The Lay of the Land: Understanding Quahog Management in Rhode Island
-
Upload
riseagrant -
Category
Education
-
view
364 -
download
2
description
Transcript of The Lay of the Land: Understanding Quahog Management in Rhode Island
The Lay of the Land:
Understanding Quahog Management in Rhode Island
Jeff Mercer
RI DEM, Principal Biologist
May 19, 2014
39.1 Million Clams 6.96 Million Pounds $5.15 million Dollars 534 Fishermen
Quahogs by The Numbers
2012 Landings 1. Squid $19 Million 2. Lobster $12 Million 3. Sea Scallop $9 Million 4. Summer Flounder $7 Million 5. Quahog $5 Million
CHERRY3%
CHOWDER10%
LITTLE NECK64%
TOP NECK23%
• Management Goals
– What do we hope to accomplish through management?
• Management Tools
– What are the specific ways which we manage the resource and fishery?
• Assessment Methods
– How do we go about assessing existing strategies and potential modifications to management?
Outline
Management Philosophy
The marine fishery resources belonging to, allocated to, and of interest to Rhode Island need to be preserved and protected, at healthy, sustainable levels-
– Because of their ecological value, and
– Because they are renewable natural resources that provide food, recreation, income, employment, and other economic, social, and cultural benefits.
• Maintain the health of the State’s marine ecosystem
• In accordance with sustainable harvest levels, manage harvest in ways that
– Make full and effective use of available harvest opportunities, while minimizing discards, ecological impacts, habitat degradation, and other wasteful practices
– Balance the interests of different user groups and stakeholders
Management Goals
• Recreational Harvesters – Provide fair, open, and equitable access and harvest opportunities
with certain preferences to residents of the State
• Commercial Industry – Maintain an economically strong viable and diverse industry
– Support the business interest of fishermen and economic interest of the industry
– Support safe fishing operations
– Support enhanced marketing opportunities
• Prospective Fishermen – Provide meaningful access opportunities without unduly impacting
the interests of those currently engaged in the industry
• General Public – Maintain the health of the State’s marine ecosystem
– Provide a stable supply of safe, fresh, locally caught seafood
Management Goals
– Minimum Size
– Harvest Methods
– Licensing
– Daily Catch Limits
– Area Based Management
• Limited Access Time
• Reduced Daily Limits
• Rotational Harvest
• Spawner Sanctuaries
– Transplants
– Harvesting and Handling Requirements (OWR &DOH)
Management Tools
– Fishery Dependent
• Landings Data - SAFIS
• Catch Per Unit Effort (CPUE)
– Fishery Independent
• Dredge Survey
• Other field surveys
– Life History Studies
• Age and Growth
• Maturity schedule
• Fecundity
• Natural Mortality
Models
Bay-Wide Population Modeling
Area-Specific Depletion Modeling
Computer Simulations
Assessment Methods
Harvesting and Handling – OWR & DOH
Density 8-20 X Greater than Avg
• Pollution closures act as de facto marine reserves
• 50% of nitrogen in quahog has origin from waste water
• More tolerant to hypoxia than predators = predation refuge
Harvesting and Handling – OWR & DOH
• Pollution closures act as de facto marine reserves
• 50% of nitrogen in quahog has origin from waste water
• More tolerant to hypoxia than predators = predation refuge
0
500
1000
1500
2000
2500
3000
19
45
19
50
19
55
19
60
19
65
19
70
19
75
19
80
19
85
19
90
19
95
20
00
20
05
20
10
Lan
din
gs (
MT)
& L
ice
nse
s (#
)
# of Licenses Meat Weight (MT)
Minimum Size
0
10
20
30
40
50
60
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30
Sh
ell
Wid
th (
mm
)
Age (yrs)
Legal Size
Growth Curve
Sexual Maturity
*1987 moved from 1.5” length to 1” width
0
500
1000
1500
2000
2500
3000
1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010
Lan
din
gs (
MT)
& L
ice
nse
s (#
)
Year
# of Licenses Meat Weight (MT)
* NMFS Landings Data
Harvest Methods
31,000,000 lbs
0
500
1000
1500
2000
2500
3000
1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010
Lan
din
gs (
MT)
& L
ice
nse
s (#
)
Year
# of Licenses Meat Weight (MT)
* NMFS Landings Data
Harvest Methods
31,000,000 lbs =
3,500 Elephants
0
500
1000
1500
2000
2500
3000
1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010
Lan
din
gs (
MT)
& L
ice
nse
s (#
)
Year
# of Licenses Meat Weight (MT)
* NMFS Landings Data
Harvest Methods
0
500
1000
1500
2000
2500
3000
1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010
Lan
din
gs (
MT)
& L
ice
nse
s (#
)
Year
# of Licenses Meat Weight (MT)
* NMFS Landings Data
Harvest Methods
TITLE 20 § 20-6-7 Use of dredges …no
person shall take any oysters, bay quahaugs, or soft-shell clams from the waters of this state by dredges, rakes, or other apparatus operated by mechanical power or hauled by
power boats.
Harvest Methods
0
500
1000
1500
2000
2500
3000
1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010
Lan
din
gs (
MT)
& L
ice
nse
s (#
)
Year
# of Licenses Meat Weight (MT)
* NMFS Landings Data
Harvest Methods
Licensing
0
500
1000
1500
2000
2500
3000
1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010
Lan
din
gs (
MT)
& L
ice
nse
s (#
)
Year
# of Licenses Meat Weight (MT)
* NMFS Landings Data
• Open Access (through mid 1990s)
• 1st Moratorium (1995 – 1998)
• Open Access (1999)
• 2nd Moratorium (2000-2002)
• New Licensing Program (2003)
Licensing
• Use of License Endorsements to limit access to certain species
• Use of Exit/Entry Ratios to control effort levels
– Currently 2:1 for Quahog Endorsement
• Annual process of regulatory review and modification, based on input from industry and advice from RI Marine Fisheries Council
Licensing
Licensing
0
500
1000
1500
2000
2500
3000
1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010
Lan
din
gs (
MT)
& L
ice
nse
s (#
)
Year
# of Licenses Meat Weight (MT)
* NMFS Landings Data
1984
1985
1986
1987
1988 1989
1990 1991
1992
1993
1994
1995 1996
1997
1998 1999 2000
2001 2002
2003 2004
2005 2006 2007
2008
2009
2010 2011
2012
0
100
200
300
400
500
600
0.00 0.10 0.20 0.30 0.40 0.50 0.60 0.70
Ab
un
da
nce i
n M
illio
ns (
t)
F Rate (t-1)
Licensing – Stock Assessment model
License Type 2003 Total 2013 Total Net Change
MPL 1191 829 -362
PEL w/QH 924 376 -548
CFL w/QH 271 420 +149
Student SF 107 48 -59
65 & ↑ SF 50 268 +218
TOTALS 2,543 1,941 -602
Licensing
0
200
400
600
800
1000
1200
1400
2003 2004 2005 2006 2007 2008 2009 2010 2011 2012
# o
f Li
cen
ses
Year
MPURP PEL CFL SFO65 STUD
MPURP Active PEL Active CFL Active SFO65 Active STUD Active
Licensing - # of Active Licenses
0
20
40
60
80
100
120
140
1-5 6-10 11-25 26-50 51-100 101-150 151-200 201-250 251-306
# o
f Fi
she
rme
n
Days Fished
PEL MPURP CFL SF065 Stud
Licensing - 834 Total Active
~ 150 Fishermen
0
20
40
60
80
100
120
# o
f A
ctiv
e F
ish
erm
en
Age
PEL MPURP CFL SFO65 STUD
93 fishermen under 40 years old
Licensing – Age of Fishermen
0
20
40
60
80
100
120
# o
f A
ctiv
e F
ish
erm
en
Age
PEL MPURP CFL SFO65 STUD
Only 19 full-time
fishermen under 40 years old
(100+ days)
Licensing – Age of Fishermen
0
2
4
6
8
10
12
0
500
1000
1500
2000
2500
3000
1945 1950 1955 1960 1965 1970 1975 1980 1985 1990 1995 2000 2005 2010
Un
em
plo
yme
nt
Rat
e (
%)
Lan
din
gs (
MT)
& L
ice
nse
s (#
)
Year
# of Licenses Meat Weight (MT) Unemployment Rate
* NMFS Landings Data
Licensing – & unemployment
Daily Catch Limits License
Type Endorsements Limits Cost
Full Harvest
Principal Effort (PEL)
Quahog Soft Shell
Whelk Other
12 bu/day (3 in MAs)
$150 License No Fee for 1st Endorsement
$75 each add’l
Multipurpose (MPL) N/A 12 bu/day (3 in MAs) $300
Limited Harvest
Commercial Fishing (CFL)
Quahog Soft Shell
Whelk Other
3 bu/day $50 License $25 for each Endorsement
Student *Quahog only 3 bu/day $50
Over 65 *Quahog only 3 bu/day No Fee
Recreational (Resident) N/A ½ bu/day (1 peck in MA) No license
Recreational (Non-res) N/A 1 peck/day (1/2 peck in MA) $200 / $25/ $11
𝑁𝑖𝑗 = 𝑁𝑖𝑗−1 ∗ 1 − 𝑝 ∗ 𝑒− 𝐹𝑖𝑗−1+𝑀 + 𝑁𝑖−1𝑗−1 ∗ 𝑝 ∗ 𝑒− 𝐹𝑖−1𝑗−1+𝑀
N = population size F = fishing mortality rate P = promotion probability governed by von Bertalanffy growth equation derived from Henry & Nixon (2008) M = natural mortality rate i = size class j = year
Inputs to Model
1. Landings 2. Fisheries Independent Abundance Index 3. Fishing Effort Index
Daily Catch Limits – Size-structured Stock Assessment Model
0
20
40
60
80
100
120
140
160
# o
f Q
uah
og
s (
millio
ns)
Year
Landings
Size Structured Stock Assessment Model
Gibson, 2010
0
100
200
300
400
500
600
# o
f Q
uah
og
s (
millio
ns)
Year
Abundance Landings
Gibson, 2010
Daily Catch Limits – Size-structured Stock Assessment Model
Polynomial
Logarithmic
Stock-Recruitment Models Great South Bay, NY
How Many Quahogs do We Need?
Kraeuter et al, 2005
Density Dependence
0.75 Adults/m2 = Recruitment Failure
Daily Catch Limits
0
100
200
300
400
500
600
# o
f Q
uah
og
s (
millio
ns)
Year
AbundanceLandingsRecruitment Failure
0.75 Adults/m2 X 125km2 Fishable Area
Daily Catch Limits – Size-structured Stock Assessment Model
Kraeuter et al, 2005
Daily Catch Limits – Spawning Stock & Recruitment
0
100
200
300
400
500
600
# o
f Q
uah
og
s (
millio
ns)
Year
AbundanceLandingsReduced Recruitment
1.5 Adults/m2 X 125km2 Fishable Area
Daily Catch Limits – Size-structured Stock Assessment Model
West Passage
Conditional B
Conditional A
Greenwich
East Passage
ma
ma
ma
ma
West Passage25.9%
Conditional A23.6%
Conditional B20.9%
Greenwich Bay14.4%
East Passage
11.9%
Management Areas0.9%
Coastal Ponds0.8%
Not Identified
0.7%Sakonnet
0.6%Mt Hope Bay
0.3%
Block Island
0.0%
• No info on Closed Waters • Tagging Areas are Large
Area Based Management
• 1993-2013 • Use hydraulic dredge
to sample adult populations
• Stratified Random Sampling Design
• 2368 tows of 30 m • 26,000+ clams
Area Based Management – Dredge Survey
• Not corrected for
dredge efficiency
• High densities correspond to productive fishing grounds
• Shallow areas poorly assessed
• Closed Areas highest densities
Area Based Management – Dredge Survey
Adapted from Gaylord, et al., 2005
Habitat Area
Habitat Area
Protected
Fished
P F
Protected
P
Area Based Management
Habitat Area
Habitat Area
Protected
Fished
P F
49% of Studies Fisheries Yield
Higher with Traditional
Management
51% of Studies Fisheries Yield
Higher with MPAs
Gaines, et al., 2010
Area Based Management
Habitat Area
Habitat Area
Protected
Fished
P F
Protected
P
Area Based Management
Habitat Area
Habitat Area
Protected
F
P F P
P P P P P P P P P
F F F
Area Based Management
Rhode Island Management
Habitat Area
Habitat Area
Protected
P F P
P
f
• Management = 67.8km2
• Est. Fishable Area ~ 125km2
F P
F F
P F P p
f p p
f
P P
Area Based Management
Rhode Island Management
Management Areas = 67.8km2
Estimated Fishable Area ~ 125km2
Area Based Management – Greenwich Bay
Area Based Management – Greenwich Bay
DEC JAN FEB MARCH APRIL
GB Sub Area 1 & 2 CLOSED OWR 8-12 Jan 2 and starting Jan 6
8-12 MWF 8-12 MWF 8-12 MWF 8-12 MWF
High Banks & Pot C Open Open Open Open Open
Bristol CLOSED 8-12 MWF beginning Jan 3 Open Open Open
Bissel/Fox Opens 2nd Wed* Open* Open* Open* Open*
Mill Gut Opens 2nd Wed Open Open Open Open
• LESLIE'S METHOD • Assume • Nt= No - Ct • Kt = Ct = cumulative catch • Nt = No-Kt • but, “N" is not an observable variable in most studies,so after multiplying
through by q (the catchability coefficient) • qNt = qNo - q(Ct) • CPUE= a + b (Kt) • Fit a regression then
– a) the slope of the line is an estimate of q – b) the intercept is qNo = CPUEo – c) the initial population can be estimated by Intercept a/ slope b
Area Based Management – Leslie Depletion Model
Area Based Management – Leslie Depletion Model
0
5
10
15
20
25
30
35
40
0 50 100 150 200 250
Me
an C
PU
E (m
arsh
mal
low
s/h
and
ful)
Cumulative Catch (Total # of Marshmallows)
Area Based Management – Leslie Depletion Model
0
5
10
15
20
25
30
35
40
0 50 100 150 200 250
Me
an C
PU
E (m
arsh
mal
low
s/h
and
ful)
Cumulative Catch (Total # of Marshmallows)
Area Based Management – Leslie Depletion Model
0
5
10
15
20
25
30
35
40
0 50 100 150 200 250
Me
an C
PU
E (m
arsh
mal
low
s/h
and
ful)
Cumulative Catch (Total # of Marshmallows)
Area Based Management – Leslie Depletion Model
0
5
10
15
20
25
30
35
40
0 50 100 150 200 250
Me
an C
PU
E (m
arsh
mal
low
s/h
and
ful)
Cumulative Catch (Total # of Marshmallows)
Area Based Management – Leslie Depletion Model
0
5
10
15
20
25
30
35
40
0 50 100 150 200 250
Me
an C
PU
E (m
arsh
mal
low
s/h
and
ful)
Cumulative Catch (Total # of Marshmallows)
240 Total Marshmallows
Area Based Management – Leslie Depletion Model
y = -0.1519x + 38.173 R² = 0.9817
0
5
10
15
20
25
30
35
40
0 50 100 150 200 250
Me
an C
PU
E (m
arsh
mal
low
s/h
and
ful)
Cumulative Catch (Total # of Marshmallows)
Starting N Catch exp rate
Volume Start Dens.
End Dens.
F Rate End N
251 240 0.955 12 20.9 0.94 3.1 11
Area Based Management – Leslie Depletion Model
y = -0.1162x + 34.888 R² = 0.9657
0
5
10
15
20
25
30
35
40
0 50 100 150 200 250
Me
an C
PU
E (m
arsh
mal
low
s/h
and
ful)
Cumulative Catch (Total # of Marshmallows)
Estimated 262 Total
Marshmallows
Starting N Catch exp rate
Volume Start Dens.
End Dens.
F Rate End N
262 207 0.791 12 21.8 4.56 1.56 55
Area Based Management – Leslie Depletion Model
y = -0.1162x + 34.888 R² = 0.9657
0
5
10
15
20
25
30
35
40
0 50 100 150 200 250
Me
an C
PU
E (q
uah
ogs
/fis
he
r/d
ay)
Cumulative Catch (Total # of Quahogs)
Starting N Catch exp rate
Area Start Dens.
End Dens.
F Rate End N
262 207 0.791 12 21.8 4.56 1.56 55
Area Based Management – Leslie Depletion Model
December 2009 – March 2010
y = -0.0002x + 1362.9 R² = 0.2653
0
200
400
600
800
1000
1200
1400
1600
0 500,000 1,000,000 1,500,000
Me
an C
PU
E (q
uah
ogs
/fis
he
rme
n/d
ay)
Cumulative Catch (# of quahogs)
Starting # Start #/m2
Catch End # End
#/m2
5,963,116 2.82 1,458,649 4,504,467 2.13
2002-May 2010
Area = 2,109,619 m2
F Rate = 0.281
Area Based Management – Leslie Depletion Model
• May 2010 pollution line changes
Area Based Management – Leslie Depletion Model
• May 2010 pollution line changes
• Summer 2010 DEM conducts dredge survey
• Densities as high as 26 quahogs/ m2 when adjusted for efficiency
• SAP & RIMFC decide to open only Area A (north side)
Area Based Management – Leslie Depletion Model
Dec. 2010- March 2011
y = -5E-05x + 1901.2 R² = 0.6006
0
500
1000
1500
2000
2500
0 1,000,000 2,000,000 3,000,000 4,000,000 5,000,000 6,000,000
Me
an C
PU
E (q
uah
ogs
/fis
he
rme
n/d
ay)
Cumulative Catch (# of quahogs)
Starting # Start #/m2
Catch End # End
#/m2
40,983,314 27.09 5,866,505 35,116,809 23.21 Area = 1,512,589 m2
F Rate = 0.154
Area Based Management – Leslie Depletion Model
Dec. 2011- March 2012
y = -8E-05x + 1728.2 R² = 0.5128
0
500
1000
1500
2000
2500
0 2,000,000 4,000,000 6,000,000
Me
an C
PU
E (q
uah
ogs
/fis
he
rme
n/d
ay)
Cumulative Catch (# of quahogs)
Starting # Start #/m2
Catch End # End
#/m2
20,765,498 6.51 6,588,476 6,588,478 4.45 Area = 3,189,110 m2
F Rate = 0.382
Area Based Management – Leslie Depletion Model
• May 2012 pollution
lines extended
• Dredge Survey results from Summer 2012
• Densities reduced from ~ 9/m2 to < 1/m2
Area Based Management – Leslie Depletion Model
Jan 2013- March 2013
y = -0.0003x + 1471.7 R² = 0.4798
0
200
400
600
800
1000
1200
1400
1600
1800
2000
0 500,000 1,000,000 1,500,000 2,000,000 2,500,000
Me
an C
PU
E (q
uah
ogs
/fis
he
rme
n/d
ay)
Cumulative Catch (# of quahogs)
Starting # Start #/m2
Catch End # End
#/m2
4,872,719 1.79 2,012,279 2,860,440 1.05 Area = 2,727,668m2
F Rate = 0.533
Area Based Management – Leslie Depletion Model
Jan 2014 - March 2014
y = -0.0004x + 1522.1 R² = 0.4154
0
200
400
600
800
1000
1200
1400
1600
1800
2000
0 500,000 1,000,000 1,500,000
Me
an C
PU
E (q
uah
ogs
/fis
he
rme
n/d
ay)
Cumulative Catch (# of quahogs)
Starting # Start #/m2
Catch End # End
#/m2
3,544,222 1.30 1,482,124 2,062,099 0.76 Area = 2,727,668m2
F Rate = 0.542
Habitat Area
Habitat Area
Protected
P F P
P
f
• Management = 67.8km2
• Est. Fishable Area ~ 125km2
F P
F F
P F P p
f p p
f
P P
Area Based Management
Rhode Island Management
Habitat Area
Habitat Area
Protected
P F P
P
f
• Management = 67.8km2
• Est. Fishable Area ~ 125km2
F P
F F
P F P p
f
p p
f
P P
Area Based Management
Rhode Island Management
Habitat Area
Habitat Area
Protected
Fished
P F
Protected
P
SOURCE SINK
For reserves to be effective they must also increase populations beyond reserve borders through: 1. Larval Export 2. Adult Spillover (Transplants?)
Area Based Management - Spawner Sanctuaries
• Larvae released randomly over 30 day period
• Released in top 2 meters
• Passive for 11 days
• Swim towards bottom for 24 hours – randomness added
• Site Specific Settlement
– OFF
LTRANS
Area Based Management
Greenwich Cove Prohibited
Area Based Management
• ~100 million eggs/m2
• Larval Duration 8-12 days
• Large potential reproductive output
Area Based Management
Marroquin-Mora & Rice (2008)
• Too Dense?
• Crowding may lead to poor condition and low reproductive output
• CI = dry soft tissue wt X 1000/ (total wt - shell wt)
Area Based Management
Matt Griffin RWU/URI
Area Based Management - Transplants
Since 1977 ~ 9 million lbs of quahogs transplanted
High Banks
Potowomut Sanctuary
Greenwich Cove
Area Based Management – Transplants
Potowomut Spawner Sanctuary Approved-Closed
High Banks Management Area Approved
Area Based Management - Transplants
Area Based Management - Spawner Sanctuaries
Data from TNC
Questions?