### -- m. 4



## . ** 

# . .. I



# .

# :. * 'I 

# - N-'77 CONTRACT PROPUSAL- . 

# .. * 

# - INTRODUCTION The 

## FY-77 Annual 

## tiork Plan P.dvlce 

## for the 

## East Lansing Field OfficeEcological Services containEd 

## a specific coiuni

## trnent requfrlng this 

## station to 

## test and analyze contract methodologies 

## in the-permtts and 

## licenses program. After 

## corsidcrable discussion 

## &mons the 

## East Lanslng Field 

## Office staff, It 

## was cccided that 

### 31C(b) 

## denonstration studies 

## should be the 

## target projccl. Both 

## Sect'ion 10 

## and 

## NPDES progrems are

. 

## directly affected and, 

## to 

## a lesser degree, Nuclear 

## Regulatory Comjssion 

## projects 

## are related to the proposed 

## contract. !;TATEKE!IT 

## OF WORK 

## Utflfties in tfic 

## Great 

## Lake:; Region, as 

## in 

## the rest 04 the 

### Unfted States, 

## are requlred undcr Section 

### :!16 

### of 

## the 

## FeCeral \.later Pollution 

## Control Act 

## hmndments of 1972 

## to amduct 316(b 

## denonstration studies 

## on toolfng water intake 

## structures. Slxtion 316(b 

## requfres that 

## cooling water 

## intake 

## .structures reflect tile 

### best 

## available technology for ninimjzfng adverse 

## cnvironaental lnpacx. 

## These adverse 

## impacts generally 

## result from 

## entrainirent of 

## snafl a 

## quatic 

## organisms 

## such as 

## macrobenthos and 

## larval fish 

## and impingement of 

## larger organism, usualiy adult fish. 

## The 

## objectlve 

## of conducting intake 

## studies 

## is to obtain the 

## most accurate quantStative 

## estimate of 

## entrainncnt 

## and fmpfngerimt 

## losses or damages 

## occurring at 

## a 

## plant. 

## It 1s 

## then 

## possible 

## to deterinhe 

## what, If 

## any, better technologies exist 

## t3

## minimize adverse Impacts 

## at 

## a particular 

## stem electric generating station recognizing that 

## certaln Impacts 

## nay be 

## acceptable 

## to the 

## long-term 

## maintenance and 

## productivity of the aquatic ccosysten 

### In question. 

## Obvlously, the 

## real 

## problems are twofold: 

## (I) quantifying intake fn;scts and (2) 

## predicting the 

## associated impacts

. 

## on the 

## water body froin 

## which cooling 

## water 

## is withdrawn. 

## If 

## the 

## US. Fish and 

## \!ildlife Service can dmonstrate that 

## itens '1 

## and 2 

## above are adversely 'hipacting the fishery 

## and cthcr aquatic resources by 

## reviewing a 

## partlcular 

## 31G(b) denonstratlon study 

## and associated data, 

## It may 

### be 

## possible 

## to rccomend that a 

## utility 

## provide "better 

## technology" at 

## one 

## or more plants 

## utilizing the 

## Section 10 

## ard 

## NPDES routes. The 

## objectfve 

## noM becoaes clear. 

# 1 1s it 

## possible 

## to build a 

## sound case 

## out of 

## a Section 316(b) 

## demonstration 

## 1 study gfven 

## our statutory i*esponsfbill ties?. 

## SCOPE 

## OF EIORK The 

## scope of 

## work for this 

## contract Includes the revfeki and 

## anatysls 

## of selected 

### 376( b) 

### Ceraonstrat.;on studies 

## on steam electric power plant 

## intake 

## stnrctures conducted pursu.int 

## to 

## PL 92-503. 

### the 

## Federal Water 

## Pol 

## lutlon Act 

## Amendments 

## of 1972. 

## Mwk under this 

## contract shall be 

## perfomed as 

## descrtbcd 

## below:.I.. 0 

# .. 

# .. 

# - :'­

r ­ 

# . 

# .. a

.. 

## Phase I 

# . c-



## Phase 

# I Involves the revlew 

## and 

## analysls of 

## the 

## sanplfng techniques employed by the 

## utility 

## to 

## gather the 

## entrainment and 

## impingement data 

## presented 

## in 

## the 376(b) 

## report. Sarnpl ing 

## design and 

## methodologies for fish 

## including eggs, 

## larva, fry, 

## young-of-the-year and 

## other 

## small fish, 

## adult 

## or large fish, 

## macrobcnthos, and zooplankton shall be glven 

## a detalled 

## scfentlfic analysis 

## to deternine if 

## appropriate methods. 

## were employed 

## to gather 

## unblascd data 

### and 

## if 

## the 

## sampling program 

## sought answers 

## to the 

## right 

## questions. In each 

## instance cited above, the 

## contractor shall specify if 

## the methods employed 

## by the 

## applicant 

## (ut11fty) 

## are scientifical ly 

## val4d. 

## If the methods employed 

## contzin biases, 

## these shall be described. The 

## effects 

## or influences that 

## these biases 

## have on 

## the 

## results (data) shall 

## also be defined. 

# . Phase 

## I1 

## Phase 

## XI involves 

## the review and 

## analysis of 

## the 

## data obtained by 

## the app1.f

## cant (utfltty) 

## and presented t'n or as 

### a 

## part of 

## the 316(b) study. 

## Functlons to 

## be pcrfomd 

## include tiic 

## verificatfon of 

## the accuracy of 

## the 

## data pre- ,. 

## sented, 

## calculation 

## of and/or vcrification of 

## confidence intervals 

## or 1imits of 

## the data 

## presented. Appropriate 

## statistical testing methods shall be 

## utl'lfzcd 

## to verify accuracy of 

## results and 

## to determine the mgnftude of 

### the 

## sampling 

## variation. The 

## analysis conducted in 

## thls phase 

## should Oeteminc I 

### the 

## real value 

## of 

## the data 

## in 

## terns 

## of biological and 

## statistical sicpic' 

## icancf 

## a0 

## thcse data 

## accurately reflect 

## the rrignitude 

## of the 

## losscs involved due 

## to dmpfngernent 

## and ,entrajnrrrent? Delayed 

# or latent 

## mortal itles 

## and sublethal effects as 

## a 

## result of 

## entrainnent 

## or hpingement 

## should be 

## fully discussed. 

## Phase 111 

## Phase TI1 involves the 

## analysls of data 

## to detcmfne 

## or predfct the 

## fapact of 

## the cooling water Intake 

## on the fish, 

## macrobenthos, and zooplankton pqwlatlor of 

## the 

## coolins water source($). The 

## contractor will, in 

## nost Instanc.zs, 

## need 

## to utllize data 

## sources in 

## additlon to 

## the 316(b) study 

## to 

## verlfy 

## thcse pre

## dictions if made by the 

### applicant and/or to 

## predlct the 

## hpacts If not 

## done 

## by the applicant. 

## It w311 

## be 

## necessary 

## to deternine both 

## the 

## local and 

## far-fjeld effects 

## on the 

## water body 

## from which cooling water 1s 

## wlthdrawn. 

## In some 

## Instances, two 

## or 

## more cooling 

## water 

## sources sucb as a 

## river and a lake 

## rnust'be 

## considered. 

## The contractor should 

## determine if 

## the Intake Is 

### located 

## in a 

## sensitive bio

## logical area 

## such as 

## an iiiportant spawning 

## or 

## nursery area for any 

## spccles affected 

## by 

## tfie intake. Entrainment and lapingeaent Itqacts 

## caused by the 

### intake 

## under study 

## should be 

## related 

## Jn a 

## total 

## rranner 

## to inpacts 

## caused by 

### other 

## power plant 

## tntakes 

## on the same body 

## or region of 

### water 

## on 

## sensjtive 

## or otherwise important fish stocks 

### If 

## sufftcient data 

## is 

## available to pemft 

## manlngful predictions.

# . .. * .

. I .c 

# ­ ._

## . . 147 

# . -. The 

## results 

## of the 

## anatysi!. 

## performed 

## shall 

## be provlded 

## to the 

## East Lanslng Field Offfce 

### and 

## tfie Regional 

## Office in Craft 

## fomfor 

## revjcw prior to being 

## accepted as a 

## final product. The 

## report 

## shall contain 

## the data 

## analysis cs 

## dcscr:bed under 

## the Scope of 

## ti’ork. 

## The funnat 

## shall contaln 

## the 

## neccssar)’ infomation 

## In a 

## narrative 

## fomas 

## well 8s 

## approprlatc tab1es 

### graphs, 

## etc. I. 

## Tim frames 

## for the 

## report 

## arc: e 

### ‘Date 

## Project Initiated: 9/1/76 Date of 

## Interim Report: 

### 6/7/77 

## Date- of 

## Ffna’l Report: 

### 12/15/77 I



# ..

b



# .

### 148

, -

APPENDIX B Errors 

### found 

### on Detroit 

### Edison's daily 

### impingement data sheets 

### (IDS) and test 

### screenwell tally 

### sheets (listed 

### by sampling 

### date).

### 149 This is not an exhaus.:ive list. All the daily impingement data sheets 

### for the 

### nontest screens we::e checked, but 

### the tally sheets [for the fish on the 

### test screens and the 

### fish pumped into 

### the holding 

### pool) were checked for 

### only 20 

### of the 

### 164 tes: screenwell sampling days. On these 20 

### days, we found 22 discrepancies bet'geen the data recorded 

### on the tally sheets and the data summarized 

### on the daily impingement data 

### sheets. 

### Data sheets 

### for 9-24-75, 11-26-75, 4-1-76, 

### and 4-2-76 

### are 

### included as examples. 

## * = 

### corrections made 

### by GLJ?L.

### 150 ,-­ 

### 6-19-75 : 

### 6-24-75 :


### 6-26-75 : 

### 7-8-75 : 

### 7-16-75 :



### 8-14-75 : 

### 9-9-75 :


### 9-23-75 : 

### 9-24-75 : 

### 9-25-75 : 

### 9-26-75 : 

### 10-7-75 : 

### 4 channel catfish 

### are not entered in total 

### column on IDS 

### for non

### test screens. 

### 4 shad 

### are not recorded in total column on IDS 

### for non-test- screens; 

### 2 alewives counted in pool 

### were not recorded on IDS 

### for test screens. Shiner total on IDS for non-test screens equals 328, not 344. The number 

### of shiners counted in 

### pool 

### equals 

### 419, not 

### 424. The IDS for non-test screens should 

### list 

### 1 logperch 

### in the total 

### column instead 

### of 

### 1 rock 

### bass. 1 trout perch counted 

### in pool was not recorded on IDS. 3 trout-perch and 1 sunfish counted 

### on 

### test screens were not recorded 

### on IDS. The shad counted 

### in pool equal 1020, 

### not 1050; those counted on 

### test screens equal 345 not 

### 24! Shad 

### total on IDS 

### for non-test 

### screens equals 

### 796, not 

### 836. 

### 1 trout-perch 

### was counted on test screens, not 2 as recorded 

### on IDS; 

### 1 logperch 

### was counted on 

### test screens, but it 

### was not recorded on IDS: white bass counted on 

### test screens total 358, 

### not 338. White 

### bass 

### total on IDS 

### for non-test screens 

### is 373t not 

### 353. Yellow perch 

### total on IDS 

### for non-test screens is 

### 147, not 

### 113; white 

### bass 

### total for non-test screens 

### is 220, not 

### 202. White bass total on IDS for non-test screens 

### is 326 instead 

### of 361; shad total 

### for non-test screens 

### is 279, not 

### 259. White bass courrted on test screens total 52, not 

### 51. Drum counted on test screens 

### total 20, not 27. I_
" ­

_­

"­

e.-151 10-14-75: 10-29-75 : 11-4-75 : 11-11-75 :
11-13-75 :
11-14-75 : 11-18-75 : 11-26-75 : 12-3-75 :
12-11-75 : 1-23-76 : 1-27-76: 2-12-76 : 3-10-76: Yellow perch 

### total on IDS 

### for 

### non-test screens equals 81, not 80; shad total 

### equals :!9l.,not 

### 651. Drum 

### total on IDS 

### :'or non-test screens equals 98 not 88. Perch total on IDS 

### for non-test screens 

### is 37, not 36; alewife 

### total 

### is 89, 

### not 8:3; shad total 

### is 357, not 362. 10 channel catfish and 1 smallmouth bass 

### were not recorded in 

### total column on IDS 

### for ion-test 

### screens; smelt total 

### is 9, not 56; walleye 

### total 

### is 31, not 11; logperch 

### total 

### is 17, not 5. 1 

### gar and 

### 19 smallnouth 

### bass 

### were not entered in total column 

### on IDS 

### for non-test sxaens; white 

### bass total equals 13 instead of 16; 

### smelt total is 204, not 222. Smallmouth 

### total 

### cn IDS 

### for non-test screens 

### is 7, not 4. Shad 

### total on IDS 

### for non-test screens 

### is 189, not 269. Shad total 

### on IDS 

### for non-test screens 

### is 398 instead 

### of 298. c Perch total on IDS 

### for non-test screens equals 340, not 190; northern 

### pike tote1 equals 4, not 1; crappie 

### total equals 4, not 

### 1; and shad total eqt.als 8860, not 6940. 1 channel catfish was not recorded in total 

### column on IDS for non-test screens. Shiner 

### total 

### on 11)s for non-test screens is 560, not 520. 

### 1 northern 

### pike wiis 

### not recorded in 

### total column on IDS 

### for nontest screens. 2 

### smelt 

### were not recorded in total column 

### on IDS for non-test screens. Goldfish total on IDS 

### for non-test 

### screens is 26, not 27.152 3-23-76: 4-1-76:
4-2-76: 4-7-76: 4-8-76 : 4-9-76 : 4-14-76 : 4-15-76 : 4-16-76 : 4-20-76 : 4-21-76 : 5-4-76 : 5-25-76: 5-27-76 : Perch 

### total on 

### IDS for non-test screens 

### is 52, not 50. 85 

### trout perch counted in 

### pool and 39 

### counted on test screens 

### were not recorded 

### on IDS for 

### test screens; the number 

### of shiners counted in pool equals 

### 652, not 552. 

### 1 bowfin counted in 

### pool was not recorded on 

### IDS for 

### test screens; the number of shad counted in 

### pool equals 273, not 43. 1 lamprey counted in pool and 1 white bass counted on 

### screens were not recorded on 

### IDS for 

### test screens. Alewife total on 

### IDS 

### for non-test screens 

### is 182, not 184; 2 sunfish 

### were not recorded 

### in total 

### column on 

### IDS for non-test 

### scree3s. 155 shad 

### were not recorded in total column on 

### IDS 

### for non-test screens. 445 shiners 

### were counted in the pool, not 425. 28 trout-perch 

### were counted 

### in the 

### pool, not 30. 34 shad 

### were counted on the test-screens, 

### not 25. Smelt total on 

### IDS 

### for non-test screens 

### 1s 41, not 9. 63 perch 

### were counted in 

### pool, not 64 

### as recorded 

### on IDS 

### for test screens. Alewife total on 

### IDS for non-test screens (Screenhouse 1) 

### is 44 

### not 43; 

### 1 walleye 

### was not recorded in total column (Screenhouse 2). Alewife 

### total on 

### IDS for non-test screens 

### is 22, not 

### 21. Shad 

### total on IDS for non-test screens (Screenhouse 2) is 65, not 60. *... 

### 153 

### Det

### roit 

### Ed

### ison 9/24/75 

## . . .i

....

m

)-I 0 Ccl .IJ a, a, 

# c

..

4

ClilC. Fl:-:.% os: USIT 1 LWT 2 WIT 3 GXIT 4 

## 3 

## 04 3 

## 3 

# * Yellow perch 

### total = 

### 147, not 

### 113. 

### ** White 

### bass total = 

### 220, not 

### 202. 8Detroit 

### E:dison 

### 154 11/26/75



# .

SCREES COLiT: 1

# ­ 2 ­ 3 ­ 4 -

USIT 2 

# a

c 

# * Shad total = 

### 398, not 

### 298

### ----- 

# - Detroit 

### Tdison 4/1/76



### illy sheet 

### shows >at the 

### number of 

### liners counted 

### in 

### u aJ 

### mol totals 652, 

# 5 a 

### )t 552 h 4 i 

### trout perch ri Id 

### )unted 

### in pool 

### are f3 

### )t recorded on rl 0 0 Lily 

### impingement & ita sheet for !st 

### screens.

-_.___ Reproduced from best available copy., ­ 

### 156. 

# -

m 

# 5 a L4 0 ul U u) Q, t3 

### u 0 rcr cl a Q,

h rl -4 a 

### n

*Tally 

### sheet shows

that 

### the 

### number of shad counted 

### in 

### pool totals 

### 273, not 43. "­ **1 bowfin counted d 

### in pool 

### is not 0 0 

### recorded on 

### daily PI impingement 

### data I , 

### sheet.

### 157

APPENDIX 

### C Detroit Edisoi 

### daily impingement data 

### sheets 

### for the Monroe plant 

### for August 1975.._. . L Detroit 

### Edison 8/1/75 *

..

r--.*- . .__ 

### 159



# .

. .



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### Ed

### iso1 8/6j75

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### found.by GLFL: Gizzard shad counted = 199, not 209; total ='796, not 836. 1
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### Edisdn 

### .

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~ I ' 8/26/75 

# .



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# ... 8/29/75



# .

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# .

### 169



### APPENDIX 

### D Examples of effezt 

### of log

### 10 (x 

## + 1) transformation 

### on the normality of 

### estimates based on counts 

### from Detroit 

### Edison's daily impingement and entrainment data sheets. 

### Plots computed by 

### Tektronix 

### 4051 graphic calculator.Impingeme 170 Shiners August 

### 19 Normal plot 

### of untransformed daily estimates 28350 22680

5670 0 

## e. 01 1



## ..
4.6

QI +I 

### 3.8 . a E iJY

. 3.4 . h 

### a Q Y 

### 3

0 

## 6;’ 0 i4 2.6 2.2 

### x



# - 20 48 60 88 

### 99 99.99 Cumulative Frequency 

### (%I Normal 

### plot of daily estimates transformed 

### by 

### loglo (x 

## + 1)

Cumulative Frequency (

### #.I

### 171 

### Impingement 1 

### Gizzard shad 1 

### February 1976 $orma1 plot 

### of untransfomed daily estimates c 89670 

### f1736 a 4J 

# a 53882 .?I u ul 

### w
17934 0 * I 1 20 40 60 80 99 

### . 99.99 

### Cumulative 

### Frequency (%)



### Normal plot 

### of daily estimates transformed by 

### loglo (x 

### + 1)

- 5 L 4.8 

## + 4.6 4J 

# 2 4.4 $ 4 Y

0 m4 

### 3.8 f 0 I3 

### 3.6 3.4 

### e.ei 1 20 40 60 80 99 99.99 

### Cumulative Frequency (%)

### 172

St3980 

### 46962% 365268 260908

* 156540

52 i

## se

h 44 

## + 247533 202527 c 0 1575‘1 112515
h 67503 rl .PI 

### a Q 22583 

### Ent, 

### Chi. Aug1 

### Noma1 plot of daily estimates based 

### on untransformed counts

99 

### Cumulative Frequency (%) 

### Normal plot 

### of daily estimates based 

### on counts transformed by loglo (x 

## + 1)

/XX



### s4

% 

### Cumulative Frequency 

### (%I

### 173

APPENDIX 

### E Impingement and Zntrainment estimates for the 

### Monroe Power 

### Plant based 

### on l>g 

### 10 (x 

## + 1) 

### transformation and 

### counts 

### from Detroit 

### Edison's daily impingement and entrainment data 

### sheets.

### 174 Table E-1. Estimates 

### of impingement at the Monroe 

### Power Plant 

### for June 1975-May 1976 based on log10 (x 

## + 1) transformation 

### of daily estimates calculated 

### from Detroit Edison's daily impi'ngement data sheets. Table 32-2. 

### Estimates of entrainment of 

### fish eggs 

### and larvae at the 

### Monroe Power Plant for April 1975-May 1976 based 

### on log

### 10 Ix 

### + 1) transformation of counts 

### from Detroit 

### Edison's daily entrainment data sheets. Table 

### E-3. Estimates 

### of entrainment 

### of macrozoobenthos at the Monroe Power Plant for 

### May 1975-April 1976 based on log10 (x 

## + 1) transformation 

### of counts from Detroit Edison's daily entrainment data 

### sheets.

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### APPENDIX 

### F Addition31 

### errors found 

### in the 316(b).

### ____ 2 

### 36 Chapter 3 

### p. 3.2-3: There 

### is no 

### Figure 3.1-3 

### or 

### any detailed illustration 

### of the discharge structure as indicated 

### below in Section 

### 3.2~4. 3.2.4 The condenser cooling water from all four units is discharged to a common overflow canal, varying uidths and

. constant bottom north oi the East Front Street bridge, the recirculation gates. Here the heated effluent can be directed either south through the discharge canal (approximately 5,800 It x 560 ft) to Lake Erie or north through the lla&illan Road canal (approximately 1,400 ft long by 160 it wide) to the Raisin River. Table 

### 3.3-1: 2328 

### MW 

### is given 

### as 

### the maxhum net capacity. 

### The table, however, 

### lists 

### several capacity values that exceed 2328 MW. It appears that the 

### maximum 

### is 2528 MW, 

### not 2328 

### MW. Table 3.3-3: 

### The area of 1251.0 f t2 given for calculating velocity 

### in front 

### of the screens 

### is incorrect. (572.27-546.0) (8)

### (10) = 

### 2101.6 ft2 The velocity of 0.77 

### ft/sec 

### is correct however. TABU 3.3-3 IMAKE VUOcIn CALCOLATIOH AT EACU SCREENtl5USE. 1 INT UrnApril 1975-April 1976 water level x 572.27 f't Screen bottom clevatioa = s06.0 tt Sldmer wall bottom elsvstlon = 560.0 f't P .; maximum flou posslble/screenhouse = 1.624.2 ft'/sec lumber of acreens r 8 Screen uldth 8 '10.0 It Scrwnuell uldth 1 11.11 rt 1. Calculation of Velocity Directly in Front ot Scrccno Screen [it') Level tft) Elevation (It) 

### > 8 (572.27 tt

# - 546.0 ft) (8) (10 ft) 

## Z6-2

### Table 3.3-3 

### (cont'd) 237 2. Caloulmtioo of Velvity Put SUarYall A Crass-stctlon of scrteauell (re') = Skierwall Scrtca

Bottom A a (560 

# - 5461 (�1 111.17 it1 = 1251.0 ft'

8 Qf& L 1.30 h/asc. 1.251.C It Chapter 4 

### p. 

### 4.2-17: According to the Literature Cited section, the reference to "Hartman (b) 'I should 

### be "Hartman (a)

### '*. p. 4.2-26: Clupeid dersity 

### in paragraph 

### Q1 is 900/100 

### m3 

### , not 9OO/m3 

# . p. 4.2-27: The 

### smelt tata mentioned 

### is not listed 

### in Table 

### 4.2-31. p. 

### 4.2-27: The Cole (1975a) reference 

### is not listed in the Literature Cited section. The correct reference 

### is evidently Cole 11976a). p. 4.3-4: It 

### is statEd 

### that: As indicated in Table 

### 4.3-3, yellow perch impingement in 1972 was characterized by two 

### peaks: in October 

### (36,7041, and in April (28,350). whereas, Table 

### 4.3-3 (shown 

### below) indicates that impingement peaked in October and August.
Socflca Clzzara shad Rklnbow smtlt ShlEers Yallcyc 

### ,-> Xtllow perch Yhitt Sass Channel catfish Coho salmon Rock baa3 Smallmouth boa freahuater arum Yhite crappie sunfish Northern plks Broun bullhead Goldfish Carp Steelhted trout Suckers Other5

Totals dpLtlay &cle rzvLEduessQL POG (15 40 a28 99 114,793 6.580 233.275 19 93.000 1 1.732 1,479 6,671 1.500 78 12 7,530 7,4QO 14.460 

# 4 15,360 3,185 s2 99 378 1,140 108 16 62 6 9 6 12 56 15 6 9 6 12 16 39 849 1.359 155 502 501 31 6 16 90 202 6 16 6 90 68 54 25 120 a7 21 53 19 ai 07 12 6 59 12 9 30 l2 18 1,800 1,333 3 6 108 12 31 $6 87 I 30 9 31 38 78 3 90 38 21 -3 

# . 6 10 123.057 3,058 1388.055 3 6 3 1s2 38 p. 4.4-2: The 

### volume 

### of the entrainment sampling 

### pumps is listed 

### as 2.016 x 106 gal/day. 

### 530 

### l/min = 

### 2.016 x 

### 10

### 5 gal/day, 

### not 2.016 x 

### 106

# . Table 4.1-1: According 

### to 316(b) p. 

### whose presence 

### was noted 

### one 

### or more sampling effort"' 

### from 1972-1976.

bamun= Sfirer*bmpret. Sei- Ismprey Laasnose Kar Bovrin Alauffe OlZurd abrd coho ralmon Chinook salmon kinlwau trout blnbou smelt Central rudmlnnou lorthern plke GolafIsh brp Golden sblner Emerald shlner Spottall shiner Elwitnose mlnnou ( Creek Chub

Quillback yhito aucker Elack bullhead Yellow bullhead Broun bullbend Channel catflsh Stonecat Tadpole mdtoa Brladled madtom Trout-perch Burbot Brook alloorside Uteperch yhite bass Dock bass Oreen runfish Pumpklnseed BlUCKill Sm&llwuth bass Largemouth baas Ute crappie Black crappie Johnn~ darter Yellou perch togwrcb Ualleye Imahmtrr &UO 4.1-5, 

### this table 

### lists "all 

### species
,- -, 

### times during the 

### monitoring period

,-

I ­

lota: Species list includes flsh impinged and entrained; also those 'removed by nets or br pump. fer some collectiona, an19 6roup CO.DDD names were used lncludle~ crap2le. black tass. gar. sucker. .ad suafish. Because these group names were sometines used. addltlons ta the above species llst we not possible.2 39 

### Comparison 

### of the 

### table with the Monroe data base, however, revealed several discrepancies. For 

### example, the creek chub is 

### listed 

### in the table, 

### but neither the impingeiient nor the entrainment records show it 

### occurring at the 

### intake. Accordi:ig to 

### the data base, the 

### common shiner, muskellunge, and blue catfish 

### were iinpinged, but these 

### species are not listed in 

### Table 4.4-1. 

### Three additional species--shorthead redhorse, 

### slimy sculpin, 

### and silver chub--are listed in the 316(a) demonstration (Table 3-51, 

### Cole 1976; Table 4.2-5, DetrDit 

### Edison 1976) 

### but are not listed 

### in the table. Table 4.2-5: 

### Accordins 

### to the Literature Cited section,the reference to "Hartman 

### (b)'I 

### shou.lt be "Hartman (a)

# " - Table 4.2-8: 

### 316(b) frils to 

### indicate, as done 

### in VanVooren et al., 1975, 

### that the 1974 YO1 

### yellow perch catch 

### is heavily weighted. 98% 

### of the catch 

### for t1.e entire season came from one tow at the Cedar Point station {personal communication, D. H. 

### Davies, 9-6-77). 

### Table 4.2-9 : The 

### life stage labeled. "young" 

### should be "young-of -the-year" 

# . Table 4.2-11: 

### Gill ne:: total catch for longnose 

### gar 

### is 3, 

### not 0. 

### Table 4.2-13: The 

### spr:.ng collection labeled 

### as a 

### gill net 

### is really a 

### trawl that was mislabeled. 

### Most 

### of the values, however, were added into the correct total 

### column. Table 4.2-13: Mean eP:2 

### for rainbow smelt is 0.6, 

### not 0.8. Table 

### 4-2-13: Mean CP:I 

### for white 

### crappie 

### is 1.4, not 0.8. Table 4.2-14: The 

### yelLow perch catches 

### by age class for station 12 do 

### not add 

### up 

### to 1283.240 Table 4.2-14: On the computer printouts we received from the 

### DNa,, the freshwater drum total for station 14 had been changed from 390 to 410. This changes the 

### CPE from 78 to 82, the catch over all 

### age groups from 662 to 

### 682, and 

### the mean 

### CPE from 66 to 68. Table 

### 4.2-14: One 

### of the 

### 1230 young-of-the-year 

### gizzard shad in the station 

### 14 trawl should 

### be listed as a yearling or possibly 

### an adult. Table 

### 4.2-14: 

### All 54 smelt 

### in station 

### 12 trawl should be listed 

### as YOY. Table 

### 4.2-15: 

### All totals are displaced 

### from the correct species by 0 one line. 

### Table 4.2-15: Station 12 trawl data for 

### smelt should include 

### 10 adults not listed 

### in the table. Table 

### 4.2-15: Station 14 trawl for smelt YOY should be 9, not 

### 2. This r yields a total catch of 9, not 2, and 

### a CPE 

### of 3.0, not 

### 0.4. The totals and mean CPE over all age groups 

### are therefore 

### also wrong. Table 

### 4.2-15: 316b) 

### shows all 5 trout-perch in station 

### 12 trawl. 

### as YOY. The DNR printouts show both YOY and yearlings. Table 

### 4.2-15: 25 trout-perch caught 

### in station 

### 14 trawl have 

### been omitted. The 

### trawl total thus 

### is 30, not 5, and 

### mean CPE 

### is 4.7, not 0.5. Table 

### 4.2-16: 316(b) indicates no sampling 

### was done 

### in the fall. Cole's data, however, 

### show that there 

### was sampling done in the fall and that shiners 

### and white 

### bass were caught.241 Table 4.2-19: The 197C 

### estimates are incorrect 

### because of the mislabeling 

### error in Table 4.2-10. 

### Most of the 

### 1970-75 means 

### are therefore also wrong, 

### but only 

### by 1-49. Table 4.2-19: The 197:. 

### smelt estimate 

### is wrong (should be 61,000 

### not 70,000) because of the incorrect CPE value in Table 4.2-14. Table 4.2-19: The 197,1 

### estimate for freshwater 

### drum 

### is incorrect (should be 5,953,000 n3t 5,761,000) 

### because of the 

### error in Table 4.2-14. Table 4.2-19: The 197; smelt estimate 

### is low (should be 532,000 not 419,000) because of thz 

### error made in Table 4.2-15. Table 4.2-19: The 1973 

### trout-perch 

### estimate is greatly underestimated (410,000 not 44,000) 

### bxause 

### of the 25 fish omitted in Table 4-2-15, Table 4.2-20: 1974 frzshwater drum estimate 

### is incorrect 

### (from Table 4.2-19) 

# - Table 4.2-20: 1975 smslt estimate is incorrect (from Table 4.2-19). Table 4.2-20: 1975 trxat-perch 

### estimate 

### is wrong (from Table 4.2-19). Table 4.2-20: There are 

### several other errors 

### in the age 

### class divisions arising 

### from 

### errors in Tables 4.2-14 

### and 4.2-15. Table 4.2-21: August 1-4 

### estimate for 

### gizzard shad 

### is reported by 

### CLEAR 

### as 9.5 x 

## lo5, not 9.5 

### x 10 9

# . The mean value, however, 

### is correct. Peak shad population thus appears 

### to be in early June instead 

### of in August 

### as reported 

### on p. 4.2-25.

## -- 242
Table 4.2-25: July 2 count 

### for station 8 

### (bottom) is 0.4, 

### not 1.4. Table 4.2-26: July 2 count 

### for station 

### 10 (surface) 

### is 35.0, 

### not 33.8. 

### Table 4.2-31: 

### All data 

### for station 

### P-16 is displaced 

### from the 

### carrect 

### species column. Figure 

### 4.2-1: According 

### to 316(b) Literature Cited, the reference 

### should be Hartman 

### (a), 

### not Hartman tb). Chapter 

### 5 p. 

### 5.2-1: Gizzard 

### shad are said to make 

### up 

### 51.8% 

### of 

### the impingement 

### 10s Calculations of extrapolated impingement losses of fish at the Monroe power Plant over a 12-month period are presented in Subsection 4.3.2. An estimated total of 861,000 fish uere impinged during this time, of which 01.8 percent were gizzard shaQand 14.2 percent uere yellow perch. The

third moat frequently impinged fish uere shiners, uhich comprised 12.7 percent of the calculated 12-month total.

, - 

### However, according 

### to p. 4.3-1 

### and Table 4.3-1, gizzard shad comprised 

### of impinged 

### fish.

,- . fminaement at the Monroe Power Plant uas extrapolated to 861,000 fish 1976 (Table 4.3-1). Of this 14.2 percent were yellow perch, spp.), 7.0 percent were freshwater drum, and 4.3 percent were white bass. Other species were impinged less frequently.

### 243



### .-> 

### u Gitzara ahad Aleuitc Rslnbou salt Shiners trouf-pcrch Logperch Yil1et.c -1e:low perch bhlte bua 73 117 122 14434

'113 47 6 47331

206 11552 21 1 53 10184

37 52 104 889s 3689 4981h 18875 15801 T 81 1298 e 1928 11613 I2631 12679

55 120 233 37 140 369 121 9.3

~ S 35551 129P2 3164 13492 12921 5224 29060 627 2690 6056

46 22 1 36 1974 739 83239 76 69P 8191

15 39 14 1341 366 100719 143463 261197 9 472 227 609 6590 9689 2688 616 946 601

4 6 5% 8 1436 3378 992 122 224 23 

# a 1.3 0.8 11359 (1159 1658 5583

158 322 8998 5348

63 116 1966 47 12.7 0.6 0.1 (0.1 d4.2 12 -3 3777 49 160 74 QS9 122301 31235 4.3 Chncnel cmtfinh 60 66 64 204 31 10 186 79 364 15 29 20 1128 0.1 CMO rdwn 2 a.1 2 ROek ML5 64 28 21 27 15 9 29 5 83 83 56 360 tO.l ScaliaouZh bass 3 4 2 16 3 6 34 <0.1 freabwarer arua 7704 3187 14021 11799 10548 lS0U 2258 C87 1227 124 738 1051 60548 1.G VhitC crapplc Sunfirn 8 129 31 25 31 31 61 83 13 23 fP 55 169 25 34 2 38 20 36 40 19 34 29 (0.1 0.1 

### ' 2eg 783 Uorrbers pike Broun bullhead Yellow bullhead 3 2 11 4 

### '", 3 3 7 ? 24 10 16 15 6 2 9 9 (0.1 ID9

8 75 (0.1 40.1 GcXTiah Largcetuth bas cnmoou ULWS 77 1 102 53 10 3 6 73 2 3 8 3 95 '1 484 639 685 3 

# --- '836 92 6 2754 24 10 0.3 (0.1 <O.l Carp sucrera Other* 2 5 11 21 2 

### -a2 1 2 8 36 641 35 5 0.1 (0.1 (0.1 $4 3 3 5 1'12 752 41 1? Total3 12497f 76248 52232 l1911 4W3 110896 161509 32213 E61231 29572 1/92?

p. 5.3-3: Maximum staniing crop 

### of gizzard shad 

### is 2.9 

### X 

### log1 not 9.5 

## x 109 

## , due 

### to error 

### in Table 

### 4.2-21. p. 

### 5.3-4: Minimum percsnt 

### of gizzard shad 

### larvae 

### lost 

### is 0.3, 

### not 0.1, 

### due to 

### error 

### in Table 

### 4.2-21. Table 5.2-2: 

### Ohio fall 

### 1974 eetimate for shiners 

### is overestimated

(46,343,000 instead of 

### 82,913,000) 

### by an apparent error 

### in Table 

### 4.2-18. Table 5.2-2: 

### Most 

### of the Michigan 1970-75 

### means are incorrect 

### because of transfer 

### from Table 

### 4.2-19. Table 5.2-2: Michigan fall 

### 1975 estimates 

### for trout-perch and smelt are incorrect 

### by transEer 

### from Table 4-2-20,

# -- -- -- 

## --



# -- I I 

# -- -- -- 

# -- 

# -- I 244 

### Table 5.2-2: 

### Michigan fall 

### 1975 estimate 

### for shiners 

### is not the sme 

### as listed 

### in Table 4.2-20 

### from which 

### it supposedly came. Table 

### 5.2-3: Estimates listed 

### for smelt and freshwater 

### drum are 

### incorrect 

### by transfer from Table 5.2-2. 

### The percentage impinged 

### is therefore incorrect for these 2 

### species. Table 

### 5.3-1: CLEAR 

### weekly maximUm 

### for shad 

### is 2.9 x 

### 10 9 

### not 9.5 x 10

### 9 

# . Percentage 

### entrained 

### is thus 0.3, 

### not 0.1.

I 1.9 1.9 

# 9 1 .o 1.o 0.9 0.7 

# - - e 1.3 0.3 1 .'I 0.J 0.5 249.6 * U.8 

# ­ 0.1 35.5
to tea nti.


### Table 

### 5.3-1: 

### CLEAR mean value 

### for walleye should 

### be 2.5 x 

### 105 

### from

- 

### ..- Table 

### 4.2-21 below. 

### This results 

### in the tabulated percentage entrained of 163.7%. The 2.2 x 10 5 

### value yields 

### 186.0%.



# - mr AI Jlme aD8 Jub. a19 JUT AW. m- A2=u2kzSkL Uak23J3.l .u& aa0L-A' 

# - DirzaM b.Qd -(b) 4.1 1 le* 2.9 x io' 3.1 x 10' 1.3 r 10' 8.3 I 10. 1.2 x 10' 1.4 x 10' 5-1 E 10' YllnbM amlt 3.8

# - I lo' 3.5 I 90' 3.5 I IO' 2.6 x 10' 1.6 r 10' 2.5 x 10' 3.8 x M' L? I 10' 8.3 x 10' Carbld ahlner 

# - 7.4 x 10' 6.J I 10' 5.1 x 10: 5.3 I 10' 8.3 I 10' 1.2

# - 1 10' 7.6

# - x 1D' 2.0 x 10' SpDtCall shiner 3.v I 10' 3.7 a 10' 6.0 x 10 T.6 I 10' 2.3 X 10' 2.2 r 10' vrcinucar arm 3.1 I 10' 2.1 I 10. 1.0 x lo' T.O x 10' 4.9 I 10' 1.0

# - a io* 

# - - 2.I I IO' l*lloY parch 8.1 10' T.5 x 10. 1.1 x 10' 1.3 I 10' 2.0 I 10' 

# - 2.6 M' mite Bmsa 

# - 1.3 I 10' 7.1

# - 10' 2.0 I 10' 3.2 1 10' 1.6 n 10' 1.1 

# - io* __9 Wleya 

# - 1.1 I 10' I 7.4 x 10. iiwire 3.8 I 10' 1.1 I 10' 2.3 a 10' 1.01 

# - 10' tormrcb 

# - - . J.9 I 10' 1.9 a 10' 5.3 I 10' a. pram am. U0PUblIBh.d MCI &L.. b. 1Uh.a 1MlEmta 1a.ufflalml &La. e. Ibla -C nb clluy.d tu 4 to 6 to o~mot 111 m7aT 00 thauld Ubh.

### 245 Table 

### 5.3-3: 

### The 

### number; of alewife 

### and 

### shad larvae entrained 

### are not 

### the same as 

### those 

### in Table 5.3-1

5.7-7 P-- Population So. of Larvae Adult Eat Lmnte 

### s Lost to fable SDecies Entratned -(a1 -(b) ~eference(0) Aleuife p_3 Gizzard ahad Rainbon sselt Emerald shiner Channel catfish Lhitc baas lellow perch balleye Freshwater drum 35,619 0.0001 Mean oC 4.2-17 and 9.2-20 76,328 0.0007 Hean of 42-77 ad 4.2-20 722.821 419 3.8Ce) 4.2-20 170,299 2,654 0.04 4.2-20 719,528 1,851 0.2 4.2-20 391,945 20,815 0.00006 U.2-f7 4,996.92h ia ,942 0.02 4 .2-20 409 I 186 5,500 0.a03 4.2-20 1,114,515 14,200 0.005 u.2-20 a. Numbers taken from Table 5.3.2 and generated through 901 model. b. Beat estimate based on curreit abundance indices (see rationales developed in Subsection 5.2. $1. E. Rationales for estieates in ;hese tables presented in Subsection 4.2. d. Used 99.52 model based en Ro:hschllQ 1961. e. Estimated percent lost ?.a powlation ts too high if Canadian comwrolul harvest information ia consliered (Subsection 5.2.3).-- 3. Recipient's Accession No 5. Repart Date



### :.:arc;? 1978 5. E. Pedonning 0:ganiration Rept. No. .-.-- 

### _-___-__ . __.-- IO. Pmject/TasC/Work Cnil No. -. -__. 

## __ . - - 

# __ 11. ContractC) or Gnnt(G) No. 

# - (C) (GI 

## - 13. Type of Report & Period Coverec:
lementzry uotcs 

## -__--- 

# _- - act (Lknit: 200 words) 

### evaluation 

### serves (1) as a 

### det3ile2 critique of the S1onrc.e Plant 31G(b) 

### Istration;. 

### for use by the field staff 

### and other agencies 

### responsible for reviewin2 docrunent, am? (2) by way of 

### exmsle, as a guide to assist the field staff in tneir 

### !w of 316(bl demonstrations for other Great Lakes region poi.& plants.

.merit Analysis a. Dcscriplors

cntifierslOpen-Ended Tcrms 

### Erie, F-aisin 

### Xver, fish fish 

### eggs, 

### fish larvae, yelio+jperch, entrainment, ngement 3SATI 4etdlGmug

# Reproduced by 

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