and 2000 assign individual species ldquoranksrdquo that reflect the perceived level of risk to populations thatoccur in the province Such designations are determined from extensive consultations with professionaland amateur biologists and from a variety of readily available sources of population data A primaryobjective of these reviews is to identify species that may be considered for more detailed statusdeterminations

The Alberta Wildlife Status Report Series is an extension of the general statusing exercises (1996 Statusof Alberta Wildlife The General Status of Alberta Wild Species 2000) and provides comprehensivecurrent summaries of the biological status of selected wildlife species in Alberta Priority is given tospecies that are potentially at risk in the province (ldquoAt Riskrdquo ldquoMay Be At Riskrdquo) that are of uncertainstatus (ldquoUndeterminedrdquo) or those considered to be at risk at a national level by the Committee on theStatus of Endangered Wildlife in Canada (COSEWIC)

Reports in this series are published and distributed by the Alberta Conservation Association and the Fishand Wildlife Division of Alberta Sustainable Resource Development They are intended to providedetailed and up-to-date information which will be useful to resource professionals for managing populationsof species and their habitats in the province The reports are also designed to provide current informationwhich will assist the Alberta Endangered Species Conservation Committee to identify species that maybe formally designated as ldquoEndangeredrdquo or ldquoThreatenedrdquo under Albertarsquos Wildlife Act To achieve thesegoals the reports have been authored andor reviewed by individuals with unique local expertise in thebiology and management of each species

iv

EXECUTIVE SUMMARY

The western silvery minnow (Hybognathus argyritis) is a small cyprinid fish found in large plains streamsof the Missouri and Mississippi river drainages in mid-west North America Although this species isrelatively common in many areas of the United States it is extremely rare in Alberta with a confirmedpresence only in the lower Milk River Very little is known regarding the biology of western silveryminnow and much of the information available is based on studies of other silvery minnow speciesAbundance of this species in the Milk River does not appear to have changed since it was first identifiedin Alberta in the 1960s However it is suspected that both the extent of distribution and abundance ofwestern silvery minnow within the Milk River may have been altered significantly prior to this time (in theearly 1900s) when the St Mary Canal was constructed to divert irrigation water from the St MaryRiver to the Milk River The combination of water removal for irrigation and extreme drought conditionshas probably had the greatest impact on the survival of the western silvery minnow in Alberta Elsewhereit is believed that habitat alterations particularly associated with irrigation are responsible for declines inthe abundance and distribution of western silvery minnow

The western silvery minnow is currently ranked as ldquoMay Be At Riskrdquo according to The General Statusof Alberta Wild Species 2000 Nationally it is listed by the Committee on the Status of EndangeredWildlife in Canada (COSEWIC) as ldquoThreatenedrdquo The extremely limited distribution and low numbersof western silvery minnow consistently encountered in the Milk River make this species extremely vulnerableto extirpation The combination of severe drought conditions the operation of the St Mary Canal andthe removal of water for irrigation left the lower Milk River both above and below the internationalborder completely dry except for a series of shallow isolated pools during the fall and winter of 20012002 Studies are underway to determine the present status of western silvery minnow in the Albertaportion of the lower Milk River (see Addendum)

v

ACKNOWLEDGEMENTS

I wish to acknowledge a number of people for their assistance in compiling information for this documentincluding Terry Clayton (Sustainable Resource Development Lethbridge Alberta) Sean Stash (USForest Service Glacier Ranger District Girdwood Alaska) Kent Gilge (Montana Fish Wildlife andParks Havre Montana) Wayne Roberts (Zoology Museum University of Alberta Edmonton Alberta)Dr Robert Campbell (Species Specialist Subcommittee Co-chair Committee on the Status of EndangeredWildlife in Canada Ottawa Ontario) Sue Peters (Alberta Conservation Association Edmonton Alberta)and Sue Cotterill (Sustainable Resource Development Edmonton Alberta) In particular special thanksgo to Terry Clayton for taking the time to show me the key western silvery minnow locations on the MilkRiver and providing excellent background information regarding the water and fisheries issues of southernAlberta as well as a useful review of the manuscript Thank you also to Mark Steinhilber (AlbertaProvincial Museum Edmonton Alberta) Sue Peters and Robin Gutsell (Sustainable ResourceDevelopment Edmonton Alberta) for their useful comments and reviews of the manuscript Thanks toJane Bailey (Ducks Unlimited Canada) for creating the distribution maps

Preparation of this report was funded by the Alberta Conservation Association and the Fish and WildlifeDivision of Alberta Sustainable Resource Development

vi

TABLE OF CONTENTS

PREFACE iii

EXECUTIVE SUMMARY iv

ACKNOWLEDGEMENTS v

INTRODUCTION 1

HABITAT 1

1 Features 12 Trends 3

CONSERVATION BIOLOGY 3

1 Species identification 32 Life history 43 Diet 44 MovementDispersal 4

DISTRIBUTION 5

1 Alberta 52 Other Areas 7

POPULATION SIZE AND TRENDS 9

1 Alberta 92 Other Areas 9

LIMITING FACTORS 9

1 Alberta 92 Other areas 11

STATUS DESIGNATIONS 12

1 Alberta 122 Other Areas 12

RECENT MANAGEMENT IN ALBERTA 12

SYNTHESIS 12

LITERATURE CITED 14

vii

LIST OF FIGURES

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b)Specific locations correspond to collection sites summarized in Appendix 3 6

Figure 2 The distribution of western silvery minnow in North America 8

LIST OF TABLES

Table 1 Comparison of western silvery minnow sample sizes and percent species composition oftotal catch from the lower Milk River mainstem and creek mouths over time 10

TABLE OF CONTENTS cont

APPENDIX 1 Glossary of terms 17

APPENDIX 2 Definitions of selected legal and protective designations 18

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta20

ADDENDUM Summary of data collected in fall 2002 22

1

See Appendix 1 for definitions of selected statusdesignations

INTRODUCTION

The western silvery minnow (Hybognathusargyritis Girard Girard 1857) is a small fish ofthe cyprinid (carp) family native to large plainsstreams of the Missouri and Mississippi riversystems in midwest North America In Canadathis speciesrsquo presence has been confirmed in onlyone river system the Milk River (Willock 1969aScott and Crossman 1973 Nelson and Paetz1992) which runs east through the grasslandsof southern Alberta before joining the MissouriRiver in Montana The Milk River is a uniqueriver in Alberta in that it is the only system inthe province that contributes to the Missouridrainage This attribute of the Milk Riverexplains the very limited range of some fishspecies in Alberta including western silveryminnow which is believed to originate from theMississippiMissouri glacial refugium (seeGlossary Appendix 1) In addition to theextremely limited distribution of the westernsilvery minnow in Alberta its abundance withinthe Milk River has remained extremely low sincefirst documented in 1961 (see Appendix 3)

There has been some suggestion that the westernsilvery minnow was considerably more commonbefore 1917 (Willock 1969b) It was at this timethat the irrigation canal from the St Mary Riverto the North Milk River was constructed inMontana resulting in increased turbidity levelsThis diversion of water into the North Milk Riverhas also resulted in much greater water volumesduring the summer that likely allowed thewestern silvery minnow greater upstream accessinto the Alberta portion of the Milk RiverHowever the combination of water removal forirrigation from the Milk River temporary orpremature canal closures and drought conditionssuch as those experienced in 2000-2001 hasresulted in extremely low water conditions fromsummer to late winter It is this combination offactors that likely limits the abundance anddistribution of western silvery minnow inAlberta

The western silvery minnow is currentlyconsidered ldquoMay Be At Riskrdquo according to TheGeneral Status of Alberta Wild Species 2000(Alberta Sustainable Resource Development2001) Nationally the Committee on the Statusof Endangered Wildlife in Canada (COSEWIC)listed western silvery minnow as ldquoThreatenedrdquoin 2001 Although this species is considerablymore abundant in the Milk River south of theinternational border in Montana other stateshave documented a significant decline or lossof populations The intent of this status reportis to provide a summary of relevant and currentinformation regarding the status of westernsilvery minnow in Alberta

HABITAT

1 Features - In general the western silveryminnow is found in backwaters and pools oflarge silty plains streams (Pflieger 1980) InOhio the western silvery minnow appeared tobe most abundant in areas with little or nocurrent where the water was rich inphytoplankton (small aquatic plant organisms)and the gravelly sandy muddy or debris-covered bottom was not covered in silt(Trautman 1957) Spawning was found to occuronly where the rate of bottom siltation was low(Trautman 1957) One early study of a closelyrelated species eastern silvery minnow (Hregius) found that spawners moved to heavilyvegetated backwaters in slower-moving reachesof streams (Raney 1939) Rearing of botheastern and western species occurs near quietinshore areas and tributary mouths where smallschools can be found (Raney 1939 RLampL1987)

The presence and abundance of western silveryminnow in the United States appears to bestrongly associated with a number of habitatfeatures including bottom type gradient andturbidity The western silvery minnow of the

2

lower Ohio-upper Mississippi Basin occurs inthe Mississippi River proper only below themouth of the Missouri River (Burr and Page1986) This section is a transitional area withincreased turbidity increased velocity shiftingsands and silty substrates providing suitablehabitat for H argyritis (Burr and Page 1986)These characteristics are also common in theMissouri River where H argyritis is commonto dominant throughout the system (Cross et al1986) In particular the lower Missouri Riverhas extreme fluctuations in water flowthroughout the year high silt loads and unstablestreambeds devoid of vegetation (Cross et al1986) Similar habitats characterize the lowerMilk River in Alberta

A number of fish species inventories have beenconducted on the Milk River in Alberta sincethe 1960s (Willock 1969b Clayton and Ash1980 RLampL 1987 2001 2002a b) Thesestudies all found western silvery minnow limitedto the lowest section of the Milk River mainstemwhere the river has been described as low-gradient and even-flowing with many backwaterareas and shallow flat and run habitats (seeGlossary Appendix 1) This section of the MilkRiver is distinct from upstream sections wherethe habitat features include more runs riffles andrapids (RLampL 2001) The middle and lowerMilk River in Alberta flows through easilyeroded shale formations resulting in a soft-bottomed riverbed and muddy highly turbidwaters in contrast to the more erosion-resistantsandstone formations upstream (Willock 1969b)In addition the lower section receives lessprecipitation and waters are considerablywarmer (Willock 1969b) Based on theminnowrsquos limited distribution in the lowersection of the Milk River Willock (1969b)concluded that this species was restricted toregions with warm silty water Given the lackof other refugia in the lower Milk River highturbidity provides the main source of cover forthe minnow The western silvery minnowappears to be restricted to mainstem waters inthe Milk River since no individuals were

captured in small tributaries in recent studies(RLampL 2001 2002b) these results support thoseof an earlier investigation by Willock (1969a)Absence in the tributaries studied may be due tothe intermittent nature of the streams surveyedparticularly considering the extreme droughtconditions such as those observed during theyears 2000-2001

A microhabitat analysis of the data collected in2000 and 2001 found that several habitat featuresfor western silvery minnow were similar amongthe collection sites (RLampL 2002b) Thesefeatures included relatively low water velocities(00-003 ms) low silt depths (00-010 m) anda high percentage of sand as substrate (95-100) Similar results were observed forwestern silvery minnow in the Milk River fromthe International Boundary Crossing to theFresno Reservoir in Montana although the meanvelocity was higher (15 ms) (Stash 2001)

The lower Milk River in Alberta appears tocontain abundant rearing and feeding habitat forthe western silver minnow (RLampL 2001) wherewith the exception of fall 2001 quiet waters withlow to moderate velocities are usually prevalent(RLampL 2002a) Similarly overwintering habitathas also been documented in the lower MilkRiver (Clayton and Ash 1980) althoughavailability is highly dependent on winter flowsOverwintering habitat is likely one of the majorlimiting factors for the silvery minnow in theMilk River With regards to spawning habitatrequirements areas rich in aquatic vegetationhave been listed as a key feature (Raney 1939Houston 1998a) However no aquaticvegetation is present in the lower Milk RiverInstead high waters during the spring result inflooded backwater areas where terrestrialvegetation is often present particularly near thecreek mouths and spawning minnows may usethese areas (T Clayton pers comm)

2 Trends - The greatest changes to westernsilvery minnow habitat in Alberta have beenassociated with irrigation In 1917 the St Mary

3

Canal was constructed in Montana to divertwater from the St Mary River to the North MilkRiver for irrigation purposes In most years thecanal diverts water from April to Septemberincreasing the water volume in the North MilkRiver and the Milk River proper Before theconstruction of the dam the Milk River wasprobably a typical small prairie stream possiblyintermittent in times of drought and generallyless turbid (Willock 1969b) The even-flowingwaters now observed in the lower Milk River inAlberta were probably mainly restricted todownstream of the international border beforethe dam was constructed (Willock 1969b) Thesignificant increase in water volume since thecanal went into use is believed to haveextensively altered the ecological regime of theMilk River (with the exception of the South MilkRiver fork) by shifting habitat types westwardinto the Alberta portion (Willock 1969b TClayton pers comm) The result has been thecreation of a more turbid higher-flow systemwith more potential western silvery minnowhabitat available in the lower section of the MilkRiver in Alberta However Willock (1969b)also states that historically western silveryminnow may actually have used the uppersections of the Milk River before theconstruction of the canal The increased flowsassociated with the canal resulted in greater bankerosion and higher quantities of silt possiblyleading to a rapid decline in the minnowrsquospopulation size in the upper sections

Since the construction of the St Mary Canal nomajor losses or changes in habitat have occurredRather the availability of habitat is highlyvariable from year to year and mainly dependenton adequate water flows particularly in the latesummer and fall and for overwintering Duringperiods of very low flows the western silveryminnow may experience temporary reductionsin available habitat and under extremeconditions such as those of fall and winter 20012002 temporary habitat fragmentation Theextent of the drought during this period was suchthat the lower section of the Milk River in

Alberta where most silvery minnows have beendocumented was reduced to a series of isolatedpools many of which were not deep enough tosupport overwintering fish (RLampL 2002a) Awinter survey of a subset of these pools did notfind any minnows present (RLampL 2002a)Furthermore south of the international borderthe Milk River was completely dry to the FresnoReservoir from September 2001 to February2002 and the reservoir was only at 4 of itscapacity (K Gilge pers comm)

A small number of western silvery minnows wassubsequently collected (July 2002) upstream ofthe section that was dry in fall 2001 (T Claytonpers comm) It may also be present in theFresno Reservoir but has not been confirmed bysurveys (K Gilge pers comm) Thereforelimited re-colonization potential from upstreamand downstream sections in the system existsbut the re-establishment of significant numbersin the lower Milk River may require severalyears Downstream of the Fresno Reservoir andassociated dam in Montana six more impassibledams upstream of the confluence (see GlossaryAppendix 1) with the Missouri River preventany broader dispersal of western silvery minnow(Stash 2001 K Gilge pers comm)

In summary while rearing and feeding habitatfor the western silvery minnow in Albertaappears to be abundant in most years theavailability of overwintering habitat may bequite limited in some years depending on waterflow conditions In particular the combinationof extreme drought conditions canal operationand water removal could severely reduce or eveneliminate winter refugia for the western silveryminnow in the lower Milk River

CONSERVATION BIOLOGY

1 Species Identification - The western silveryminnow is a small fish belonging to the cyprinid

See glossary in Appendix 1 for definitions of thefollowing terms used in this subsection total lengthfork length caudal peduncle and subterminal mouth

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 4: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

iv

EXECUTIVE SUMMARY

The western silvery minnow (Hybognathus argyritis) is a small cyprinid fish found in large plains streamsof the Missouri and Mississippi river drainages in mid-west North America Although this species isrelatively common in many areas of the United States it is extremely rare in Alberta with a confirmedpresence only in the lower Milk River Very little is known regarding the biology of western silveryminnow and much of the information available is based on studies of other silvery minnow speciesAbundance of this species in the Milk River does not appear to have changed since it was first identifiedin Alberta in the 1960s However it is suspected that both the extent of distribution and abundance ofwestern silvery minnow within the Milk River may have been altered significantly prior to this time (in theearly 1900s) when the St Mary Canal was constructed to divert irrigation water from the St MaryRiver to the Milk River The combination of water removal for irrigation and extreme drought conditionshas probably had the greatest impact on the survival of the western silvery minnow in Alberta Elsewhereit is believed that habitat alterations particularly associated with irrigation are responsible for declines inthe abundance and distribution of western silvery minnow

The western silvery minnow is currently ranked as ldquoMay Be At Riskrdquo according to The General Statusof Alberta Wild Species 2000 Nationally it is listed by the Committee on the Status of EndangeredWildlife in Canada (COSEWIC) as ldquoThreatenedrdquo The extremely limited distribution and low numbersof western silvery minnow consistently encountered in the Milk River make this species extremely vulnerableto extirpation The combination of severe drought conditions the operation of the St Mary Canal andthe removal of water for irrigation left the lower Milk River both above and below the internationalborder completely dry except for a series of shallow isolated pools during the fall and winter of 20012002 Studies are underway to determine the present status of western silvery minnow in the Albertaportion of the lower Milk River (see Addendum)

v

ACKNOWLEDGEMENTS

I wish to acknowledge a number of people for their assistance in compiling information for this documentincluding Terry Clayton (Sustainable Resource Development Lethbridge Alberta) Sean Stash (USForest Service Glacier Ranger District Girdwood Alaska) Kent Gilge (Montana Fish Wildlife andParks Havre Montana) Wayne Roberts (Zoology Museum University of Alberta Edmonton Alberta)Dr Robert Campbell (Species Specialist Subcommittee Co-chair Committee on the Status of EndangeredWildlife in Canada Ottawa Ontario) Sue Peters (Alberta Conservation Association Edmonton Alberta)and Sue Cotterill (Sustainable Resource Development Edmonton Alberta) In particular special thanksgo to Terry Clayton for taking the time to show me the key western silvery minnow locations on the MilkRiver and providing excellent background information regarding the water and fisheries issues of southernAlberta as well as a useful review of the manuscript Thank you also to Mark Steinhilber (AlbertaProvincial Museum Edmonton Alberta) Sue Peters and Robin Gutsell (Sustainable ResourceDevelopment Edmonton Alberta) for their useful comments and reviews of the manuscript Thanks toJane Bailey (Ducks Unlimited Canada) for creating the distribution maps

Preparation of this report was funded by the Alberta Conservation Association and the Fish and WildlifeDivision of Alberta Sustainable Resource Development

vi

TABLE OF CONTENTS

PREFACE iii

EXECUTIVE SUMMARY iv

ACKNOWLEDGEMENTS v

INTRODUCTION 1

HABITAT 1

1 Features 12 Trends 3

CONSERVATION BIOLOGY 3

1 Species identification 32 Life history 43 Diet 44 MovementDispersal 4

DISTRIBUTION 5

1 Alberta 52 Other Areas 7

POPULATION SIZE AND TRENDS 9

1 Alberta 92 Other Areas 9

LIMITING FACTORS 9

1 Alberta 92 Other areas 11

STATUS DESIGNATIONS 12

1 Alberta 122 Other Areas 12

RECENT MANAGEMENT IN ALBERTA 12

SYNTHESIS 12

LITERATURE CITED 14

vii

LIST OF FIGURES

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b)Specific locations correspond to collection sites summarized in Appendix 3 6

Figure 2 The distribution of western silvery minnow in North America 8

LIST OF TABLES

Table 1 Comparison of western silvery minnow sample sizes and percent species composition oftotal catch from the lower Milk River mainstem and creek mouths over time 10

TABLE OF CONTENTS cont

APPENDIX 1 Glossary of terms 17

APPENDIX 2 Definitions of selected legal and protective designations 18

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta20

ADDENDUM Summary of data collected in fall 2002 22

1

See Appendix 1 for definitions of selected statusdesignations

INTRODUCTION

The western silvery minnow (Hybognathusargyritis Girard Girard 1857) is a small fish ofthe cyprinid (carp) family native to large plainsstreams of the Missouri and Mississippi riversystems in midwest North America In Canadathis speciesrsquo presence has been confirmed in onlyone river system the Milk River (Willock 1969aScott and Crossman 1973 Nelson and Paetz1992) which runs east through the grasslandsof southern Alberta before joining the MissouriRiver in Montana The Milk River is a uniqueriver in Alberta in that it is the only system inthe province that contributes to the Missouridrainage This attribute of the Milk Riverexplains the very limited range of some fishspecies in Alberta including western silveryminnow which is believed to originate from theMississippiMissouri glacial refugium (seeGlossary Appendix 1) In addition to theextremely limited distribution of the westernsilvery minnow in Alberta its abundance withinthe Milk River has remained extremely low sincefirst documented in 1961 (see Appendix 3)

There has been some suggestion that the westernsilvery minnow was considerably more commonbefore 1917 (Willock 1969b) It was at this timethat the irrigation canal from the St Mary Riverto the North Milk River was constructed inMontana resulting in increased turbidity levelsThis diversion of water into the North Milk Riverhas also resulted in much greater water volumesduring the summer that likely allowed thewestern silvery minnow greater upstream accessinto the Alberta portion of the Milk RiverHowever the combination of water removal forirrigation from the Milk River temporary orpremature canal closures and drought conditionssuch as those experienced in 2000-2001 hasresulted in extremely low water conditions fromsummer to late winter It is this combination offactors that likely limits the abundance anddistribution of western silvery minnow inAlberta

The western silvery minnow is currentlyconsidered ldquoMay Be At Riskrdquo according to TheGeneral Status of Alberta Wild Species 2000(Alberta Sustainable Resource Development2001) Nationally the Committee on the Statusof Endangered Wildlife in Canada (COSEWIC)listed western silvery minnow as ldquoThreatenedrdquoin 2001 Although this species is considerablymore abundant in the Milk River south of theinternational border in Montana other stateshave documented a significant decline or lossof populations The intent of this status reportis to provide a summary of relevant and currentinformation regarding the status of westernsilvery minnow in Alberta

HABITAT

1 Features - In general the western silveryminnow is found in backwaters and pools oflarge silty plains streams (Pflieger 1980) InOhio the western silvery minnow appeared tobe most abundant in areas with little or nocurrent where the water was rich inphytoplankton (small aquatic plant organisms)and the gravelly sandy muddy or debris-covered bottom was not covered in silt(Trautman 1957) Spawning was found to occuronly where the rate of bottom siltation was low(Trautman 1957) One early study of a closelyrelated species eastern silvery minnow (Hregius) found that spawners moved to heavilyvegetated backwaters in slower-moving reachesof streams (Raney 1939) Rearing of botheastern and western species occurs near quietinshore areas and tributary mouths where smallschools can be found (Raney 1939 RLampL1987)

The presence and abundance of western silveryminnow in the United States appears to bestrongly associated with a number of habitatfeatures including bottom type gradient andturbidity The western silvery minnow of the

2

lower Ohio-upper Mississippi Basin occurs inthe Mississippi River proper only below themouth of the Missouri River (Burr and Page1986) This section is a transitional area withincreased turbidity increased velocity shiftingsands and silty substrates providing suitablehabitat for H argyritis (Burr and Page 1986)These characteristics are also common in theMissouri River where H argyritis is commonto dominant throughout the system (Cross et al1986) In particular the lower Missouri Riverhas extreme fluctuations in water flowthroughout the year high silt loads and unstablestreambeds devoid of vegetation (Cross et al1986) Similar habitats characterize the lowerMilk River in Alberta

A number of fish species inventories have beenconducted on the Milk River in Alberta sincethe 1960s (Willock 1969b Clayton and Ash1980 RLampL 1987 2001 2002a b) Thesestudies all found western silvery minnow limitedto the lowest section of the Milk River mainstemwhere the river has been described as low-gradient and even-flowing with many backwaterareas and shallow flat and run habitats (seeGlossary Appendix 1) This section of the MilkRiver is distinct from upstream sections wherethe habitat features include more runs riffles andrapids (RLampL 2001) The middle and lowerMilk River in Alberta flows through easilyeroded shale formations resulting in a soft-bottomed riverbed and muddy highly turbidwaters in contrast to the more erosion-resistantsandstone formations upstream (Willock 1969b)In addition the lower section receives lessprecipitation and waters are considerablywarmer (Willock 1969b) Based on theminnowrsquos limited distribution in the lowersection of the Milk River Willock (1969b)concluded that this species was restricted toregions with warm silty water Given the lackof other refugia in the lower Milk River highturbidity provides the main source of cover forthe minnow The western silvery minnowappears to be restricted to mainstem waters inthe Milk River since no individuals were

captured in small tributaries in recent studies(RLampL 2001 2002b) these results support thoseof an earlier investigation by Willock (1969a)Absence in the tributaries studied may be due tothe intermittent nature of the streams surveyedparticularly considering the extreme droughtconditions such as those observed during theyears 2000-2001

A microhabitat analysis of the data collected in2000 and 2001 found that several habitat featuresfor western silvery minnow were similar amongthe collection sites (RLampL 2002b) Thesefeatures included relatively low water velocities(00-003 ms) low silt depths (00-010 m) anda high percentage of sand as substrate (95-100) Similar results were observed forwestern silvery minnow in the Milk River fromthe International Boundary Crossing to theFresno Reservoir in Montana although the meanvelocity was higher (15 ms) (Stash 2001)

The lower Milk River in Alberta appears tocontain abundant rearing and feeding habitat forthe western silver minnow (RLampL 2001) wherewith the exception of fall 2001 quiet waters withlow to moderate velocities are usually prevalent(RLampL 2002a) Similarly overwintering habitathas also been documented in the lower MilkRiver (Clayton and Ash 1980) althoughavailability is highly dependent on winter flowsOverwintering habitat is likely one of the majorlimiting factors for the silvery minnow in theMilk River With regards to spawning habitatrequirements areas rich in aquatic vegetationhave been listed as a key feature (Raney 1939Houston 1998a) However no aquaticvegetation is present in the lower Milk RiverInstead high waters during the spring result inflooded backwater areas where terrestrialvegetation is often present particularly near thecreek mouths and spawning minnows may usethese areas (T Clayton pers comm)

2 Trends - The greatest changes to westernsilvery minnow habitat in Alberta have beenassociated with irrigation In 1917 the St Mary

3

Canal was constructed in Montana to divertwater from the St Mary River to the North MilkRiver for irrigation purposes In most years thecanal diverts water from April to Septemberincreasing the water volume in the North MilkRiver and the Milk River proper Before theconstruction of the dam the Milk River wasprobably a typical small prairie stream possiblyintermittent in times of drought and generallyless turbid (Willock 1969b) The even-flowingwaters now observed in the lower Milk River inAlberta were probably mainly restricted todownstream of the international border beforethe dam was constructed (Willock 1969b) Thesignificant increase in water volume since thecanal went into use is believed to haveextensively altered the ecological regime of theMilk River (with the exception of the South MilkRiver fork) by shifting habitat types westwardinto the Alberta portion (Willock 1969b TClayton pers comm) The result has been thecreation of a more turbid higher-flow systemwith more potential western silvery minnowhabitat available in the lower section of the MilkRiver in Alberta However Willock (1969b)also states that historically western silveryminnow may actually have used the uppersections of the Milk River before theconstruction of the canal The increased flowsassociated with the canal resulted in greater bankerosion and higher quantities of silt possiblyleading to a rapid decline in the minnowrsquospopulation size in the upper sections

Since the construction of the St Mary Canal nomajor losses or changes in habitat have occurredRather the availability of habitat is highlyvariable from year to year and mainly dependenton adequate water flows particularly in the latesummer and fall and for overwintering Duringperiods of very low flows the western silveryminnow may experience temporary reductionsin available habitat and under extremeconditions such as those of fall and winter 20012002 temporary habitat fragmentation Theextent of the drought during this period was suchthat the lower section of the Milk River in

Alberta where most silvery minnows have beendocumented was reduced to a series of isolatedpools many of which were not deep enough tosupport overwintering fish (RLampL 2002a) Awinter survey of a subset of these pools did notfind any minnows present (RLampL 2002a)Furthermore south of the international borderthe Milk River was completely dry to the FresnoReservoir from September 2001 to February2002 and the reservoir was only at 4 of itscapacity (K Gilge pers comm)

A small number of western silvery minnows wassubsequently collected (July 2002) upstream ofthe section that was dry in fall 2001 (T Claytonpers comm) It may also be present in theFresno Reservoir but has not been confirmed bysurveys (K Gilge pers comm) Thereforelimited re-colonization potential from upstreamand downstream sections in the system existsbut the re-establishment of significant numbersin the lower Milk River may require severalyears Downstream of the Fresno Reservoir andassociated dam in Montana six more impassibledams upstream of the confluence (see GlossaryAppendix 1) with the Missouri River preventany broader dispersal of western silvery minnow(Stash 2001 K Gilge pers comm)

In summary while rearing and feeding habitatfor the western silvery minnow in Albertaappears to be abundant in most years theavailability of overwintering habitat may bequite limited in some years depending on waterflow conditions In particular the combinationof extreme drought conditions canal operationand water removal could severely reduce or eveneliminate winter refugia for the western silveryminnow in the lower Milk River

CONSERVATION BIOLOGY

1 Species Identification - The western silveryminnow is a small fish belonging to the cyprinid

See glossary in Appendix 1 for definitions of thefollowing terms used in this subsection total lengthfork length caudal peduncle and subterminal mouth

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 5: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

v

ACKNOWLEDGEMENTS

I wish to acknowledge a number of people for their assistance in compiling information for this documentincluding Terry Clayton (Sustainable Resource Development Lethbridge Alberta) Sean Stash (USForest Service Glacier Ranger District Girdwood Alaska) Kent Gilge (Montana Fish Wildlife andParks Havre Montana) Wayne Roberts (Zoology Museum University of Alberta Edmonton Alberta)Dr Robert Campbell (Species Specialist Subcommittee Co-chair Committee on the Status of EndangeredWildlife in Canada Ottawa Ontario) Sue Peters (Alberta Conservation Association Edmonton Alberta)and Sue Cotterill (Sustainable Resource Development Edmonton Alberta) In particular special thanksgo to Terry Clayton for taking the time to show me the key western silvery minnow locations on the MilkRiver and providing excellent background information regarding the water and fisheries issues of southernAlberta as well as a useful review of the manuscript Thank you also to Mark Steinhilber (AlbertaProvincial Museum Edmonton Alberta) Sue Peters and Robin Gutsell (Sustainable ResourceDevelopment Edmonton Alberta) for their useful comments and reviews of the manuscript Thanks toJane Bailey (Ducks Unlimited Canada) for creating the distribution maps

Preparation of this report was funded by the Alberta Conservation Association and the Fish and WildlifeDivision of Alberta Sustainable Resource Development

vi

TABLE OF CONTENTS

PREFACE iii

EXECUTIVE SUMMARY iv

ACKNOWLEDGEMENTS v

INTRODUCTION 1

HABITAT 1

1 Features 12 Trends 3

CONSERVATION BIOLOGY 3

1 Species identification 32 Life history 43 Diet 44 MovementDispersal 4

DISTRIBUTION 5

1 Alberta 52 Other Areas 7

POPULATION SIZE AND TRENDS 9

1 Alberta 92 Other Areas 9

LIMITING FACTORS 9

1 Alberta 92 Other areas 11

STATUS DESIGNATIONS 12

1 Alberta 122 Other Areas 12

RECENT MANAGEMENT IN ALBERTA 12

SYNTHESIS 12

LITERATURE CITED 14

vii

LIST OF FIGURES

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b)Specific locations correspond to collection sites summarized in Appendix 3 6

Figure 2 The distribution of western silvery minnow in North America 8

LIST OF TABLES

Table 1 Comparison of western silvery minnow sample sizes and percent species composition oftotal catch from the lower Milk River mainstem and creek mouths over time 10

TABLE OF CONTENTS cont

APPENDIX 1 Glossary of terms 17

APPENDIX 2 Definitions of selected legal and protective designations 18

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta20

ADDENDUM Summary of data collected in fall 2002 22

1

See Appendix 1 for definitions of selected statusdesignations

INTRODUCTION

The western silvery minnow (Hybognathusargyritis Girard Girard 1857) is a small fish ofthe cyprinid (carp) family native to large plainsstreams of the Missouri and Mississippi riversystems in midwest North America In Canadathis speciesrsquo presence has been confirmed in onlyone river system the Milk River (Willock 1969aScott and Crossman 1973 Nelson and Paetz1992) which runs east through the grasslandsof southern Alberta before joining the MissouriRiver in Montana The Milk River is a uniqueriver in Alberta in that it is the only system inthe province that contributes to the Missouridrainage This attribute of the Milk Riverexplains the very limited range of some fishspecies in Alberta including western silveryminnow which is believed to originate from theMississippiMissouri glacial refugium (seeGlossary Appendix 1) In addition to theextremely limited distribution of the westernsilvery minnow in Alberta its abundance withinthe Milk River has remained extremely low sincefirst documented in 1961 (see Appendix 3)

There has been some suggestion that the westernsilvery minnow was considerably more commonbefore 1917 (Willock 1969b) It was at this timethat the irrigation canal from the St Mary Riverto the North Milk River was constructed inMontana resulting in increased turbidity levelsThis diversion of water into the North Milk Riverhas also resulted in much greater water volumesduring the summer that likely allowed thewestern silvery minnow greater upstream accessinto the Alberta portion of the Milk RiverHowever the combination of water removal forirrigation from the Milk River temporary orpremature canal closures and drought conditionssuch as those experienced in 2000-2001 hasresulted in extremely low water conditions fromsummer to late winter It is this combination offactors that likely limits the abundance anddistribution of western silvery minnow inAlberta

The western silvery minnow is currentlyconsidered ldquoMay Be At Riskrdquo according to TheGeneral Status of Alberta Wild Species 2000(Alberta Sustainable Resource Development2001) Nationally the Committee on the Statusof Endangered Wildlife in Canada (COSEWIC)listed western silvery minnow as ldquoThreatenedrdquoin 2001 Although this species is considerablymore abundant in the Milk River south of theinternational border in Montana other stateshave documented a significant decline or lossof populations The intent of this status reportis to provide a summary of relevant and currentinformation regarding the status of westernsilvery minnow in Alberta

HABITAT

1 Features - In general the western silveryminnow is found in backwaters and pools oflarge silty plains streams (Pflieger 1980) InOhio the western silvery minnow appeared tobe most abundant in areas with little or nocurrent where the water was rich inphytoplankton (small aquatic plant organisms)and the gravelly sandy muddy or debris-covered bottom was not covered in silt(Trautman 1957) Spawning was found to occuronly where the rate of bottom siltation was low(Trautman 1957) One early study of a closelyrelated species eastern silvery minnow (Hregius) found that spawners moved to heavilyvegetated backwaters in slower-moving reachesof streams (Raney 1939) Rearing of botheastern and western species occurs near quietinshore areas and tributary mouths where smallschools can be found (Raney 1939 RLampL1987)

The presence and abundance of western silveryminnow in the United States appears to bestrongly associated with a number of habitatfeatures including bottom type gradient andturbidity The western silvery minnow of the

2

lower Ohio-upper Mississippi Basin occurs inthe Mississippi River proper only below themouth of the Missouri River (Burr and Page1986) This section is a transitional area withincreased turbidity increased velocity shiftingsands and silty substrates providing suitablehabitat for H argyritis (Burr and Page 1986)These characteristics are also common in theMissouri River where H argyritis is commonto dominant throughout the system (Cross et al1986) In particular the lower Missouri Riverhas extreme fluctuations in water flowthroughout the year high silt loads and unstablestreambeds devoid of vegetation (Cross et al1986) Similar habitats characterize the lowerMilk River in Alberta

A number of fish species inventories have beenconducted on the Milk River in Alberta sincethe 1960s (Willock 1969b Clayton and Ash1980 RLampL 1987 2001 2002a b) Thesestudies all found western silvery minnow limitedto the lowest section of the Milk River mainstemwhere the river has been described as low-gradient and even-flowing with many backwaterareas and shallow flat and run habitats (seeGlossary Appendix 1) This section of the MilkRiver is distinct from upstream sections wherethe habitat features include more runs riffles andrapids (RLampL 2001) The middle and lowerMilk River in Alberta flows through easilyeroded shale formations resulting in a soft-bottomed riverbed and muddy highly turbidwaters in contrast to the more erosion-resistantsandstone formations upstream (Willock 1969b)In addition the lower section receives lessprecipitation and waters are considerablywarmer (Willock 1969b) Based on theminnowrsquos limited distribution in the lowersection of the Milk River Willock (1969b)concluded that this species was restricted toregions with warm silty water Given the lackof other refugia in the lower Milk River highturbidity provides the main source of cover forthe minnow The western silvery minnowappears to be restricted to mainstem waters inthe Milk River since no individuals were

captured in small tributaries in recent studies(RLampL 2001 2002b) these results support thoseof an earlier investigation by Willock (1969a)Absence in the tributaries studied may be due tothe intermittent nature of the streams surveyedparticularly considering the extreme droughtconditions such as those observed during theyears 2000-2001

A microhabitat analysis of the data collected in2000 and 2001 found that several habitat featuresfor western silvery minnow were similar amongthe collection sites (RLampL 2002b) Thesefeatures included relatively low water velocities(00-003 ms) low silt depths (00-010 m) anda high percentage of sand as substrate (95-100) Similar results were observed forwestern silvery minnow in the Milk River fromthe International Boundary Crossing to theFresno Reservoir in Montana although the meanvelocity was higher (15 ms) (Stash 2001)

The lower Milk River in Alberta appears tocontain abundant rearing and feeding habitat forthe western silver minnow (RLampL 2001) wherewith the exception of fall 2001 quiet waters withlow to moderate velocities are usually prevalent(RLampL 2002a) Similarly overwintering habitathas also been documented in the lower MilkRiver (Clayton and Ash 1980) althoughavailability is highly dependent on winter flowsOverwintering habitat is likely one of the majorlimiting factors for the silvery minnow in theMilk River With regards to spawning habitatrequirements areas rich in aquatic vegetationhave been listed as a key feature (Raney 1939Houston 1998a) However no aquaticvegetation is present in the lower Milk RiverInstead high waters during the spring result inflooded backwater areas where terrestrialvegetation is often present particularly near thecreek mouths and spawning minnows may usethese areas (T Clayton pers comm)

2 Trends - The greatest changes to westernsilvery minnow habitat in Alberta have beenassociated with irrigation In 1917 the St Mary

3

Canal was constructed in Montana to divertwater from the St Mary River to the North MilkRiver for irrigation purposes In most years thecanal diverts water from April to Septemberincreasing the water volume in the North MilkRiver and the Milk River proper Before theconstruction of the dam the Milk River wasprobably a typical small prairie stream possiblyintermittent in times of drought and generallyless turbid (Willock 1969b) The even-flowingwaters now observed in the lower Milk River inAlberta were probably mainly restricted todownstream of the international border beforethe dam was constructed (Willock 1969b) Thesignificant increase in water volume since thecanal went into use is believed to haveextensively altered the ecological regime of theMilk River (with the exception of the South MilkRiver fork) by shifting habitat types westwardinto the Alberta portion (Willock 1969b TClayton pers comm) The result has been thecreation of a more turbid higher-flow systemwith more potential western silvery minnowhabitat available in the lower section of the MilkRiver in Alberta However Willock (1969b)also states that historically western silveryminnow may actually have used the uppersections of the Milk River before theconstruction of the canal The increased flowsassociated with the canal resulted in greater bankerosion and higher quantities of silt possiblyleading to a rapid decline in the minnowrsquospopulation size in the upper sections

Since the construction of the St Mary Canal nomajor losses or changes in habitat have occurredRather the availability of habitat is highlyvariable from year to year and mainly dependenton adequate water flows particularly in the latesummer and fall and for overwintering Duringperiods of very low flows the western silveryminnow may experience temporary reductionsin available habitat and under extremeconditions such as those of fall and winter 20012002 temporary habitat fragmentation Theextent of the drought during this period was suchthat the lower section of the Milk River in

Alberta where most silvery minnows have beendocumented was reduced to a series of isolatedpools many of which were not deep enough tosupport overwintering fish (RLampL 2002a) Awinter survey of a subset of these pools did notfind any minnows present (RLampL 2002a)Furthermore south of the international borderthe Milk River was completely dry to the FresnoReservoir from September 2001 to February2002 and the reservoir was only at 4 of itscapacity (K Gilge pers comm)

A small number of western silvery minnows wassubsequently collected (July 2002) upstream ofthe section that was dry in fall 2001 (T Claytonpers comm) It may also be present in theFresno Reservoir but has not been confirmed bysurveys (K Gilge pers comm) Thereforelimited re-colonization potential from upstreamand downstream sections in the system existsbut the re-establishment of significant numbersin the lower Milk River may require severalyears Downstream of the Fresno Reservoir andassociated dam in Montana six more impassibledams upstream of the confluence (see GlossaryAppendix 1) with the Missouri River preventany broader dispersal of western silvery minnow(Stash 2001 K Gilge pers comm)

In summary while rearing and feeding habitatfor the western silvery minnow in Albertaappears to be abundant in most years theavailability of overwintering habitat may bequite limited in some years depending on waterflow conditions In particular the combinationof extreme drought conditions canal operationand water removal could severely reduce or eveneliminate winter refugia for the western silveryminnow in the lower Milk River

CONSERVATION BIOLOGY

1 Species Identification - The western silveryminnow is a small fish belonging to the cyprinid

See glossary in Appendix 1 for definitions of thefollowing terms used in this subsection total lengthfork length caudal peduncle and subterminal mouth

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 6: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

vi

TABLE OF CONTENTS

PREFACE iii

EXECUTIVE SUMMARY iv

ACKNOWLEDGEMENTS v

INTRODUCTION 1

HABITAT 1

1 Features 12 Trends 3

CONSERVATION BIOLOGY 3

1 Species identification 32 Life history 43 Diet 44 MovementDispersal 4

DISTRIBUTION 5

1 Alberta 52 Other Areas 7

POPULATION SIZE AND TRENDS 9

1 Alberta 92 Other Areas 9

LIMITING FACTORS 9

1 Alberta 92 Other areas 11

STATUS DESIGNATIONS 12

1 Alberta 122 Other Areas 12

RECENT MANAGEMENT IN ALBERTA 12

SYNTHESIS 12

LITERATURE CITED 14

vii

LIST OF FIGURES

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b)Specific locations correspond to collection sites summarized in Appendix 3 6

Figure 2 The distribution of western silvery minnow in North America 8

LIST OF TABLES

Table 1 Comparison of western silvery minnow sample sizes and percent species composition oftotal catch from the lower Milk River mainstem and creek mouths over time 10

TABLE OF CONTENTS cont

APPENDIX 1 Glossary of terms 17

APPENDIX 2 Definitions of selected legal and protective designations 18

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta20

ADDENDUM Summary of data collected in fall 2002 22

1

See Appendix 1 for definitions of selected statusdesignations

INTRODUCTION

The western silvery minnow (Hybognathusargyritis Girard Girard 1857) is a small fish ofthe cyprinid (carp) family native to large plainsstreams of the Missouri and Mississippi riversystems in midwest North America In Canadathis speciesrsquo presence has been confirmed in onlyone river system the Milk River (Willock 1969aScott and Crossman 1973 Nelson and Paetz1992) which runs east through the grasslandsof southern Alberta before joining the MissouriRiver in Montana The Milk River is a uniqueriver in Alberta in that it is the only system inthe province that contributes to the Missouridrainage This attribute of the Milk Riverexplains the very limited range of some fishspecies in Alberta including western silveryminnow which is believed to originate from theMississippiMissouri glacial refugium (seeGlossary Appendix 1) In addition to theextremely limited distribution of the westernsilvery minnow in Alberta its abundance withinthe Milk River has remained extremely low sincefirst documented in 1961 (see Appendix 3)

There has been some suggestion that the westernsilvery minnow was considerably more commonbefore 1917 (Willock 1969b) It was at this timethat the irrigation canal from the St Mary Riverto the North Milk River was constructed inMontana resulting in increased turbidity levelsThis diversion of water into the North Milk Riverhas also resulted in much greater water volumesduring the summer that likely allowed thewestern silvery minnow greater upstream accessinto the Alberta portion of the Milk RiverHowever the combination of water removal forirrigation from the Milk River temporary orpremature canal closures and drought conditionssuch as those experienced in 2000-2001 hasresulted in extremely low water conditions fromsummer to late winter It is this combination offactors that likely limits the abundance anddistribution of western silvery minnow inAlberta

The western silvery minnow is currentlyconsidered ldquoMay Be At Riskrdquo according to TheGeneral Status of Alberta Wild Species 2000(Alberta Sustainable Resource Development2001) Nationally the Committee on the Statusof Endangered Wildlife in Canada (COSEWIC)listed western silvery minnow as ldquoThreatenedrdquoin 2001 Although this species is considerablymore abundant in the Milk River south of theinternational border in Montana other stateshave documented a significant decline or lossof populations The intent of this status reportis to provide a summary of relevant and currentinformation regarding the status of westernsilvery minnow in Alberta

HABITAT

1 Features - In general the western silveryminnow is found in backwaters and pools oflarge silty plains streams (Pflieger 1980) InOhio the western silvery minnow appeared tobe most abundant in areas with little or nocurrent where the water was rich inphytoplankton (small aquatic plant organisms)and the gravelly sandy muddy or debris-covered bottom was not covered in silt(Trautman 1957) Spawning was found to occuronly where the rate of bottom siltation was low(Trautman 1957) One early study of a closelyrelated species eastern silvery minnow (Hregius) found that spawners moved to heavilyvegetated backwaters in slower-moving reachesof streams (Raney 1939) Rearing of botheastern and western species occurs near quietinshore areas and tributary mouths where smallschools can be found (Raney 1939 RLampL1987)

The presence and abundance of western silveryminnow in the United States appears to bestrongly associated with a number of habitatfeatures including bottom type gradient andturbidity The western silvery minnow of the

2

lower Ohio-upper Mississippi Basin occurs inthe Mississippi River proper only below themouth of the Missouri River (Burr and Page1986) This section is a transitional area withincreased turbidity increased velocity shiftingsands and silty substrates providing suitablehabitat for H argyritis (Burr and Page 1986)These characteristics are also common in theMissouri River where H argyritis is commonto dominant throughout the system (Cross et al1986) In particular the lower Missouri Riverhas extreme fluctuations in water flowthroughout the year high silt loads and unstablestreambeds devoid of vegetation (Cross et al1986) Similar habitats characterize the lowerMilk River in Alberta

A number of fish species inventories have beenconducted on the Milk River in Alberta sincethe 1960s (Willock 1969b Clayton and Ash1980 RLampL 1987 2001 2002a b) Thesestudies all found western silvery minnow limitedto the lowest section of the Milk River mainstemwhere the river has been described as low-gradient and even-flowing with many backwaterareas and shallow flat and run habitats (seeGlossary Appendix 1) This section of the MilkRiver is distinct from upstream sections wherethe habitat features include more runs riffles andrapids (RLampL 2001) The middle and lowerMilk River in Alberta flows through easilyeroded shale formations resulting in a soft-bottomed riverbed and muddy highly turbidwaters in contrast to the more erosion-resistantsandstone formations upstream (Willock 1969b)In addition the lower section receives lessprecipitation and waters are considerablywarmer (Willock 1969b) Based on theminnowrsquos limited distribution in the lowersection of the Milk River Willock (1969b)concluded that this species was restricted toregions with warm silty water Given the lackof other refugia in the lower Milk River highturbidity provides the main source of cover forthe minnow The western silvery minnowappears to be restricted to mainstem waters inthe Milk River since no individuals were

captured in small tributaries in recent studies(RLampL 2001 2002b) these results support thoseof an earlier investigation by Willock (1969a)Absence in the tributaries studied may be due tothe intermittent nature of the streams surveyedparticularly considering the extreme droughtconditions such as those observed during theyears 2000-2001

A microhabitat analysis of the data collected in2000 and 2001 found that several habitat featuresfor western silvery minnow were similar amongthe collection sites (RLampL 2002b) Thesefeatures included relatively low water velocities(00-003 ms) low silt depths (00-010 m) anda high percentage of sand as substrate (95-100) Similar results were observed forwestern silvery minnow in the Milk River fromthe International Boundary Crossing to theFresno Reservoir in Montana although the meanvelocity was higher (15 ms) (Stash 2001)

The lower Milk River in Alberta appears tocontain abundant rearing and feeding habitat forthe western silver minnow (RLampL 2001) wherewith the exception of fall 2001 quiet waters withlow to moderate velocities are usually prevalent(RLampL 2002a) Similarly overwintering habitathas also been documented in the lower MilkRiver (Clayton and Ash 1980) althoughavailability is highly dependent on winter flowsOverwintering habitat is likely one of the majorlimiting factors for the silvery minnow in theMilk River With regards to spawning habitatrequirements areas rich in aquatic vegetationhave been listed as a key feature (Raney 1939Houston 1998a) However no aquaticvegetation is present in the lower Milk RiverInstead high waters during the spring result inflooded backwater areas where terrestrialvegetation is often present particularly near thecreek mouths and spawning minnows may usethese areas (T Clayton pers comm)

2 Trends - The greatest changes to westernsilvery minnow habitat in Alberta have beenassociated with irrigation In 1917 the St Mary

3

Canal was constructed in Montana to divertwater from the St Mary River to the North MilkRiver for irrigation purposes In most years thecanal diverts water from April to Septemberincreasing the water volume in the North MilkRiver and the Milk River proper Before theconstruction of the dam the Milk River wasprobably a typical small prairie stream possiblyintermittent in times of drought and generallyless turbid (Willock 1969b) The even-flowingwaters now observed in the lower Milk River inAlberta were probably mainly restricted todownstream of the international border beforethe dam was constructed (Willock 1969b) Thesignificant increase in water volume since thecanal went into use is believed to haveextensively altered the ecological regime of theMilk River (with the exception of the South MilkRiver fork) by shifting habitat types westwardinto the Alberta portion (Willock 1969b TClayton pers comm) The result has been thecreation of a more turbid higher-flow systemwith more potential western silvery minnowhabitat available in the lower section of the MilkRiver in Alberta However Willock (1969b)also states that historically western silveryminnow may actually have used the uppersections of the Milk River before theconstruction of the canal The increased flowsassociated with the canal resulted in greater bankerosion and higher quantities of silt possiblyleading to a rapid decline in the minnowrsquospopulation size in the upper sections

Since the construction of the St Mary Canal nomajor losses or changes in habitat have occurredRather the availability of habitat is highlyvariable from year to year and mainly dependenton adequate water flows particularly in the latesummer and fall and for overwintering Duringperiods of very low flows the western silveryminnow may experience temporary reductionsin available habitat and under extremeconditions such as those of fall and winter 20012002 temporary habitat fragmentation Theextent of the drought during this period was suchthat the lower section of the Milk River in

Alberta where most silvery minnows have beendocumented was reduced to a series of isolatedpools many of which were not deep enough tosupport overwintering fish (RLampL 2002a) Awinter survey of a subset of these pools did notfind any minnows present (RLampL 2002a)Furthermore south of the international borderthe Milk River was completely dry to the FresnoReservoir from September 2001 to February2002 and the reservoir was only at 4 of itscapacity (K Gilge pers comm)

A small number of western silvery minnows wassubsequently collected (July 2002) upstream ofthe section that was dry in fall 2001 (T Claytonpers comm) It may also be present in theFresno Reservoir but has not been confirmed bysurveys (K Gilge pers comm) Thereforelimited re-colonization potential from upstreamand downstream sections in the system existsbut the re-establishment of significant numbersin the lower Milk River may require severalyears Downstream of the Fresno Reservoir andassociated dam in Montana six more impassibledams upstream of the confluence (see GlossaryAppendix 1) with the Missouri River preventany broader dispersal of western silvery minnow(Stash 2001 K Gilge pers comm)

In summary while rearing and feeding habitatfor the western silvery minnow in Albertaappears to be abundant in most years theavailability of overwintering habitat may bequite limited in some years depending on waterflow conditions In particular the combinationof extreme drought conditions canal operationand water removal could severely reduce or eveneliminate winter refugia for the western silveryminnow in the lower Milk River

CONSERVATION BIOLOGY

1 Species Identification - The western silveryminnow is a small fish belonging to the cyprinid

See glossary in Appendix 1 for definitions of thefollowing terms used in this subsection total lengthfork length caudal peduncle and subterminal mouth

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 7: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

vii

LIST OF FIGURES

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b)Specific locations correspond to collection sites summarized in Appendix 3 6

Figure 2 The distribution of western silvery minnow in North America 8

LIST OF TABLES

Table 1 Comparison of western silvery minnow sample sizes and percent species composition oftotal catch from the lower Milk River mainstem and creek mouths over time 10

TABLE OF CONTENTS cont

APPENDIX 1 Glossary of terms 17

APPENDIX 2 Definitions of selected legal and protective designations 18

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta20

ADDENDUM Summary of data collected in fall 2002 22

1

See Appendix 1 for definitions of selected statusdesignations

INTRODUCTION

The western silvery minnow (Hybognathusargyritis Girard Girard 1857) is a small fish ofthe cyprinid (carp) family native to large plainsstreams of the Missouri and Mississippi riversystems in midwest North America In Canadathis speciesrsquo presence has been confirmed in onlyone river system the Milk River (Willock 1969aScott and Crossman 1973 Nelson and Paetz1992) which runs east through the grasslandsof southern Alberta before joining the MissouriRiver in Montana The Milk River is a uniqueriver in Alberta in that it is the only system inthe province that contributes to the Missouridrainage This attribute of the Milk Riverexplains the very limited range of some fishspecies in Alberta including western silveryminnow which is believed to originate from theMississippiMissouri glacial refugium (seeGlossary Appendix 1) In addition to theextremely limited distribution of the westernsilvery minnow in Alberta its abundance withinthe Milk River has remained extremely low sincefirst documented in 1961 (see Appendix 3)

There has been some suggestion that the westernsilvery minnow was considerably more commonbefore 1917 (Willock 1969b) It was at this timethat the irrigation canal from the St Mary Riverto the North Milk River was constructed inMontana resulting in increased turbidity levelsThis diversion of water into the North Milk Riverhas also resulted in much greater water volumesduring the summer that likely allowed thewestern silvery minnow greater upstream accessinto the Alberta portion of the Milk RiverHowever the combination of water removal forirrigation from the Milk River temporary orpremature canal closures and drought conditionssuch as those experienced in 2000-2001 hasresulted in extremely low water conditions fromsummer to late winter It is this combination offactors that likely limits the abundance anddistribution of western silvery minnow inAlberta

The western silvery minnow is currentlyconsidered ldquoMay Be At Riskrdquo according to TheGeneral Status of Alberta Wild Species 2000(Alberta Sustainable Resource Development2001) Nationally the Committee on the Statusof Endangered Wildlife in Canada (COSEWIC)listed western silvery minnow as ldquoThreatenedrdquoin 2001 Although this species is considerablymore abundant in the Milk River south of theinternational border in Montana other stateshave documented a significant decline or lossof populations The intent of this status reportis to provide a summary of relevant and currentinformation regarding the status of westernsilvery minnow in Alberta

HABITAT

1 Features - In general the western silveryminnow is found in backwaters and pools oflarge silty plains streams (Pflieger 1980) InOhio the western silvery minnow appeared tobe most abundant in areas with little or nocurrent where the water was rich inphytoplankton (small aquatic plant organisms)and the gravelly sandy muddy or debris-covered bottom was not covered in silt(Trautman 1957) Spawning was found to occuronly where the rate of bottom siltation was low(Trautman 1957) One early study of a closelyrelated species eastern silvery minnow (Hregius) found that spawners moved to heavilyvegetated backwaters in slower-moving reachesof streams (Raney 1939) Rearing of botheastern and western species occurs near quietinshore areas and tributary mouths where smallschools can be found (Raney 1939 RLampL1987)

The presence and abundance of western silveryminnow in the United States appears to bestrongly associated with a number of habitatfeatures including bottom type gradient andturbidity The western silvery minnow of the

2

lower Ohio-upper Mississippi Basin occurs inthe Mississippi River proper only below themouth of the Missouri River (Burr and Page1986) This section is a transitional area withincreased turbidity increased velocity shiftingsands and silty substrates providing suitablehabitat for H argyritis (Burr and Page 1986)These characteristics are also common in theMissouri River where H argyritis is commonto dominant throughout the system (Cross et al1986) In particular the lower Missouri Riverhas extreme fluctuations in water flowthroughout the year high silt loads and unstablestreambeds devoid of vegetation (Cross et al1986) Similar habitats characterize the lowerMilk River in Alberta

A number of fish species inventories have beenconducted on the Milk River in Alberta sincethe 1960s (Willock 1969b Clayton and Ash1980 RLampL 1987 2001 2002a b) Thesestudies all found western silvery minnow limitedto the lowest section of the Milk River mainstemwhere the river has been described as low-gradient and even-flowing with many backwaterareas and shallow flat and run habitats (seeGlossary Appendix 1) This section of the MilkRiver is distinct from upstream sections wherethe habitat features include more runs riffles andrapids (RLampL 2001) The middle and lowerMilk River in Alberta flows through easilyeroded shale formations resulting in a soft-bottomed riverbed and muddy highly turbidwaters in contrast to the more erosion-resistantsandstone formations upstream (Willock 1969b)In addition the lower section receives lessprecipitation and waters are considerablywarmer (Willock 1969b) Based on theminnowrsquos limited distribution in the lowersection of the Milk River Willock (1969b)concluded that this species was restricted toregions with warm silty water Given the lackof other refugia in the lower Milk River highturbidity provides the main source of cover forthe minnow The western silvery minnowappears to be restricted to mainstem waters inthe Milk River since no individuals were

captured in small tributaries in recent studies(RLampL 2001 2002b) these results support thoseof an earlier investigation by Willock (1969a)Absence in the tributaries studied may be due tothe intermittent nature of the streams surveyedparticularly considering the extreme droughtconditions such as those observed during theyears 2000-2001

A microhabitat analysis of the data collected in2000 and 2001 found that several habitat featuresfor western silvery minnow were similar amongthe collection sites (RLampL 2002b) Thesefeatures included relatively low water velocities(00-003 ms) low silt depths (00-010 m) anda high percentage of sand as substrate (95-100) Similar results were observed forwestern silvery minnow in the Milk River fromthe International Boundary Crossing to theFresno Reservoir in Montana although the meanvelocity was higher (15 ms) (Stash 2001)

The lower Milk River in Alberta appears tocontain abundant rearing and feeding habitat forthe western silver minnow (RLampL 2001) wherewith the exception of fall 2001 quiet waters withlow to moderate velocities are usually prevalent(RLampL 2002a) Similarly overwintering habitathas also been documented in the lower MilkRiver (Clayton and Ash 1980) althoughavailability is highly dependent on winter flowsOverwintering habitat is likely one of the majorlimiting factors for the silvery minnow in theMilk River With regards to spawning habitatrequirements areas rich in aquatic vegetationhave been listed as a key feature (Raney 1939Houston 1998a) However no aquaticvegetation is present in the lower Milk RiverInstead high waters during the spring result inflooded backwater areas where terrestrialvegetation is often present particularly near thecreek mouths and spawning minnows may usethese areas (T Clayton pers comm)

2 Trends - The greatest changes to westernsilvery minnow habitat in Alberta have beenassociated with irrigation In 1917 the St Mary

3

Canal was constructed in Montana to divertwater from the St Mary River to the North MilkRiver for irrigation purposes In most years thecanal diverts water from April to Septemberincreasing the water volume in the North MilkRiver and the Milk River proper Before theconstruction of the dam the Milk River wasprobably a typical small prairie stream possiblyintermittent in times of drought and generallyless turbid (Willock 1969b) The even-flowingwaters now observed in the lower Milk River inAlberta were probably mainly restricted todownstream of the international border beforethe dam was constructed (Willock 1969b) Thesignificant increase in water volume since thecanal went into use is believed to haveextensively altered the ecological regime of theMilk River (with the exception of the South MilkRiver fork) by shifting habitat types westwardinto the Alberta portion (Willock 1969b TClayton pers comm) The result has been thecreation of a more turbid higher-flow systemwith more potential western silvery minnowhabitat available in the lower section of the MilkRiver in Alberta However Willock (1969b)also states that historically western silveryminnow may actually have used the uppersections of the Milk River before theconstruction of the canal The increased flowsassociated with the canal resulted in greater bankerosion and higher quantities of silt possiblyleading to a rapid decline in the minnowrsquospopulation size in the upper sections

Since the construction of the St Mary Canal nomajor losses or changes in habitat have occurredRather the availability of habitat is highlyvariable from year to year and mainly dependenton adequate water flows particularly in the latesummer and fall and for overwintering Duringperiods of very low flows the western silveryminnow may experience temporary reductionsin available habitat and under extremeconditions such as those of fall and winter 20012002 temporary habitat fragmentation Theextent of the drought during this period was suchthat the lower section of the Milk River in

Alberta where most silvery minnows have beendocumented was reduced to a series of isolatedpools many of which were not deep enough tosupport overwintering fish (RLampL 2002a) Awinter survey of a subset of these pools did notfind any minnows present (RLampL 2002a)Furthermore south of the international borderthe Milk River was completely dry to the FresnoReservoir from September 2001 to February2002 and the reservoir was only at 4 of itscapacity (K Gilge pers comm)

A small number of western silvery minnows wassubsequently collected (July 2002) upstream ofthe section that was dry in fall 2001 (T Claytonpers comm) It may also be present in theFresno Reservoir but has not been confirmed bysurveys (K Gilge pers comm) Thereforelimited re-colonization potential from upstreamand downstream sections in the system existsbut the re-establishment of significant numbersin the lower Milk River may require severalyears Downstream of the Fresno Reservoir andassociated dam in Montana six more impassibledams upstream of the confluence (see GlossaryAppendix 1) with the Missouri River preventany broader dispersal of western silvery minnow(Stash 2001 K Gilge pers comm)

In summary while rearing and feeding habitatfor the western silvery minnow in Albertaappears to be abundant in most years theavailability of overwintering habitat may bequite limited in some years depending on waterflow conditions In particular the combinationof extreme drought conditions canal operationand water removal could severely reduce or eveneliminate winter refugia for the western silveryminnow in the lower Milk River

CONSERVATION BIOLOGY

1 Species Identification - The western silveryminnow is a small fish belonging to the cyprinid

See glossary in Appendix 1 for definitions of thefollowing terms used in this subsection total lengthfork length caudal peduncle and subterminal mouth

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 8: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

1

See Appendix 1 for definitions of selected statusdesignations

INTRODUCTION

The western silvery minnow (Hybognathusargyritis Girard Girard 1857) is a small fish ofthe cyprinid (carp) family native to large plainsstreams of the Missouri and Mississippi riversystems in midwest North America In Canadathis speciesrsquo presence has been confirmed in onlyone river system the Milk River (Willock 1969aScott and Crossman 1973 Nelson and Paetz1992) which runs east through the grasslandsof southern Alberta before joining the MissouriRiver in Montana The Milk River is a uniqueriver in Alberta in that it is the only system inthe province that contributes to the Missouridrainage This attribute of the Milk Riverexplains the very limited range of some fishspecies in Alberta including western silveryminnow which is believed to originate from theMississippiMissouri glacial refugium (seeGlossary Appendix 1) In addition to theextremely limited distribution of the westernsilvery minnow in Alberta its abundance withinthe Milk River has remained extremely low sincefirst documented in 1961 (see Appendix 3)

There has been some suggestion that the westernsilvery minnow was considerably more commonbefore 1917 (Willock 1969b) It was at this timethat the irrigation canal from the St Mary Riverto the North Milk River was constructed inMontana resulting in increased turbidity levelsThis diversion of water into the North Milk Riverhas also resulted in much greater water volumesduring the summer that likely allowed thewestern silvery minnow greater upstream accessinto the Alberta portion of the Milk RiverHowever the combination of water removal forirrigation from the Milk River temporary orpremature canal closures and drought conditionssuch as those experienced in 2000-2001 hasresulted in extremely low water conditions fromsummer to late winter It is this combination offactors that likely limits the abundance anddistribution of western silvery minnow inAlberta

The western silvery minnow is currentlyconsidered ldquoMay Be At Riskrdquo according to TheGeneral Status of Alberta Wild Species 2000(Alberta Sustainable Resource Development2001) Nationally the Committee on the Statusof Endangered Wildlife in Canada (COSEWIC)listed western silvery minnow as ldquoThreatenedrdquoin 2001 Although this species is considerablymore abundant in the Milk River south of theinternational border in Montana other stateshave documented a significant decline or lossof populations The intent of this status reportis to provide a summary of relevant and currentinformation regarding the status of westernsilvery minnow in Alberta

HABITAT

1 Features - In general the western silveryminnow is found in backwaters and pools oflarge silty plains streams (Pflieger 1980) InOhio the western silvery minnow appeared tobe most abundant in areas with little or nocurrent where the water was rich inphytoplankton (small aquatic plant organisms)and the gravelly sandy muddy or debris-covered bottom was not covered in silt(Trautman 1957) Spawning was found to occuronly where the rate of bottom siltation was low(Trautman 1957) One early study of a closelyrelated species eastern silvery minnow (Hregius) found that spawners moved to heavilyvegetated backwaters in slower-moving reachesof streams (Raney 1939) Rearing of botheastern and western species occurs near quietinshore areas and tributary mouths where smallschools can be found (Raney 1939 RLampL1987)

The presence and abundance of western silveryminnow in the United States appears to bestrongly associated with a number of habitatfeatures including bottom type gradient andturbidity The western silvery minnow of the

2

lower Ohio-upper Mississippi Basin occurs inthe Mississippi River proper only below themouth of the Missouri River (Burr and Page1986) This section is a transitional area withincreased turbidity increased velocity shiftingsands and silty substrates providing suitablehabitat for H argyritis (Burr and Page 1986)These characteristics are also common in theMissouri River where H argyritis is commonto dominant throughout the system (Cross et al1986) In particular the lower Missouri Riverhas extreme fluctuations in water flowthroughout the year high silt loads and unstablestreambeds devoid of vegetation (Cross et al1986) Similar habitats characterize the lowerMilk River in Alberta

A number of fish species inventories have beenconducted on the Milk River in Alberta sincethe 1960s (Willock 1969b Clayton and Ash1980 RLampL 1987 2001 2002a b) Thesestudies all found western silvery minnow limitedto the lowest section of the Milk River mainstemwhere the river has been described as low-gradient and even-flowing with many backwaterareas and shallow flat and run habitats (seeGlossary Appendix 1) This section of the MilkRiver is distinct from upstream sections wherethe habitat features include more runs riffles andrapids (RLampL 2001) The middle and lowerMilk River in Alberta flows through easilyeroded shale formations resulting in a soft-bottomed riverbed and muddy highly turbidwaters in contrast to the more erosion-resistantsandstone formations upstream (Willock 1969b)In addition the lower section receives lessprecipitation and waters are considerablywarmer (Willock 1969b) Based on theminnowrsquos limited distribution in the lowersection of the Milk River Willock (1969b)concluded that this species was restricted toregions with warm silty water Given the lackof other refugia in the lower Milk River highturbidity provides the main source of cover forthe minnow The western silvery minnowappears to be restricted to mainstem waters inthe Milk River since no individuals were

captured in small tributaries in recent studies(RLampL 2001 2002b) these results support thoseof an earlier investigation by Willock (1969a)Absence in the tributaries studied may be due tothe intermittent nature of the streams surveyedparticularly considering the extreme droughtconditions such as those observed during theyears 2000-2001

A microhabitat analysis of the data collected in2000 and 2001 found that several habitat featuresfor western silvery minnow were similar amongthe collection sites (RLampL 2002b) Thesefeatures included relatively low water velocities(00-003 ms) low silt depths (00-010 m) anda high percentage of sand as substrate (95-100) Similar results were observed forwestern silvery minnow in the Milk River fromthe International Boundary Crossing to theFresno Reservoir in Montana although the meanvelocity was higher (15 ms) (Stash 2001)

The lower Milk River in Alberta appears tocontain abundant rearing and feeding habitat forthe western silver minnow (RLampL 2001) wherewith the exception of fall 2001 quiet waters withlow to moderate velocities are usually prevalent(RLampL 2002a) Similarly overwintering habitathas also been documented in the lower MilkRiver (Clayton and Ash 1980) althoughavailability is highly dependent on winter flowsOverwintering habitat is likely one of the majorlimiting factors for the silvery minnow in theMilk River With regards to spawning habitatrequirements areas rich in aquatic vegetationhave been listed as a key feature (Raney 1939Houston 1998a) However no aquaticvegetation is present in the lower Milk RiverInstead high waters during the spring result inflooded backwater areas where terrestrialvegetation is often present particularly near thecreek mouths and spawning minnows may usethese areas (T Clayton pers comm)

2 Trends - The greatest changes to westernsilvery minnow habitat in Alberta have beenassociated with irrigation In 1917 the St Mary

3

Canal was constructed in Montana to divertwater from the St Mary River to the North MilkRiver for irrigation purposes In most years thecanal diverts water from April to Septemberincreasing the water volume in the North MilkRiver and the Milk River proper Before theconstruction of the dam the Milk River wasprobably a typical small prairie stream possiblyintermittent in times of drought and generallyless turbid (Willock 1969b) The even-flowingwaters now observed in the lower Milk River inAlberta were probably mainly restricted todownstream of the international border beforethe dam was constructed (Willock 1969b) Thesignificant increase in water volume since thecanal went into use is believed to haveextensively altered the ecological regime of theMilk River (with the exception of the South MilkRiver fork) by shifting habitat types westwardinto the Alberta portion (Willock 1969b TClayton pers comm) The result has been thecreation of a more turbid higher-flow systemwith more potential western silvery minnowhabitat available in the lower section of the MilkRiver in Alberta However Willock (1969b)also states that historically western silveryminnow may actually have used the uppersections of the Milk River before theconstruction of the canal The increased flowsassociated with the canal resulted in greater bankerosion and higher quantities of silt possiblyleading to a rapid decline in the minnowrsquospopulation size in the upper sections

Since the construction of the St Mary Canal nomajor losses or changes in habitat have occurredRather the availability of habitat is highlyvariable from year to year and mainly dependenton adequate water flows particularly in the latesummer and fall and for overwintering Duringperiods of very low flows the western silveryminnow may experience temporary reductionsin available habitat and under extremeconditions such as those of fall and winter 20012002 temporary habitat fragmentation Theextent of the drought during this period was suchthat the lower section of the Milk River in

Alberta where most silvery minnows have beendocumented was reduced to a series of isolatedpools many of which were not deep enough tosupport overwintering fish (RLampL 2002a) Awinter survey of a subset of these pools did notfind any minnows present (RLampL 2002a)Furthermore south of the international borderthe Milk River was completely dry to the FresnoReservoir from September 2001 to February2002 and the reservoir was only at 4 of itscapacity (K Gilge pers comm)

A small number of western silvery minnows wassubsequently collected (July 2002) upstream ofthe section that was dry in fall 2001 (T Claytonpers comm) It may also be present in theFresno Reservoir but has not been confirmed bysurveys (K Gilge pers comm) Thereforelimited re-colonization potential from upstreamand downstream sections in the system existsbut the re-establishment of significant numbersin the lower Milk River may require severalyears Downstream of the Fresno Reservoir andassociated dam in Montana six more impassibledams upstream of the confluence (see GlossaryAppendix 1) with the Missouri River preventany broader dispersal of western silvery minnow(Stash 2001 K Gilge pers comm)

In summary while rearing and feeding habitatfor the western silvery minnow in Albertaappears to be abundant in most years theavailability of overwintering habitat may bequite limited in some years depending on waterflow conditions In particular the combinationof extreme drought conditions canal operationand water removal could severely reduce or eveneliminate winter refugia for the western silveryminnow in the lower Milk River

CONSERVATION BIOLOGY

1 Species Identification - The western silveryminnow is a small fish belonging to the cyprinid

See glossary in Appendix 1 for definitions of thefollowing terms used in this subsection total lengthfork length caudal peduncle and subterminal mouth

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 9: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

2

lower Ohio-upper Mississippi Basin occurs inthe Mississippi River proper only below themouth of the Missouri River (Burr and Page1986) This section is a transitional area withincreased turbidity increased velocity shiftingsands and silty substrates providing suitablehabitat for H argyritis (Burr and Page 1986)These characteristics are also common in theMissouri River where H argyritis is commonto dominant throughout the system (Cross et al1986) In particular the lower Missouri Riverhas extreme fluctuations in water flowthroughout the year high silt loads and unstablestreambeds devoid of vegetation (Cross et al1986) Similar habitats characterize the lowerMilk River in Alberta

A number of fish species inventories have beenconducted on the Milk River in Alberta sincethe 1960s (Willock 1969b Clayton and Ash1980 RLampL 1987 2001 2002a b) Thesestudies all found western silvery minnow limitedto the lowest section of the Milk River mainstemwhere the river has been described as low-gradient and even-flowing with many backwaterareas and shallow flat and run habitats (seeGlossary Appendix 1) This section of the MilkRiver is distinct from upstream sections wherethe habitat features include more runs riffles andrapids (RLampL 2001) The middle and lowerMilk River in Alberta flows through easilyeroded shale formations resulting in a soft-bottomed riverbed and muddy highly turbidwaters in contrast to the more erosion-resistantsandstone formations upstream (Willock 1969b)In addition the lower section receives lessprecipitation and waters are considerablywarmer (Willock 1969b) Based on theminnowrsquos limited distribution in the lowersection of the Milk River Willock (1969b)concluded that this species was restricted toregions with warm silty water Given the lackof other refugia in the lower Milk River highturbidity provides the main source of cover forthe minnow The western silvery minnowappears to be restricted to mainstem waters inthe Milk River since no individuals were

captured in small tributaries in recent studies(RLampL 2001 2002b) these results support thoseof an earlier investigation by Willock (1969a)Absence in the tributaries studied may be due tothe intermittent nature of the streams surveyedparticularly considering the extreme droughtconditions such as those observed during theyears 2000-2001

A microhabitat analysis of the data collected in2000 and 2001 found that several habitat featuresfor western silvery minnow were similar amongthe collection sites (RLampL 2002b) Thesefeatures included relatively low water velocities(00-003 ms) low silt depths (00-010 m) anda high percentage of sand as substrate (95-100) Similar results were observed forwestern silvery minnow in the Milk River fromthe International Boundary Crossing to theFresno Reservoir in Montana although the meanvelocity was higher (15 ms) (Stash 2001)

The lower Milk River in Alberta appears tocontain abundant rearing and feeding habitat forthe western silver minnow (RLampL 2001) wherewith the exception of fall 2001 quiet waters withlow to moderate velocities are usually prevalent(RLampL 2002a) Similarly overwintering habitathas also been documented in the lower MilkRiver (Clayton and Ash 1980) althoughavailability is highly dependent on winter flowsOverwintering habitat is likely one of the majorlimiting factors for the silvery minnow in theMilk River With regards to spawning habitatrequirements areas rich in aquatic vegetationhave been listed as a key feature (Raney 1939Houston 1998a) However no aquaticvegetation is present in the lower Milk RiverInstead high waters during the spring result inflooded backwater areas where terrestrialvegetation is often present particularly near thecreek mouths and spawning minnows may usethese areas (T Clayton pers comm)

2 Trends - The greatest changes to westernsilvery minnow habitat in Alberta have beenassociated with irrigation In 1917 the St Mary

3

Canal was constructed in Montana to divertwater from the St Mary River to the North MilkRiver for irrigation purposes In most years thecanal diverts water from April to Septemberincreasing the water volume in the North MilkRiver and the Milk River proper Before theconstruction of the dam the Milk River wasprobably a typical small prairie stream possiblyintermittent in times of drought and generallyless turbid (Willock 1969b) The even-flowingwaters now observed in the lower Milk River inAlberta were probably mainly restricted todownstream of the international border beforethe dam was constructed (Willock 1969b) Thesignificant increase in water volume since thecanal went into use is believed to haveextensively altered the ecological regime of theMilk River (with the exception of the South MilkRiver fork) by shifting habitat types westwardinto the Alberta portion (Willock 1969b TClayton pers comm) The result has been thecreation of a more turbid higher-flow systemwith more potential western silvery minnowhabitat available in the lower section of the MilkRiver in Alberta However Willock (1969b)also states that historically western silveryminnow may actually have used the uppersections of the Milk River before theconstruction of the canal The increased flowsassociated with the canal resulted in greater bankerosion and higher quantities of silt possiblyleading to a rapid decline in the minnowrsquospopulation size in the upper sections

Since the construction of the St Mary Canal nomajor losses or changes in habitat have occurredRather the availability of habitat is highlyvariable from year to year and mainly dependenton adequate water flows particularly in the latesummer and fall and for overwintering Duringperiods of very low flows the western silveryminnow may experience temporary reductionsin available habitat and under extremeconditions such as those of fall and winter 20012002 temporary habitat fragmentation Theextent of the drought during this period was suchthat the lower section of the Milk River in

Alberta where most silvery minnows have beendocumented was reduced to a series of isolatedpools many of which were not deep enough tosupport overwintering fish (RLampL 2002a) Awinter survey of a subset of these pools did notfind any minnows present (RLampL 2002a)Furthermore south of the international borderthe Milk River was completely dry to the FresnoReservoir from September 2001 to February2002 and the reservoir was only at 4 of itscapacity (K Gilge pers comm)

A small number of western silvery minnows wassubsequently collected (July 2002) upstream ofthe section that was dry in fall 2001 (T Claytonpers comm) It may also be present in theFresno Reservoir but has not been confirmed bysurveys (K Gilge pers comm) Thereforelimited re-colonization potential from upstreamand downstream sections in the system existsbut the re-establishment of significant numbersin the lower Milk River may require severalyears Downstream of the Fresno Reservoir andassociated dam in Montana six more impassibledams upstream of the confluence (see GlossaryAppendix 1) with the Missouri River preventany broader dispersal of western silvery minnow(Stash 2001 K Gilge pers comm)

In summary while rearing and feeding habitatfor the western silvery minnow in Albertaappears to be abundant in most years theavailability of overwintering habitat may bequite limited in some years depending on waterflow conditions In particular the combinationof extreme drought conditions canal operationand water removal could severely reduce or eveneliminate winter refugia for the western silveryminnow in the lower Milk River

CONSERVATION BIOLOGY

1 Species Identification - The western silveryminnow is a small fish belonging to the cyprinid

See glossary in Appendix 1 for definitions of thefollowing terms used in this subsection total lengthfork length caudal peduncle and subterminal mouth

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 10: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

3

Canal was constructed in Montana to divertwater from the St Mary River to the North MilkRiver for irrigation purposes In most years thecanal diverts water from April to Septemberincreasing the water volume in the North MilkRiver and the Milk River proper Before theconstruction of the dam the Milk River wasprobably a typical small prairie stream possiblyintermittent in times of drought and generallyless turbid (Willock 1969b) The even-flowingwaters now observed in the lower Milk River inAlberta were probably mainly restricted todownstream of the international border beforethe dam was constructed (Willock 1969b) Thesignificant increase in water volume since thecanal went into use is believed to haveextensively altered the ecological regime of theMilk River (with the exception of the South MilkRiver fork) by shifting habitat types westwardinto the Alberta portion (Willock 1969b TClayton pers comm) The result has been thecreation of a more turbid higher-flow systemwith more potential western silvery minnowhabitat available in the lower section of the MilkRiver in Alberta However Willock (1969b)also states that historically western silveryminnow may actually have used the uppersections of the Milk River before theconstruction of the canal The increased flowsassociated with the canal resulted in greater bankerosion and higher quantities of silt possiblyleading to a rapid decline in the minnowrsquospopulation size in the upper sections

Since the construction of the St Mary Canal nomajor losses or changes in habitat have occurredRather the availability of habitat is highlyvariable from year to year and mainly dependenton adequate water flows particularly in the latesummer and fall and for overwintering Duringperiods of very low flows the western silveryminnow may experience temporary reductionsin available habitat and under extremeconditions such as those of fall and winter 20012002 temporary habitat fragmentation Theextent of the drought during this period was suchthat the lower section of the Milk River in

Alberta where most silvery minnows have beendocumented was reduced to a series of isolatedpools many of which were not deep enough tosupport overwintering fish (RLampL 2002a) Awinter survey of a subset of these pools did notfind any minnows present (RLampL 2002a)Furthermore south of the international borderthe Milk River was completely dry to the FresnoReservoir from September 2001 to February2002 and the reservoir was only at 4 of itscapacity (K Gilge pers comm)

A small number of western silvery minnows wassubsequently collected (July 2002) upstream ofthe section that was dry in fall 2001 (T Claytonpers comm) It may also be present in theFresno Reservoir but has not been confirmed bysurveys (K Gilge pers comm) Thereforelimited re-colonization potential from upstreamand downstream sections in the system existsbut the re-establishment of significant numbersin the lower Milk River may require severalyears Downstream of the Fresno Reservoir andassociated dam in Montana six more impassibledams upstream of the confluence (see GlossaryAppendix 1) with the Missouri River preventany broader dispersal of western silvery minnow(Stash 2001 K Gilge pers comm)

In summary while rearing and feeding habitatfor the western silvery minnow in Albertaappears to be abundant in most years theavailability of overwintering habitat may bequite limited in some years depending on waterflow conditions In particular the combinationof extreme drought conditions canal operationand water removal could severely reduce or eveneliminate winter refugia for the western silveryminnow in the lower Milk River

CONSERVATION BIOLOGY

1 Species Identification - The western silveryminnow is a small fish belonging to the cyprinid

See glossary in Appendix 1 for definitions of thefollowing terms used in this subsection total lengthfork length caudal peduncle and subterminal mouth

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 11: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

4

(carp) family (Scott and Crossman 1973) Theadult western silvery minnow generally rangesfrom 75 mm to 125 mm in total length (Pflieger1980) Until very recently the maximum forklength recorded in Alberta was 100 mm (Nelsonand Paetz 1992) However studies conductedduring 2001 documented fork lengths up to 140mm (RLampL 2002b) The western silveryminnow is a slender fish with moderate lateralcompression and a broad caudal peduncle(Houston 1998a) The snout is blunt with asubterminal mouth and the eyes are relativelylarge (Scott and Crossman 1973) Specimensin Alberta tend to be brownish-yellow on theback with silver sides and no obvious lateralband but dusky spots may occur (Nelson andPaetz 1992) Males in spawning colour are lightyellow along the sides and lower fins (Scott andCrossman 1973)

The genus Hybognathus contains seven speciesin North America three of which are found inCanada (Schmidt 1994) Originally both thewestern silvery minnow and eastern silveryminnow (H regius) were considered to besubspecies of the central silvery minnow (Hnuchalis) (Scott and Crossman 1973) Howeverother studies concluded that the three should beconsidered distinct species based onmorphological differences (Pflieger 1971Hlohowskyj et al 1989 Schmidt 1994) and thisdecision was accepted by the American FisheriesSociety (Robins et al 1991)

2 Life History - In general very little is knownabout the life history of the western silveryminnow (Nelson and Paetz 1992) Mostinformation comes from references for othersilvery minnow species The only informationavailable on spawning fecundity (egg-producing capacity) and early developmentrefers to an early study conducted by Raney(1939) in the Cayuga Lake drainage (New YorkState) on the eastern silvery minnow This studyfound that female eastern silvery minnows likelymatured at one year of age (50-55 mm long)whereas males were not thought to spawn until

their second year Spawning was documentedin the spring (late April to early May) whentemperatures reached 130o to 205oC (Raney1939) Spawning of western silvery minnow inAlberta is believed to occur in May but noevidence has confirmed this time (Scott andCrossman 1973) Prior to spawning adulteastern silvery minnows were observed movingto well-vegetated lagoons in the lower reachesof lake tributaries or slower-moving areas inlarger rivers These fish laid non-adhesivedemersal eggs (eggs that sink) on the muddybottom of quiet areas in water about 03 m deepthat supported abundant aquatic and shorelinevegetation (Raney 1939) The fecundity of Hregius was found to range from 2000 eggs in a60-mm female (standard length) to 6600 eggsin a 90-mm female and egg diameter wasapproximately 1 mm (Raney 1939) Newlyhatched larvae measured 6 mm in total lengthand began to form schools along the shorelineapproximately 2 weeks after hatching (Raney1939) No information was available regardinglongevity of the western silvery minnow

3 Diet - Although no information on diet isavailable for the western silvery minnow thecentral silvery minnow is a bottom-orientedfeeder found in large schools (Pflieger 1980)Both the central and the eastern silvery minnowspecies ingest bottom detritus and mud fromwhich they digest algae diatoms and otherorganic matter (Raney 1939 Eddy and Underhill1974 Pflieger 1980)

4 MovementDispersal - No informationregarding movement patterns or dispersal abilityis available for the western silvery minnowHowever Raney (1939) noted that adult easternsilvery minnows migrated to inshore waters oflakes and larger rivers in the spring to spawnbut it is not clear how far these fish migratedSimilarly no information is available regardingthe ability of the species to disperse and re-colonize new or empty habitats The fact thatthe western silvery minnow has likely undergonefairly regular drought conditions in the past and

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 12: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

5

still persists in the Milk River suggests that ithas the ability to disperse short distances intoempty habitats that may have temporarily beendevoid of water

DISTRIBUTION

1 Alberta - The western silvery minnowcolonized Alberta after the last glaciation (LateWisconsinan) when access became availableapproximately 13 000 years ago (Nelson andPaetz 1992) Based on present-day distributionpatterns it is believed that western populationsof H argyritis such as those found in the MilkRiver moved north from a Missouri refugiumrather than a Mississippian one (unlike othersilvery minnow species) (Crossman andMcAllister 1986)

The only confirmed occurrence of westernsilvery minnow in Canada is in southern Albertaspecifically in the Milk River system The MilkRiver is one of the northernmost tributaries ofthe Missouri River and the northernmost extentof western silvery minnowrsquos distribution It wasfirst collected in the Alberta section of the MilkRiver in 1961 (see Appendix 3) but the firstpublished occurrence here was documented byWillock (1968) Limited collections have sincebeen made between 1971 and 1979 in 1986 andduring more detailed surveys of the Milk Riverin 2000 and 2001 (See Appendix 3 for details ofcollections)

A number of studies have been conductedthroughout the Milk River mainstem the NorthMilk River and tributaries to the system (Willock1969b Clayton and Ash 1980 RLampL 19872002b) All of these studies concluded that thedistribution of the western silvery minnowappears to be restricted to the lower Milk Rivermainstem This section of the Milk River occursin the Dry Mixedgrass Natural Subregion ofAlberta (Alberta Natural Heritage InformationCentre 2002a) The minnowrsquos westernmostoccurrence was documented approximately 30km downstream of the town of Milk River

(Willock 1969b) (Figure 1) Recent surveysfound silvery minnows to be limited to moredownstream sites in the Pinhorn Ranch area ofthe Milk River mainstem in 2000-2001 and toDeer Creek bridge and Pinhorn Ranch area in1986 (Figure 1) Earlier studies noted theminnowrsquos presence extended to the United Statesborder (Willock 1969b) but the more recentsurveys (RLampL 2002) did not conductcollections this far downstream to confirm itspresence here There is no reason to believe thisdistribution has changed A large number ofminnows (n=368) were collected by Willock(1969b) from the mouth of the Lost River atributary to the lower Milk River in MontanaHowever most recently this tributary was drywhere sampled in Alberta (approximately 30 kmupstream of confluence with the Milk River)(RLampL 2001) and it is not known whether theminnow actually uses the tributary or just themouth No specimens have been collected fromany other tributaries in Alberta but given theintermittent nature of these small systems usewould be opportunistic at best

Henderson and Peter (1969) documented a singlespecimen of western silvery minnow from theSouth Saskatchewan River within the city limitsof Medicine Hat in 1963 However a series ofmore recent sampling efforts in 1974-1975 andduring 1994-1996 in this area as well asupstream and downstream of this section didnot detect any additional specimens (W Robertspers comm) This specimen is believed to be aspurious account and not representative of abreeding population (W Roberts pers comm)Its presence is thought to be the result of anaccidental release of bait fish (Henderson andPeter 1969) rather than misidentificationbecause its identification was confirmed byexperts in the field (W Roberts pers comm)However the possibility of an extremely smallpopulation existing here cannot be ruled out (MSteinhilber pers comm)

There is no information available on the numberof subpopulations that exist in the Milk River

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 13: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

6

Figure 1 The distribution of western silvery minnow in Alberta (modified from RLampL 2002b) Specificlocations correspond to collection sites summarized in Appendix 3 The collection from the SouthSaskatchewan River listed in Appendix 3 is not shown on this map because the coordinates were notavailable

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 14: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

7

Habitat fragmentation is at most only temporaryoccurring during extreme drought conditionsAlthough the distribution of western silveryminnows in the lower Milk River appears to bepatchy the patchiness may in part be associatedwith the difficulties of sampling a very limitedpopulation size rather than reflect the truedistribution of the species in the river Thepotential for gene flow throughout this entiresection in most years is high and probablyprevents the development of genetically distinctsubpopulations Conservatively it is likely thatAlberta contains only one population in the MilkRiver (although the status of the minnow in theSouth Saskatchewan River remains unclear)Given the lack of obvious barriers between thelowest section of the Milk River in Alberta andthe section immediately south of the UnitedStates border it is likely that the Albertapopulation of western silvery minnows is partof a larger genetic population found in MontanaCompared to the surveys conducted in theCanadian portion of the Milk River (seeAppendix 3) a significantly larger number ofminnows (n=64) were collected in the MilkRiver a few kilometres on either side of agauging station in Montana close to the border(station 06135000 lat 48o 49rsquo 03rdquo long 110o

28rsquo 10rdquo) (S Stash pers comm)

In summary the distribution of the westernsilvery minnow in Alberta appears to be limitedto the lower Milk River a section approximately200 km in length and variable in width rangingfrom 0 m in some sections at lowest flows toapproximately 20 m at high flows (T Claytonpers comm) Within that stretch the areaactually occupied by the species is difficult tocalculate given that no studies have conductedsurveys along the entire length of the river The200 km section of the lower Milk River thatcontains western silvery minnows represents arelatively small proportion of the total present-day range of this species in North America(Figure 2) Too few data are available to evaluateannual fluctuation in the extent of occurrencewithin Alberta but some fluctuation appears to

be associated with the variability in water levelsHowever there are likely no major changes inextent of occurrence since the western silveryminnow was first documented within the MilkRiver

2 Other Areas - Beyond Alberta the westernsilvery minnow is distributed in large lowlandplains streams of the Mississippi River systemextending from the mouth of the Ohio Rivernorth to the Missouri River basin and the MilkRiver in Montana (Pflieger 1980) (Figure 2) Itis found in the Mississippi River mainstem onlybelow the mouth of the Missouri River (Burrand Page 1986) and throughout the MissouriRiver (Cross et al 1986) Within these systemsdistribution appears to be fairly continuous(Pflieger 1980) although the creation ofreservoirs and dams has fragmented somesections of rivers South of the internationalborder the nearest known population of thewestern silvery minnow occurs in the Milk Riverbetween the border and Fresno Reservoir inMontana (located approximately 80 kmdownstream of the border) (Stash 2001)Western silvery minnow populations in the MilkRiver south of the United States border arefragmented by a series of seven impassableirrigation diversions and dams (from FresnoReservoir downstream to the Vandalia diversiondam in Montana) before the confluence with theMissouri River (Kent Gilge pers comm)

With regards to changes in distribution Willock(1968) indicated that the loss of the westernsilvery minnow had occurred throughoutextensive areas in the United States but nospecific locations were provided Trautman(1957) believed that increased turbidity wasresponsible for the extirpation of eastern silveryminnow in Ohio These older studies suggestthat changes in extent of distribution likelyoccurred much earlier in the century but nospecific records for western silvery minnow wereavailable

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 15: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

8

Figure 2 The distribution of western silvery minnow in North America From Pflieger (1980) USFish and Wildlife Service (1995) Houston (1998b) and United States Geological Survey (2001)

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 16: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

9

POPULATION SIZE AND TRENDS

1 Alberta - There is virtually no informationavailable to establish population size or trends(Houston 1998a) Willock (1968) hypothesizedthat the abundance of western silvery minnowin the upper reaches of the Milk River may havedeclined in the early 1900s as a result ofincreased turbidity associated with thechanneling of irrigation water into the systemUnfortunately this decline is only speculativeas no data are available from before the 1960sand it is impossible to estimate to what degreethese altered conditions might have affected thesize of the population Although too few datahave been collected in the past to accuratelyestimate the population size it is clear that sincefirst identified in the early 1960rsquos the westernsilvery minnow remains a very rare species inthe Milk River The western silvery minnowpopulation in Alberta likely does not exceed afew thousand individuals in a year of averageflow however their numbers may besignificantly lower depending on intensity andfrequency of drought conditions and timeelapsed since the most recent drought Samplingefforts from the 1960rsquos (Willock 1969b) 1980rsquos(RLampL 1987 Clayton and Ash 1980) and 2000-2002 (RLampL 2001 2002a b) consistently foundthis species to make up a very small portion ofthe fish species composition (=05) (Table 1)

The most recent surveys permit the comparisonof catch-per-unit-effort (CPUE see GlossaryAppendix 1) data for a single location on thelower Milk River based on beach seine catchesIn fall 1986 CPUE was 057 fish100 m2 (RLampL1987) whereas in fall 2000 CPUE was 122fish100 m2 and in fall 2001 CPUE was 48 fish100 m2 (RLampL 2002b) The higher value in2001 likely reflects improved capture efficiencyassociated with the isolated pools rather than anincrease in abundance (RLampL 2002b) Giventhe recent drought event in the Milk Riversystem the present abundance of western silveryminnow is unknown but likely reduced Because

the majority of the lower Milk River section usedby the minnow was reduced to isolated pools in2001 the population may have decreasedsubstantially Surveys on the lower Milk Riverin fall 2002 will be used to address this issue (TClayton pers comm)

2 Other Areas - The nearest population ofwestern silvery minnow to that in Alberta occursin the Milk River between the United Statesborder and the Fresno Reservoir in MontanaHere the minnow comprises a significantlylarger proportion of the fish community than inAlberta making up 586 of the total fishspecies composition second only to the flatheadchub (Stash 2001) However it is unclear howthe extreme drought conditions and lack of waterin this section during fall and winter of 2001-2002 may have affected the population size (KGilge pers comm) From a broaderperspective the western silvery minnow iscommon throughout the Missouri River whereit is a dominant species in the lower reaches(Cross et al 1986) In general Pflieger (1980)stated that where they still occur in the UnitedStates the western silvery minnow is consideredcommon Unfortunately no specificinformation was available to establish populationsizes or trends for any of these areas (Houston1998a)

LIMITING FACTORS

1 Alberta - Potential rearing feeding and evenoverwintering habitats in the lower section ofthe Milk River appear to be widely available inmost years (RLampL 2002b) Therefore otherfactors are believed to be influencing thedistribution and abundance of the western silveryminnow in Alberta (RLampL 2002b) The MilkRiver in Alberta is situated in a geographicregion that is subject to extreme yearly andseasonal climatic fluctuations This variabilityin addition to anthropogenic influences on theriver system may be responsible for limiting thedistribution and abundance of this species

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 17: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

10

The Milk River is highly susceptible to heavysilt load associated with continuous erosion ofthe surrounding grasslands and river banks(Willock 1968) Willock (1968) stated that theincreased rate of erosion associated withchannelization for irrigation and overgrazingcould result in the decline or extirpation of thewestern silvery minnow from its Canadian rangeand may be the reason for its extirpation in areasin the United States Similarly Trautman (1957)believed that the western silvery minnow likeits eastern counterpart has a limited tolerancefor suspended sediment However given itsapparent preference for highly turbid waters itis unlikely that the high sediment load in theMilk River is the primary limiting factor forwestern silvery minnow distribution in AlbertaNonetheless the silt content andor channel typedoes appear to be correlated with differences inabundance in Alberta versus immediatelydownstream of the international borderUpstream of the border where minnowabundance is relatively low (=05 of totalcomposition) the lower Milk River is

characterized by a single meandering channeland channel banks with a siltclay content of 65(Simpson and Smith 2000) howeverimmediately downstream of the border wherethe minnow is common the river is morecharacteristic of the braided shifting sand-bottomed Missouri River Here the siltclaycontent is significantly lower at 18 (Simpsonand Smith 2000) and minnow abundance ismuch greater (gt5 of total composition)Possibly extreme levels of silt affectreproductive success (T Clayton pers comm)However it is not clear if there is a point at whichsilt load in the water becomes detrimental to thewestern silvery minnow In addition there isno information available to compare silt loadsover time for the Milk River (T Clayton perscomm)

The highly variable water volume is likely theprimary limiting factor affecting survival ofwestern silvery minnow in the Milk RiverSpecifically the combination of drought canaloperation and water removal in the southern part

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 18: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

11

of Alberta is probably the biggest potential factorthat could lead to the extirpation of westernsilvery minnow Southern Alberta is susceptibleto extreme drought conditions during thesummer Naturally low flows at this time maybe exacerbated by the seasonal operation of theSt Mary Canal and by water removal forirrigation mainly in the vicinity of the town ofMilk River (T Clayton pers comm) Forexample the mean monthly discharge duringAugust 2000 was approximately the same asaverage historic value since 1910 (RLampL2002b) However the mean discharge duringOctober and December 2000 was 11 and 20of historic values respectively (RLampL 2001)In 2001 the situation was even worse with meandischarge in August October and Decemberbeing approximately 50 7 and 6 of theaverage respectively (RLampL 2002b) Inparticular such low flows could severely limitthe availability of overwintering habitat (RLampL2001) greatly reducing overwintering survivalIn the late fall and winter of 20012002 the lowerMilk River where most western silveryminnows were previously observed dried upcompletely except for a series of isolated pools(RLampL 2002a) Ten of the 32 isolated pools inthis section were evaluated in March 2002 forhabitat quality and fish presence Althoughdissolved oxygen levels were not limiting waterdepth was very limiting and no western silveryminnows were observed (RLampL 2002b) Theseverity of the drought conditions observed in2001 is not uncommon for southern Alberta (TClayton pers comm see also historicaldischarge for the Milk River in Fig 39 of RLampL2002b) The western silvery minnow haspersisted under similar drought conditions in thepast although the frequency of such conditionsmay prevent the population from expandingbeyond the low abundance levels that have beenobserved What makes 2001 somewhat moresignificant is the unusually high temperaturesthat accompanied the drought during the summermonths all fish species including the minnowwere therefore at increased risk of prolongedexposure to high water temperatures in low water

levels (T Clayton pers comm)

Extended periods of isolation in pools duringthe fall and winter months when turbidity ismuch reduced increases the minnowrsquosvulnerability to predation by other fish speciesincluding the sauger (Stizostedion canadense)(T Clayton pers comm) Similarly extremelylow water levels during the summer monthscould result in dangerously low oxygen levelselevated water temperatures and reducedturbidity exposing the fish to aquatic andterrestrial predators These conditions may beexacerbated by repair work and maintenance ofthe St Mary Canal that result in temporary orpremature closure of the diversion (T Claytonpers comm) For example the canal was closedin mid-August rather than mid-September in2001 because of repair work (T Clayton perscomm) exacerbating the conditions associatedwith low water levels

2 Other Areas - Elsewhere in the Great Plainsmodifications to habitat particularly thoseassociated with irrigation have become a seriouslimiting factor for the western silvery minnow(Cross et al 1986) Impoundments haveprobably had the greatest cumulative effects onfish fauna of the western Mississippi Basinincluding H argyritis (Cross et al 1986) Theseimpoundments alter habitat type stimulateintroductions of exotic species (see GlossaryAppendix 1) and alter flow regimes sedimentloads and microbiota (small often microscopicorganisms) resulting in streams that aregenerally narrower less turbid less subject todischarge and temperature variations (Cross etal 1986) and less productive Although thesechanges to streams have resulted in increaseddiversity of some prairie fish species severalspecies have declined including the westernsilvery minnow even though they have adaptedto shallow sandy streams with widely fluctuatingflows high turbidity and extreme summertemperatures (Cross et al 1986) Such speciesthat were once abundant and widespread are nowout-competed by pelagic planktivores (see

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 19: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

12

Glossary Appendix 1) and sight-feedingcarnivores including introduced salmonids(Cross et al 1986)

Increased turbidity and the loss of aquaticvegetation and organic matter as a result ofsiltation may also be responsible for the loss ofwestern silvery minnow populations in extensiveareas in the United States (Willock 1968)Finally the greatest threats listed for the westernsilvery minnow in North Dakota are non-pointsource pollution water depletion from irrigationdegradation of riparian areas and mainstemimpoundments affecting natural flow regimes(United States Geological Survey 2002)

STATUS DESIGNATIONS

1 Alberta - The western silvery minnow iscurrently ranked as ldquoMay be At Riskrdquo accordingto The General Status of Alberta Wild Species2000 (Alberta Sustainable ResourceDevelopment 2001) The Alberta NaturalHeritage Information Centre (2002b) tracksprovincial and global rankings Provincially thewestern silvery minnow is ranked as ldquoS1rdquo (as ofApril 2000) which is the highest ldquoSrdquo rank

2 Other Areas - The western silvery minnowwas first designated by COSEWIC asldquoVulnerablerdquo (equivalent to the currentdesignation of ldquoThreatenedrdquo) in April 1997 Thenational ranking for the United States is N4 (asof August 28 1998) (NatureServe Explorer2001) In the United States western silveryminnow was formerly considered a candidatefor the federal rare and endangered species listbut as of February 28 1996 was removed fromthis list although it remains a ldquospecies ofmanagement concernrdquo The western silveryminnow is ranked ldquoS1rdquo in Iowa ldquoS2rdquo inWyoming Kansas Missouri and Illinois ldquoS4rdquoor ldquoS5rdquo in Montana Nebraska and South

Dakota and is unranked in North Dakota(NatureServe Explorer 2001) Globally theNature Conservancy gave this species a statusof ldquoG4rdquo (as of November 1998)

RECENT MANAGEMENT IN ALBERTA

No specific management for western silveryminnow has occurred in Alberta However theextremely limited distribution of this species inthe Milk River and its vulnerability to waterconditions prompted the Fish and WildlifeDivision of Alberta Sustainable ResourceDevelopment to commission recent and ongoingsurveys in the Milk River (2000 to present seeAddendum) The purpose of this work was tohelp determine the status of the western silveryminnow in Alberta and to providerecommendations with regards to protectionThese recommendations include themaintenance of monitoring studies on a regularbasis at specific index sites to track abundanceand more detailed studies on the distributionabundance and habitat preferences of the westernsilvery minnow (RLampL 2002b)

It should be noted that to date no minimumflows to address fisheries requirements havebeen established for the Milk River (T Claytonpers comm) Such guidelines would ensure thatadequate refugia are available for the westernsilvery minnow at most times The identificationand protection of critical habitat requirementsfor juvenile and adult western silvery minnowin the lower Milk River is crucial to thecontinued existence of this rare species inAlberta

SYNTHESIS

The western silvery minnow is a unique speciesin Alberta as it is one of the two emigrants (theother being stonecat Noturus flavus) from theMissouri glacial refugium to disperse no furthernorth than the Milk River The population ofwestern silvery minnow in the lower Milk Rivermainstem appears to be extremely small

See Appendix 2 for definitions of the statusdesignations referred to in this section

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 20: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

13

occurring only sporadically throughout the areafrom the international border to downstream ofthe town of Milk River Use of the tributaries isunknown but at best only temporary dependingon adequate water flows This population andtherefore the speciesrsquo presence in Alberta (andCanada) is extremely vulnerable to habitatperturbations in the Milk River systemassociated with the operation of the St MaryCanal and water withdrawal for irrigation aswell as the severe drought conditions that thisregion regularly experiences In particular thesurvival of western silvery minnow is likelylimited by low water flows affectingoverwintering habitat availability and the lackof refugia in the lower Milk River Thecombination of severe drought and waterremoval in southern Alberta is probably thebiggest potential threat to the western silveryminnow in Alberta

At present very little is understood about thebiology life history population size or dynamicsof the one confirmed western silvery minnowpopulation in Alberta Recent studies on theMilk River in 2000-2001 suggest that itsabundance has not changed since the species wasfirst documented in the 1960s although this

conclusion may change depending on the resultsof 2002 surveys All studies have concludedthat this species is extremely low in abundancewith an extremely limited range of distributionThe western silvery minnow in Alberta requiresprotection to ensure that some refugia areavailable particularly during the winter

The first step in the protection of western silveryminnow must be to confirm its status in the MilkRiver since the drought during 2001-2002 Thiswork is currently underway (see Addendum)Future studies should focus on better definingthe life history biology and habitat requirements(especially spawning habitat) of western silveryminnow Long-term monitoring studies shouldbe established using index sites to track trendsin population size In addition it is unclear howsiltation and turbidity affect the species in theMilk River although it has been suggested thatincreased levels associated within irrigationwater diversions may limit abundance anddistribution Finally it is essential that Montanaand Alberta work collaboratively to putbiologically meaningful minimum water flowsin place for the Milk River to ensure that refugiaare always available to the western silveryminnow

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 21: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

14

LITERATURE CITED

Alberta Natural Heritage Information Centre2002a Natural Regions and Subregionsof Alberta URL httpwwwcdgovabcapreservingparksanhic natura l_regions_mapasp (Updated October 2002)

Alberta Natural Heritage Information Centre2002b Fish Tracking List URL httpwwwcdgovabcapreservingparksanhicfish_trackingasp (UpdatedOctober 2002)

Alberta Natural Heritage Information Centre2002c Rank Definitions URL httpwwwcdgovabcapreservingparksanhicdefinitionsasp (Updated october2002)

Alberta Sustainable Resource Development2001 The General Status of AlbertaWild Species 2000 Alberta SustainableResource Development Fish andWildlife Service Edmonton Alberta 46pp

Burr BM and LM Page 1986 Zoogeographyof fishes of the lower Ohio-upperMississippi Basin In CH Hocutt andEO Wiley (Editors) The Zoogeographyof North American Freshwater FishesJohn Wiley amp Sons Toronto CanadaPages 287-324

Clayton TD and GR Ash 1980 A fisheriesoverview study of the Milk River BasinPrepared for Alberta EnvironmentPlanning Division by RLampLEnvironmental Services Ltd 93 pp

COSEWIC 2002 Committee on the Status ofEndangered Wildlife in Canada URLhttpwwwcosewicgcca (UpdatedJanuary 2002)

Cross FB RL Mayden and JD Stewart1986 Fishes in the western Mississippidrainage In CH Hocutt and EO Wiley(Editors) The Zoogeography of NorthAmerican Freshwater Fishes JohnWiley amp Sons Toronto Canada Pages363-412

Crossman EJ and DE McAllister 1986Zoogeography of freshwater fishes of theHudson Bay drainage Ungava Bay andthe Arctic Archipelago In CH Hocuttand EO Wiley (Editors) TheZoogeography of North AmericanFreshwater Fishes John Wiley amp SonsToronto Canada Pages 53-104

Eddy S and JC Underhill 1974 NorthernFishes University of Minnesota PressMinneapolis Minnesota

Girard CF 1857 Researches upon thecyprinoid fishes inhabiting the freshwaters of the United States west of theMississippi Valley from specimens inthe museum of the SmithsonianInstitution Proceedings of the Academyof National Science 8165-213

Henderson NE and RE Peter 1969Distribution of fishes of southernAlberta Journal of the FisheriesResearch Board of Canada 26325-338

Hlohowskyj CP MM Coburn and TMCavender 1989 Comparison of apharyngeal filtering apparatus in severalspecies of the herbivorous cyprinidgenus Hybognathus (PiscesCyprinidae)Copeia 1989172-183

Houston J 1998a Status of the Western SilveryMinnow Hybognathus argyritis inCanada Canadian Field-Naturalist112174-153

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 22: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

15

Houston J 1998b Addendum for westernsilvery minnow COSEWIC report

National Research Council 1995 Science andthe Endangered Species Act NationalAcademy Press Washington DC 271pp

NatureServe Explorer 2001 URL httpwwwna tu rese rve o rg exp lo re r (Updated November 2001)

Nelson JS and MJ Paetz 1992 The Fishes ofAlberta Second Edition The Universityof Alberta Press Edmonton AlbertaCanada 437 pp

Pflieger WL 1971 A distributional study ofMissouri fishes University of KansasMuseum of Natural History Publication20225-570

Pflieger WL 1980 Hybognathus argyritisGirard western silvery minnow In DSLee CR Gilbert CH Hocutt REJenkins DE McAllister and JRStauffer Jr (Editors) Atlas of NorthAmerican Freshwater Fishes NorthCarolina State Museum of NaturalHistory North Carolina BiologicalSurvey Publication 1980-12 Page 174

Raney EC 1939 The breeding habits of theEastern Silvery Minnow Hybognathusregius Girard American MidlandNaturalist 21215-218

RLampL Environmental Services Ltd 1987 Aninventory of aquatic habitats and fishresources in the Milk River AlbertaPrepared for Alberta EnvironmentPlanning Division 80 pp plusappendices

RLampL Environmental Services Ltd 2001 Fishspecies at Risk in the Milk and St MaryDrainages Prepared for Alberta

Sustainable Resource DevelopmentAlberta Species At Risk Interim Report53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fishspecies at risk in the Milk River Albertandash late winter 2002 survey Prepared forDepartment of Fisheries and OceansFreshwater Institute 13 pp

RLampL Environmental Services Ltd 2002b Fishspecies at risk in the Milk and St MaryDrainages Prepared for AlbertaSustainable Resource DevelopmentAlberta Species At Risk Report No 4582 pp plus appendices

Robins RC RM Bailey CE Bond JRBrooker EA Lachner RN Lea andWB Scott 1991 Common andscientific names of fishes from theUnited States and Canada Fifth EditionAmerican Fisheries Society SpecialPublication 20 Bethesda Maryland

Schmidt TR 1994 Phylogenetic relationshipsof the genus Hybognathus (TeleostiCyprinidae) Copeia 1994622-630

Scott WB and EJ Crossman 1973Freshwater fishes of Canada FisheriesResearch Board of Canada Bulletin 184966 pp

Simpson CJ and DG Smith 2000 Channelchange and low energy braiding on thesand-bed Milk River southern Alberta -northern Montana GeoCanada 2000Calgary Alberta May 29-June 2 2000

Stash SW 2001 Distribution relativeabundance and habitat associations ofMilk River fishes related to irrigationdiversion dams MSc Thesis MontanaState University Bozeman MT 67 pp

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 23: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

16

Trautman MB 1957 The Fishes of Ohio OhioState University Press Columbus Ohio683 pp

United States Geological Survey 2001 SouthDakota Gap Analysis Project ndash Fishesof South Dakota URL httpwfssdstateedusdgapfishfisheshtm(Updated April 2001)

United States Geological Survey 2002Northern Prairie Wildlife ResearchCenter URL httpwwwnpwrcusgsgov (UpdatedSeptember 2002)

US Fish and Wildlife Service 1995 NorthDakotarsquos federally listed endangeredthreatened and candidate species 1995US Fish and Wildlife ServiceBismarck ND Jamestown ND

Northern Prairie Wildlife ResearchCenter Home Page URL httpwwwnpwrcusgsgovresourcedistrothersnddangernddangerhtm (Version16JUl97)

Willock TA 1968 New Alberta records of thesilvery and brassy minnows stonecatand sauger with a preliminary list offishes of the Milk River in AlbertaCanadian Field-Naturalist 8218-23

Willock TA 1969a Distributional list of fishesin the Missouri drainage of CanadaJournal of Fisheries Research Board ofCanada 261439-1449

Willock TA 1969b The ecology andzoogeography of fishes in the Missouri(Milk River) drainage of Alberta MScThesis Carleton University OttawaOntario

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 24: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

17

Appendix 1 Glossary of terms

Catch-per-unit-effort (CPUE) ndash A standard fisheries term that quantifies fish abundance in terms ofeffort applied to catch fish using a particular sampling methodology

Caudal peduncle ndash The portion of the body between the end of the anal fin (between pelvic and tailfins) and the base of the tail fin (Nelson and Paetz 1992)

Confluence ndash Where the mouth of a tributary joins the mainstem

Exotic species ndash Species that are non-native or non-indigenous to an ecosystem and have usually beenreleased into these systems through human activities

Flat and run habitats - Flat habitat is a depositional area of channel characterized by low currentvelocities and no turbulence uniform in nature and often predominantly sandsilt substrate Run habitat isa section of channel characterized by moderate to high current velocities and relatively unbroken watersurface (from RLampL 2002b)

Fork length ndash The straight length distance from the tip of the snout laterally to the central part of themargin of the tail fin (Nelson and Paetz 1992)

Pelagic planktivores ndash Refers to species of fish that occur within the water column (not on the bottom)and usually rely on sight to capture plankton (small plant and invertebrate organisms)

Refugium (glacial) ndash Ice-free areas that provided habitat for species during glacial periods

Subterminal mouth ndash The upper jaw overhangs the lower jaw

Total length ndash The straight line distance from the tip of the snout to the extreme end of the tail fin(Nelson and Paetz 1992)

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 25: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

18

APPENDIX 2 Definitions of selected legal and protective designations

A The General Status of Alberta Wild Species 2000 (after Alberta Sustainable Resource Development 2001)

C Committee on the Status of Endangered Wildlife in Canada (after COSEWIC 2002)

2000 Rank 1996 Rank Definitions

At Risk Red Any species known to be ldquoAt Riskrdquo after formal detailed statusassessment and designation as ldquoEndangeredrdquo or ldquoThreatenedrdquo inAlberta

May Be At Risk Blue Any species that may be at risk of extinction or extirpation and istherefore a candidate for detailed risk assessment

Sensitive Yellow Any species that is not at risk of extinction or extirpation but mayrequire special attention or protection to prevent it from becomingat risk

Secure Green Any species that is not ldquoAt Riskrdquo ldquoMay Be At Riskrdquo orldquoSensitiverdquo

Undetermined StatusUndetermined

Any species for which insufficient information knowledge or datais available to reliably evaluate its general status

Not Assessed na Any species known or believed to be present but which has not yetbeen evaluated

ExoticAlien na Any species that has been introduced as a result of humanactivities

ExtirpatedExtinct na Any species no longer thought to be present in Alberta(ldquoExtirpatedrdquo) or no longer believed to be present anywhere in theworld (ldquoExtinctrdquo)

AccidentalVagrant na Any species occurring infrequently and unpredictably in Albertaie outside their usual range

Extinct A species that no longer existsExtirpated A species that no longer exists in the wild in Canada but occurs elsewhereEndangered A species facing imminent extirpation or extinctionThreatened A species that is likely to become endangered if limiting factors are not reversedSpecial Concern A species of special concern because of characteristics that make it particularly

sensitive to human activities or natural eventsNot at Risk A species that has been evaluated and found to be not at riskData Deficient A species for which there is insufficient scientific information to support status

designation

B Alberta Wildlife ActRegulation

Species designated as ldquoEndangeredrdquo under Albertarsquos Wildlife Act include those listed as ldquoEndangeredrdquo or ldquoThreat-enedrdquo in the Wildlife Regulation

Endangered A species facing imminent extirpation or extinction

Threatened A species that is likely to become endangered if limiting factors are not reversed

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 26: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

19

D Heritage Status Ranks Global (G) National (N) Sub-National (S) (after Alberta Natural Heritage InformationCentre 2002c)

G1N1S1 5 or fewer occurrences or only a few remaining individuals May be especiallyvulnerable to extirpation because of some factor of its biology

G2N2S2 6-20 or fewer occurrences or with many individuals in fewer locations May beespecially vulnerable to extirpation because of some factor of its biology

G3N3S3 21-100 occurrences may be rare and local throughout its range or in a restricted range(may be abundant in some locations) May be susceptible to extirpation because oflarge-scale disturbances

G4N4S4 Typically gt100 occurrences Apparently secure

G5N5S5 Typically gt100 occurrences Demonstrably secure

GXNXSX Believed to be extinct or extirpated historical records only

GHNHSH Historically known may be relocated in future

E United States Endangered Species Act (after National Research Council 1995)

Endangered Any species which is in danger of extinction throughout all or a significant portion ofits range

Threatened Any species which is likely to become an endangered species within the foreseeablefuture throughout all or a significant portion of its range

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 27: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

20

APPENDIX 3 Specific locations of all recorded western silvery minnow collected in Alberta

System Directions Coordinates DateCollected Reference 1 Sample

SizeMilk R NA 8-2-6-W4 13-May-61 UAMZ 5320 2

SouthSaskatchewan R near Medicine Hat NA May-June 63 Henderson and

Peter 1969 1

Milk R274 km E 48 km Sof the Town of MilkRiver at Weir Bridge

S8 Twp2 R13 14-Jun-66 Willock 1969b 1

Milk R129 km N 16 km Wof Aden below AdenBridge

S20 Twp 2 R10 4-Sep-66 Willock 1969b 2

Lost R2(tributary to

Milk R)

Mouth of Lost RCoulee 8 km N and129 km W ofSimpson Montana

NA 11-Jun-67 Willock 1969b 368

Milk R 64 km E of Writing-on-Stone Park NA 12-May-71 UAMZ 2846 2

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3335 1

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3338 21

Milk R 354 km S 48 km Wof Orion NA 30-May-72 UAMZ 3339 21

Milk R 37 km S 32 km W ofOrion NA 28-Apr-73 UAMZ 3241 1

Milk R 16 km W of Deer Cr NA 28-Apr-73 UAMZ 3244 1

Milk R 274 km W ofWildhorse NA 16-May-73 UAMZ 3234 5

Milk R 16 km W of Deer Cr NA 23-Jul-74 UAMZ 3548 26

Milk R 48 km S of Crofton atHwy 880 crossing NA 30-Jun-76 UAMZ 3838 2

Milk R Deer Cr Bridge 1253km upstream of border

49o 05rsquo 1151rsquorsquo N111 o 32rsquo 5426rdquo W 20-Nov-79 Clayton and Ash

1980 2

1 UAMZ = University of Alberta Museum of Zoology specimen record number

2 Only location from outside of Alberta included in this list (but not on the map) Significant because of the largesample size in comparison to the other sites and its proximity to Alberta (approximately 17 km downstream of theborder)

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 28: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

21

System Directions Coordinates DateCollected Reference 1 Sample

Size

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 3-Jul-86 RLampL 1987 2

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 29-Aug-86 RLampL 1987 4

Milk RPinhorn Ranch 564 -518 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 2

Milk RDeer Cr Bridge 1290- 1245 km upstreamof border

49 o 05rsquo 0336rdquo N111 o 34rsquo 5225rdquo W 27-Aug-86 RLampL 1987 1

Milk RPinhorn Ranch 564 -562 km upstream ofborder

49 o 07rsquo 2955rdquo N110 o 54rsquo 1502rdquo W 20-Oct-86 RLampL 1987 1

Milk R Pinhorn Ranch 49 o 06rsquo 2193rdquo N110 o 54rsquo 1853rdquo W 21-Oct-00 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2278rdquo N110 o 54rsquo1358rdquo W 19-Oct-01 RLampL 2002b 13

Milk R Pinhorn Ranch 49 o 07rsquo1672rdquo N110 o 55rsquo 0623rdquo W 19-Oct-01 RLampL 2002b 2

Milk R Pinhorn Ranch 49 o 07rsquo 2565rdquo N110 o 57rsquo 3508rdquo W 20-Jul-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2908rdquo N110 o 55rsquo 2334rdquo W 19-Oct-01 RLampL 2002b 1

Milk R Pinhorn Ranch 49 o 07rsquo 2520rdquo N110 o 54rsquo 4644rdquo W 19-Oct-01 RLampL 2002b 11

Milk R Ross Ranch 49 o 08rsquo 5928rdquo N111 o 11rsquo 4462rdquo W 20-Oct-01 RLampL 2002b 6

Milk R Ross Ranch 49 o 08rsquo 1718rdquo N111 o 09rsquo 3904rdquo W 20-Oct-01 RLampL 2002b 1

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 29: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

22

Addendum to Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta

Summary of data collected in fall 2002

The schedule for the completion of the main report Status of the Western Silvery Minnow

(Hybognathus argyritis) in Alberta did not permit the inclusion of the most recent data collected

in the fall of 2002 on the Milk River However the results of these collections have implications

to the status evaluation of the western silvery minnow and are discussed here

In October 2002 additional surveys of fish and fish habitat were conducted on the Milk River

(PampE 2002) The purpose of these surveys was to sample areas of the Milk River not previously

sampled in 2000-2001 (RLampL 2001 2002a 2002b) particularly the most downstream section

of the Milk River in Alberta Given the severe drought conditions of late summer and fall 2001

these additional surveys were also conducted to determine the post-drought status of fish species

of interest especially the western silvery minnow The surveys were restricted to a narrow

sampling window of October 22-27 2002 by high water conditions and the onset of winter

Sampling was conducted primarily in the stretch of river 57 km downstream of Pinhorn Ranch

(see attached map) and included 29 sites (24 beach-seined and 5 electro-fished) located

approximately every 2 km to the international border In addition a secondary section

approximately 40 km in length above the Town of Milk River was evaluated at 6 sites (1 beach-

seined and 5 electro-fished) Surveys employed sampling techniques similar to those used in

2000-2001 by RLampL

The western silvery minnow was the second most common fish species after flathead chub

(Platygobio gracilis) in the section downstream of Pinhorn Ranch The minnow made up 437

of the total composition of species captured and a total of 63 specimens were collected All

specimens were collected via beach seine and were found at nine of the 24 beach seine sites (see

attached map) The overall catch rate or CPUE was 062 fish100 m2 and ranged from 022 to

578 fish100 m2 No minnows were captured in the upstream section of river above the Town of

Milk River

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 30: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

23

The number of western silvery minnows captured during October 2002 is higher than any

previous collection on the Milk River It is unlikely that this value reflects a true increase in

abundance compared to previous years In part this high value is likely the result of the

improved fishing efficiency of the survey crew who were able to apply the knowledge gained

during 2000 and 2001 In addition the comparatively high number of western silvery minnows

likely reflects the type of habitat available in the downstream section of the Milk River Sand

was the predominant substrate in the downstream section (81) whereas larger substrates were

more common upstream of the Town of Milk River where sand only comprised 11 of the total

substrate composition In addition turbidity was higher downstream while silt was negligible at

most sites The results of this most recent work are similar to the findings of Stash (2001) who

conducted surveys of the Milk River downstream of the international border He also noted that

western silvery minnow had the second highest level of abundance after flathead chub and

collected a total of 64 minnows between the border and the Fresno Reservoir

In summary these results indicate that the western silvery minnow is capable of finding refugia

in the lower Milk River during times of severe drought conditions such as those observed in

2001 Furthermore the lowest section of the Milk River downstream of Pinhorn Ranch appears

to provide the best habitat for the minnow This section is probably the most similar in habitat

type to the section immediately downstream of the border where higher numbers of western

silvery minnow have been recorded

Literature Cited

PampE Environmental Consultants Ltd 2002 Fish species of concern survey on the Milk River ndashOctober 2002 Prepared for Alberta Sustainable Resource Development and the AlbertaConservation Association PampE Report No 02018D 11 pp plus 3 appendices

RLampL Environmental Services Ltd 2001 Fish species at Risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskInterim Report 53 pp plus appendices

RLampL Environmental Services Ltd 2002a Fish species at risk in the Milk River Alberta ndash latewinter 2002 survey Prepared for Department of Fisheries and Oceans Freshwater Institute 13pp

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 31: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

24

RLampL Environmental Services Ltd 2002b Fish species at risk in the Milk and St MaryDrainages Prepared for Alberta Sustainable Resource Development Alberta Species At RiskReport No 45 82 pp plus appendices

Stash SW 2001 Distribution relative abundance and habitat associations of Milk River fishesrelated to irrigation diversion dams MSc Thesis Montana State University Bozeman MT 67pp

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 32: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

List of Titles in This Series(as of January 2003)

No 1 Status of the Piping Plover (Charadrius melodus) in Alberta by David R C Prescott 19 pp (1997)

No 2 Status of the Wolverine (Gulo gulo) in Alberta by Stephen Petersen 17 pp (1997)

No 3 Status of the Northern Long-eared Bat (Myotis septentrionalis) in Alberta by M Carolina Caceres and M J Pybus 19 pp (1997)

No 4 Status of the Ordrsquos Kangaroo Rat (Dipodomys ordii) in Alberta by David L Gummer 16 pp (1997)

No 5 Status of the Eastern Short-horned Lizard (Phrynosoma douglassii brevirostre) in Alberta by Janice D James Anthony P Russell and G Lawrence Powell 20 pp (1997)

No 6 Status of the Prairie Rattlesnake (Crotalus viridis viridis) in Alberta by Sheri M Watson and Anthony P Russell 26 pp (1997)

No 7 Status of the Swift Fox (Vulpes velox) in Alberta by Susan E Cotterill 17 pp (1997)

No 8 Status of the Peregrine Falcon (Falco peregrinus anatum) in Alberta by Petra Rowell and David P Stepnisky 23 pp (1997)

No 9 Status of the Northern Leopard Frog (Rana pipiens) in Alberta by Greg Wagner 46 pp (1997)

No 10 Status of the Spraguersquos Pipit (Anthus spragueii) in Alberta by David R C Prescott 14 pp (1997)

No 11 Status of the Burrowing Owl (Speotyto cunicularia hypugaea) in Alberta by Troy I Wellicome 21 pp (1997)

No 12 Status of the Canadian Toad (Bufo hemiophrys) in Alberta by Ian M Hamilton Joann L Skilnick Howard Troughton Anthony P Russell and G Lawrence Powell 30 pp (1998)

No 13 Status of the Sage Grouse (Centrocercus urophasianus urophasianus) in Alberta by Cameron L Aldridge 23 pp (1998)

No 14 Status of the Great Plains Toad (Bufo cognatus) in Alberta by Janice D James 26 pp (1998)

No 15 Status of the Plains Hognose Snake (Heterodon nasicus nasicus) in Alberta by Jonathan Wright and Andrew Didiuk 26 pp (1998)

No 16 Status of the Long-billed Curlew (Numenius americanus) in Alberta by Dorothy P Hill 20 pp (1998)

No 17 Status of the Columbia Spotted Frog (Rana luteiventris) in Alberta by Janice D James 21 pp (1998)

No 18 Status of the Ferruginous Hawk (Buteo regalis) in Alberta by Josef K Schmutz 18 pp (1999)

No 19 Status of the Red-tailed Chipmunk (Tamias ruficaudus) in Alberta by Ron Bennett 15 pp (1999)

No 20 Status of the Northern Pygmy Owl (Glaucidium gnoma californicum) in Alberta by Kevin C Hannah 20 pp (1999)

No 21 Status of the Western Blue Flag (Iris missouriensis) in Alberta by Joyce Gould 22 pp (1999)

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 33: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

No 22 Status of the Long-toed Salamander (Ambystoma macrodactylum) in Alberta by Karen L Graham and G Lawrence Powell 19 pp (1999)

No 23 Status of the Black-throated Green Warbler (Dendroica virens) in Alberta by Michael R Norton 24 pp (1999)

No 24 Status of the Loggerhead Shrike (Lanius ludovicianus) in Alberta by David R C Prescott and Ronald RBjorge 28 pp (1999)

No 25 Status of the Plains Spadefoot (Spea bombifrons) in Alberta by Richard D Lauzon 17 pp (1999)

No 26 Status of the Trumpeter Swan (Cygnus buccinator) in Alberta by M Lynne James 21 pp (2000)

No 27 Status of the Pygmy Whitefish (Prosopium coulteri) in Alberta by William C Mackay 16 pp (2000)

No 28 Status of the Short-eared Owl (Asio flammeus) in Alberta by Kort M Clayton 15 pp (2000)

No 29 Status of the Willow Flycatcher (Empidonax traillii) in Alberta by Bryan Kulba and W Bruce McGillivray 15pp (2001)

No 30 Status of the Woodland Caribou (Rangifer tarandus caribou) in Alberta by Elston Dzus 47 pp (2001)

No 31 Status of the Western Spiderwort (Tradescantia occidentalis) in Alberta by Bonnie Smith 12 pp (2001)

No 32 Status of the Bay-breasted Warbler (Dendroica castanea) in Alberta by Michael Norton 21 pp (2001)

No 33 Status of the Cape May Warbler (Dendroica tigrina) in Alberta by Michael Norton 20 pp (2001)

No 34 Status of the Whooping Crane (Grus americana) in Alberta by Jennifer L White 21 pp (2001)

No 35 Status of Soapweed (Yucca glauca) in Alberta by Donna Hurlburt 18 pp (2001)

No 36 Status of the Harlequin Duck (Histrionicus histrionicus) in Alberta by Beth MacCallum 38 pp (2001)

No 37 Status of the Grizzly Bear (Ursus arctos) in Alberta by John L Kansas 43 pp (2002)

No 38 Status of the Wood Bison (Bison bison athabascae) in Alberta by Jonathan A Mitchell and C CormackGates 32 pp (2002)

No 39 Status of the Bull Trout (Salvelinus confluentus) in Alberta by John R Post and Fiona D Johnston 40 pp(2002)

No 40 Status of the Banff Springs Snail (Physella johnsoni) in Alberta by Dwayne AW Lepitzki 29 pp (2002)

No 41 Status of the Shortjaw Cisco (Coregonus zenithicus) in Alberta by Mark Steinhilber 23 pp (2002)

No 42 Status of the Prairie Falcon (Falco mexicanus) in Alberta by Dale Paton 28 pp (2002)

No 43 Status of the American Badger (Taxidea taxus) in Alberta by Dave Scobie 17 pp (2002)

No 44 Status of the Yucca Moth (Tegeticula yuccasella) in Alberta Alberta Sustainable Resource Development 21pp (2002)

No 45 Status of the White-winged Scoter (Melanitta fusca deglandi) in Alberta Alberta Sustainable ResourceDevelopment 15 pp (2002)

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)

Page 34: Status of the Western Silvery Minnow in Alberta€¦ · the removal of water for irrigation left the lower Milk River both above and below the international border completely dry,

No 46 Status of the Lake Sturgeon (Acipenser fulvescens) in Alberta Alberta Sustainable Resource Development30 pp (2002)

No 47 Status of the Western Silvery Minnow (Hybognathus argyritis) in Alberta Alberta Sustainable ResourceDevelopment 24 pp (2003)