MODIFICATION OF FISH LADDERS AT JOHN DAY DAM … · Fish ladders 241 A§SSNACT (Came - ,ewee N nemi...
Transcript of MODIFICATION OF FISH LADDERS AT JOHN DAY DAM … · Fish ladders 241 A§SSNACT (Came - ,ewee N nemi...
AD-A145 949 MODIFICATION OF FISH LADDERS AT JOHN DAY DAM COLUMBIA l/'2.RIER OREGON AND WA..AU ARMY ENDINEER DIV NORTH
PACIC BONNEAILE OR DIV HYDRAULIC L.P M SMITH
UNCLASSIFED AUG 84 TR-03-2 FIG 20/4!
- 161. L 0
II ,, 1.1 1
111W j .
MICROCOPY RESOLUTION TEST CHARTNATIONAL BUREAU OT STANO4fAD-1963-A
H A C DTECHNICAL REPORT NO.103-2~HYDRAULIC MODEL
INVESTIGATION
9
Modification of Fish LaddersNO
:2 M at John Day Dam0,
:2 'n Columbia River,10
Oregon and WashingtonSPONSORED BYU. S. ARMY CORPS OF ENGINEERS
a PORTLAND DISTRICTa
CONDUCTED BY>DIVISION HYDRAULIC LABORATORY
U. S. ARMY CORPS OF ENGINEERS
0 NORTH PACIFIC DIVISION DTIC8 BONNEVILLE, OREGON ELECTE
zSEP 2 6 8'
AUGUST 1084
1"Cnof Englmm
THIS DOCUMENT HAS BEEN APPROVED FOR PUBLIC RELEASE
F84 09 17 054
Destroy this report when no longer needed. Do not returnit to the originator.
The findings in this report are not to be construedas an officialDepartment of the Army position unless so designated
by other authorized documents.
UnclassifiedSECURITY CLASSIFICATION OF THIS PAGE tRlen Date Inters
REPORT DOCUMENTATION PAGE READ mNT cUoNsBEFORE COMPLETING FORMA
A. REPORT NUMBER ,,.RECIPIENT S CATALOG NUMBER
Technlcal Report No. 103-24. TITLE (and Subtitle) S. TYPE OF REPORT & PERIOD COVERED
MODIFICATIONS OF FISH LADDERS AT JOHN DAY DAM,COLUMBIA RIVER, OREGON AND WASHINGTON Final ReportHydraulic Model Investigation 6. PERFORMING ORG. REPORT NUMBER
7. AUTHOR(q) S. CONTRACT OR GRANT NUMBER(&)
9. PERFORMING ORGANIZATION NAME AND ADDRESS 10. PROGRAM ELEMENT, PROJECT, TASK
U.S. Army Engineer Division, North Pacific AREA & WORK UNIT NUMBERS
Division Hydraulic LaboratoryBonneville, Oregon 97008
II. CONTROLLING OFFICE NAME AND ADDRESS 12. REPORT DATE
U.S. Army Engineer District, Walla Walla August 1984Building 1602, City-County Airport IS. NUMBER OF PAGES
Walla Walla, Washington 99362 11714. MONITORING AGENCY NAME & AOOR$SS(lf dlffernt ifom Controllirg Office) 15. SECURITY CLASS. (of thie report)
UnclassifiedIS&. DECLASSI FICATION/ DOWNGRADING
SCHEDULE
16. DISTRIBUTION STATEMENT (of thls Report)
Approved for public release; distribution unlimited.
17. DISTRIBUTION STATEMENT (of tIe abesract entered In Block 20, If different from Report)
IS. SUPPLEMENTARY NOTES
IS. KEY WORDS (Continue an reverse sidO it neceeasy and Identi y by block niumber)
Hydraulic modelsJohn Day DamColumbia RiverFish ladders
241 A§SSNACT (Came - ,ewee N nemi and identiyt by block nmober)
-Prototype operation of the originally constructed fish ladders at John Day Damrevealed the need for ladder modifications to improve fish passage. A 1:10-scale model was used to evaluate the design modifications for both the north-and south-shore ladders. Improvements were desired in the flow-regulatingsections and at the fish counting station for both fish ladders. The model was
instrumental in developing a successful modification to the Hell's Gate slot-orifice type regulating section. The modification consisted of a slot-only
O , 3,, ,,oo oF I Nov6s Is OBSOLETE Unclassified
SECUMTY CLASSIFICATION OF THIS PAGE (Man Date Entered)
UnclassifiedSECURITY CLASSFICATION OF THIS PAG9jWheM Da 80"904
design having a maximum head drop of approximtely 6 iniche. A verticalcounting station was developed for the north-shore ladder. Successful opera-tion in the prototype has verifted. the effectiveness of the design.,
UnclassifiedSECURITY CLASSIFICATION OF THIS PAGE(When Dante BEeeIrd)
PREFACE
This report describes model studies made to develop modifica-
tions for the regulating section and counting stations of the fish
ladders at John Day Dam. Model studies made to develop the orig-
inal ladders are described in Technical Report No. 103-1, "Fish
Ladders for John Day Dam, Columbia River, Oregon and Washington,"
dated December 1968.
Hydraulic model studies for the John Day project were author-
ized 14 July 1958 by the Office of Chief of Engineers, at the
request of the U.S. Army Engineer District, Walla Walla, through
the U.S. Army Engineer Division, North Pacific. The model tests
reported here were conducted from September 1969 to October 1970
at the Division Hydraulic Laboratory, Bonneville, Oregon, under
the general direction of the North Pacific Division Engineer.
Personnel of the Office of Chief of Engineers, North Pacific
Division, and Portland and Walla Walla Districts visited the
Laboratory to observe the model tests and discuss the results.
Flow conditions in the model were demonstrated for representatives
of the U.S. Fish and Wildlife Service and the fish and game depart-
ments of Oregon, Washington, and Idaho. Tests of the regulating
sections were coordinated with full-scale tests of parts of the
same sections conducted at the Fisheries-Engineering Research
Laboratory (FERL), National Marine Fisheries Service, North Bonne-
ville, Washington.
The studies were conducted by Mr. D.E. Fox under the supervi-
sion of Messrs. P.M. Smith and A.J. Chanda, Chiefs of Structures
Section and Hydraulics Branch, respectively, and H.P. Theus,
Director. This report was prepared by Mr. Smith.
TABLE OF CONTENTS
page
PREFACE . i
CONVERSION FACTORS, U.S. CUSTOMARY TO METRIC (SI) UNITS
OF MEASUREMENT ....... ...................... .. .i
PART I: INTRODUCTION ........ ................... 1
The Prototype ... ...................... 1
Need for Model Studies ....... .............. 3
PART II: THE MODEL ........ ........ ....... 5
Description ......... . . ........ . 5
Facilities .......... .................... 5
Scale Relationships .... ............... 5
PART III: TESTS AND RESULTS ........ ................ 6
North Shore Regulating Section ..... .......... 6
North Shore Counting Station ... ........... ... 14
South Shore Regulating Section ............. ... 17
South Shore Counting Station ............. . 19
PART IV: PROTOTYPE OPERATION ..... .............. . . 22
PART V: SUIMARY ........ ..................... ... 23
FIGURE 1
TABLES A THROUGH E
PHOTOGRAPHS 1 THROUGH 21
PLATES 1 THROUGH 43
ii
C0NVIRSIGt FACTORS, U.S. CUSTOIARY TO NITRIC (SI)
UNITS OF HKASUREMgYT
U.S. Customary units of measurement used in this report can be con-
verted to metric (SI) units as follows:
Multiply By To Obtain
feet 0.3048 metres
miles (U.S. statute) 1.609344 kilometres
square feet 0.092903 square metres
feet per second 0.3048 metres per second
feet per minute 0.3048 metres per minute
cubic feet per second 0.0283168 cubic metres per second
Tce zton For
DTIC H-~EL AV7Ai'ii'y odeDDiltributlion/
1AvnI1 aud/cr
S Dist ' c1::- IA/ t I
iii
MODIFICATION OF FISH LADDERS AT JOHN DAY DAM
COLUMBIA RIVER, OREGON AND WASHINGTON
Hydraulic Model Investigations
PART I: INTRODUCTION
The Prototype
1. John Day Dam is a multipurpose project located on the
Columbia River about 25 miles* upstrean from the city of The
Dalles, Oregon, at the head of the reservoir of The Dalles Dam
(figure 1). The reservoir extends slack water navigation upstream
77 miles to McNary Dan and provides 500,000 acre-feet of storage
for flood control between pool elevations 257 and 268**. The
project has a 20-bay spillway (design discharge 2,250,000 cfs), a
20-unit powerhouse (ultimate capacity 2,700,000 kilowatts), a
single-lift navigation lock having clear dimensions of 86 by 675
feet with a maximum lift of 113 feet, and facilities for passing
migratory fish upstream over the dam (plate 1). Additional details
of the project, especially the fish facilities, are given in Tech-
nical Report No. 103-1.
2. The fish facilities include two fish ladders--one near
each end of the dam-to pass the fish migrating on both sides of
the river (plate 1). Each ladder has a sloping section of cas-
cading pools, a flow regulating section, and a fish-counting and
identification station. The sloping section is a series of
10-foot-long by 24-foot-wide pools separated by vertical weirs
having overflow notches at each end and an orifice opening on the
floor beneath each overflow. Another orifice is provided on the
* A table of factors for converting British unit of measurement
to metric units is presented on page iii.** Elevations are in feet above mean sea level.
BRITISH COLUMBIA0 VANCOUVER CANADA1
UNITED STATESI
OLYMPIA
JOHN DAr aAN
z0columb/a Rvr.
0 PORTLAND
SAL EM '
IDAHO
C.) EUGENIE
CLOREGON BOISE*
LOCATION MAPMEOORO0 a 100
0 KLAMATHD FALLS SCALE IN MILES
Figure I
floor at the center of each weir. The center orifices are closed
but can be opened if the need for additional passage area is indi-
cated.
3. Initially the regulating section consisted of 19 nonover-
flow bulkheads with orifices. As the forebay pool fluctuated, the
section passed 50 to 90 percent of the discharge required for the
sloping section, and the remaining water required to maintain a
constant discharge was supplied through a floor diffuser at the
downstream end of the regulating section. Each bulkhead of the
regulating section had a submerged orifice near each wall. All
but two of the bulkheads had a third, higher orifice at the center
that operated under shallow submergence to aid the passage of
shallow-swimming fish such as shad and sockeye or blueback salmon.
The counting station of the north shore ladder was an older-style
station with a shallow horizontal counting board viewed from above
the water surface. The station was located between the floor dif-
fuser at the downstream end of the regulating section and the top
weir of the sloping section. The counting station of the south
shore ladder was a newer style with a vertical counting board
extended from the surface to 2 feet above the bottom and viewed
through a submerged window. The station was located within the
sloping section between weirs 193 and 194.
Need for Model Studies
4. After the first year of ladder operation, several fish-
passage problems were apparent. The shallow-swimming fish-- par-
ticularly the shad--were reluctant to pass through the regulating
sections. Although the high center orifices had been installed in
the bulkheads for the shallow swimmers, only a limited number of
fish were attracted to them. Before the second year of opera-
tion, the shallow orifices of the north shore regulating section
were enlarged to provide free-surface flow. Fish passage was
3
improved, but further improvement was needed. At the north shore
counting station, all species of fish were reluctant to pass over
the counting board. Of those that did pass over, many milled in
the diffuser pool just upstream and were reluctant to enter the
regulating section. Visibility for counting with the horizontal
counting board was reduced by surface disturbances and light
reflection. At the south shore counting station many shad milled
in the pool upstream from the counting board where upstream sur-
face flow led the shad away from the narrow overflows at the ends
of weir 194. In addition, fish identification at the south shore
counting board was hampered by fine bubbles entrained in the out-
flow of weir 194 and carried through the counting channel.
5. Model studies of the regulating sections and the counting
stations were made to develop revised designs that would create
hydraulic flow conditions conducive to the passage without delay
of all species. Special emphasis was placed on developing flow
conditions for easy, continuous passage of shad. Two of the regu-
lating section designs developed were studied further in full-size
models at the FERL at Bonneville Dam by the National Marine Fish-
eries Service to evaluate fish passage.
4
PAU II: THE MODEL
Description
6. Initially the 1:10-scale model reproduced the upstream nine
pools of the sloping section of the ladder, the counting station,
the regulating section, the exit channel through the dam, and a small
section of forebay of the north shore ladder. Following development
of the north shore regulating-section and counting-station designs,
the model was modified to reproduce both the south shore regulating
section with exit channel and forebay and the south shore counting
station with adjacent pools of the sloping section.
Facilities
7. Water used in the model was recirculated by a pump, and the
discharge was measured with a V-notch weir. Velocities were measured
with a midget current meter having a horizontal axis. Water surface
elevations were measured with piezometers and electronic point gages
in stilling wells, and depths were measured with staff gages. Tail-
water elevations were controlled by adjustable tailgates.
Scale Relationships
8. Model measurements were converted to prototype values using
equations of similitude based on the Froude model law. The following
model-to-prototype data equivalents were used:
Characteristic Dimension Model: Prototype
Length Lr 1:10
Area Ar = Lr 2 1:100
Velocity Vr = Lr 1/2 1:3.16
Discharge Qr - Lr 5/2 1:316.23
Pressure Pr a Lr 1:10
5
PAU III: TESTS AND RESULTS
North Shore Regulating Section
Plan A
9. The Plan A regulating section was a slot-orifice type
similar to that developed for Lower Granite Dam (plate 2). The
section had 19 pools to control flow with a forebay fluctuation of
11 feet. Pools were separated by non-overflow baffles, each having
a deep, narrow slot and a deep, submerged orifice (photograph 1).
The drops in water surface from pool to pool were to be approxi-
mately equal with an average maximum drop of 1.0 foot and a mini-
mum drop of 0.5 foot. Nineteen pools were required to meet the
criteria with the maximum forebay but this number was excessive
with the minimum forebay. With low forebay levels, the head drop
criteria could be met by diverting flow around the seven upstream
baffles and through the bypass channel adjacent to them. When not
in use, the channel was bulkheaded at the upstream end and fish
entry was blocked by a screen at the downstream end (photograph I).
10. Flow conditions in the Plan A pools were not satisfac-
tory, and the drops in head varied from 0.85 to 1.14 feet with
maximum forebay and from 0.31 to 0.92 feet with minimum forebay.
The need for modification of pool shape to create a better flow
pattern and of slot sizes to create a more uniform head drop was
indicated. With a high forebay, the slot flow short-circuited
across all the pools and utilized less than half of the pool
volume for fish passage and efficient energy dissipation (photo-
graph 2). The orifice flow impacted against the downstream baffle
and caused a boil that would attract shad and other shallow swim-
mers into a dead end corner. A very turbulent eddy occurred in the
upstream right corner of the pools adjacent to the slot inflow, and
a vertical upwelling occurred along the face of the left panel of
the upstream baffles. The upwelling would attract shallow-swimming
6
A1
fish to the baffle rather than to the slot. Outflow from the down-
stream slot (baffle 249) was a concentrated jet that extended into
the counting station (photograph 2). With low forebay levels, the
flow pattern was satisfactory and the bypass channel functioned as
designed. When the channel was open and baffles 261 to 267 were
not in use, the right half of pool 260 at the downstream end of the
channel had a large low-velocity eddy that might be a milling area
for shad. Closing the orifices eliminated the boil created by the
orifice jets; however, the drop in head from pool to pool with the
maximum forebay increased to a variation of 0.83 to 1.33 feet. A
large 45-degree fillet in the upstream right corner of pools 250
through 259 eliminated the eddy in that corner and directed the
slot jets along the walls of the right side of the pools.
Plan B
11. The Plan B design (plate 3) increased the size of all
slots except for slot 267. Large 45-degree fillets were added to
the upstream right corners of pools 249 through 259. The slots in
baffles 261 through 267 were moved to the left side, and the ori-
fices were moved to the right side. The two baffles in the exit
channel through the non-overflow dam were changed to single slot
baffles. Baffle 249 was changed from a slot-orifice design to a
modification of the existing orifice design.
12. Flow conditions improved with Plan B but were still not
fully satisfactory (photograph 3). In general, flow was satisfac-
tory in the pools downstream from the bypass but not in the pools
adjacent to the bypass. The large 45-degree fillets in pools 250
through 259 were effective in eliminating the eddy in that corner
and initiating an S-pattern of flow that utilized most of the
pool. In the other pools in which such a fillet would have blocked
the orifice, the slot flow short-circuited across the pools as in
7
Plan A. At the downstrem wall of the pools the orifice flow
caused intermittent boils which were considered acceptable but not
desirable. The single slots in baffles 268 and 269 in the exit
channel along with a wall deflector downstream from the baffles
created a more distinct attraction flow in the channel. Outflow
of baffle 249 was also improved. Surface flow attraction was
created along both walls of the counting station exit pool from
the baffle to the counting channel. The drops in head were more
nearly uniform with the revised slot sizes.
Plan C
13. The bypass of baffles 261 through 267 in Plans A and B
was hydraulically satisfactory; however, a simpler, more automatic
means of operation with low forebays was desirable because of
operational problems such as clearing fish from the bypass during
closure of the bypass. This was achieved in Plan C with full-width
baffles throughout the section and removable sills in the slots of
baffles 263 through 267. The sills were designed to be out of the
flow with forebay elevation 257 through 262. Baffle 249 was the
.ame as in Plan B except that the top left orifice, which func-
tioned as a weir, was reproportioned. Baffles 250 through 267 were
the same as the slot-orifice baffles 250 through 260 of Plan B.
The slot widths and sill heights were adjusted to produce nearly
uniform head drops with maximum forebay pool. Baffles 268 and 269
in the exit channel were unchanged from Plan B. Details of Plan C
are shown in photograph 4 and on plate 4.
14. Plan C functioned satisfactorily in the model, but the
right side of the pools was very turbulent with the higher fore-
bays (photograph 5). The turbulence and, according to some
observers, the 8- to 9-fps velocities at the slots with the 1-foot
drops in head were thought to be excessive for easy passage of
8
shad. However, tests of six full-scale pools in the FEEL showed
that shad and salmonoids would pass through the pools without
delay or difficulty.
15. The slot-orifice flow of Plan C created head drops vary-
ing from 0.04 to 1.04 feet, which were considered acceptable
because strong flow patterns occurred in all pools and energy
carry-through produced accompanying slot velocities of 2.1 to 8.4
fps (table A and plates 5A through 6B). The regulating section
discharge varied from 18.9 to 85.0 cfs. These discharges were
23 to 103 percent of the desired ladder discharge for a 12-inch
head on the weirs (82.2 cfs) and were also considered acceptable.
The maximum discharge would create a head of 12.8 inches on the
ladder weirs. The removable sills functioned well. Flow condi-
tions were good with the removable sills either in or out with a
changeover at forebay elevation 261 to 263 (plate 6A and 6B and
tables A and B).
16. Although the orifice flow of Plan C did not appear objec-
tionable in the 1:10-scale model, full-scale model tests at the
FElL revealed that with all of the orifices located on the floor,
the orifice jets switched back and forth and from side to side
causing intermittent boiling at the next downstrean baffle. Due
to this condition, tests with the orifices closed were made at
both laboratories. The flow condition in the model with the ori-
fices closed (slot flow only) is shown in photograph 6, and flow
data are given in table B and on plates 7A through 8B. In general,
flow conditions were similar to those with slot and orifice flow.
With slot flow only, ladder discharges decreased and most slot
velocities were slightly lower. Drops in head varied from 0.04 to
1.06 feet with accompanying slot velocities of 1.9 to 8.3 fps.
Discharges varied from 16.3 to 72.4 cfs-20 to 88 percent of the
ladder discharge for a 12-inch head on the weirs. Turbulence in
the right side of the pools was about the sme as occurred with
9
the orifices open. With the maximum forebay and slot flow only, a
boil occurred in the upstream left corner of pool 263 (plate 7A).
A rolling flow occurred in that corner of the other pools (photo-
graph 6). In the FERL tests with slot flow only, shad and salmon
passed through the full-scale pools without difficulty or delay.
Representatives of the Corps and the fisheries agencies verbally
concurred that the degree of acceptance by shad would determine
the acceptability of the design; by this criterion Plan C was
acceptable.
17. Due to turbulence and the objection of some to slot velo-
cities of 8 fps, other improvement of flow condition with Plan C
besides elimination of orifice flow was sought. When the orifices
were closed, removal of the 18-inch fins near the orifices caused
a slightly improved and less turbulent flow pattern in the left
side of the pools (photograph 7 and plate 9). Also, narrowing the
pools by moving the left wall nearer the slot decreased the size
of the large eddy in the left side of the pools and caused a more
distant flow path to develop. The rolling flow along the left
side of the upstream wall was greatly reduced and velocities
increased because of the loss of dissipation area. Flow condi-
tions improved as the pools were narrowed until the walls were
moved in approximately 8 feet. With pools narrower than 8 feet,
boiling occurred along the left wall. The improvement did not
appear to warrant the cost of narrowing the existing prototype
ladder section. Large fillets in the corners of the walls also
caused a slight, but not significant, improvement of flow condi-
tions.
Plan D
18. In attempting to develop better flow conditions, simpler
pool shapes designed for less head drop were studied. Details of
typical parts of Plan D as tested in preliminary studies are shown
10
on plate 10. The pool length was shortened from 16 to 10 feet to
permit additional pools to be located in the available space sub-
sequently lowering the maximum drop in head to 8 inches per pool.
The Hell's Gate slot and baffles used in earlier plans were
replaced with a simple slot perpendicular to the ladder centerline
to utilize the width of the ladder for energy dissipation of the
slot flow and a wall baffle to train the flow into an S-pattern in
the pool. In preliminary tests with pools of shallow and medium
depths, the flow conditions were good (plate 11); however, in the
deep pools having higher sills some instability of flow pattern
occurred with the larger drops in head (6 to 8 inches). To stabi-
lize the flow, fillets were required in all four corners of those
pools and orifices were required in the high sills to introduce
flow to the lower portion of the pools. With low head drops, the
S-pattern did not form in the deeper pools and there was no dis-
tinct attraction path through the pools. Slotted longitudinal
(parallel with flow) baffle walls, extending across the pools
between the slots in the lateral baffles (photograph 8), were
required to maintain a desirable flow pattern with all flows
(2- to 8-inch drops in head). Further development of Plan D was
halted in favor of a new design--Plan E.
Plan E, Final Design
19. Plan E was the result of a progressive change in pool
shape and flow criteria from the Hell's Gate type slot-orifice baf-
fle, with a maximum head drop of 1 foot and a low-flow bypass, to
a simpler slot baffle with a maximum average drop in head of
6 inches and removable sills. To permit regulation with the full
11 feet of forebay fluctuation with a maximum drop of 6 inches,
the number of typical pools was increased to 34 and their size was
decreased to approximately 11 by 15 feet. A minimum distance of 6
feet was maintained from corners to center of slots to assure ade-
quate alignment space for large fish. The two pools and baffles
11
268 and 269 in the exit channel were the same as those in Plan C.
The orifices in the Plan C baffle 249 at the downstream end of the
regulating section were modified for Plan D by closing the bottom
center orifice and replacing the two top orifices with three ori-
fices which operated as shallow slots. The two 1.5-foot fins on
the upstream face of the baffle were replaced by a single fin on
the right side. Details are shown in photograph 9 and on plate 12.
20. Flow conditions with Plan E were satisfactory in the model
and in 10 full-scale pools tested concurrently at the FERL. A con-
sistent, distinct, and continuous attraction path was formed by the
S-pattern flow in pool 249, along the walls from slot to slot in
pools I to 34, and from slot to slot in the exit channel. This
flow in the model and the same attraction flow along the walls in
full-scale pools 1 and 2 observed at the FERL are shown in photo-
graph 10. Slot velocities and minimum depths at the slots observed
in the model are listed in tables C and D; velocities and flow
directions are shown on plates 13A through 15. Due to the super-
elevated water surface caused by the circular flow pattern in the
pools, a representative water surface in the pools from which to
compute head drops could not be easily obtained. Since velocity
created by the head drop was the significant criterion, slot velo-
cities were substituted for head drops as an indicator of uniform
flow conditions from pool to pool and of conditions within accept-
able limits. The desired maximum average head drop of 6 inches
was represented by a theoretical slot velocity of 5.7 fps and,
with energy carry-through, by a slot velocity of approximately 7.0
fps.
21. With forebay elevation 268--the maximum and design forebay
pool-velocities at slots 1 to 35 varied from 5.8 to 6.9 fps and
those at the three slots of baffle 249 varied from 5.1 to 6.6 fps.
The velocities were acceptable in magnitude and uniformity. The
velocities at slots 268 and 269 were 4.6 and 4.0 fps, respectively,
12
and carried through the exit channel sufficiently to create a dis-
tinct attraction path from slot 35 to the forebay. The velocities
were not uniform with other forebay levels within this operating
range but had an acceptable magnitude (table C). Operation was
satisfactory both with and without the removable sills in place
with forebay levels 1 foot above and below the changeover eleva-
tion of 262. With all operating conditions the minimum passage
depth was greater than 3 feet (table D). The regulating section
discharge varied from 20.0 to 70.2 cfs-24 to 86 percent of the
total ladder discharge.
22. Fillets were required in certain corners to help turn the
flow and to prevent boiling or excessive rolling of the flow. The
need for the fillets (plate 12) was determined by observation in
the model. Afterwards, fillets of the same size were desired in
all corners for structural reasons. Tests showed that such fillets
were satisfactory and perhaps improved flow conditions slightly.
No noticeable change in slot velocities was found to occur; how-
ever, the overall increase in flow efficiency resulted in a 2k-per-
cent increase in discharge (from 70.2 to 72.0 cfs) with maximum
forebay elevation 268.
23. In order to facilitate shad passage, special attention
was given to flow in the right downstream corner of pool 35 at the
entrance to the exit channel. With higher discharges and deeper
flows, the flow moved to the corner of the surface and out along
the bottom; with lower discharges a large eddy formed. In either
case, shad that entered the area would be attracted out to the
main flow stream from slot 268 to the left wall of the pool (photo-
graph 10 and plates 13A through 15).
24. Two other special items were also studied--use of the
existing fins on baffle 249 and larger bevels on the edges of the
slots. The existing fins on baffle 249 were not satisfactory.
13
Flow buildup occurred on the left side of each fin causing exces-
sive outflow from the left slot and interference with the S-pattern
of flow through the pool (photograph 11). The new single fin near
the third point of the weir was needed to stabilize the S-pattern
(photograph 10). Bevels 3 or 6 inches long were not needed in
place of the standard 3/4-inch bevels on the edges of the slots.
In the even-numbered pools, flow conditions were the same with all
bevel sizes. In the odd-numbered pools, the eddy was slightly
less stable with the 3- or 6-inch bevels. Flow conditions with
the 6-inch bevels are shown on plate 16.
North Shore Counting Station
Plan A
25. The counting station in the north shore fish ladder was
located at the top of the sloping ladder section and immediately
downstream from the regulating section. The existing station,
which had a shallow horizontal counting board and viewing from
above the water, was to be replaced with one having a vertical
counting board and underwater viewing. The new counting station,
which was to be similar to that ',. the south shore ladder, was to
provide a greater range of depth for fish passage and better view-
ing for counting. Details of the initially proposed design are
shown on plate 16. After construction of the model, the proposed
width of the counting channel was reduced from 4 to 3 feet. This
change was simulated in the model by setting the adjustable count-
ing board at a maximum opening of 3 feet as shown on plate 17.
Because the station was to be built a year before the revised
regulating section, initial studies were made with the existing
regulating section (partially shown on plate 17). Afterwards the
station was studied with the different plans as the revised regu-
lating section was developed. The studies were principally con-
cerned with flow conditions for good fish attraction and passage
14
upstream and downstream of the counting board, self cleaning of
the trash rack, and flow conditions upstream of the board for min-
imum flow of air bubbles across the board. Good self cleaning of
the rack was especially desirable near the water surface where
weak shad might become trapped against the rack by the flow.
26. Observations of the self-cleaning characteristics of the
trashrack with three vane alignments are listed in table E. Vanes
aligned 90 degrees to the flow were the best, especially when all
the flow for the sloping ladder was introduced through the regulat-
ing section (maximum normal forebay). Vanes set 45 degrees to the
flow were almost as effective as the perpendicular vane. Vanes
parallel to the flow performed poorly. Larger discharges through
the regulating section caused more turbulence at the rack and aided
self cleaning. Throttling of the regulating gate to create greater
head drop across the counting board also aided self cleaning--less
flow passed through the rack and more flow swept across the rack to
the counting channel. None of the alignments readily shed debris
with the minimum forebay conditions (diffuser discharge of 37 cfs).
27. The flow patterns and velocities in the counting station
for the extreme operating conditions of maximum and minimum (zero)
diffuser flow, 3-inch and minimum head drop across the counting
board, and maximum (36-inch) and minimum (9-inch) board opening are
shown on plates 18 through 21 with the trashrack vanes 90 degrees
to the flow. The velocities were acceptable for fish attraction
and passage for all conditions, but the flow patterns were not
acceptable. With all conditions tested, an eddy with horizontal
and vertical flow directions occurred on the right side of the
section in the square corner formed by the upstream side of the
counting house. The eddy, which could have been a milling area
for shad, was eliminated by blocking off the corner with a diagonal
wall (plate 22). An eddy also occurred along the diagonal wall
downstream from the counting house. Although downstream flow
15
along the wall was preferable, the low-velocity return flow was
not considered objectionable. Good attraction flow to the count-
ing board existed along the edge of the eddy. The flow pattern
along the fish guides downstream from the counting board was gen-
erally good; however, with the minimum head drop condition across
the counting board, reverse flow existed at the very upstream end
of the guides at forebay elevation 265 (plates 23 and 24). When
the regulating gate was throttled to create a head drop of 2 inches
across the counting board, flow was into--rather than out of-most
of the guides. Deflectors in the bypass flow area on both sides
of the regulating gate eliminated the reverse flow at the upstream
end of the guides with forebay elevation 265 but had little affect
on the reverse flow when the gate was throttled (plate 25). Set-
ting the trashrack vanes at 45 degrees to the flow had the same
effect as the deflectors (plate 26). As on the other side by the
diagonal wall, the desired flow conditions along the guides were
not obtained with all operating conditons but were considered
acceptable. When an eddy formed along the guides, the velocities
in it were low and good attraction flow to the counting board
occurred along the edge of the guide. The top orifices of baffle
249, which were upstream from the counting station, functioned as
weirs with the surface outflow entraining air. Although this model
did not reproduce bubble flow to scale, the surface turbulence of
the outflow in the model indicated that the entrained air would be
carried through the short diffuser pool and to the counting chan-
nel. The bubbles were not desirable because they would interfere
with counting.
28. Along with the development of the new regulating section,
changes were made in the design of the vertical counting station.
To provide a longer diffuser pool for bubble dissipation, the
Plan C station that evolved was 8 feet farther downstream than
that of Plan A. A diagonal wall was placed upstream from the
counting house to create a positive attraction flow along the
16
wall. The trashrack vanes were placed 45 degrees to the flow for
best overall flow conditions and structural simplicity. The top
13 to 15 inches of flow at the trashrack were blocked by a 2-foot-
high solid plate on the vanes to provide a smooth surface for pas-
sage of floating debris along the rack. A low sill was placed
across the center half of the pool at the downstream edge of the
diffuser to prevent upstream flow from developing along the floor.
Details of the plan are shown in photograph 12 and on plate 27.
29. Plates 28 and 29 show flow patterns and velocities that
existed in the Plan C counting station with the Plan E regulating
section with the minimum drop in head across the counting board
and forebay elevations 257 and 268. The flow conditions existing
with both forebay elevations are also shown in photograph 13. The
counting station functioned well. With both extremes of operating
conditions, attraction flow patterns and velocities were good.
Floating debris passed readily along the trashrack. The surface
turbulence indicated that most of the entrained air should be
expelled in the longer diffuser pool and would not enter the
counting station.
South Shore Regulating Section
Adapted Plan
30. The Plan E regulating section developed for the north
shore ladder had to be modified for use in the south shore fish
ladder since several aspects were different. The diffuser pool
(pool 248) at the downstream end of the south shore regulating
section was 16 feet long and had no counting station since it was
located in pool 193 of the sloping ladder. The upstream end of
the regulating section was 1.42 feet wider than that of the north
shore ladder. The exit channel was narrower and had no baffles.
The right half of the old regulating baffle section downstream
17
from baffle 265 was to be used as the walls of the new pools;
therefore, pool 249 was to be 2.75 feet shorter than that devel-
oped for the north shore ladder and pools 29 and 30 were to be
1.92 feet longer than those developed for the north shore ladder.
Details of the modifications at each end of the section to adapt
Plan E to the south shore ladder are shown on plate 30. The model
was modified to include all of the special features shown on plate
30 except the extra width of pools 28 through 35.
31. Baffle 249 was developed to have two 18- by 18-inch ori-
fices on the floor and two higher orifices against the walls to
function as submerged weirs (plate 30). The baffle at the down-
stream end of the exit channels had a 15-inch slot against the
left wall to create an attraction path along the wall to slot 35.
Flow conditions in the modified pools were satisfactory. Veloci-
ties and flow patterns in the pools with maximum and minimum fore-
bay are shown in photograph 14 and on plates 31 and 32. With
maximum forebay (elevation 268), velocities at slots 1 through 35
varied 5.3 to 6.7 fps and the velocity at slot 36 was 3.9 fps.
32. The tops of the existing baffles that were to be utilized
in the modified regulating section were stiffening beams that
overhung the baffles on the upstream side. The new baffles at
slots 31, 33, and 35 were to have stiffening beams that overhung
the downstream side of the downstream wall. With forebay eleva-
tion 267, only the beam in pool 30 was in the water. The water
just touched the underside of the left two-thirds of the beam and
rode up a maximum height of 0.3 foot on the right one-third. With
forebay elevation 268, water was on the beams in pools 20, 22, 4,
and 26 through 34 (photograph 15); however, the flow pattern was
not disturbed by the shallow submergence of the beams. The beamsdid not appear to interfere with fish passage.
18
33. Fish passage in the prototype south shore ladder was to be
evaluated after the modification. During those prototype observa-
tions, a temporary underwater counting station was to be installed
at the upstream edge of slot 1. Flow around the proposed temporary
station was observed in the model and revealed that the station
would not disrupt the attraction path along the walls of pool 1 or
create any disruptive flow pattern (photograph 16).
South Shore Counting Station
Original Weir 194
34. The existing south shore counting station, located in pool
193 of the sloping ladder section, was ineffective. Steelhead
crossing the counting board fell back through it instead of enter-
ing the pool upstream, while shad entering the pool milled about
and were reluctant to cross to weir 194. Apparently the high
level of turbulence and the adverse flow direction in the upper
three-quarters of the depth repelled the fish. The flow was highly
entrained with air and the bubbles passing across the counting
board made observation of the fish difficult. Studies to improve
the flow pattern downstream from weir 194 and to create flow that
would entrain less air were studied in the model. Details of the
original weir 194, the pool downstream, and the counting station
are shown in photograph 17 and on plate 33. The flow pattern in
pool 194 and the adverse pattern in the upstream pool of the count-
ing station are shown in photograph 17 and on plate 34.
Plan A Modification
35. In Plan A, weir 194 was modified to include deep notches
in the weir at each wall and a shallow notch in the center of the
weir with an orifice in the flow beneath the center notch. A baf-
fle was installed on the wall downstream from the right notch to
19
deflect the flow toward the counting channel. Baffles were placed
on the floor of pool 194 to disperse the outflow jets from the
orifices of weir 195. The upper part of the vanes of the trashrack
were covered with a solid plate which projected 1.5 feet into the
water. Details of the modified weir (Plan A) are shown in photo-
graph 18 and on plate 35. The modification created satisfactory
velocities and flow patterns with both a 10- and 12-inch head on
the weir (plates 36 and 37). Good attraction paths occurred
through the full depth of the pool from the counting channel to
both the right and center notches but only near the surface of the
pool to the left notch. The absence of a deep attraction path to
the left notch was considered acceptable since deep attraction
paths existed to the other two notches. The baffles were needed
to help create and stabilize the flow pattern. Although the deep
notches created shooting flow that should entrain less air than
the plunging flow of the original notches, the level of turbulence
was high (photograph 18) and might have carried entrained air into
the counting channel.
Plan A-1 Modification
36. In an attempt to create a larger pool upstream from the
counting station to better dissipate the entrained air bubbles,
weir 194 was removed (photograph 19) and a new weir was installed
upstream to create the required head drop. Unacceptable attrac-
tion flow occurred in most of the enlarged pool (photograph 19 and
plate 38). Flow conditions were improved by modifying weir 195 to
be similar to the Plan A modification of weir 194 (plate 39). Good
velocities and attraction paths occurred in the full depth through
the center of the pool, near the right wall of the pool, and near
the surface along the left wall of the pool (photograph 20 and
plate 40). However, surface turbulence indicated that air would
still be carried into the counting channel.
20
Plan B (Final Design) Modification
37. Plans A and A-1 both resulted in almost identical improve-
ments in flow conditions; however, Plan A was selected for further
study because it involved modifying only one weir. In Plan B (the
final design which was constructed in the prototype) the lower part
of the Plan A left notch was raised and widened. All of the vanes
in the 2.5-foot section of the trashrack near the wall and the
upper 1.5 feet of those in the adjacent 3.5-foot section of the
trashrack were blocked with solid plates. The remaining portion of
the trashrack was left open (photograph 21 and plate 41). Flow
conditions with the Plan B modification were acceptable (photograph
21 and plates 42 and 43), and attraction flow along the trashrack
was improved slightly over Plan A.
21
PART IV: PROTOTYPE OPERATION
38. Modifications developed in the model studies were incor-
porated in the prototype south and north shore fish ladders in the
winters of 1970-71 and 1971-72, respectively. The south shore
ladder regulating section was evaluated by the National Marine
Fisheries Service during the sumer of 1971 and performed satis-
factorily.* Prototype operation, as evidenced in the model, indi-
cates that flow from upstream of weir 194 is highly saturated with
bubbles which remain in suspension and pass through the counting
channel.
* Charles R. Weaver, Clark S. Thompson, and Frank J. Ossiander,
"Evaluation of Fish Passage in the Vertical Slot Regulating Section
of the South Shore Ladder at John Day Dam," National Marine Fisher-
ies Service, June 1972.
22
V: SUMARY
39. The flow regulating sections and fish-counting stations at
both the north and south shore fish ladders at John Day Dam were
modified to more effectively pass shallow-swimming fish such as
shad and to improve fish counting and identification. A 1:10-scale
model was used in modifying the Hell's Gate slot-orifice type regu-
lating section into a slot-only design having a maximum head drop
of approximately 6 inches per pool. The design was initially
developed for the north shore ladder and adapted for the south
shore ladder. The effectiveness of the design in passing fish was
verified in full-scale tests at a fisheries laboratory and then
later in the prototype. A vertical counting station was developed
for the north shore ladder to replace a horizontal counting sta-
tion. The station was developed for use with the then existing
regulating section and with the modified section. The weir
upstream from the south shore counting station was modified to
create flow patterns that would attract fish to pass quickly from
the counting station and continue on upstream.
23
TABLE A
EADS ON BAFFLES
North Shore Regulating Section, Slot-Orifice Plan C
Slot and Orifice Flow
Forebay Elevation in Feet-NSL
268 265 263 262 261 263 262 261 257
Slot Sills of Baffles 263 to 267Baffle -
In Place RemovedNumber
Discharge in CFS
85.0 61.0 45.2 37.8 31.4 j 61.6 54T I 47.7T 18.9
Head on Baffle in Feet
249 0.64 0.37 0.19 0.15 0.10 0.38 0.31 0.23 O.O4250 0.85 0.52 0.31 0.22 0.15 0.52 0.42 0.33 0.05251 1.01 0.68 0.45 0.32 0.24 0.69 0.59 o.49 O.10252 1.00 0.71 0.52 o.41 0.30 0.7-4 0.65 0.55 0.12253 1.O4 0.77 0.56 o.46 0.36 0.76 0.67 0.60 0.17
254 0.98 0.70 0.52 o.41 0.33 0.71 0.63 0.54 0.14255 1.02 o.84 0.68 0.59 0.51 0.85 0.79 0.72 0.29256 1.02 0.85 0.72 0.63 0.54 0.85 0.79 0.74 0.36257 1.02 0.87 0.75 0.69 0.61 0.88 0.82 0.76 0.64258 0.97 0.92 0.79 0.77 0.70 0.92 0.85 0.81 0.81
259 1.03 0.90 0.83 0.75 0.74 0.90 0.85 0.83 0.79260 1.O4 0.95 0.87 0.87 0.80 0.94 0.95 0.89 0.87261 o.98 0.91 0.88 0.85 o.84 0.92 0.92 0.89 o.86262 0.93 0.86 0.84 0.83 0.78 0.87 0.85 o.84 0.80
263 0.94 0.89 0.87 0.82 0.86 0.148 o.45 0.42 0.21264 0.92 0.90 0.90 0.92 0.84 o.46 0.42 0.37 0.27265 0.914 0.94 0.95 0.97 1.02 0.43 0.141 0.141 0.25266 0.93 0.89 0.92 0.93 o.86 0.39 0.36 0.35 0.24267 0.93 0.92 0.96 0.97 1.04 0.32 0.29 0.26 0.23
268 0.38 0.30 0.24 0.21 0.18 0.54 0.52 0.51 0.38269 0..0 0.31 0.25 0.23 0.20 O.45 0.46 0.46 0.38
NOTES: 1. Details of regulating section shown on plate 4.2. All orifices of baffle 249 open.
TABLE A
TAIBL 5
BADS ON BAFFLIS
North Shore Regulating Section, Slot-Orifice Plan C
Slot Flow Only
Forebay Elevation in Feet-MSL
268 265 263 262 261 263 262 261 257
Slot Sills of Baffles 263 to 267Baffle
In Place RemovedNumber
Discharge in CFS
72.4 48.7 33.6 25.7 18.9 52.5 145.2 38.7 16.3
Head on Baffle in Feet
249 0.52 0.27 0.14 0.09 0.04 0.30 0.23 0.18 0.04250 1.06 0.57 0.28 0.18 0.11 0.61 0.50 0.37 0.08251 1.03 0.65 0.38 0.26 0.15 0.72 0.58 0.49 0.11252 1.03 0.73 0.47 0.32 0.20 0.79 0.68 0.57 0.15253 1.03 0.78 0.58 0.47 0.32 0.79 0.74 0.64 0.26
254 0.99 0.71 0.53 0.39 0.27 0.75 0.67 0.61 0.23255 1.05 0.89 0.73 0.65 0.54 0.91 0.87 0.80 0.47256 1.03 0.90 0.78 0.68 0.59 0.93 0.86 0.83 0.53257 1.01 0.91 0.80 0.76 0.69 0.93 0.87 0.82 0.66258 n.99 0.94 0.86 0.83 0.83 0.94 0.90 0.87 0.82
259 1.03 0.93 0.83 0.81 0.76 0.95 0.94 0.88 0.75260 1.O4 0.98 0.93 0.91 0.93 0.99 0.97 0.95 0.93261 0.99 o.94 0.91 0.88 0.88 0.94 0.93 0.92 0.89262 0.92 0.87 0.86 0.82 0.81 0.86 0.84 0.85 0.79
263 0.95 0.89 0.88 0.86 0.86 0.43 0.41 0.36 o.16264 0.93 0.92 0.93 0.95 0.93 0.42 0.38 0.33 0.15265 0.97 o.94 1.00 1.O4 1.03 0.39 0.36 0.35 o.16266 0.93 0.88 0.92 o.96 0.98 0.38 0.34 0.32 0.14267 o.94 0.92 o.94 0.95 0.95 0.30 0.29 0.26 0.16
268 0.27 0.17 0.11 0.09 0.05 0.44 0.33 0.29 0.24269 0.29 0.21 o.14 0.10 0.08 0.23 0.31 0.31 0.28
NOTES: 1. Details of regulating section shown on plate 4.2. Side orifices of baffle 249 open; center
orifice closed.
TABLE B
0 LA Cu~ N CVm I\ D O\ 00(Y) 0n\ t- mCCuko %D0 - 40 -
Cuj 0 C CC% C CC C l ;CA (AU If\~ U Lt\U\Cuj
H V) (0 (fl~ L- t- -4 0\ _ D0 0 co 0\O ~a a\C\ C\ co \ \
Cuj -UL ~ -- U U% LC\ U'.C U U" Lt U.\ LC U \ W\ tP L(\ L(\ Lr\ tA
0
Cuj VH LA;. Vf 'A U V;%'.O \O j\10\D\D\ Iz 1 1 1
U)'
4J) ('1 U' U' ~L\ H m ULr UNO CP\ 00-O\..$C0u -t Y) C\ jC CYuC' () zz\4
4o S) Cu CY 0)C 'tLfUL ~ Or\lO ~ f\\''O ~ " \
-40 U'\
Cul
1J 1- -3_r 04~ NHW .C\ rCur4 (Y)'k' C'\ C0 \ U'O \00 0 0 m WN --~4- \,. 0 Wi *.
as Cuj H r -I W.J 1 C C C C C P;(") ((1;'-- 4LC U' U(\Lt\LE- 1.cf . Cu -4
u n H .r 0
? 1-4
> 104 N~ Cu H Cuj -=r \0 \ C\HriCur\10 aCY\ uj0 \.O\D 0 Q~ C)C) 4-t ': _tC \ u-\E-0 41 S) \fl r.4 .
E- Cu C/ q ) t: C C Cum(';1; 1;'A c; Z;f 1 tr\'. U 'Ut AL\ U U U U00 Cuj
mY __r O\Df ('1w\ t- Cu Cuj \0 t- \0 fn M' U'.4- \D Lr~~. \D l 0~ C\ M a'
41WIU C y Lt4U '~COCO0f V;-44'- a'HH WCW U AVU A'CO
zCuj \40 --- 4 U' U' U' U' U\ U' U' V' \ \ZO"\ \\0 \Z0 \Z U V"'
co C \0 H CC) --s \0 -4,(-t--- Y Z - t-t-- t- _- _- \Z__\0 .
Cu 0 \O'U 0\\ \3lflf 0\16 0 \OD\\O
0 .t 0 mi _Si v4C-UN \0 t-0C\a'0 Cu('1V _tUN \ Ot-CC) a\0Hl H H H H H 4C
Cu
mC\\0 -4 r-40 4Hr- Z00% \ 0 O mmcra% O\O\a\O C)th-
ir\ ir\ ir\ U\ U"\ ir\ U-\ Lf\ Ut r v l f\V ir\ ir\ % ir\ W\ U _4 irs _r _r ir\ -Z -. -;r_: __r irs.
0
44
0
414
-4 0
41
* .. . .. -4 0J44 M
4)
irsU Wsf't' U"\sU"'s '\ L\ N A L(' ir\U'sL V\U'Ws W U V\L('sW's t\ LisL ' \ L(V\ C' U41EU4j
E0 I44
>1g 0OCsHH CsJ !-!01 C9 J -! C -! Ca .-4c J H '19 O' O'-? -4 '00' \ _
O's\\DOD'0 \D 0'0 Lf's5' t u\\sD's0\ Lr \0O\0 LI\ N s U Lt's t' U~Li'sLi'sLir \ V C Aj -
u -4____ ___ ___ ____ ___ ___ ___ ____ ___ ___ __0 to~4
'0\O'0\.0'0 ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~ - 41s\'' 0O 000 I'\'s'Ot 0tss'00 4
~~~~~~~~~~~~~~~~~~~~~ o)*' s '~ ' - ' n? L' s -)0s0 ~ 4(Ui.?L' ',-4-te4H'sJC'sC'CU 'U~O~n i v~fl~ ''>
TABL C~
TABLE D
MINIMUM DEPTHS
North Shore Regulating Section, Slot Plan I
Forebay Elevation in Feet-MSL
262 261 257
Removable SillsSlot No.
In In Out
Tailvater Depth at Slot in Feet
Floor Sill Floor Sill Floor Sill
1 5.6 5.5 5.5
10 4.3 4.0 3.911 4.2 3.9 3.812 4.3 3.8 3.713 4.2 3.7 3.6
14 h.3 3.8 3.615 4.3 3.7 3.616 4.4 3.8 3.617 4.4 3.7 3.618 4.4 3.8 3.6
19 h.5 4.2 3.7 3.4 3.6 3.320 4.8 4.3 4.o 3.5 3.8 3.321 5.0 4.2 4.2 3.4 4.0 3.222 5.3 4.3 4.5 3.5 4.3 3.323 5.5 4.3 h.7 3.5 4.5 3.3
31 8.8 4.9 7.9 4.0 4.932 9.3 4.6 8.5 3.8 5.233 9.7 4.6 8.8 3.7 5.134 10.3 4.8 9.4 3.9 5.435 10.9 5.4 10.0 4.5 5.4
NOTES: Details of regulating section shown on plate 12.
1.&. D
TABLE 3
SELF-CLEANING CHARACTI3R TICS
North Shore Countinmg StatLon Trash Rack
Vane Discharges - CFS Read DropSelf-cleanin
Alignment acrossRegulating Time - Minutes
to Flow Section- Counting Board
Parallel 86 0 Minimum Trash retainedover 16 minutes
45 degrees 11.0
90 degrees 4.2
Parallel 86 0 3 in. 1.9
45 degrees 1.7
90 degrees 1.5
Parallel 45 37 Minimum Trash retained
45 degrees 70 percent oftrash retainedover 30 minutes
90 degrees 70 percent oftrash retainedover 30 minutes
Parallel 45 37 3 in. 8.2
45 degrees 5.9
90 degrees 7.3
NOTES: 1. Time was average time of 3 to 5 tests in whichapproximately 20 pieces of trash 5/8- by 2 1/2- by 15in. were spread across the trash rack at the watersurface at the beginning of each test.
2. Location of the trash rack is shown on plate 17.
TABLE E
41
.0
'0.
1 )
04
or
V> 0
0
0 CW
-4 r-~
1>1
(0.0
0 4)
41
'lU
0
00064
I0
0 0
41
ci)
C144
0.
ci)
C',4
0
41
0'
UlU444
-44-
a C'4
'0
44
0n
(Na .- 441
W > 1
0 a
0 C:
4.)
('I
(N.k
0
"o -1 3
4
o 0
4-))
00
Q) 0
C4 .0W-
-4
4-4
4-J
100
4-0)
E-4 r
"4
-4
131
-4
44
0 )
4j
4.)
'-441.
0TV-
L
- .-
4 0
(o
-~ w-
0 o
~Io
i(
. .. . ,, , , .. . ... .. ... .. . .. ... .... . . . . .. . . . • .. . . .. . . . . . . .
'U)
41
0A-'-
0-
Fly
AWL= -
44
0
x
0"-4
41
C14
4o
W- AS-
cN .-4
0))0U .0
14 '44
AS 0 0
0 a)f1 LP
0 (a
4
'-4
0
>4
U)
-4
U, 0-1 w N
0 4)
0 to
0
- 44
- 00
4J 4
* 0
4.) 0
o u
4)
-4-
0 u0LA 4
' 0 4~C.,4
.4j 0o 0'-4 P4 0C2 -4
"-4
002
-14
'-44C14 -u
Q0
4 J
-4 4
04
4
0P4
P4
0
4)0
4
to -I 4
0 u cC14 U) .4
4.)0
C
0
a)wl
040
0 0)
ON
w0 (01 S.0
(44
-1
x
CD0
'0 -1
-4
'00
K ('N
00
04 0
.4-J
4 J
C-4
-4140
0-
04
U,
-4*0
4.)
-4
44
on w
o 0~rd -4
-4Ln.-
o 0P
0-.)
Ln
NU
('1
M-4-
0 0
('4
r-4
-4
040
LA
0
0'
-4
4 J
CzN
-Io C04 -4
>4
.0 0r14
Z4 44
C14
0-a
41-M0 c
004
0 -
H
4JJ
IP
0~-4 0
0)40
44 0'a
$,x-1 0)-0 .1-i
4 z4J1-l 00)
Cn I
%.0CN
0
-44J
V))
'4-4-3
44 0
0J -4
a 0)-4)
44
0440e
04
0
ie
0
4-)
.-
14
to44
Od0w
0 d
41i
C 0 A
.- 4 .4 0P4'
4
0
00oQ
0
0
-4 4
CT4C
0~04.a0
co4
e-400
0N -441
0 01-1
U)
.41
0
C
04
-4J
01.0
ci 0
w 4
0 .0
x 0
(Jr,~
-1
0 4)
0 $4
0
to 0
-4
(a
00
'UC4.
ro0
o .00 4
Ike'04a)
(n2
14)
41Lm ~0(V*)O
w'~ 0
4-4 4J1
0(12
~44
4)
'0
0 -'-
0u
0
0 0I
00
12~
>0
4 J 4J
u
'-1
(U
a-'
ul-4
w1
44
'-1
U)
J44
4 0
04
0
wwmw
0
0
* .Q
- 41
too
0'
414
4J 0
ji0
00l
44!44.)
.)
0
('a
41
041)0
/ F W~A
r_ 1*-A 0x~~b( SPILLWAY
I, S, rOR5 f45,, ITrF
.cl55 FISH LADDER
-' I OISCeARGE )tFkET
K -1
A-111 A7,P
6,A,
VOuNOARV- I -
I, j, N
SCAI M (Eam 0 M 4
161
<'~~' W E I "-j E
K A
1.I A
o PROEC LAYOUT
-~ *PLATE.I
580 2-0SPIEZOMTER - " _
"1 IL4 PFL E f6 0C' -- 28' 0
PLAN
'CALE
26C
SECTION A-A
- -i-----' I
p~.VARIES T'1 CC
BAFFLES 249 TO 260 BAFFLES 261 TO 267
DOWNSTREAM ELEVATIONS
8,A- 1S 261 T0 ,' L "
6-1 ,
60 4'- 0
SECTION B-B SECTION C-C
SCALE0 $ tO 15 20
/M AaBAL.olFu
_ I.8-o ,9-0
L AS *:' u'~ * I , " *1SLOT DETAILS
- ~'sso--?-- I'5BAFFLE SLOT SILL SLOTA' ~ -~ 3NO. HEIGHT WIDTH&ULKHEADO
. .249" 2 6' ."
'0". UPSTREAM 1 6,?6FACE OF 04M 2CC C-' -6
000 252 1-' -6,
253 4 -662'-.0 2- 4 I-8 '
255 2-~ -
256 2 - -4
2'7 2 b 4
2 "1- - 26'3 5 B" :
26: . 3
262 4 . -3
BAFFLE 263 4-8 3265 267 264 5- - 3
265 !-c'* .*266 6 -8 -
VARIES
T0 267 TYPICAL ORIFICE
2-3
7 REGULATING SECTIONDETAIL A lSLOT-ORIFICE PLAN A
fNORTH SORE FISH LADDER
2 I 2 3 ,4 5r
PLATE 2,
3J
_ . , --... . _ .. .. . . . ... . . . . .. ..... .... .. .
.... .... II ---- I IREGULATING SETI ON I .. I ill
-, .-P0..
"'. ... : , -,, , -._ "- " - " '" " :
PLAN
26 65
SECTION A-A
,,_,_ _ .__ _. ___ _'__ _. ..
BAFFLES 250 TO 260 BAFFLES 261 TO 267
DOWNSTREAM ELEVATIONS
- A 84-LfS 2(-1 %
SECTION B-B SECTION C-C
'i, AL
03 M~
• I
" :' SLOT DETAILS"BAFLE SLOT SILL SLOT
N LE 25 II 9 - '<~ b~wNO. HE,GHT WIDTH
Az
FACE OF DAY.-" I : .
9'F l D E T A IL
265 "2b7
269
25 -N4 -IDwH
TO 267 TYPICAL ORIFICE %.
o. :. 6 -0" 1-"
-D -E
', ' L REGULATING SECTIOND I SLOT-ORIFICE PLAN B
0$ F' DETAIL A .
NORTH SHORIF F .H L ADDER
S{ A, t
PLATE 3
IIIIf III 2II r66 i-1 i 'l i ii i i
SPIEZOMEER
-REMOVA8LE SILLS :
-- BAFFL E5 P63 TO 267
NI 9 BAF I 16 -0" *288"- C,
~!
PLAN
SCALF
260 2b5
BAFF E255249 T 1fl
ELEV 2 , 032
SECTION A-A
-4-6
F " *OAIIICBi B
. TYPICAL ORIFICE
BAFFLES 250 TO 267
BAFFLES 250 TO 263 -24'-0'
BAFFLES 264 TO 267z22'-7"
6 " -3" ! " -.O
4-4 - S
(- ". 8
SECTION B-BA
SCALE
"5 1) 5 ?o 25FT S.A I
9-0"
5K5'58-5 - 9 0
K 9 . 2 A
70 SLOT DETAILSBA-FFLE 0" 1 BAFFLE SLOTSILL SLOT'I CHAMFER SCAM No. HEIGHT WIDTH
SC .-
REOVBL SLL 5:B2H '-5 -0 "
l5 268 0 ' ; 2 -
BAFFL ES 263 TO 267 0. SE TA'
r -I
62 -"'D-
UPS "REA 1 2" _FACE OF DM2. '258
100 FT DETAIL A 261 4-262 3-2632 3 6 -3
B F BAFFLE 264 4 31L265 267 268 269 265 5 32 -
266 6 ' -FLOW 267 7- 3 1
268 3'- 2-'
1ELEV 2505
0-~
TYPIAFLLOWORIFIC
CHAMFER
BAFFLE 249
SECTION C-C SECTION O-O
DETAIL S REGULATING SECTION
SLOT- ORIFICE PLAN CSCALE NORTH SHORE FISH LADDER
1 2_______ 3__________
PLATE 4/o/
WI 7. -w
Ny ll l l l l liii i .. ,-. .
U)
z
w
k..
0 *h^
~~0
I -z
Wi z j
0 0
w w
0(0
* A- PLATE 5 A
an.4i PAwLU"FL
vU
IC IO
0
VJ-
> ~w .ZO
"L0I F
0 0 (
F wz
1kU.-- U
In
-
;I9 9- 09.
PLATE 58~
j
W
I I 0
wz
Ilk p.A
0 ZJo pe #'p. S.-
Z44
69 - I. w-
07 ..d, d
InW
I- 0
z
0 -J0
* -0V-~ -~ I-
PLT 6AI
P44
0
4Qi4
k \j 10 Ib m
-a.- 00(00
-~-~.0 -. (f -
4
0~~ L)~---
IeA, I-- I
7K -J w-\ m v-.. ~ I
ILv L)-. ~ o co
II( <4 ,%.- ( -V
'U, /
*s z0I-
et .Vji
T' t 4le
PLAT 6B )Q~
> 4nF, WO-
j-Z z
ae-
0 w
392 01 it'
.-
1-0
/lb 4. . 0
wF to~ 15
I0 0 0
PLTET
U)
w L x I,-J
7- S
0' V0
roo
Fn ' i
VM..
00
~2-j
V0 9 '0
00
R -iI0I
m 4JW
LLLi.
04
-N 0'
0 1 9 01- X .0
+~L4 -~~co m. '' 0*
~G
R-T 7B
t: -J k
0 0
if zo4w I
>-J'(I
lo
( a
0,2 >- w
00-
*~ .J
- W U./ '-o~ 4 ,.
'A- u
NO 7" 7 q
PLAT BA
U
z
~sJ 1a
CA
-0 0
Je0 z
13 .~ 0 04
u-- U
4 Wo o
w mt-_j 0. > x
0 -j , 0 Z
J44
A
o
IFa
-7o
It~' - o
0 ;
- * -Z or2-
I- o
PLT 8B
~===woo
Z
>z
ml L A -Q
7~m
Av. "23x .0, '
/ (flU.
os' 1 -20
2.04A- -
PLATE
-II
-II
45" FLOOR
to '.- fON '52
I0
FLOW I1 !" 3 v
I-
445.
PLAN
0 5 1O FT
DETAILS
REGULATING SECTIONSLOT PLAN D
PRELIMINARY TEST POOLS
NORTH SHORE FISH LADDER
PLATE 10
3 2.62.38 2.4B8
2.48 2.48826.8 T t6es
-/ '
6.OT4 6.OTI
6.18 5.281
I 201.6T\ -1.78* 2.28 7
K16T r 12r138 kl,-0
NOTES
i. VELOCITIES MEASURED WITH MIDGETCURRENT METER, METER AXIS HORIZONTAL.
2. POOL AND BAFFLE DETAILS SHOWNON PLATE I0.
VELOCITIESLEGEND 8-IN. HEAD DROP
VELOCITY IN FPS SLOT PLAN D
T i FT BELOW WATER SURFACE PRELIMINARY TEST POOLSB 1 FT ABOVE UPSTREAM SLOT SILL NORTH SHORE FISH LADDER
PLATE 1 1
4 00 '~PO-°Q 2 PIEZOME TER40O 12 14 16 18 2G 22 24 2E" '"I 'I , • • 8 l
u.iL " L / . , l ' "* " i * . l . I - . . , • ... ,
600' POOL 7 13
170 - FIXED SILL - REM4& F 51-L(TypI l '18 POOL5 @ 1600'' 2R8 90
PLAN
SECTION A-A
SCALE
B-1 2400
4 00' 150, 'b 920
Fj CL OSED 4"~ ,h 'A4B--
BAFFLE 249 SECTION B-B SECTi-ON C-C/
SCALE0 5 10 15 2- 1 T
INA POOLS5 2, 4, 6,8, 10, 12, AND 14 ONL Y ,
4, , LOPS LbS3? ~
+o65,,'
O I [ *:Z#2
'-'0*-- -
S E EC I F-B 4 C IO
0 67 ll5'I 0
SIN ALL 0oNUMBERED POOL
/IN POOLS 1,3, , 0,, N 1 41 ONYp)
AND 9 ONLY
POOL DETAILS
SCAL E, 1
I m r BE-
II > N M~e D p ~z ---
5X 580 'V SLOT DETAILSWIDTH' SILL IWALL LENGTH I
26 2 2 ' SNEO".AS" IN FT ELEVATIONI L IN FT26 28.. 30 32 It 34 SEL D rIL .4 - - - -- -.. .
-A e 2' . .. . 0 ' . . . . .
92
,5 7' 29 SI 7 5 " 1 "I ,.de'*. * ',4 II '06 e 8°
~-8771 8i 7 70M14
UPSTREAM FACE 4 i
OF DAM h 5 5 ,9
2 : 4. ' 6 Be, ?& 9B A '.. . 8 2. -5 6
fLOP,
2'
'411
EXIT CHANNEL DETAILS
SCALE
REGULATING SECTION
SLOT PLAN E
-4 Fl T, ',,(R f , D E
PLATE 12
- -, ' 2.. . . . ., . . . . . . ' : ' -- -:-: '
an. w
a:H 0
liWr
~ ~ t4 O~qT
w Ina. - w
0 0 u
> -
'u' ki' I
0''
PLTz3'a..
zziLfil-
o c110o x
'>cnI-0
z
ApLL
-
A2\ '00w I i
c4 vcI -- .
CL 49wwf
w w ~> a: - 1~
~~;1 .00 w
-'I
go-l
00 L0
IN
PLAT 13
w2 x
-IL
0j
00 z
4"4
-ti
f--
o Nr
0Y 0 LL
Go i
uou
10
t' tt
I I
o 0
----- - --
PLTE4
_j 1'-- 0
0ow
050
-7-0
PISI
im N
(n, 0 wj00 4
cc w
0L 0 w
z w
030I~r Ul
o o
cob .0v.- It I
43 42go 4 Z11102
PLATE 14B
9 Ie w55w
Vz LAJ
Cs 0A,
z
4N N
3 Vl
II,
fr~
0 Cm4 0
0....... -j >0
0 -w Nj
w 133
I-1 00
4o I0 OF z
'k Nil
6 Nil
i
-cT
azw A
FIZ Z -10,
~k; ~J~i
0I~ wS*. 0 w
01 -
POT2 0 0
- 2I
PLATE 15
FOREBAY ELEV 268 FOREDAY ELEV 257
POOL 26POOL 26
t {
POOLPOOL 25
I FT BELOW WATER SURFACE
-3.4 .- 3.
I-'
2116 O
1 FTAOEIF BV
26' Jf--jSq
CENTER LINE OF LADDER
NOTES
1. VELOCITIES MEASURED WITH MIDGETCURRENT METER, METER AXIS HORIZONTAL.
2. POOL AND BAFFLE DETAILS SHOWNON PLATIE It.
VELOCITIESSLOT PLAN E
6-IN. SLOT BEVELNORTH SHORE FISH LADDER
PLATE 16
PLAN TAWR
to ::O:sf. Z0M~EERs SECTION ALONG CENTER LINE
PLAN
,-A,
WEIR 248 SE;IONA-A
PLAN
*': ,-,*"--1
I i i j V C - F E RL'f!lT fIt.l .
*: I.,.. I .3
ELEVATION SECTION B-9 SECTION C-CBAFFLE 249 -
1 0'i p:PLAN J-6,
.1 Il l ,: . , , !1 . 1, - J CNAj'E,', k i I " * .' 4
.*.t l il: I r1 :J~ l~ :
SECTION 0-0 SECTION E-EELEVATION
BAFFLES 250 ANO 2 1
VERTICAL COUNTING STATIONNORTH FISH LADOER
EXISTING CONTROL SECTION
PLATE 17
MINIMUM DROP AT COUNTING BOARD 3-IN. DROP AT COUNTING BOARD
WEIR BFL ERBFL246 249 248 249_
o0 OfO cl 9 %J
0,9JjJ 'g, OA9"0 .9 _,7 _0~ ~ 9
TOP OF DOWNSTREAM WEIR TOP OF DOWNSTREAM WEIR
JI.Q ~ 0 7;2 e5 1,'- 0 3
.. 6 L4 _46 _L8 _23 _213 24 _I 9 1-9 2. 0 17194
CENTE LINE OF UPSTREAM ORIFICE -CENTER LINE OF UPSTREAM ORIFICE
BAFFLE BAFFLE
WEIR 249 WEIR 249
9 19 29 L9 23277x-,090994 0j 4- 3 0_26 73 86
_ 14 .16 18 23 _12V 24 1.9 19 21 33 4.0 _I?19 40
DIFFUSER IFJE
CENTER LINE OF LADDER CENTER LINE OF LADDER
OPERATING CONDITIONS OPERATING CONDITIONS
HEAD ON WEIR 240 12 6 INCHES HEAD ON WEIR 248 130 INCHES
FORESAY ELEVATION 265 FORESAY ELEVATION ?65
CONTROL SECTION DISCHARGE 860 CFS CONTROL SECTION DISCHARGE A660 CFS
DIFFUSER DISCHARGE 00 CFS DIFFUSER DISCHARGE "10 CIS
LADDER DISCHARGE 860 CFS LADDER DISCHARGE 960 CFS
NOTE 4EADON OVERFLOW WEIRS 1.2.9 INCHES
VELOCITIES MEASURED WITH MIDGET CURRENT VELOCITIES AT VERTICALMETER. METER AXIS HORIZONTAL COUNTING STAT ION
2 HEAD OH WE IRS DETERMINED FROM WATER-SURFACE 9-FT UPSTREAM FROM WEIR FACE NORTH SNORE FISH LADDER WITH PLAN tO WEIRS
EXISTING CONTROL SECTIONCOUNTING BOARD OPEN 36 INCHES
PL ATE 1 8
MINIMUM DROP AT COUNTING BOARD 3-IN. DROP AT COUNTING BOARD
WeIR RAFFLE WEIR 1AFFLE246 24 248 249
.,4~ " ,o. ....33. .9~ fIIQo( II qo~.0 ~
.'5 ,,d 4.2 414 L2 v-O (t.4 J9.J 0
00
TOP OF DOWNSTREAM WEIR TOP OF DOWNSTREAM WEIR
0' -5' --- "I L5'77 5 4
CENTER LINE OF UPSTREAM ORIFICE CENTER LINE OF UPSTREAM ORIFICE
BAFFLE BAFFLEWEIR IWI 2IR REI248i m 248
IHQ ei.L, .j,,4 t 140 74 L4 4 _L,
DIFUSER /DIFFUSER
CENTER LINE OF LADDER CENTER LINE OF LADDER
OPERATING CONDITIONS OPERATING CONOITIONS
HEAD ON WEIR 248 126 INCHES HEAD ON WEIR 248 12 7 INCHES
FORESAY ELEVATION 265 FOREBAY ELEVATION 265CONTROL SECTION DISCHARGE 860 CFS CONTROL SECTION DISCHARGE 86 0 CrS
DIFFUSER DISCHARGE 00 CFS DIFFUSER DISCHARGE 00 crsLADDER DISCHARGE 86 0 CFS LADDER DISCHARGE 860 CF-
M4EADOW OVERFLOW WEIRS 129 INCHESNOTES
L VELOCITIES MEASURED WITH MIDGET CURRENT VELOCITIES AT VERTICALMETER, METER AXIS HORIZONTAL. COUNTING STATION
2. HEAD ON WEIRS DETERMINED FROM WATER-SURFACE S- FT UPISTREAM FROM WEIR FACE, NORTH SHORE FISH LADDER WITH PLAN 1O WEIRS
EXISTING CONTROL SECTIONCOUNTING BOARD OPEN 9 INCHES
PLATE,9
AD-AA45 949 MOD BCATON OF SO ADDERS AT JOHN DAY DAM COLUMBI ARI VER OREGON AND WAU ARMY ENGNEER D IV NOR HPACI C BONNEVIL OR DIV HYDRAULIC L. P M SMITH
UNCASFE A UG84TR10-2F/ 2/4
IIN
11111- 111II 2
~ 125 *1.4 11111_1.6
MICROCOPY RESOLUTION TEST CHARTN~ATIONAL BUREAU OF STANDARDS- 1963-A
MINIMUM CROP AT COUNTING BOARD 3-IN. DROP AT COUNTING BOARD
TOPR OFFL DOWSTIR WERAOPFFDWNTEALWE
04 2j4 49 240 40 4
-1 -1 5o*
'.9, ...
.. a aj 43j 4.8
jJ5
.0 7
.t 07 2 4 as
HEA P O ONRA WEIR 24TOP NCE HA O F DOWSTER W4 6IC E R
Pa~~~~dAS~~ EL VAIO 2sO E Y EE ATO 5
COTOFETO ICAG 5 F OTO ETO ICAG 5 P
HEAD aN 03RFO 6ER 2.0 INCHES C
MENTER METERO AXISRENAL.RFCECNE COING USTAT OIONC
WEI HEAD ONI WER2EERIE4RO9AE
PLATE220
MINIMUM DROP AT COUNTING BOARD 3- IN, DROP AT COUNTING BOARD
MURSAPPLE WEIR BAFFLE54etAB240 241
-'4 I. -'
e? 4'j aL~ *I(
TOP OF DOWNSTREAM WEIR TOP OF DOWNSTREAM WEIR
-v e s ;s.r.a5 4 Y,4 _42 _&f' 4 7 -5 5
CENTER LINE OF UPSTREAM ORIFICE CENTER LINE OF UPSTREAM ORIFICE
BAFFLE BAFFLEEIN 249 WEIR 249
2402 24644
D IFFUSER DFUE
CENTER LINE OF LADDER CENTER LINE OF LADDER
OPERATING CONDITIONS OPERATING CONDITIONS
HEAD 041 WEIR 249 11Ia INCHES HEAD ON WEIR 246 116 INCHESFORESAY IELEVATION 25? FORESAY ELEVATION 257
CONTRIOL SECTION DISCHARGE 450 CFS CONTROL SECTION DISCHARGE 450 CFSDIFFUSERI DISCHARGE 372 CPS DIFFUSER DISCHARGE 372 CFS
LADDER DISCHARGE 62 2 CPS LADDER DISCHARGE 62 2 CFS
HEAD ONd OVERFLOW WEIRS 12.0 INCHES
NOTESVELOCITIIES MEASURED WITH MIDGET CURRENT VELOCITIES AT VERTICAL
MEYER. l METR 518 HORIZONTAL COUNTING STATIONa Me"AD O WEIRS DEtERMINiED FROM WATER-
SURFACE 5' -PT U PSTREAM PROGM WEIR PACE. NORTH SHORE FISH LADDER WITH PLAN 10 WERSEXISTING CONTROL SECTION
COUNTING BOARD OPEN 9 INCHES
PLATE 21
MINIMUM DROP AT COUNTING BOARD 3-IN. DROP AT COUNTING BOARD
WIR BAFFLE WEIR BAFFLE246 249 4 249
TOP OF DOWNSTREAM WEIR TOP OF DOWNSTREAM WEIR
rl~~~j -- TT i1-03 odo 5 ' '249 ~ .01 -o
1. 2 .0f,, 1. o1 1 -.2 ---5 .
09'a00
CENTER LINE Of UPSTREAM ORIFICE CENTER LINE OF UPSTREAM ORIFICE
BAFF .--- ,LE B= ---' "--''F --' AFFLE
,=., ,o=, 1.,- ,- -, 4: /1 5'_ .75-.5 0 -5 ? 8 0.,
-- - I
CENTER LINE OF LADDER IFICE CENTER LINE OF LADDER
OPERATING CONDITIONS OPERATING CONDITIONS
W EAD ON WEIR 249 12 6 INC ES HEAD ON WEIR 4 S 15.0 INCHES
FOREBAT ELEVATION Z69 FORESAY ELEVATION 265
CONTROL SECTION DISCHARGE 660 CFS CONTROL SECTION DISCHARGE 860 CFS
DIFFUSER DISCHARGEf
0 0 CFS DIFFUSER DISCHARGE 0.0 CFSLADDER DISCHARGE 8.0 CFS LADDER DISCHARGE 60 CFS
REVISED UPSTREAM POOL
HEAD ON OVERFLOW WEIRS 1.0 INC.ES
NOTESSVLocTIE EASURED WITH MIDET CRRNT VELOCITIES AT VERTICALMETER, METER £x,5 HORIZONTAL COUNTING STATION
2. HEAD ON W(IRS DETERMINErD FROM WATErR-SURFACE S-FT UISTNRA FROM WEiR FACE. NORTH SNORE FISH LADDER WITH PLAN 10 WEIRS
EXISTING CONTROL SECTION
COUNTING BOARD OPEN 36 INCHES
PLATE 22
CONROLSECIONDISHARE 80 CS CNTRL SCTIN DSCHRGE860CFDIFFUSE DIC A G 00l ll DIFU E DICH RG 0. milrCFlSlll . .
MINIMUM DROP AT COUNTING BOARD
___-__ I______C ic
1 FT BELOW SURFACE MID-DEPTH t FT ABOVE FLOOR
Sol E SfL
SECTION A-A SECTION B-B SECTION C-C
OPERATING CONDITIONS NOTES
HEAD ON OVERFLOW WEIRS 12.9 INCHES I. HGAD OH WEIRS DETERMINED FROM WATER-
HEAD ON WEIR 248 12.6 INCHES SURFACE S-FT UPSTREAM FROM WEIR FACE
FOREBAY ELEVATION 265 2. COUNTING STATION DETAILS SHOWN ON
CONTROL SECTION DISCHARGE 86.0 CPS PLATE 17
DIFFUSER DISCHARGE 0.0 CFS
LADDER DISCHARGE 66.0 CFSCOUNTING BOARD OPEN 36 INCHES
2-IN. DROP AT COUNTING BOARD
- III II1!__j
I FT BELOW SURFACE MID-DEPTH I FT ABOVE FLOOR
SECTION A-A SECTION B-B SECTION C-C
OPERATING CONDITIONS
HEAD ON OVERFLOW WEIRS 12.9 INCHES
HEAD ON WEIR 246 12.5 INCHES 90-DEGREE TRASH RACK VANESFORESAY ELEVATION 26S
CONTROL SECTION DISCHARGE M.O CFS
DIFFUSER DISCHARGE 0.0 CFSLADDER DISCHARGE 660 CFS
COUNTNG NBOARD OPtN S INCHES
FLOW DIRECTIONS ATFISH GUIDES
VERTICAL COUNTING STATIONEXISTING CONTROL SECTIONNORTH SHORE FISH LAOOER
PLATE 23
MINIMUM DROP AT COUNTING BOARD
106I __ A4_. A~~ B-
--f"C. . :.-~GIDES RiA
I FT BELOW SURFACE MID-DEPTH t FT ABOVE FLOOR
CA Tr S&L"
SECTION A-A SECTION B-B SECTION C-C
OPERATING CONDITIONS NOTES
HEAD ON OVERFLOW WEIRS 12 0 INCHES I. HEAD ON WEIRS DEtERMINED FROM WATER-
HEAD ON WEIR 248 I 6 INCHES SURFACE S-FT UPSTREAM FROM WEIR FACE
FORESAY ELEVATION 257 2. COUNTING STATION DETAILS SHOWN ONPIATE 17.CONTROL SECTION DISCHARGE 450 CFS
DIFFUSER DISCHARGE 37 2 CFS
LADDER DISCHARGE 82 2 CFSCOUNTING BOARD OPEN 36 INCHES
2-IN. DROP AT COUNTING BOARD
: ",,, i - , ,
- - -,-U-- /-J,',,. / - = t- L-II FT BELOW SURFACE MID-DEPTH I FT ABOVE FLOOR
SECTION A-A SECTION B-B SECTION C-C
OPERATING CONDITIONS
HEAD ON OVERFLOW WEIRS 120 INCHES
HEAD ON WEIR 2Al 11.6 INCHES 90-DEGREE TRASH RACK VANESFORESAY ELEVATION 257CONTROL SECTION DISCHARGE 45.0 CFS
DIFFUSER DISCHARGE 372 CFS
LADOER DISCHARGE 822 CFS
COUNTING BOARD OPEN N INCHES
FLOW DIRECTIONS ATFISH GUIDES
VERTICAL COUNTING STATIONEXISTING CONTROL SECTIONNORTH SHORE FISH LADDER
PLATE 24
MINIMUM DROP AT COUNTING BOARD
GUIDES RACK
i FT BELOW SURFACE MID-DEPTH 1 FT ABOVE FLOOR
CA rU swr:.
SECTION A-A SECTION B-B SECTION C-C
OPERATING CONDITIONS NOTES
4EAD ON OVERFLOW WEIRS 129 INCHES I HEAD ON WEIRS DETERMINED FROM WATER-HEAD ON WEIR 248 126 INCHES SURFACE 5-FT UPSTREAM FROM WEIR FACE
FOREAY ELEVATION 265 2 COUNTING STATION DETAILS SHOWN ONPLATE I?
CONTROL SECTION DISCHARGE 860 CFS
DIFFUSER DISCHARGE 00 CFS
LADDER DISCHARGE 860 CFSCOUNTING BOARD OPEN 346 INCHES
2-IN. DROP AT COUNTING BOARD
I FT BELOW SURFACE MID-DEPTH I FT ABOVE FLOOR
SECTION A-A SECTION B-B SECTION C-C
OPERATING CONDITIONS
HEAD ON OVERFLOW WEIRS |2 9 INCHES
HEAD ON WEIR 240 12 5 INCHES 90-DEGREE TRASH RACK VANESFOREBAY ELEVATION 265 FLOW DEFLECTORSCONTROL SECTION DISCNARGE 660 CFS
DIFFUSER DISCHARGE 00 CFSLADDER DISCHARGE 960 CFS
COUNTING BOARD OPEN 3 INCHES
,, , ,. "FLOW DIRECTIONS ATFISH GUIDES
resorPC u VERTICAL COUNTING STATION
IEFLEGTOR DETAILS EXISTING CONTROL SECTIONET TNORTH SHORE FISH LADDER
PLATE 25
IL
MINIMUM DROP AT COUNTING BOARD
I FT BELOW SURFACE MID-DEPTH i FT ABOVE FLOOR
RECUL A FN
SECTION A-A SECTION B-8 SECTION C-C
OPERATING CONDITIONS NOTES
HEAD ON OVERFLOW WEIRS 129 INCHES I HEAD ON WEIRS DETE RMINED FROM WAfER-
HEAD ON WEIR 246 12 6 INCHES SURFACE -FT UPSTREAM FROM WEIR FACE
FOREBAY ELEVATION R65 2 COUNTING STA'"N DETAILS SHOWN ONPLATE IT.
CONTROL SECTION DISCHARGE 860 CFS
DIFFUSER DISCHARGE 00 CFS
LADDER DISCHARGE 860 CFSCOUNTING BOARD OPEN 36 INCHES
2-IN. DROP AT COUNTING BOARD
I FT BELOW SURFACE MID-DEPTH I FT ABOVE FLOOR
7= I I Jl I '' . !! [
SECTION A-A SECTION B-8 SECTION C-C
OPERATING CONDITIONS
HEAD ON OVERFLOW WEIRS 12.9 INCHES
HEAD ON WEIR 248 12 5 INCHES
FOREMAY ELEVATION 265 45-DEGREE TRASH RACK VA :SCONTROL SECTION DISCHARGE 860 CFS
DIFFUSER DISCHARGE 0 0 CFSLADDER DISCHARGE 06.0 CFS
COUNTING BOARD OPEN 36 INCHES
FLOW DIRECTIONS ATFISH GUIDES
VERTICAL COUNTING STATIONEXISTING CONTROL SECTIONNORTH SHORE FISH LADDER
PLATE 26
WEI24249
4 ~ 4 ' .
.~LQUVrIf5
SHOWN~MAS ONPATL
NRHSOEFISH LADDE
PLAN ELV 248 T 27
WEIR BAFFLE246 24, POOL 2
407
POOL I
TOP OF DOWNSTREAM WEIR
h-If
CENTER LINE OF UPSTREAM ORIFICE
- - f 0.8 , I 422ZM __ '
CENTER LINE OF LADDER
OPERATING CONDITIONS
HEAD ON OVERFLOW WEIRS f2.O INCHES
HEAD ON WEIR 246 12 0 INCHESREGULATING SECTION DISCHARGE 200 CFSDIFFUSER DISCHARGE 622 CFSLADDER DISCHARGE 82.2 CFS
COUNTING BOARD OPEN 36 INCHESWITH MINIMUM DROP
NOTES
I VELOCITIES MEASURED WITH MIDGET CURRENTMETER, METER AXIS HORIZONTAL
2 HEAD ON WEIRS DETERMINED FROM WATER-SURFACE S-FT UPSTREAM FROM WEIR FACE VELOCITIES
3 REGULATING SECTION, SLOT-ORIFICE PLAN E
4 VELOCITIES IN POOL 249 SHOWN ON PLAN C VERTICAL COUNTING STATIONPLATE 5 NORTH SHORE FISH LADDER
FOREBAY ELEV 2!7
PLATE 28
WEIR BAFFLE
248 249 POOL 2
10- _ o
POOL 1
TOP OF DOWNSTREAM WEIR
;I-l 0
75_ 08
CENTER LINE OF UPSTREAM ORIFICE
CENTER LINE OF LADDER
OPERATING CONDITIONSHEAD ON OVERFLOW WEIRS 120 INCHES
HEAD ON WEIR 246 120 INCHES
REGULATING SECTION DISCHARGE 70 CFS
DIFFUSER DISCHARGE 12 1 CFSLADDER DISCHARGE 82.2 CFS
COUNTING BOARO OPEN 36 INCHESWITH MINIMUM DROP
NOTES
I VELOCITIES MEASURED WITH MIDGET CURRENT
METER, METER AXIS HORIZONTAL
2 HEAD ON WEIRS DETERMINED FROM WATER-
SURFACE 5-FT UPSTREAM FROM WEIR FACE VELOCITIES3 REGULATING SECTION, SLOT-ORIFICE PLAN E
4 VELOCITIES IN POOL 249 SHOWN ON PLAN C VERTICAL COUNTING STATIONPLATE 13A NORTH SHORE FISH - AtrIR
FORESEF ELEV 266
PLATE 29
0
74 z 0
z J) xw
a oIw 148 w4
~cux- U 0 4 e .K 4 2 g
0 W
C(%A z
-~0
I'OjO
00
44
-~ -~jv - -- J-- -
90 WU.
4 so
PLT 30 ,0
WEIR BAFFLE248 249 POOL
FLOO4 SIL53
714 t8_ /.8--,o_ _, . , '
26 POOL
3l . . l I-- -- -4 l Ht -
CFTBELO WAER SURLAE
HEA .8 WER24 2 ICEREGULTINGSECTON DSCHAGE L9 3F
DIFFUSER DIS3ARG.6$. 0.F
1 OLAN A FT EAB SOE SOT LAOVE
ON PLATS 12 ADCENTERUTLINEREOFILADADER
HEAD ON FERRB48Y 20EINCHE
RGAI SECAIO DDI..USE...ISCHARG. 8.5 1 C
LADDE DIC A088 F
2 -POOL ANPOOELEAL SONSOTPA
I ~ ~ ~ ~ ~ LT 3TBLWWTE1UFC
WEIR BAFFLE~28 49POOL 3
58 1.8 33 22 '
0 .3 03 w n .4
55 ~07f 2. 11j58PO
I FT BELOW WATER SURFACE
76 Of 0 34w18-1N
-U. 2.-
CETE LLN OFLADE
OPERATING CONDITIONS
HEAD ON WEIR 248a 120 ICHESREGULATING SECTION DISCHARGE 200 CFSO;FFUSER DISCHARGE 622 CFSLADDER DISCHARGE 822 CFS
NOTES VELOCITIESI VELOCITIES MEASURED WITH MIDGET
CURRENT METER, METER AXIS HORIZONTAL. ENTRANCE AND EXIT POOLS2 POOL AND BAFFLE DET4ILS qMAWN SLOT PLAN E
ON PLATES 12 AND 30. SOUTH SHORE FISH LADDERFOREBAY ELEV 25?
PLATE 32
IR W-3-14
R5'-1 10
14 t-O'b 4-6"- 6-5' 915'8 STA NDARD WEIR DETrAI1LS
SHOWN ON PLATE /7
PLAN
- ~ -~i A-* 1 ,CONTROLGA TE
I j CHAMFER
_4 -1
SECTION A-A SECTION 8-9
DOWNSTREAM ELEVATION
ORIGINAL WEIR 194SOUTH SHORE FISH LADDER
PLATE 33
WATER SURFAC EL
1 FT BELOW WATER SURFACE
- -f
i FT ABOVE FLOOR
CENTER LINE OF LADOER
NOTESI POOL AND WEIR DETAILS SHOWN
ON PLATE 33,2 HEAD ON WEIR 12 INCHES
DISCHARGE 82.2 GFS.
FLOW DIRECTIONS
ORIGINAL WEIR 194
SOUTH SHORE FISH LADDER
PLATE 34
WEIR WEIR194 195
6'-1 * Z) _ . "
1,I
*~r J 9 ij5
SOL ID
PL ArE
(SrANDARD WEIR DELS
4t-o".11 ,-6"j 6'-5" . -8, ' SHowv ON PLArE /7
PLAN
JL~T~JA -
A-ElSECTION A-A SECTION 8-8
DOWNSTREAM ELEVATION
PLAN A
MODIFIED WEIR 194
SOUTH SHORE FISH LADDER
PLATE 35
WEIR194 195
-d-
._7 1
WATER SURFACE ELE V ..1 5 ,3,v ' .4194.0 Jem-.... )
I FT BELOW WATER SURFACE
As .6, .
g.2 j. 76
2 --
7S
CENTER LINE OF LADDER
NOTESL. POOL AND WEIR DETAILS SHOWN
ON PLATE 3&
2. HEAD ON WEIR 10 INCHESDISCHARGE 76,0 CFS.
33 VELOCITIES MEASURED WITH MIDGETCURRENT METER. METER AXIS
HORIZONTAL, VELOCITIES
PLAN A MODIFIED WEIR 194
SOUITH SHORE FIAtH LADDER10-INCH HEAD
PLATE 36 2. HEA ON WIR *-ICHE
WEIR194 195
WATER SURFACE EL V -, )6._
1940
I FT BELOW WATER SURFACE
2 . L 0 1"
3 FT ABOVE FLOOR
.L .L6
CENTER LINE OF LADDER
NOTES
L. POOL AND WEIR DETAILS SHOWN00 PLATE40
2 HEAD ON WEIR 12 INCHESDISCHARGE 92,2 CFS
&. VELOCITIES MEASURqED WITH MIDGET
URENT METER. METER AXIS
3 F ABV LVELOCITIES
PLAN A MODIFIED WEIR 194SOUTH SHORE FISH LADLER
1t-INCH HEADO
PLATE 372.HED...... . 2 ICHE
...... S...R.E..2.2.C S3. VELOCITIES MIEASUREI ..T..MID ET
WATER SURFACE ELEV
I FT BELOW WATER SURFACE
- - - -
I FT ABOVE FLOOR
1-Z
CENTER LINE OF LADDER
NOTESI POOL AND WEIR DETAILS SHOWN
ON PLATE 33.
2 HEAD ON WEIR 12 INCHESD#SCHARG 82 2 CFS.
FLOW DIRECTIONSWEIR 194 REMOVED
SOUTH S"ORE ISH LADDER
PLATE 38
WEIR WEIR, l 1, t 96
15'.-9" 9 4* lot,-. 0-
SOLID PLArESLiEV J92.5_ TO J95.0
_ ELEv 188.0Vo 1-9.0o_
41-0'-1- 4'-6"-1 6-5 i5 -8 STANDARD WEIR DETAILSSHOW#VoN PLArT 17.
PLAN
r OA 8- ow.01
SECTION A-A SECTION 8-8
UPSTREAM ELEVATION
MODIFIED WEIR 195
SOUTH SHORE FISH LADDER
PLATE 39
-6 -- 70_
WATER SURFACE ELEV 3 6 .4 .J 4i 700
- ,67 70'
i FT BELOW WATER SURFACE
-w-
3 FT BELOW WATER SURFACE
MODIFLE WEI 19
09 23 5_9 78-
CENTER LINE OF LADDER
NOTESI POOL AND WEIR DETAILS SHOWN
ON PLATE 39.
2 HEAD ON WEIR 12 INCHESDISCHARGE 82.2 CFS ,
E OCTE
MODIFIED WEIR 195SOUTH SHORE FISH LADDER
PLATE 40
WEIR WEIR
194 195
R15'--O*
FLEV 192.5
i TO 195.0 L,
TO 194 -o"1 4'-6" L 6'-5" j "e ,Ro WERDETILS
PLAN S 0S
A-4- B-4 C i
SECTION A-A SECTION B-BDOWNSTREAM ELEVATION
PLAN
MODIFIED WEIR 194SECTION C-C
SOUTH SHORE FISH LADDER
PAt
PLATE 1
WEIR
194 195
5' )6 ~ 73
WATER SURFACE ELEY .9~3 ~ 3 5
194.0 ( ,
i FT BELOW WATER SURFACE
) . ) * •
A-8
CN RiL
3 FT ABOVE FLOOR
I I Dlii ~ .41 .
CENTER LINE OF LADDER
NOTESI POOL AND WEIR DETAILS SHOWN
ON PLATE 42.
2 HEAD ON WEIR 22 INCHESDISCHARGE 32 2 CFS.
3, VELOCITIES MEASURED WITH MIDGETCURRENT METER METER AXISHORIZONTAL.
VELOCITIESPLAN B MODIFIED WEIR 194
SOUTH SHORE FISH LADDER12-INCH HEAD
PLATE 42
WEIR194 195
WATER SURFACELE 2 3 2 54 6 -
194.0 . .
t FT BELOW WATER SURFACE
A0~ A~w 76ho~
:3 FT ABOVE FLOOR
NOTES
I POOL AND WEIR DETAILS SHOWN00N PLATE 41 .
2 HEAD ON WEIR 10 INCHESDISCHARGE 76.0 CFS,
& VELOCITIES MEASURED WITH MIDGETCURRENT METER, METER AXIS
HORIZONTAL. VELOCITIES
PLAN 8 MODIFIED WEIR 194SOUTH SHORE FISH LADDER
1O- INCH HE[AD
PLATE 43
. . ..HEAD. . . . ..O.. . . . .. . .. .. . . ...10 INCHE. ...S,,
A~~l