ML20198T070
| ML20198T070 | |
| Person / Time | |
|---|---|
| Site: | FitzPatrick  |
| Issue date: | 05/31/1986 |
| From: | EA ENGINEERING, SCIENCE & TECHNOLOGY, INC. |
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| References | |
| NMP11K, NUDOCS 8606110284 | |
| Download: ML20198T070 (45) | |
Text
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'I I New York Power Authority l
I I O
. ~
I g
I I May 1986 I
g James A. FitzPatrick Nuclear Power Plant 1985 I SPDES Annual Biological Monitoring Report I
I I
l I EA ENGINEERING, 1 SCIENCE, AND /
TECHNOLOGY, INC. N g ag e :88= 88888 6 R PDR
>/i
EA Report NMP11K JAMES A. FITZPATRICK NUCLEAR POWER PLANI 1985 SPDES ANNUAL BIOLOGICAL MONITORING REPOEI SPDES PERMIT NO. NY 002 0109 SECTION IV I
Prepared for New York Power Authority James A. FitzPatrick Nuclear Power Plant Lake Road, P.O. Box 41 Lycoming, New York 13093 Prepared by EA Science and Technology R.D. 2', Coshen Turnpike Middletown, New York 10940 A Division of EA Engineering, Science, and Technology, Inc.
May 1986 I
CONTENTS PJLEA
- 1. INTRODUCTION 1-1
- 2. METHODS AND MATERIALS 2-1 2.1 Schedule (Permit Section 11.B.1) 2-1 2.2 Sampling Procedure (Permit Section ll.B.2,3,4,5) 2-1 I 2.3 2.4 2.5 Laboratory Processing (Permit Section 11.B.4)
Water Quality Determinations (Permit Section ll.A)
Data Presentation (Permit Section 11.C) 2-4 2-4 2-4 2.6 Collection Efficiency (Permit Section ll.B.6) 2-5
- 3. RESULTS 3-1 I 3.1 3.2 3.3 Impingement Abundance and Composition (Permit Section ll.C.3)
Length Distributions (Permit Section 11.B.4)
Biomass (Permit Section ll.B.4) 3-1 3-3 3-15 3.4 Water Quality (Permit Section ll.A) 3-15 3.5 Historical Impingement Comparisons (Permit Section 11.C.3d) 3-18 REFERENCES APPENDIX A - EXCEPTIONS TO STANDARD OPERATING PROCEDURES APPENDIX B - PLANT OPERATING CONDITIONS APPENDIX C - SCIENTIFIC AND COMMON NAMES OF ALL TAXA COLLECTED IN 1985 l
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_ _ _ _ _ _ _ _ _ _ _ _ _ _ _ ________]
LIST OF TABLES Number Title 2-1 Impingement Sampling Intensity as Required by the SPDES Permit for the James A. FitzPatrick Nuclear Power Plant, 1985.
I 2-2 Impingement Sampling Dates for the James A. FitzPatrick Nuclear Power Plant, 1985.
I 3-1 Actual Monthly Impingement Collection, James A. FitzPatrick Nuclear Power Plant,1985.
3-2 Mean Daily Impingement Rates by Species at James A. FitzPatrick Nuclear Power Plant, 1985.
3-3 Monthly Impingement Rate Based on Flow at the James A. FitzPatrick Nuclear Power Plant, 1985.
3-4 Estimated Monthly Impingement Based on Daily Average Rate at James A. FitzPatrick Nuclear Power Plant, 1985.
3-5 Estimated Monthly Impingement Based on Flow at James A. FitzPatrick Nuclear Power Plant, 1985.
3-6 Length Distribution of Select Representative Important Species Impinged at James A. FitzPatrick Nuclear Power Plant,1985.
3-7 Total Biomass of Impinged Organisms Collected at James A. FttzPatrick Nuclear Power Plant, 1985.
3-8 Estimated Monthly Biomass of Collected Taxa at James A. FitzPatrick Nuclear Power Plant, 1985.
I 3-9 Estimated Monthly Impingement (by Flow) at James A. FitzPatrick Nuclear Power Plant, 1976-1985.
3-10 Estimated Impingement Abundance (by Flow) for Dominant Species at James A. FitzPatrick Nuclear Power Plant, 1976-1985.
3-11 Estimated Impingement Abundance (by Flow) for the Representative Important Species at James A. FitzPatrick Nuclear Power Plant, 1976-1985.
I
- 1. INTRODUCTION James A. FitzPatrick (JAF) nuclear power plant is located on the shore of Lake Ontario approximately 11 kilometers (7 miles) northeast of the City of Oswego, I New York. JAF is an 821-MWe boiling water reactor with the water intake structure located near shore in approximately 7.3 meters (24 feet) of water and the discharge, with a 236-meter (774-f t) diffuser, located offshore in approxi-mately 9.1 meters (30 feet) of water.
Aquatic organisms, detritus, and debris enter with the water pumped from the I
vicinity of the submerged intake structure. Organisms, detritus, and debris flow through trash racks, which are used for removing large items, such as logs, and are impinged on traveling screens, which are used for screening out smaller materials. Periodically, the traveling screens are rotated and washed I to remove any accumulation of impinged organisms or other material into a sluiceway which empties into an impingement collection basket. The aquatic organisms impinged at JAF nuclear power plant have been monitored yearly since 1975 in order to estimate species abundance and composition.
This report presents the results of aquatic ecological studies conducted by EA Science and Technology, a Division of EA Engineering, Science, and I Technology, Inc. , during 1985, as required by the State Pollutant Discharge Elimination Systems (SPDES) Permit No. NY 002 0109 Section IV (dated 1 November 1985) covering the New York Power Authority's (NYPA) JAF nuclear powar plant.
Irapingement catches were monitored on a frequency of 4-20 samples per month irom January through December 1985 (a total of 73 samples in 1985).
Impingement sampling at JAF in 1985 resulted in the collection of 192,923 organisms. The collection was categorized into 28 fish taxa; of the 28 taxa, 2 were families, the remaining 26 were species. Two invertebrate taxa (crayfish and clam) were also represented in the 1985 samples. Alewife was the most numerous species (180,994) comprising 94 percent of the total catch.
I Alewife, rainbow smelt, and gizzard shad accounted for 99 percent (190,534) of all fish collected (192,798).
As required by correspondence from NYPA to the Nuclear Regulatory Commission, I (NYPA 1981, personal communication) all fish impingement samples are checked for the presence of the Asiatic clam (Corbicula sp.). No Corbicula sp.
molluscs were found in the 1985 impingement collections.
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l-1
- 2. METHODS AND MATERIALS 2.1 SCHEDULE (PERMIT SECTION 11.B.1)
In accordance with permit requirements, 78 impingement collections were I scheduled between 1 January and 31 December 1985. The new permit decreases the number of samples in June from 6 to 4, and increases the schedule in August from 4 to 6. The scheduling change did not occur until July 1985 resulting in I two additionally scheduled samples in August. The annual schedule of samples (Table 2-1) shows a total of 80 scheduled samples. Table 2-2 lists the scheduled sampling dates for 1985.
Samples were collected over a 24-hour period on randomly selected days.
Randomly selected sample dates were scheduled such that no more than 10 days occurred between samples.
In 1985, the actual number of completed samples was 73. From February through June 1985, JAF nuclear power plant was shut down for refueling and maintenance.
During the outage, the main circulating water pumps and the traveling screens were shut down for extended periods of time. Whenever the screens were operating, attempts were made to collect impingement samples regardless of whether the main circulating water pumps were operating, although the SPDES I permit does not require sampling when the pumps are shut down. Maintenance on the traveling screens prevented sample collections in March 1985. A total of 13 of the 16 scheduled samples were collected in April. During April and May, scheduled sample dates were of ten changed to conform with working conditions at the plant. On three other occasions in the year, maintenance on the traveling screens prevented samples from being collected on scheduled dates. These samples were rescheduled and successfully collected on other available dates
( Appendix A) .
2.2 SAMPLING PROCEDURE (PERMIT SECTION 11.B.2,3,4,5)
Samples were initiated around 1300 hours0.015 days <br />0.361 hours <br />0.00215 weeks <br />4.9465e-4 months <br /> of the sampling day. At the beginning of the sample collection period, the traveling screens were rotated and washed I for 15 minutes. The collection basket, with a 9.5-mm (3/8-in.) stretch mesh liner, was then positioned at the end of the sluiceway. The collection basket remained in place for the duration of the sample, unless high impingement or debris loads required that it be emptied, in which case it was removed, emptied, and repositioned.
l - At the end of the 24-hour period, the traveling screens were rotated and washed for 15 minutes. The impinged organisms were washed into the collection basket, and the basket was removed and emptied.
I Plant operational data were obtained for each sample date to document cooling water flow rates, intake and discharge temperatures, and power production (Appendix B).
j A subsampling routine was utilized for occasions when high impingement rates or l high debris loads were encountered. The subsampling technique was based on volume, and the total 24-hour catch was estimated using the formula:
t 2-1 I
I I TABLE 2-1 IMPINGEMENT SAMPLING INTENSITY AS REQUIRED BY THE SPDES PERMIT FOR THE JAMES A. FITZPATRICK NUCLEAR POWER PLANT.1985 I Number of Sampling
__ Month Days Scheduled eer Month ( a)
January 4 February 4 March 4 April 16 May 20 I June July August 6
4 6(b)
September 4 I October November December 4
4 4
(a) Days assigned within each month were selected randomly using random numbers tables (Rand Corporation 1955).
(b) A change in the SPDES Permit (Section II.B.I) now requires 6 samples to be completed in August and 4 in June. This I change was required in July 1985. At that time, 6 samples had already been completed in June. For 1985 only, the number of scheduled samples was 80.
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I I TARE 2-2 INPilMFHENT CAMPLING MTES FOR TE JAMES A. FITZPATRICK ElCLE a w e Pt af,_j g __
Scheduled Scim!nled S m ling Saarlins Datet._ "aeulioLResulte __Date3 _ SaarlinLEssults.__
04 JAN C 18 MY Rtti Completed 25 MY 10 JAN C 19 MY R*Ci CoopIsled 26 MY 18 JAN C 22 MY R8Ci CoePlated 27 MY I 25 Jidi 04 FEB 14 TEB C
R8Ci Complet+4 04 FEB C
23 MY 24 MY 30 MY 31 MY R*Ci Completed 20 MY RtCi Completed 29 MY C
C 21 FEB 01 JtW I
C C 28 FEB C 06 JW C 00 MR V 07 .AJN C 13 MR V 11 JtW RtCi Completed 10 JIN I ?! HAR 28 HAR 02 AF1t V
V RICi Completed 18 APR 21 JtW 27.AW 23 JW C
C C
03 APR R$CI Coseleted 20 AIR 02 Jtt RIC; Completed 10 J!L 05 MR RICi CcePleted 11 APR 11 JUL C 09 APR RSCI Completed 22 APR 19 Jtt C 10 APR RtCi Completml 30 APR 25 .RL C 12 APR V 16 APR C 02 AUC C 17 APR C 09 AUG RtCi CoePIste'l 15 AUG 19 APR C 14 AllG C 24 APR V 19 AUG C 25 APR I
V 21 AUC C 24 APR C 29 AUG C 27 APR C 28 APR C 04 SEP C W MR C 12 EP C I 01 MY 02 NAY 05 MY C
C C
20 CEP 24 SEP 03 007 C
C C
06MY C 11 OCT C 07 MY C 21 OCT C 03 MY C 31 OCT C 09 MY C j 10 MY C 07 NOV C i E 11MY C 12 NOV C E 23 MY 14 MY C
C 22 N0v 26 NOV C
C 15 MY C 16MY C 04 KC C 12 KC C 18 KC C 23 KC C E0TE! T E ConPleted SasPle.
Rtc : Samples rvscheduled and coepleted on a different. date within the confines of a randos numbers table and any remainins available dates in the sonth.
- = Saarle collection date.
V = Void sanelve sample not C0ePleted (APPefMIiX A).
I I
I Estimated No. of Fish = Volume of Total Samole x No. of Fish in Aliauot in Total Sample Volume of Subsample The volume of the total sample was determined by repeatedly filling a volume-trically graduated container, recording the values, and adding them. The total I volume was thoroughly mixed by hand or with a shovel and spread out evenly over a flat surface. An aliquot (s) of the total sample was randomly selected and this portion of the sample was removed and measured to determine its volume.
I During 1985, subsamples constituted at least 25 percent by volume of the total sample. The fish in the subsample were then processed according to regular laboratory procedures (Section 2.3) .
2.3 LABORATORY PROCESSING (PERMIT SECTION 11.B.4)
After the impingement sample was collected, it was returned to the laboratory and all organisms were sorted, identified, and enumerated. Identification was made to the lowest possible taxonomic level, which was usually species. For the convenience of the reader, common names are used in the text, however, a list of common names and their associated scientific names are include'd in Appendix C.
specimens (to a maximum of 25 individuals) of the following species were I analyzed for length and weight: white perch, alewife, rainbow smelt, small-mouth bass, yellow perch, and each species of salmonid. Any other species ,
present in the collections were enumerated and weighed to obtain a total count and total weight for each species (or lowest taxonomic level).
Total lengths were measured to the nearest millimeter. For the purposes of this report,100 millimeters were used as a determinant of size class differ-entiation between young of the year and adults based on size sample information in Scott and Crossman (1973) . Weights were meacured to the nearest 0.1 gram for specimens less than 10 grams, to the nearest 1.0 gram for specimens between 10 and 2,000 grams, and to the nearest 25 grams for specimens over 2,000 grams based on the precision of the scales used for measurement. Any unusual con-ditions, abnormalities, or presence of fish tags were noted on the data sheets.
2.4. WATER QUALITY DETERMINATIONS (PERMIT SECTION ll .A)
At the onset and completion of each impingement sample, intake and discharge temperatures (S).5 C) were determined from a bucket of water retrieved at both locations.
2.5 DATA PRESENTATION (PERMIT SECTION ll .C)
Data are presented according to the requirements set forth in the SPDES permit.
t Monthly "mean" is equal to the total number of fish impinged by species on all sampling days in a given month divided by the total number of sampling days.
Annual ,"mean" is equal to the total number of fish impinged by species on all sampling days in the year divided by the total number of sampling days in the year.
I 2-4
I I Total estimated impingement for each month was calculated using the formula:
D=h(x) where D = total estimated impir.gement c = the number of fish collected during the sampling period I v = the volume of cooling water used during the sampling period x = the total monthly volume of cooling water used.
The annual impingement estimate was then calculated by adding the 12 monthly I ~
impingement estimates.
2.6 COLLECTION EFFICIENCY (PERMIT SECTION ll.B.6)
To assess the efficiency of the traveling screens in removing impinged organisms from the circulating water intake system, a callection efficiency I study will be conducted at JA7. The study will be submitted to the New York State Department of Environmental Conservation and, subject to approval, will be perfctmed in 1986.
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2-5
- 3. RESULTS I 3 .1 IMPINGEMENT ABUNDANCE AND COMPOSITION (PERMIT SECTION 11.C.3)
Impingement sampling at the JAF nuclear power plant during 1985 resulted in the collection of 192,923 organisms. The collection was categorized into 28 fish taxa; 2 were identifiable to the family level and 26 to the species level. Two invertebrate categories (crayfish and clam) were also represented in the 1985 samples (Table 3-1) .
Alewife was the most numerous species, comprising 94 percent of the total I catch. Alewife, together with rainbow smelt and gizzard shad, accounted for 99 percent of the total catch.
Because no samples were collected during March 1985, no one species was collected in all 12 months of the year. Alewife, rainbow smelt, and spottail shiner were collected in 11 months during 1985. Trout perch, sculpins, rock I bass, and crayfish were found in the samples during 9 months of 1985. White perch were found in 8 months of 1985. Yellow perch and smallmouth bass were collected in 6 months of 1985. The salmonids as a group were represented by three species (lake trout, brown trout, and rainbow trout) which were each collected during 2 months of 1985.
Species diversity in 1985 was highest in the winter (January and February),
spring (April and May), and late fall (December). The number of species represented in impingement collections ranged from 20 in January to 5 in October 1985.
In January and February, the sample collections were dominated by rainbow smelt. Alewife dominated the impingement in April, May, June, and July, with May being the month of peak impingement in 1985. Alewife comprised 97 percent of the fish impinged in April. The percentage rose in May (99 percent) and June (99 percent) and dropped to 98 percent in July. In August and September, rainbow smelt rose in abundance to dominate the impingement. I. total of I 65 percent of the August collections and 55 percent of the September collec-tions were rainbow smelt. Alewife again dominated the impingement in October and November, comprising 87 percent of the samples in October and 97 percent in November. Rainbow smelt dominated the samples in Decemb r, comprising 48 percent of the fish collected. A peak in the impingement of white perch occurred in January and was the result of an increase in the number of young of the year and existing meteorological conditions. A total of 41 percent of I all yellow perch were collected during the month of August. No abundance peaks in the impingement collections were seen for smallmouth bass or the salmonid group. ,
Generally, greater impingement collections occurred during the spring and early summer months as adult fish (particularly alewife and rainbow smelt) migrated inshore to spawn. Impingement decreased in the summer as the fish finishcd spawning and moved offshore to cooler, deeper water. The increase in abundance in the fall and winter months was caused by an increased occurrence of young of the year in the impingement (Section 3.2) . Often high impingement rates, in isolated occurrences, were the result of strong west or northwest winds and corresponding high wave action. Previous samples in the Nine Mile Point 3 -1
M M M _
m M M restr 1-1 ein nnWIILLIBEIllGOENT inIECIIDWSa.JeHER L rIIZPAIEIClLIAICLEAR.EfEFP F1aMTs.Jf" Annual
% elec _JeiL EEB liet _.aER. __flAL. 11W. 1L. .auS_ .SEE. OCI _.liOU. _DEC. _Iotal.
No. of Saarles 4 4 0 13 20 6 4 6 4 4 4 4 73 Alevife 198 8 NSC 14,693 114,924 24 596 4,735 1 409 1,799 301 16,300 26 180,994 Rainbow seelt 17185 423 NSC 377 804 100 12 2sB03 2:306 41 117 629 8,799 Gizzard shad 374 41 NSC -- - -- -- ---
12 -
16 298 741 Threestine stickleback 161 285 NSC 2 8 -- - - --
36 43 535 lihlte bass 25 - NSC -- --- - --- -- --- --
311 116 452 Trout eerch 4 i NSC 24 176 60 44 3 1 - 4 ---
317 IAsite Perch 87 34 NSC 6 32 12 ---
4 -- --
20 16 211 Scu1rin family (non-ricel) 12 32 NSC 25 36 8 12 17 - -
17 41 200 Srottail shtrwr 22 9 NSC 6 4 16 40 21 44 1 5 5 173 Tessellated darter 4 1 NSC -
40 8 17 23 - -
4 -
97 Cravfish 4 25 NSC 3 20 8 3 1 4 28 96 Bluestli --
3 NSC - -- - -- -- - - -
57 60 Rock bass 3 9 NSC 7 4 4 2 3 2 +-- --
12 46 Stonecat 4 6 NSC 5 12 4 5 -- -- -
1 37 Yellow rerch 1 1 NSC -
4 -- ---
14 -- ---
4 8 34 Smalleouth bass 2 6 NSC 5 --
4 5 1 23 Cravfish (damaged) --
9 NSC -- --- -
2 ---
7 - -- -
18 White sucker 1 -
NSC 1 4 -- 1 $ 1 1 14 Eserald shiner 4 4 NSC 1 4 13 Puerkinseed -
- NSC - - -- --
4 9 13 Clan 1 --- NSC ---
4 -- --- --- --- --- --
5 10 American eel (daeased) -- - NSC - - - --
2 4 -
4 -
10 American eel --
--- NSC -- -- --
3 --
4 -- --- --
7 Lake trout - - NSC -- -- - --
1 4 5 Minnov family (damaged) -
--- NSC -- --- - --- --- -- --- ---
4 4 Sea laePres - - NSC -
4 - -- - -- --- -
4 Brown trout 1 - NSC -- - -- -
1 --- --- --- ---
2 Central sudainnow 2 -- NSC - - -- -- - -- --- -
2 Rainbow trout - --- NSC --- -- -- --
1 1
2 Brown bullhead -
1 NSC - -- - - - -- - -
1 Lake chub - -- NSC 1 --- -- -- -- -- -- --- --
1 Longnose dace - - WSC 1 1
Clae (dasaged) - -- NSC - -- -- -- --
1 --- -- ---
1 Total 2,097 900 NSC 15:162 116:076 24e820 6:281 4:313 4:181 345 16 842 1:306 192e923 NOTE! NSC = no saePles collected. !! ashes ( - ) indicate no catches Sade.
i
I i vicinity (EA 1982, 1983, 1984, 1985) have indicated that the rates of impinge-ment are affected by specific weather conditions such as high winds from the northwest or west, and associated wave action. At JAF, the above stated meteorological occurrences were responsible for the high impingement numbers for the month of January 1985. On 24 and 25 January, winds of 10-25 knots from the west and associated high waves were responsible for the collection of 77 percent of the rainbow smelt and 83 percent of the white perch collected in January.
The mean daily impingement rate (Table 3-2) was highest for the month of May and is reflective in the presence of large numbers of alewives moving inshore to spawn. In general, the mean daily impingement rates reflect the same trends seen in Table 3-1.
Impingement rates based on flow (Table 3-3) are lower than the mean daily impingement rates since the number of fish collected is expressed by volume (number per million cubic meters) of circulating water pumped. Outage conditions and changes in the volume of water pumped during day-to-day plant operations would account for some of the variation in rates of impingement between the two methods of data expression. A plant outage in April with a relatively small volume of water pumped during the samples increased the rate of impingement based on flow for the month.
The estimated number of aquatic organisms impinged at JAF (based on daily average rate) was 607,643 (Table 3-4) . The estimate of impinged organisms based on flow was 595,969 (Table 3-5) . The differences in the two estimates may be attributed to the two bases from which the estimations were made and the influence of plant operating conditions and weather on data collected. Esti-mated annual alewife impingement for the year was 534,374 and 522,672 (respec-tively) for both methods. These values represented 88 percent of the total estimated annual impingement (same percent for both methods). Estimated impingement of rainbow smelt based on a daily average rate was 52,716, esti-mated impingement of rainbow smelt based on flow was 52,789 and represents 9 percent (percentage equivalent for both methods) of the total annual estimated impingement.
Estimated impingement bared on daily average rate for the other representative important species (RIS) are as follows: white perch - 1,331, yellow perch
- 200, and smallmouth bass - 133. Estimated impingement based on flow for the RIS are: white perch - 1,324, yellow perch - 202, and smallmouth bass - 128.
Variations in the impingement estimate may be attributed to the two bases from which the estimates were made and which are influenced by plant operating conditions (flows) and meteorological conditions.
3.2 LENGTH DISTRIBUTION (PERMIT SECTION ll .B.4)
Length-frequency distributions are given for the representative important species (RIS): alewife, rainbow smelt, white perch, yellow perch, smallmouth bass, and the salmonid group which includes brown trout, rainbow trout, and lake trout (Tables 3-6a through 3-6g) . Alewife collections were dominated by adults and subadults in 6 months of 1985, from January through July. Young of the year dominated the alevife collections from August through December.
3 -3
M M m r 1-2__lfEAN MILLINEllNiEHEMLEAIE BLSEECIrn at wS_A _EIIZEAIEICLEUCLEat_EDER_ELAMIa_1m Annual
__JeN_ __EEB Het eER.- HAL. ___JulL. ___JtL__ __eUG_ W _ _0CL ___NOIL. _DEC. __Heaa._
No. of Saarles 4 4 0 13 23 6 4 6 4 4 4 4 73 Seecies Alewife 49.50 2.00 NSC 1 130.62 5,746.20 4,099.33 1 683.75 234.83 449.75 75.25 4:075.00 6.50 2:479.37 Rainbo.s saett 296.25 106.25 NSC 29.00 40.20 16.67 3.00 467.17 576.50 10.25 29.25 157.25 120.53 Gizzard shad 93.50 10.25 NSC - - - - -
3.00 - 4.00 74.50 10.15 ThreesPine stickleback 40-25 71.25 MSC 0.15 0.40 - - - -- --
9.00 10.75 7.33 White bass 6.25 - NSC - - - - - -- -
77.75 29.00 6.19 front Perch 1.00 0.25 NSC 1.85 8.80 10.00 !!.00 0.50 0.25 -- 1.00 -
4.34 White cerch 21.75 8.50 NSC 0.46 1.60 2.00 --
0.67 -- -
5.00 4.00 2.89 Scu! Pin fanity 3.00 8.00 NSC 1.92 1.80 1.33 3.00 2.83 - --
4.25 10.25 2.74 SPottail shiner 5.50 2.25 NSC 0.46 0.20 2.67 10.00 3.50 11.00 0.25 1.25 1 25 2.37 Tessellated darter 1.00 0.25 NSC -
2.00 1.33 4.25 3.83 -- -
1.00 --
1.33 Cravfish 1.00 6.25 NSC 0.23 1.00 1.33 0.75 0.17 - --
1.00 7.00 1.32 Bluesill -- 0.75 NSC - --- -- - -- -- --
-- 14.25 .82 Rock bass 0.75 2.25 HSC 0.54 0.20 0.67 0.50 0.50 0.50 - -- 3.00 .63 Stonecat 1.00 1.50 NSC 0.38 0.60 0.67 1.25 --- --- -
- 0.25 .51 Yellow perch 0.75 0.25 NSC -
0.20 -
- 2.33 -- -
1.00 2.00 .47 Smallaouth bass 0.50 1.50 HSC 0.38 -
0.67 1.25 0.17 - -- --- -
.32 Crasfish (damased) - 2.25 NSC - -- --
0.50 ---
1.75 - - -
.25 White sucker 0.25 - NSC 0.08 0.20 -
0.25 0.83 0.25 0.25 - -
.19 Emerald shiner 1.00 1.00 NSC 0.08 -- - -- - - - -
1.00 .18 Punekinseed ---
- NSC -- - --
--- 0.67 - -- --
2.25 .18 Clan 0.25 - NSC -
0.20 -- - - - -
-- 1.25 .14 American eel (dasased) --
-- NSC - --- --
- 0.33 1.00 -
1.00 --
.14 American eel *
- NSC - - -
0.75 -
1.00 - - -
.10 Lake trout ---
- NSC -- - --
--- 0.17 -- -
- 1.00 .07 Nirnos family (damaged) - - NSC - - - - - - -
- 1.00 .05 Sea laaPres --
--- NSC --
0.20 -- - - -- - - ---
.05 Brown trout 0.25 - NSC - -- -
- 0.17 - -- -- -
.03 Central nudainnov 0.b0 - NSC - - - -- -- -- - - --
.03 Rainbow trout -
- NSC - - --
-- 0.17 - 0.25 - -
.03 Brown bullhead - 0.25 NSC - - - -- - - - -- -
.01 Lake chub -
- NSC 0.08 - - - - - - - -
.01 Lonsnose dace ---
- NSC 0.08 -- -- - -- - - --- --
.01 Clas (dasased) --
- NSC - -- -- - --
0.25 - - -
.01 Iotal 524.25 225.00 NSC 1,166.31 3,803.80 4:136.67 1s720.25 718.84 1:045.25 84.25 4e210.50 326.50 2:442.79 NOTE! NSC = no sanPles collected. Dashes ( - ) indicate no Catches made.
M M M M -
M M ram r 1-1 mIE LWINGEMENI_EAIF RAcIn DN_EL0iLAI.IHr taarn a. FIT 7PATEffT MID FAP Pf1MFP Pt ANT. 19R's Annual IAN _EER__ ME AP9 __.M Y_ m __JtL__ __AUG _ __SEE__ _0CI_ ___NOV_ __DEC__ _Jotal_
No. of SaaPles 4 4 0 13 20 6 4 6 4 4 4 4 73 Flow (MCM) 7.486 6.107 0 8.992 28.044 11.088 8.267 10.566 8.984 8.699 8.212 7.995 114.440 Seecies Alewife 26.449 1.310 NSC 1 634.564 4 097.989 2,218.254 814.685 133.352 200.245 34.602 1,984.900 3.252 NA Rainbou smelt 158.295 69.592 NSC 41.926 28.669 9.019 1.452 265.285 256.679 4.713 14.247 78.674 NA Gizzard shad 49.960 6.714 NSC --- - - --
- 1.336 -
1.948 37.273 NA Threespine stickleback 21.507 46.668 NSC 0.222 0.285 - -- -- - -
4.384 5.378 NA White bass 3.340 - NSC -- -- -- -- --- --- --
37.871 14.509 NA Trout perch 0.534 0.164 NSC 2.669 6.276 5.411 5.322 0.284 0.111 ---
0.487 ---
NA White Perch 11.622 5.567 NSC 0.667 1.141 1.082 --- 0.379 --- ---
2.435 2.001 NA Sculpin family 1.603 5.240 NSC 2.780 1.284 0.722 1.452 1.609 -- --
2.070 5.128 NA Spottail shiner 2.939 1.474 NSC 0.647 0.143 1.443 4.839 1.988 4.898 0.115 0.609 0.625 NA Tessellated darter 0.534 0.164 NSC -
1 44 0.722 2.056 2.177 -- -
0.487 --
NA Cravfish 0.534 4.094 NSC 0.334 0./d, 0.722 0.363 0.095 --- -
0.487 3.502 NA Bluegill - 0.491 'NSC - --- - --- --- --- --
--- 7.129 NA Rock bass 0.401 1.474 NSC 0.778 0.143 0.361 0.242 0.284 0.223 ---
--- 1.501 NA Stonecat 0.534 0.982 NSC 0.556 0.428 0.361 0.605 -- -- --
--- 0.125 NA Yellow perch 0.401 0.164 NSC ---
0.143 -- ---
1.325 -- ---
0.487 1.001 NA Smallmouth bass 0 267 0.982 NSC 0.556 -
0.361 0.605 0.095 - - --- ---
NA Cravfish (damased) -- 1.474 NSC -- --
-- 0.242 --- 0.779 --- - ---
NA idhite sucker 0.134 - NSC 0.111 0.143 --
0.121 0.473 0.111 0.115 -- ---
NA Emerald shiner 0.534 0.655 NSC 0.111 --- -- -- --- --- ---
--- 0.500 NA PuePkinseed --
- NSC -- - - --
0.379 -- -
--- 1.126 NA Clan 0.134 -- NSC -
0.143 --- --- --- --- ---
--- 0.625 NA American eel (damased) -
- NSC -- - -
-- 0.189 0.445 ---
0.487 -
NA American eel --
- NSC -- - --
0.363 - 0.445 -- --- --
NA Lake trout -
-- NSC --- -- --
--- 0.095 -- -
-- 0.500 NA Minnow family (damaged) -
- NSC --- - - --- - - ---
--- 0.500 NA Sea lanPres -
- NSC ---
0.143 --- - --- --- --- --- ---
NA Brown trout 0.134 -- NSC -- - --
--- 0.095 - - --- ---
NA Central audainnou 0.267 -- NSC - --- --- --- --- --- --- --- ---
NA Rainbow trout -
- NSC - - --
--- 0.095 -- 0.115 -- ---
NA Brown bullhead - 0.164 NSC -- --- -- --- --- - --- --- --
NA Lake chub -
- NSC 0.111 -- - --- -- - --- --- ---
NA Longnose dace --
-- NSC 0.111 -- -- --- --- --- --- --- ---
NA Clan (damaged) -
- NSC --- -- - --
-- 0.111 - --- ---
NA Total 280.123147.373 NSC 1686.163 4:139.069 2,238.458 832.347 408.199 465.383 39.66 2 050.899 163.349 NA NOTE: NSC = no sanPles collected. NA = not applicable. Dashes (--) indicate no catches madee
M -
M M M M M M M raser 1-4 rtTIMIrn MMIntI_IEIEEEWI BASE 1LON.MILI_aureanr eair at LarS A _EIIZEAIRICK.MUCLEat_EDWER ELAMIs.l e Annual
- JeM. EEB. MR AEE. MI_. AAL. _JtL. AUG_ _ SEE. 0CI_ NOV._ K C. _Iotal.
No. of SasPles 4 4 0 13 20 6 4 6 4 4 4 4 73 Seecies Alevife 1:534 56 NSC 33e919 178:132 122,980 52,196 7,280 13,492 2:333 122:250 202 534,374 Rainbau smelt 9,184 2 975 NSC 870 1:246 500 93 14:482 17:295 318 878 4 875 52,716 Gizzard shad 2,898 287 NSC -- -- --- - --
90 ---
120 2:310 5s705 Threeseine stickleback 1,248 1s995 NSC 4 12 - -- --- - ---
270 333 3,862 White bass 194 - NSC - - -- --- - -- - 2,332 899 3:425 Trout Perch 31 7 NSC 56 273 300 341 16 8 -
30 ---
1e032 White Perch 674 238 NSC 14 50 60 -
21 - --
150 124 1 331 SculPin family 93 224 NSC 58 56 40 93 88 -- ---
128 318 1 098 SPottail shiner 170 63 MSC 14 6 80 310 108 330 8 38 39 1:164 Tesse11ated darter 31 7 NSC ---
62 40 132 119 --- --
30 --
421 Crawfish 31 175 NSC 7 31 40 23 5 - --
30 217 559 Bluesill --
21 MSC -- -- -- - -- -- -- ---
442 463 Rock bass 23 63 NSC 16 6 20 16 16 15 - ---
93 268 Stonecat 31 42 NSC 11 19 20 39 --- -- -- ---
8 170 Yellow perch 23 7 NSC ---
6 -- ---
72 -- -
30 62 200 Smallmouth bass 16 42 NSC 11 --
20 39 5 - -- -- --
133 Crawfish (damaged) -
63 NSC -- - --
16 ---
52 --- - ---
131 White sucker 8 --- NSC 2 6 ---
8 26 8 8 -- --
66 Emerald shiner 31 28 NSC 2 -- - -- --- --- --- ---
31 92 Pusekinseed -
- NSC --- --- - ---
21 -- -- --
70 91 Clas 8 -- NSC -
6 -- -- --- - -- ---
39 53 American eel (dasased) --
- NSC -- -- --- --
10 30 --
30 ---
70 American eel -
-- NSC - - ---
23 ---
30 -- -- -
53 Lake trout -
- NSC -- -- -- ---
5 --- --- -
31 36 Mirinos family (damaged)
- NSC - -- -- - --- -- -- --
31 31 Sea lasPrew ---
- NSC --
6 -- --- --- -- --- -- ---
6 Broun trout 8 --
NSC - - - --
5 -- - -- ---
13 Central sudoinnou 16 -
NSC -- --- -- --- -- -- -- --- --
16 Rainbow trout -
- NSC - --- - -
5 --
8 -- ---
13 Brown bullhead ---
7 NSC -- -- -- -- --- --- --- -- -
7 Lake chub -
- NSC 2 -- -- - - - -- -- --
2 Longnose dace -
- NSC 2 --- -- --- -- --- --- --- ---
2 l Clas (damased) - - -- - - -- - ---
8 -- -- --
8 Total 16,252 6:300 NSC 34,988 179,917 124,100 53,329 22:284 31,358 2s675 126,316 10:124 607,643 l
l NOTE! NSC = no saePles collected. NA = not #PP15 cable. Dashes ( ~ ) indicate no catches made.
M M M M M M M M M Tam r 1-s rRIIgIrn MMIILLINEIWrINFWT RacIn M FLOW _AI JenER A FIIZEAIRIClLMUCLEAILEOKE.ELANI _19R5 Annual
__JAN. __EEB. Het __AER. _RL. IN _JtL__ _AUG. __SEP_ __0CI_ __NOV__ _DEC. _Iotal_
No. of Saarles 4 4 0 13 20 6 4 6 4 4 4 4 73 Flow Saarled (MCM) 7.486 6.107 0 8.992 28.044 11.088 8.267 10.566 8.984 8.699 8.212 7.995 114.440 Total Monthis flow (MCM) 57.348 44.010 0 12.285 44.964 52.550 63.794 56.106 67.596 68.468 62.789 61.341 591.253 Seccles Alevife 1,517 58 NSC 20:082 184,269 !!6 564 51 972 7,482 13 535 2,369 124,623 199 522,672 Rainbow seelt 9 078 3,063 NSC 515 1,289 474 93 14,884 17,350 323 894 4,826 52 789 Gizzard shad 2,865 295 MSC -- -- -- - --
90 - 122 2,286 5,658 Threespine stickleback 1,233 2:054 NSC 3 13 -- --- --- -- -
275 330 3,908 White bass 191 --
NSC -- - - - - - --
2:378 890 3,459 Trout perch 31 7 NSC 33 282 284 340 16 8 -
31 ---
1 032 White perch 666 245 HSC 8 51 57 --
21 -- --
153 123 1:324 Sculpin family 92 231 NSC 34 58 38 93 90 --- ---
130 315 1 081 Scottail shiner 168 65 NSC 8 6 76 309 111 331 8 38 38 1:158 Tessellated darter 31 7 NSC -
64 38 131 122 -- -
31 ---
424 Cravfush 31 180 NSC 4 32 38 23 5 - ---
31 215 559 Bluesill ---
22 NSC -- --- -- --- --- -- --- --
437 459 Rock bass 23 65 NSC 10 6 19 15 16 15 - --
92 261 Stonecat 31 43 NSC 7 19 19 39 -- --- - --
8 166 Yellow Perch 23 7 NSC --
6 - ---
74 - ---
31 61 202 Seallmouth bass 15 43 NSC 7 ---
19 39 5 --- --- --- --
128 Crawfish (daeased) --
65 NSC - -- -
15 --
53 --- --- ---
133 White sucker 8 -
NSC 1 6 --
8 27 8 8 - --
66 Emerald shiner 31 29 NSC 1 31 92 Puerkinseed -- --
NSC - -- -- --
21 -- --- ---
69 90 Claa 8 -
NSC --
6 - -- -- -- --- -
38 52 American eel (damaged) --
-- NSC - --- -- --
11 30 ---
31 ---
72 American eel -
-- NSC -- -- --
23 --
30 --- --- ---
53 Lake trout - -
NSC - --- --- ---
5 --- --- --
31 36 Minnov family (damaged) -
-- NSC - --- - -- -- -- -- ---
31 31 Sea lanPrew --
- NSC -
6 --- --- -- --- -- -- ---
6 Brown trout 8 --
NSC -- - - -
5 - --- --- ---
13 Central nudainnov 15 -
NSC -- --- --- -- --- -- -- --- --
15 Rainbow trout - -
NSC - --- -- ---
5 ---
8 --- --
13 Brown bullhead --
7 NSC -- --- -- - -- --- --- -- --
7 Lake chub -- -
hSC 1 -- - -- --- -- - -- -
1 Lonsnose dace -- -
NSC 1 1
Clas (daeased) - -
NSC -- - - -- -
8 --- -- ---
8 Total 16:065 6:486 HSC 20:715 186,113 117,628 53,100 22,900 31 458 2,716 128,768 10 020 595,969 NOTE! NSC = no saarles collected. Dashes ( - ) indicate no catches made.
i
M M M M M M M M M M M M TABLE 3-64 LENGTH DISTRIMITION OF SELECT REPRESENTATIVE IMPORTANT SPECIES IMPINSED AT JAMES A. FITZPATRICK mre ran Pnure rt md9as ALEVIEE Lensth Intervals Interval Centimeters _Ical _Jelf _EER HAR _A22 _MAY E _.AL _AUG _SEE OCI _Il0ll _DEC ._Iolal_
3.0 - 4.9 0 0 --
0 0 0 0 61 20 9 1 0 91 5.0 - 6.9 6 1 -
0 5 0 0 0 44 28 48 4 136 7.0 - 8.9 5 0 -
28 100 11 1 0 2 2 34 1 184 9.0 - 10.9 0 0 -
19 75 4 0 1 0 0 0 1 100 11.0 - 12.9 0 0 -
!$ 43 8 2 0 0 0 0 0 68 13.0 - 14.9 0 0 -
10 24 22 18 7 2 0 0 0 83 15.0 - 16.9 14 2 -
31 121 52 61 0 2 0 0 0 283 17.0 - 18.9 23 3 --
43 124 52 17 0 2 0 0 0 264 19.0 - 20.9 2 0 --
3 7 1 0 0 0 0 1 0 14 21.0 - 22.9 0 0 -
2 1 0 1 0 0 0 0 0 4 Total Measured 50 4 -
151 500 150 100 69 72 39 84 6 1,227 Mean Length 14.9 15.5 -
13.9 13.5 15.4 15.8 4.9 6.2 5.4 6.8 7.1 12.3 Length R mse (MIN) 5.9 6.2 --
7.0 6.6 7.5 8.7 3.0 3.3 3.9 4.9 5.9 3.0 (MAX) 19.4 18.5 -
21.8 22.7 19.0 21.2 14.9 18.4 7.4 19.1 10.3 22.7 NOTE! Dashes (-) irdicate no samples collected.
m M M M M M M M M M M M M M M TAKE 3-6b LEM6TH DISTRIBUTION OF SELECT REPRESENTATIVE IlFORTANT SPECIES IMPINGED AT . LAMES A. FITZPATRICK mrt ran sure Pt MIz_19" RAInnd wit Length Intervals Interval Cecilmeiers_ Leal _m _EER Bt _AER _MI _m .tL _AUS SEE _0CI _MOU _DEC __Iolal_
3.0 - 4.9 2 1 1 1 1 0 65 28 3 1 0 103 5.0 - 6.9 16 16 -
19 53 3 2 10 26 4 9 9 167 7.0 - 8.9 55 48 -
61 102 14 1 2 0 1 17 18 319 9.0 - 10.9 5 5 -
2 5 1 0 2 0 1 11 21 53 11.0 - 12.9 2 3 -
8 12 1 6 1 0 0 1 28 56 13.0 - 14.9 8 3 -
15 15 3 0 0 0 0 1 5 50 15.0 - 16.9 5 10 -
8 1 1 0 0 0 0 1 2 28 17.0 - 18.9 6 4 -
0 1 1 0 0 0 0 0 1 13 19.0 - 20.9 0 1 0 0 0 0 0 0 0 0 0 1 21.0 - 22.9 1 0 -
0 0 0 0 0 0 0 0 0 1 Total Neasured 100 91 -
114 190 25 3 80 54 9 41 84 791 Mean Length 9.2 9.4 -
9.2 8.2 9.2 4.6 4.6 4.8 5.9 8.4 10.2 8.2 Lensth Range (MIN) 4.9 4.8 -
4.9 4.4 4.9 6.2 3.5 3.6 4.0 4.9 5.2 3.5 (MAX) 22.0 19.4 -
16.2 17.2 17.6 7.0 11.5 6.6 10.0 15.2 18.5 22.0 NOTE: Dashes ( - ) indicate no saarles collected.
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I Impingement collections of rainbow smelt were dominated by young of the year in I all months of 1985. Numbers of adults increased in the collections in April, May, June, and December, but were always dominated by young of the year. In some months, the young-of-the-year rainbow smelt were damaged to an extent that made it impossible to accurately obtain length measurements.
A total of 94 percent of the white perch measured were young of the year.
Young-of-the-year white perch were collected in 8 months of 1985 and dcminated I the white perch collections in the winter (January and February), spring (April and May), and late f all (November and December). Adult white perch dominated the white perch collections in June.
Yellow perch were collected primarily as adults in 1985. A total of five young-of-the-year yellow perch were measured in the samples collected in 4 months (January, February, August, and December) of 1985.
Smallmouth bass were collected exclusively as adults in 1985. They were generally collected as individuals or in small numbers.
The salmonid group was represented by brown trout, rainbow trout, and lake trout at JAF in 1985. All three species were collected as adults.
3.3 BIOMASS (PERMIT SECTION 11.B.4)
The total biomass cellected in the 1985 impingement samples at JAF nuclear power plant was 4,0( 4 097 (4,064 kilograms). Alewife comprised 91 percent of the total biomass (3,607.200 grams) . Gizzard shad (7 percent) and rainbow smelt (0.3 percent) wert. second and third in rank, respectively, by weight I (Table 3-7) . Other RIS are represented by a trace percentage (by weight) of the total biomass.
The estimated biomass (based on flow) was 11,265,074 grams (11,265 kilograms),
of which 8,521,948 grams (8.522 kilograms and 76 percent) was estimated as the weight of alewife (Table 3-8). The biomass of gizzard shad was estimated to be 2,312,808 grams (2,313 kilograms), or 21 percent of the total estimated biomass I for 1985. Rainbow smelt biomass was estimated at 81,817 grams (818 kilograms),
or 0.7 percent of the estimated total.
3.4 WATER QUALITY (PERMIT SECTION 11. A)
Intake and discharge temperatures were measured at the beginning and end of each impingement sample. Intake temperatures were measured in the intake (in I front of the trash bars). The discharge temperatures were measured in the discharge canal. Intake and discharge temperatures were also recorded from the plant operational log on sample days.
Intake temperatures recorded from grab samples taken during impingement sampling at JAF ranged from a minimum of 2.0 C on 18 December 1985 (when the plant was operating near maximum output) to 22.0 C on 18 and 19 August 1985.
Discharge temperatures taken on sample days when the plant was operating near capacity ranged from a low of 11.0 C on 13 February 1985 to a high of 37.5 C on I 18 July 1985.
3-15
M M M M M M M M M M raar r t-7 70IAL IIrmaet nr iBEI16ED_DEGEIgns cruIrrTED AI .tanrs adIIZEAIRICLiprf m POKR_f1 mis _19" Annual leiL. - rrt liet __AEIL_ m 8W II __eUS. _SEE_ _DCI_ NOIL. __1)EC__ __IotaI__
No. of Saarles 4 4 0 13 20 6 4 6 4 4 4 4 73 Seecies Alewife 5,003 147 NSC 347 697 2,631,134 505 804 145,800 957 2,779 303 27:450 124 3,687 200 Rainbow seelt 2 161 1:124 NSC 1,373 2,764 516 17 1e079 1 287 46 416 3 822 14 605 Gizzard shad 155,733 18:164 NSC - - - - -
44 -- 56 128,791 302,790 Threespine stickleback 213 387 NSC 3 8 -- - - --- ---
38 48 697 White 1, ass 225 - NSC - - - -
- - - 3:545 1432 --- 5 202 Trout perch 22 19 NSC 253 1,825 693 521 49 6 -- 60 3448 White Perch 235 1 022 NSC 21 173 2:432 -
24 - -
30 42 3 979 Sculpin famils 41 117 NSC 85 121 27 37 63 - --
60 121 472 Scottail shiner 123 59 NSC 14 8 174 379 33 128 2 17 55 992 Tessellated darter 10 <1 NSC --
115 16 24 13 - -
2 --
180 Crastish 3 18 NSC 13 110 80 40 1 12 84 361 Bluesill -
2 NSC - -- -- --- -- - -- ---
69 71 Rock bass 7 771 NSC 2:332 54 1080 810 1 037 812 - -
673 7:586 Stonecat 100 14 NSC 12 22 544 403 --- --- -- --
11 1,106 Yellow perch 266 6 NSC -
580 - -- 2,692 - - 344 392 4:280 Smalleouth bass 326 685 NSC 1,272 - 3 832 6 083 584 - - -- -- 12,782 Crawfish (damased) --
3 NSC - - -
3 -
5 - - -
11 White sucker 45 -- NSC 40 10 -- 25 3,708 1,056 733 - -- 5,617 Emerald shiner 6 5 NSC 1 - - - - - - -
14 26 Pusekinseed -
- NSC - -- -- --
476 --- --- -
127 603 Clas 15 - NSC -
56 - - - - --- ---
50 121 American eel (damaged) --
- NSC - -- --- --
54 132 -- 32 --
220 American eel -
- NSC - -
- 1e151 -- 288 - - --
1 439 Lake trout -
-- NSC - --- -- - 2,350 -- -- ---
37 2,387 Nirmos family (damaged) -
- NSC - - - - - - - -
11 11 Sea laarrew -
- NSC -
452 -- --- - -- --- -- ---
452 Brown trout 3e775 - NSC - - --
- 1:394 - - - -
5:169 Central sudoinnow 10 - NSC - -- -- -- - -- - -- --
10 Rainbow trout -
- NSC - - -
- 1 654 -
354 -- - 2,008 Brown bullhead -
22 NSC - - -- -- -- -- -- --- ---
22 Lake chub -
- NSC 25 - - -- - - - - --
25 Longnose dace --
- NSC 12 -- -- - - -- -- -- --
12 Clas (dasased) -
- NSC - - - - -
13 - - --
13 Total 168,319 22:567 NSC 373153 2,637,436 515,206155 29316:170 6:5501438 32,062135,903 4,064,097 NOTE! NSC = No saarles collected. Dashes ( - ) indicate no catches made.
l l
M M M M M IARf F LR FRTINATFIl MfWTlf Y RiflMAR9 rF ff1fIFrTFil Tara af taxrg_gdIIZggIgItug1Fae ragg,gtagI,,19Rs Annual u __EER._ Me8 __A28 _ MAY siv '8 Ailn crP _ 0CI. __NOV._ _ DEC___ _ Iotal._
No. of SasPles 4 4 0 13 20 6 4 6 4 4 4 4 73 Flow Saarled (MCM) 7.486 6.107 0 8.992 28.044 11.088 E.267 10.566 8.984 8.699 8.212 7.995 114.440 Total Monthis flow (MCM) 57.348 44.010 0 12.285 44.966 52.550 63.794 56.106 67.596 68.468 62.789 61.341 591.253 Seecies Alevife 38 325 1 059 NSC 502:379 4e218,770 2,397,115 1:125:102 5,082 20,908 2 385 209 872 951 Be521 948 Rainbou seelt 16:554 8,100 NSC 1 876 4:432 2:445 131 5 729 9,683 362 3 181 29 324 81 817 Gizzard shad 1,192 977 130,920 NSC - - - - -
331 - 428 988,152 2:312 808 Threespine stickleback 1 632 2,789 NSC 4 13 - - - - -
291 368 5 097 White bass 1,724 - NSC -- -- - - -- -- - 27,104 10,987 39,815 Trout perch 168 137 NSC 346 2,926 3,284 4:020 260 45 -
459 --- 11,645 White Perch le800 7:365 NSC 29 277 11:526 -
127 --- --
229 322 21e675 Scu1rin famils 314 843 WSC 116 194 128 285 335 - -
459 928 3,602 Spottail shiner 942 425 NSC 19 13 825 2,925 175 963 16 130 422 6,855 Tessellated darter 77 4 HSC -
184 76 185 69 - -
15 --
610 Cravfish 23 130 NSC 18 176 379 309 5 -- --
92 644 1,776 Bluesill -
14 NSC' - - - - - - - ---
529 543 Rock bass 54 5,556 NSC 3:186 90 5:156 6,251 5,506 6:109 -- -
5:164 37 072 Stonecat 766 101 NSC 16 35 2:578 3 110 - - - --
84 6 690 Yellow perch 2:038 43 NSC -
930 ---
- - 14:294 - -
2 630 3 008 22,943 Seallsouth bass 2 497 4 937 NSC 1 738 -
18 161 46,941 3:101 - --- --- ---
77:375 Crawfish (damaged) -
22 NSC - - --
23 ---
38 -- -- ---
83 White sucker 345 - NSC 55 16 -- 193 19,689 7,945 Se769 -- --
34 012 Emerald shiner 46 36 MSC 1 107 190 Pumpkinseed -
- NSC - - - --
2:527 - - ---
974 3:501 Clas 115 - NSC --
90 -- -- --- -- - ---
384 589 American eel (daeased) -
- NSC - --- - --
297 993 -
2 15 --
1e535 American eel -
- NSC - -- - 8,882 -- 2,167 -- -- ---
!!s049 Lake trout -
- NSC --- - -
- - 12:478 --- -- --
284 12 762 Minnou family (daeased) -
-- NSC - - -- - --- -- -- ---
84 84 Sea laePrew -
- NSC -
725 --- - - -- -- -- ---
725 Brown trout 28e918 - NSC - - -
-- 7 402 - -- -- ---
36 320 Central sudelnnov 77 - NSC - --- -- - -- --- -- -- ---
77 Rainbow trout -
- NSC - - -
- 8 783 -- 2 786 --- ---
11:569 Brown bullhead -
159 NSC - -- -- - --- --- - --- ---
159 Lake chub -
--ISC 34 - - --- -- - - -- ---
34 Lonsnose dace ---
-- NSC 16 --- -- -- --- --- -- --- ---
16 Clan (damased) -
- NSC -- - -- --- -
98 - --- --
98 Total 1,289 392162,640 NSC 509,833 4:228,8712:441,6731:198,357 85,859 49,280 !!s318 245,1351:042 71611:265,074 NOTE! NSC = no sasPles collected. Dashes (--) indicate no catches made.
4
3.5 HISTORICAL IMPINGEMENT COMPARISONS (PERMIT SECTION 11.C.3D)
Impinged fish have been collected annually at JAF since 1975. Estimates (by flow) of total impingement for the years 1976-1985 are shown in Table 3-9.
Abundance peaks generally occur in the spring and early summer months as adult l alewives and rainbow smelt move inshore to spawn. This seasonal movement is l primarily determined by water temperature and may cause the position of the '
abundance peaks to vary from year to year. After spawning, the adult fish move offshore into deeper, cooler water, and impingement abundances are reduced.
Mditional peaks in impingement occur in the late summer and f all when young of the year of both species (which remain in shallow, inshore nursery areas) are impinged.
The species composition of impingement collections at JAF has ranged from 26 to 54 fish species per year. Alevife generally dominated the impingement collec-tions with the exception of 1978, when threespine stickleback dominated the collection; and 1977, when rainbow smelt were first in abundance (Table 3-10).
Other species which have been collected in large numbers in the impingement include: white perch, gizzard shad, trout perch, spottail shiner, and tessellated darter. Biological factors such as population size, m:.gration patterns, schooling, and spawning behavior, in conjunction with environmental factors such as water temperatures, currents, and local meteorological condi-tions can influence the number of fish available for possible impingement. The number of alewife and rainbow smelt available for impingement is influenced by the seasonal movements already discussed, and by natural oscillations occurring l in their respective populations. It is well documented in the literature (Scott and Crossman 1973; Christie 1974) that both species exhibit definite l periodic fluctuations in population size.
l Large die-of fs of alewife have been reported since their appearance in the Great Lakes. According to the U.S. Fish and Wildlife Service and New York State Department of Environmental Conservation (Elrod et al. 1979, 1980; 0'Corman and Schneider 1986), the population of alewife declined du to a die-off during 1976-1977, a winter of severe cold. Losses were estimated as high as 60-75 percent of the population in the vicinity of the Nine Mile Point promontory upon which JAF is situated. Decreased collections of alewife were evident for several years (through 1979). In 1980, impingement abundance of alewife increased until 1982-1983 when another winter die-off occurred and caused a reduction in the alewife population. The abundance of alewife in the impingement increased in 1984 and 1985.
Rainbow smelt populations have also displayed some oscillations in the Great Lakes from year to year. U.S. Fish and Wildlife Service biologists have noted yearly oscillations in the rainbow smelt populations with high recruitment occurring in the odd years (O'Gorman and Bergstedt 1982, 1983, personal communication.) Reflections of these lakewide natural oscillations in the impingement data may not be as easily discernable as one might expect, since a large collection of young of the year could be impinged at a time prior to their recruitment. This would be demonstrated as a peak in abundance at a time when predictably the natural population would be showing a decrease in overall population size.
3-18
m TARff 1-9 FRTIll6IFD MMIlLLIEllEEllEHLIBLELOW1.ALINF .tANFH A. FIIZE6IRICLKt FAR POER.ELAWIs_1926:19a5 11 0 . ___122A.- __1222__ 1228._ __122f__ __1280__ __1281._ __1282 _ __1283._ __198L. _ 1285._
JAN 12 208 19:526 41,595 13:436 45,794 6:169 47,283 4,826 1,441 16 065 FEB 1:300 5:068 16,646 9,115 10:197 B 046 3 533 1:421 1e538 de4868 MR 50,037 13,813 87,854 8 362 2,998 17:572 14:095 3,945 2 539 0 APR 489 466 50,490 23:014 5 629 27,371 44,405 91 148 9,832 3:332 20 715 MY 2 850 935 !!9,725 88 712 14 453 13,8548 34,936 110:301 51,562 140 421 186,113 JUN 304:206 15e9108 42,847 1,675 59 916 35e879 38,996 2,7398 43 211 117,628 JUL 160,379 152 13:392 219 19,690 55,165 142:100 832 95 471 53,100 AUG 5 147 223 33,708 227 5,964 116:356 22 753 4 945 6e958 22 900 SEP 6:524 15,560 31,5708 18:132 4:072 49,081 11 453 15:071 3,616* 31,458 l OCT 8,178 32:428 246 30,649 42,751 153,2238 877 2 870 101 2,716 NOV 188,928 29,711 558 46,209 40,026 2,378 2:205 1,277 2,788 128,768 DEC 36,254 30,837 42,051 96,123 23,632 4:050 118,508 16e674 71,168 10:020 Total 4:313:562 332e963 424:193 , 244:234 296,267 527,260 603:252 115,994 372 584 595 969
- Dutases! 1976 - No Plant operatins data. 1981 - 30 DCT 1981 - 09 MR 1982 1977 - 22 JUN 1977 - 23 SEP 1977 1983 - 04 JUN 1983 - 02 SEP 1983 1978 - 17 SEP 1978 - 06 KC 1978 1984 - 16 SEP 1984 - 05 NOV 1984 1979 - 14 MR 1979 - 07 SEP 1979 1985 - 16 FEB 1985 - 01 JUN 1985 1980 - 07 MY 1980 - 13 AUG 1980 Other outases saw have occurred from 1976-1985, however, ihPinsetent $5 influenced tost by extended outases as sho m
M M = .
M TAKE 3-10 ESTIMATED IIFIN6EENT ABUNDANCE (BT FLDI) FOR DOMINANT SitCIES AT TE JAMES A. FITZPATRICK mrt M PGMFP Pt &ilIs,192f::19M hecie= ___122&__ __1222_ __1228. __1222. __1280. __1281. __1282. __1283. __1f84. __1285.
Alevife 3 877 550 185,432 67,311 81 112 169,750 453,093 346 503 6te404 271el?2 522,672 Rainbou saelt 259,783 % 563 74e962 136e722 78e245 52 722 235e289 36e254 78e851 52,789 Threestine stickleback 95:883 - 222,837 - - - - -- -- --
White Perch -
11 617 - - - - -
5:260 - -
SPottail shiner - - -
6:296 - -
3:440 - -- --
6 izzard shad - - - -
14:017 - - -- --
5:458 Trout perch - -- -- -- --
3 571 --- --- -- ---
Tessellated darter - - - - - - -- -
4:496 ---
NOTE: Dashes (-) denote the species held an alundance rank lower than third in abursdance for the aPPlicaDIe Vear. It does not indicate 'none collected.' For the abundance estimate for that species, please refer to the report issued for tiw wear in euestion.
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Short-term meteorological conditions also influence impingement abundance. As !
previously stated (Section 3.1), impingement collections at JAF are affected by specific weather conditions such as high winds and waves. Lifton and Storr (1977) found statistically significant correlations between environmental l factors (wave height, water temperatures, and wind action) and impingement at power plants on Lake Erie and Lake Ontario. They hypothesized that wave induced turbulence, and possibly turbidity, interfere with a fish's normal ability to detect and avoid an intake structure, resulting in higher impinge- !
ment.
Perhaps the most influential determinant of impingement abundance estimates is the timing and duration of plant outages. During outage conditions, the main I circulating water pumps are generally shut down for extended periods of time.
Since little or no water is being pumped through the intakes, the impingement process is greatly reduced. Plant outages in the spring months can coincide I with seasonal movements of fish species (particularly alewife and rainbow smelt) inshore to spawn, substantially reducing the impingement abundances
" normal" to that season.
Impingement abundance estimates for the RIS are shown in Table 3-11. White perch and smallmouth bass numbers are most likely attributable to the natural fluctuations within their respective populations and the influence of plant operating conditions and weather on the impingement process. Since 1979, yellow perch impingement numbers have followed a lakevide decline in the overall population. The estimated n'unber of impinged yellow perch did increase slightly in 1982 and 1984. During both years, the plant remained in operation without a lengthy outage. This fact may account for any small impingement increases seen.
Overall, the impingement of fish at JAF appears to have little effect on the species composition of fish population size in the vicinity of the nuclear power plant. Rather, it is a reflection of the result of natural mortality, spawning success, and meteorological influences on the local fish community structure. Impingement estimates will also reflect the plant operating conditions and patterns. No long-term trends toward reductions in the major fish populations in the vicinity of JAF have been apparent.
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1 3-21
M M M M M M M TAK E 3-11 ESTIMATED IMPINSEENT ABUNDANCE (BY FLOW) FOR THE REPRESENTATIVE IMPORTANT SPECIES AT THE we a. nIZEaIgItr urt reg _E0gr.E.EtaWIs 1226:1E beclec ___1224._ __1222. __1228. __1222. 1980. __1981. __1982. __1283. __128L __1285.
Alevife 3,877,550 185,432 67,311 81 112 169,750 453,093 346 503 41 404 271 192 522 672 Rainbau snelt 259,783 98 563 74e962 136e722 78 245 52e722 235,289 36e254 78 851 52e789 White cerch 7:339 11,617 5 863 5:406 5 234 2,786 2 253 5:260 2,704 1 324 Yellow cerCh 3 695 1:495 9 874 2,615 1,750 639 1 211 398 519 202 Smallmouth bass 511 538 1 135 269 231 71 951 217 245 128 Salaanidss- 159 122 !!4 105 65 79 185 117 193 62 i NOTE 1 Salmonids are treated as a grOUPe estitales Of abundance for all species in a War are tallied.
For individual species abundance, PleaSe refer LO the rePurt issued for a diWn Ware i
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I REFERENCES I Christie, W.J. 1974. Changes in the Fish Species Composition of the Great Lakes. J. Fish Res. Bd. Canada. 31(5):827-854.
Ecological Analysts, Inc. ( EA) . 1982. 1981 Nine Mile Point Aquatic Studies.
Prepared for Niagara Mohawk Power Corporation and Power Authority of the State of New York.
EA. 1983. 1982 Nine Mile Point Aquatic Studies. Prepared for Niagara Mohawk Power Corporation and Power Authority of the State of New York.
EA. 1984. Nine Mile Point Nuclear Station 1983 SPDES Annual Biological Monitoring Report. SPDES Permit No. NY 0001015 Section IV.C.
EA. 1985. Nine Mile Point Nuclear Station 1984 SPDES Annual Biological Monitoring Report. SPDES Permit No. NY 0001015 Section IV.C.
Elrod , J.H. , R. O'Corman, R. Bergs ted t, and C.P. Schneider. 1979. Status of the Major Forage Fish Stocks, U.S. Waters of Lake Ontario,1978. Report presented at the Great Lakes Fishery Commission, Lake Ontario Committee Meeting. 13-14 March 1979.
Elrod, J.H., R. O'Gorman, R. Bergstedt, and C.P. Schneider. 1980. Status of I Major Forage Fish Stocks, U.S. Waters of Lake Ontario,1979. Report presented at the Great Lakes Fishery Commission, Lake Ontario Committee Meeting. 4-5 March 1980.
Lifton and Storr. 1977. The Effect of Environmental Variables on Fish Impingement, in Fourth National Workshop on Entrainment and Impingement (L.D. Jensen, ed.) , pp. 299-311.
I New York Power Authority. 1981. Personal Communication. Letter to the Nuclear Regulatory Commission (JAFP-81-0533), dated 21 May 1981.
O'Gorman, R. and R. Bergstedt. 1982. Oswego Fish and Wildlife Station.
Personal Communication.
O'Gorman, R. and R. Bergstedt. 1983. Oswego Fish and Wildlife Station.
Personal Communication.
O'Gorman, R. and C.P. Schneider. 1986. Dynamics of Alewives in Lake Ontario Following a Mass Mortality. Trans. of the Amer. Fish. Soc. Vol. 115.
pp. 1-14. January.
Rand Corporation. 1955. A Million Random Digits with 100,000 Normal Deviates.
Free Press, Glencoe, Illinois.
Scott, W.B. and E.J. Crossman. 1973. Freshwater Fishes of Canada.
Fish. Res. Bd. Canada, Ottawa, Canada. 966 pp.
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i I APPENDIX A EXCEPTIONS TO STANDARD OPERATING PROCEDURES FOR IMPINGEMENT AT JAMES A. FIT 2 PATRICK NUCLEAR POWER PLANT,1985 I
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I I APPENDIX A EXCEPTIONS TO STANDARD OPERATING PROCEDURES
_ FOR IMPINGEMENT AT JAMES A. FITZPATRICK NUCLEAR POWER PLANT.1985 04 FEB 1985 Void Imnincement Samnie - At the time of collection of the scheduled impingement sample, no plant operators I were available to remove the sample collection basket.
me sample period went over the 26-hour time limit set in the S0P and was declared void. The sample was rescheduled and successfully completed on 06 February 1985.
21 FEB 1985 Void Imnincement Samnie - At the time of collection of the scheduled impingement sample, the service water pumps were inoperable; no water was available to wash the screens due to a plant outage. The sample was rescheduled and collected on 27 February 1985.
07 MAR - 15 APR 1985 Void Imnincement Samnies - In 1985, 73 of the 80 23 APR - 26 APR 1985 scheduled samples were successfully completed. From I 17 MAY - 01 JUN 16 February 1985 through 01 June 1985, JAF nuclear power plant was shut down for refueling and routine maintenance. During that time, the circulating water pumps were shut down for extended periods of time, as were the traveling screens. When the traveling screens were operable on a scheduled sampling date, the sample I was declared void and rescheduled according to random numbers procedures and available dates remaining in the month. Attempts were made at every opportunity to collect the required number of samples, regardless of whether the circulating pumps were operating. In all, no samples were collected in March, and 13 of the 16 samples scheduled in April were collected. In the month of May, all 20 required samples were collected though many dates were rescheduled throughout the month when conditions at the plant allowed EA to sat ple.
10-11 JUN 1985 Void Imnincement Samnie - The *.npingement sample scheduled for a set date of 10 June 1985 was declared void at the time of the set. The traveling screens I were broken and could not be rotated. The sample was rescheduled based on information from the control room operators and remaining dates in June. The sample was successfully completed on 18 June 1985.
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A-1
I I 02 JUL 1985 Void Imnineement Samnie - The impingement sample I scheduled for collection on 02 July 1985 could not be completed. Repair work requiring divers in the area of the traveling screens prevented the screens from being j
rotated at the collection. The sample was rescheduled (using the random numbers method) and completed on 10 July 1985.
09 AUG 1985 Void Imnineement Samnie - The impingement sample scheduled for completion on 09 August 1985 was declared void at the time of collection. Divers were in the area of the screens and the overhead crane was in I operation, preventing rotation of the screens and rer oval of the collection basket. The sample was rescheduled and completed on 15 August 1985.
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A-2 g
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I I I APPENDIX B i PLAET OPERATING CORDITIONS (PERMIT SECTION IV.C.9)
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I I IABLE kl. ELMLOCERAIING.COWDIIIOWLAL.!AHELL.IIIZEAI2ICLidUCLEet E0Wl0LitMLDURING.1785 STATION! Jsavs.k.EitzE4 trick HONTH: .!anuarx.1785 No. of No. of Circulatird Service Tatal Val m (e3) of Mean Electrical Iesseratures.fCL I Water.funts Date Water.funes Faler.Euarmt 0uteut IdWeL Jotake Discharse 1 3 2 2,093 607.6 836 4.8 20.8 2 3 2 2 093,607.6 834 4.8 20.0 3 3 2 2e073,407.6 834 4.7 20.8 I 4 3
6 7
3 3
3 3
2 2
2 2
2 093,607.6 2,072,024.1 2 072,024.1 2,050,440.5 831 333 C35 834 4.9 4.7 3.7 4.4 20.9 20.7 19.8 20.4 I 8 3 2 2,020,854.9 836 3.9 19.9 9 3 2 1,935,639.7 650 3.7 14.8 10 3 2 1,740,270.3 772 5.7 20.2
!! 3 2 1,743,270.3 308 5.7 20.8 12 3 2 1 856e100.2 801 4.4 19.6 I 13 14 t5 16 3
3 3
3 2
2 2
2 1,813 021.1 1 834 604.4 ie771e437.5 ie740,270.3 833 834 833 835 3.6 4.3 3.9 4.3 19.1 19.9 19.4 19.8 1 791,437.3 I 4.7 17 3 2 835 20.3 10 3 2 1,031e4C4.6 826 4.3 19.8 19 3 2 1:034,604 6 830 4.0 19.6 20 3 2 1 769,853.9 837 3.6 19.2 21 3 2 1.726,686'7 627 3.2 15.8 I
22 3 2 1 724,606.7 507 2.9 14.2 23 3 2 1,726,486.7 - 639 3.1 16.3 24 3 2 1,461 934.0 658 3.3 15.9 25 3 2 to/24,6R4.7 745 3.8 17.8 2(. 3 2 1,724,684.7 827 3.7 19.1 27 3 2 1 726,606.7 330 3.7 17.1 20 3 2 1,724,606.7 C77 3.7 19.1 29 3 2 1,748,270.3 825 3.8 19.2 30 3 2 1 740,270.3 823 4.0 19.4 31 3 2 1 748,270.3 790 4.4 19.3 STATION! Jc.aes A.Ellreatrick MONTH: Eshruarv.1505 Ka. of No. of I Date Circulatird Water Eume1.
Service Water Eumes Total Volues (s3) of Wzier Euseeci Hean Electrical 0uirut.1NWeb Isseeratures.ICL Intake Discharse 1 3 2 1 743,270.3 739 4.3 20.3 I 2 3
4 5
3 3
3 3
2 2
2 2
1 748,2/0.3' 1,748,270.3 1,748,270.3 1,740 270.3 832 833 834 332 3.8 4.4 3.9 4.1 21.4 22.2 21.8 21.8 I 6 7
8 9
3 3
3 3
2 2
2 2
1,748,270.3 1,743,2/0.3 le740 270.3 1 743 270.3 830 827 824 822 4.2 4.2 3.9 4.3 21.8 21.8 21.5 21.8 10 3 2 1,740,270.3 3.8 21.4 I
819 11 3 2 le748 270.3 818 3.7 21.3 12 3 2 1,748 270.3 800 4.2 21.4 13 3 2 te743 270.3 002 4.3 21.4 14 3 2 1,748,770.3 800 4.2 21.4 15 3/2 2 1 573,441.3 536 3.3 15.4 14 2 2 1 504 310.4 0 0.4 0.1 17 2 2 te504,310.4 0 0.5 0.1 1R 2 2 1,504:310.4 0 0.4 0.0 19 2 2 1,504,310.4 0 0.4 0.2 I 20 21 22 2
2 2
2/0 0
0/1 1 439,559.6 te303,096.0 1,404,203.2 1,406 203 2 0
0 0
0.2 0.0 0.8 0.1 0.0 0.8 23 2 1 0 0.9 0.9 24 2 1 1,406,203.2 0 1.7 1.7 25 2 1 190,367.4 1.7 1.6 I-24 2 1 1
1 170.367.4 0
0 1.3 1.2 27 2 1 1,404 203.2 0 1.0 0.9 20 2 1 1.t90e367.4 0 1.4 1.2
I IA11LD LICont.1 STAT 10N1 .!ames.Lfitdatrick MONTH 1 ' h rch.1285 No. of No. of Circulatird Service Total Voho (s31 of Meen Electrical __Iraverstures_ICL I
Date Watar_Euses Water _Eumes Valer_Eusee<f .0uieutIMeL Ioiske Discharse 1 2/3 1 2 040,251.2 0 1.8 1.7 2 3 1 2,060,251.2 0 1.7 1.6 3 J/2 1 te406,203.2 0 1.2 1.2 I 4 5
6 7
2/1 1/0 1
0 1
1 1
1 752 155.2 7Fh t'i'i.2 425,131.2
% 107.2 0
0 0
0 0.3 0.5 0.9 0.9 0.5 0.8 2.7 4.3 I 2.2 8 0 1 98 107.2 0 5.1 9 0 1 90s107.2 0 2.3 5.0 10 0 1 98,107.2 0 2.1 5.7 11 0 1 93,107.2 0 1.0 4.4 12 0 1 98 107.2 0 2.2 5.0 I 13 14 15 16 0
0 0
0 1
1 t
1 93 107.2 98,107.2 E 107.2 98e107.2 0
0 0
0 2.7 3.9 3.1 2.2 5.8 6.8 4.3 5.6 W 107.2 I
17 0 1 0 2.3 5.4 10 0 1 98e107.2 0 1.8 4.4 19 0 1 % I07.2 0 3.2 5.9 20 0 1 98,107.2 0 3.4 6.7 21 0 1 98,107.2 0 2.6 5.7 I 22 73 24 25 0
0 0
0 1
1 1
1 98e107.2 90,107.2 98e107.2 98,t07.2 0
0 0
0 2.0 1.9 1.9 1.7 5.2 5.0 5.0 4.7 I
26 0 1 98e107.2 0 2.9 5.5 27 0 1 % t07.2 0 3.7 7.2 20 0 1 % 107.2 0 3.8 7.7 29 0 1 % t07.2 0 3.8 7.6 30 0 1 % 107.2 0 3.3 5.3 31 0 1 % 107.2 0 2.5 4.3 STATION: Janas a riidatrick forfH: 6eriL1285 No. of No. of Circulatird Service Total Voheme (s3) of mean Electrical __Ieneeratures ICL Date Water.Euses Water _Eunas ____ Waist.Pussed __Dutrut_IMeL Intake Discharse 1 0 1 % 107.2 0 3.6 5.3 2 0 1 98,107.2 0 4.4 6.7 3 0 1 % 107.2 0 3.9 6.9 4 0 1 % 107.2 0 3.4 6.7 5 0 1 % 10/.2 0 3.3 6.7 4 0 1 % 107.2 0 4.4 7.2 7 0 1 98 107.2 0 5.2 1.9 8 0 1 % 107.2 0 5.2 8.4 9 0 1 % 107.2 0 3.8 4.8 10 0 % 207.2 0 4.6 7.2 I
1 11 0 1 E 107.2 0 5.4 S.1 12 0 1 % 107.2 0 4.0 6.0 13 0 1 % t07.2 0 4.1 5.7 14 0 1 98 107.2 0 3.9 5.3 I 15 16 17 18 0
0 0
0 1
1 1
1
% 10/.2 65,404.8 2 107.2
% 107.2 0
0 0
0 4.6 5.1 5.1 3.8 6.2 6.8 6.8 5.1 19 0 E107.2 4.2 I
1 0 5.4 20 0 1 98,107.2 0 3.8 6.1 21 0 1 % 107.2 0 4.4 6.4 22 0 1 98 107.2 0 4.7 6.6 23 0 1 45,404.8 0 4.1 5.8 I
24 25 26 27 0/1 1/2 2
2 1
1 1
2 % 718.4 1 106,203.2 1,406 203.2 1,4 % 203.2 0
0 0
g.7 5.1 6.4 5.9 4.9 6.1 1 0 7.1 4.8 28 2 1,406:203.2 7.4 7.2 I
1 0 29 2 1 1,404,203.2 0 0.0 7.7 30 2 1 1 406 203 7 0 7.4 7.1
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i STATION: James.LElidatrick MONTH: Itas.1285 No. of No. of Circulatirol Service Total Volume (e3) of Mean Electrical Ivaneratures ICL I Pah _ Water.fuered Int.ie Watar Euans Water Pumps Duiaui.IHWeL Discharse 1 2 1 1,404,203.2 0 0.3 0.2 2 2 1 1,404,203.2 0 7.3 7.2 3 2 1 1,404,703.2 0 7.9 7.8 I 4 5
6 7
2 2
2 2
1 1
1 1
1,404 203.2 1e404e203.2 1,404,203.2 1,406 203.2 0
0 0
0 7.3 7.0 7.4 8.6 7.1 6.8 7.3 3.3 I 8 9
10 11 2
2 2
2 1
1 1
1 1,404,203.2 te404e?03.2 1:404 203.2 1 404,203.2 0
0 0
0 8.4 7.8 8.9 7.5 7.9 7.2 8.3 7.0 12 2 1 1,406 203.2 0 9.4 9.0 13 2 1 1,404 203.2 0 9.3 3.9 14 2 1 1,406 203.2 0 9.8 9.4 15 2 1 1,404,203.2 0 7.7 7.3 16 2 1 1,404,203.2 0 9.1 8.3 I 17 18 19 20 2
2 2
2 1
1 1
1 te404 203.2 1,404,203.2 1,406,203.2 1,373e500.8 0
0 0
0 10.3 11.0 10.6 9.0 9.2 9.8 9.3 8.6 21 2 1 1 404,203.2 0 10.4 9.3 22 2 1 1,406 203.2 0 10.6 9.4 23 2 1 1,404 203.2 0 11.9 10.7 24 2 1 1,404e?03.2 0 11.9 10.7 23 2 1 1,404 203.2 0 12.4 11.3 I 26 27 28 29 2
2 2
2 1
1 1
1 1 406:203.2 1:104,203.2 1,404 203.2 1 404 203.2 0
0 0
0 11.9 11.8 12.9 12.8 10.7 10.4 11.8 12.3 9.2 30 2 1 te404e203.2 0 9.1 31 2 1 te404,203.2 0 9.6 9.1 STATION James.LEitdatrick MONTH: June 1285 No. of No. of Circulating Service Total Valune (a3) of Hvan Elvetrical Isauratures.ICL Date Water Pumas Water Euses Water.Euased ._ Duiput IHWe b Iciate Discharse 1 2 1 1,364,017.1 49 11.1 14.3 2 2 1 1,406,203.2 165 11.3 19.6 3 2 1 1,413,470.4 167 12.2 20.2 4 2 1 1,392,141.2 91 12.9 10.3 5 2 1 1,279,644.9 0 12.1 11.8 I 6 7
8 9
2 2
2 2
1 1
1 1
1e321 C31.0 1,251,520.8 1,279,644.9 1,433 905.4 0
0 0
44 10.9 12.1 12.1 12.1 10.7 11.7 12.0 15.8 10 1,344,017.1 13.3 I
2 1 152 20.1 11 2 1 te265 502.9 0 12.9 13.1 12 2 1/2 1,504,310.4 207 13.2 22.1 13 2/3 2 2,153,358.4 479 13.8 25.5 14 3 2 2,158 358.4 584 13.4 27.2 I 15 14 17 19 3
3 3
3 2
2 2
2 2,153,353.4 2,158,358.4 2 134,774.8 2 072,024.1 613 722 805 758 13.7 13.4 15.1 14.6 27.9 29.3 31.8 30,7 19 3 2 2 115,191.2 743 14.7 30.9 20 3 2 2,158 358.4 808 13.6 31.7 21 3 2 2 153 358.4 761 14.2 31.9 22 3 2 2el'.0 358.4 738 13.1 28.7 23 3 2 2,t58e350.4 023 13.8 30.7 I
24 25 26 27 3/2 2/3 2
3 2
2 2
2 1 397 046.5 707 025.9 i,940,342.4 2,153,331.4 525 409 628 3
14.5 14.8 14.9 14.8 26.7 13.5 26.2 28.6 20 3 2 2,158 358.4 764 14.5 30.5 I 29 30 3 3 2 2
2,153,350.4 2,150,358.4 818 825 15.4 15.3 32.0 31.9
I
__ _______IABLE.B:LICuaL1 I STATION! James.n.Eil2 Patrick No. of Cireviating No. of Service Tot:1 Valuer (e3) of MONTH: Juh:_1285 Mean Electrical __Ireveratures_ICL Data Water _Punes Watar_Ptmes _ Water _Euere<f __0uttuLIMvL Inizke Discharse 1 3 2 2,158,L8.4 823 16.1 31.9 2 3/2 2 1 504 310.4 727 16.4 34.3 3 2/3 2 2 153,358.4 724 17.6 J4.3 I 4 3
6 7
3 3
3 3
2 2
2 2
2 158.358.4 2 153 358.4 2el58,358.4 2,t50,358.4 803 321 822 820 18.8 18.4 19.2 t9.6 34.3 34.2 35.1 35.3 8 3 2 2 150.1"4.4 822 19.4 35.4 I ?
10 11 12 3
3 3
3 2
2 2
2 2,158 L8.4 2,158.350.4 2,158,358.4 2e150e358.4 824 822 823 821 19.3 19.9 19.9 19.5 35 1 35.6 35.6 35.1 13 3 2 2,158 358.4 821 19.3 35.0 14 3 2 2 19t 358.4 821 19.4 34.9 13 3 2 2,158 358.4 321 19.7 35.4 16 3 2 2 158 358.4 C19 19.9 35.4 17 3 2 2 153 358.4 822 20.4 36.1 I 18 19 20 21 J/2 2/3 3
2 2
2 3
2 2,158 32.4 1,504,310.4 1,504 310.4 2,158 358.4 817 494 19 21.2 21.7 21.4 37.0 31.2 22.2 339 21.3 32.3 22 3 2 2 158,358.4 649 21.6 34.6 23 3 2 2e 158.Ii8.4 733 21.6 36.9 24 3 2 2 158 358.4 817 20.3 36.1 23 3 2 2et53,358.4 8t8 20.9 36.6 26 3 2 2,158 358.4 721 21.2 35.2 I 27 28 29 30 3/2 2/3 2
3 2
2 2
2 1,504,310.4 1,659,337.9 2,158 358.4 2e12e358.4 0
432 673 773 21.4 21.2 2t.1 22,9 22.1 31.5 34.3 37.9 I 31 3 2 2 153,353.4 812 21.3 36.8 STATION! James _4._Eit2 Patrick HONTH! eurust_1f85 No. of No. of I Dale 1
Circulating Water _Punes 3
Service Water _Euses 3
Total Value (s3) of
_ _ Water fuereal 2 223,763.2 HvareElectrical
__0uteui IWcL 815
__Iesteratures_ICL Iotake 21.1 Discharse 36.7 2 3 3 2,256,465.4 816 21.0 36.5 3 3 3 2,256,465.6 604 21.1 33.4 4 3 3 2 256,465.4 658 21.1 33.9 5 3 3 2,256,465.6 802 20.8 36.1 2,223,763.2 I
6 3 3 816 21.0 36.5 7 3 3 2,256,465.6 stb 21.7 3/.2 8 3 3/2 2,158,358.4 818 22.0 37.4 9 3/1 2 1e068 2/3.4 34 22.6 23.1 10 1 2 850.262.4 0 22.2 22.1 I 11 12 13 14 1/2 1
1 1
2 2
2 2
8',0,262.4 850.262.4 850,262.4 1,286 294.4 0
0 0
0 22.5 21.9 20.7 22.7 22.3 21.7 20.4 22.1 13 2 1 236 274.4 2 23.2 24.0 I
2 16 2/3 2/3 1 973,044.8 419 22.8 32.3 17 3 3 2e254e463.6 632 22.7 33.3 18 3 3 2:223,763.2 748 22.3 36.8 19 3 3 2 223 763.2 803 22.3 37.9 I 20 21 22 23 3/2 2
2 2
3/2 2
2 2
1e504,310.4 1 433,905.6 1 504 310.4 1 504 310.4 90 0
0 0
22.4 22.3 22.4 22.3 23.9 21.9 21.9 21.8 24 2 2 1,504,310.4 0 21.7 21.8 25 2 2 1 504,310.4 117 21.6 20.1
'" '" "" 2,256.465.6 21.',
675 34.7 27 3 3 2,256,465.6 477 21.7 35.1 28 3 3 2,256,465.6 805 21.7 37.3 I 29 30 31 3
3 3
3 3
3 2 256 445.6 2,256 465.6 2e256e465.6 808 813 820 21.6 21.0 19.6 37.2 36.6 3'i. !
I I - ___1k1LE B:LLConid ___
I STATION: .!ases.A._Eitdatrick No. of Circulating No. of Service Total Valos (s3) of HONTH: Serivaber.1285 Me.m Electrical __Ieeeeratures.ICL Baia Water _Euses Water _Punes _ Water.Euerel___ __Dutaut_IdWeL Ialake Itischarse 1 3 3 2.2 % 465.6 824 17.7 33.1 2 3 3 2 223,763.2 823 18.3 34.0 3 3 3 22% E.4 820 20.0 35.7 4 3 3 2,2 % 445.6 820 20.4 36.2 5 3 3 22% M.6 318 20.4 36.2 6 3 3 2 2 % 445.6 818 20.7 36.6 7 3 3 2,254,465.6 818 21.1 34.7 2,2 % 465.6 I
8 3 3 816 21.5 37.0 9 3 3 2 256 465.6 316 21.5 37.2 10 3 3 2,2% M.6 817 20.5 36.0 11 3 3 2 256. M .6 824 10.0 33.4 12 3 3 2,223,763.2 824 17.4 33.3 13 3 3 2,2 % 165.6 321 16.3 31.8 14 3 3 2 2 % 465.6 288 15.3 31.1 15 3 3 2,256,465.6 325 17.9 33.6 16 3 3 2,2 % 445.6 825 17.2 32.8 I
17- 3 3 2,2 % 465.4 827 17.2 32.9 18 3 3 2,2 % 465.6 826 18.0 33.7 19 3 3 2,2 % 465.6 824 18.9 34.7 20 3 3 2 2 % 465.6 823 18.9 34.7 21 3 3 2,2 % 465.6 824 19.4 35.9 22 3 3 2 2 % 465.6 825 18.8 34.6 23 3 3 2,2 % 465.6 826 18.5 34.3 24 3 3 2,2 % 445.6 825 18.7 34.7 25 3 3 2 2 % 465.6 823 13.6 34.6 26 3 3 2,256 465.6 725 10.3 32.6 27 3 3 2 2 % 465.4 809 13.9 34.7 28 3 3 2 223 743.2 824 17.9 34.1 29 3 3 2 2 % 445.6 * *
- 30 3 3 2,2 % 465.6 824 18.2 34.3 STATION: .! anes.A.Eitdatrick MONTH! Deinhar_1285 No. of No. of Circulatird Service Total Voluna (s3) of HeariElvetrical __Ieseeratures_ICL Date Water _Pusas Water _Punes _ Water _Pusted __0uteut_IHWeL Iniske Discharse 1 3 3 2 2 % 465.6 824 18.6 33.8 2 3 3 2,2 % 465.6 824 18.4 33.6 3 3 3 2,2 % 465.6 826 13.3 33.4 I 4 5
3 3
3 3
2 2 % 465.6 2,2 % 445.6 825 026 18.4 13.2 33.5 33.3 6 3 3 2,223,763.2 828 17.2 32.4 I 3 2 2 % 465.6 17.5 32.7 7 3 829 8 3 3 2 2 % 465.6 825 17.4 32.5 9 3 3 2s256445.6 828 17.6 32.8 10 3 3 2 2 % 465.4 826 17.7 32.9
! 11 3 3 2,254,465.6 829 17.2 32.7 lEg 12 13 3
3 3
3 2 2 % 465.6 2 2 % 465.6 690 776 16.8 17.0 30.1 31.5 14 3 3 2,2 % 465.6 824 17.5 32.8 15 3 3 2,2 % 465.6 827 16.9 32.2 I la 17 18 19 3
3 3
3 3
3 3
3 2 2 % 465.6 2,2 % 465.6 2 2 % 465.6 2 2 % 465.6 828 328 825 326 16.5 16.1 16.1 16.5 31.9 31.5 31.4 31.8 20 3 3 2,2 % 445.6 827 16.I 31.5 I 21 22 23 24 3 3
3 3
3/2 2
3 2
2,223,763.2 2,158,358.4 2 158 353.4 2,1 % 358.4 828 830 831 C29 15.1 14.9 14.6 14.4 30.6 30.6 30.3 30.2 25 3 2 2,133,353.4 825 14.8 30.4 14.7 30.1 t I 2,6, 3, 2, 2
- e. 1.ea% 358. 4 815 28 3 2 2 1 % 358.4 828 14.4 35.9 29 3 2
~
2 158 353.4 830 14.6 30.3 30 3 2,1 % 358.4 831 14.0 29.9 I- 31 3 2 1 722,326.4 325 13.2 19.7
- Consuter irovrative. Data rmt av.ailable.
I __.__ _IMLC.B:1_LCoot,1 I STATIONI James _A.Elidatrick
- k. of Circulating No. of Service Total Valune (e3) of HONTH: Wovember jf85 Mean Electrical __Iseestatures.1C1.
Data Watar_Euses Water _Euses _ Water _Euseed..__ __0uieut_IHWe1. Iciate Discharse 1 3 2 1,940,342.4 223 12.3 17.7 2 3 2 2,158 358.4 481 11.0 21.3 3 3 2 2,158 353.4 483 8.7 19.1 I 4 5
6 7
3 3
3 3
2 2
2 2
2,150,358.4 2,158.353.4 2 15R,358.4 2,158 353.4 485 501 555 789 4.9 9.8 11.1 11.2 17.2 20.3 22.5 24.8 2,158,358.4 I
8 3 2 818 10.7 26.8 9 3 2 2 153,358.4 327 11.2 27.4 10 3 2 2 158 358.4 829 10.4 26.8 11 3 2 2 153 358.4 333 9.1 25.4 12 3 2 2e158 358.4 836 5.8 22,3 13 3 2 2,153,353.4 335 7.8 24.2 14 3 2 2 158,358.4 834 8.6 25.1 15 3 2 2,153,358.4 330 8.4 24.9 II. 3 2 2 158,358.4 835 6.8 23.2 2,153,358.4 I
17 3 2 834 6.9 23.3 18 3 2 2,158 358.4 834 7.8 24.3 19 3 2 2,158 353.4 334 7.7 24.2 20 3 2 2,158,358.4 835 8.1 24.4 21 3 2 2 158 353.4 336 7.7 24.2 I 22 23 24 25 3/2 2
3 2
2 2
2 2
2,158,358.4 te940,342.4 1,504 310.4 1 722,326.4 797 408 0
0 7.7 7.7 6.5 4.5 23.5 17.4 6.6 6.6 24 2/3 I
2 1 722:326.4 174 7.2 13.1 27 3 2 2,t53,353.4 616 7.3 19.8 28 3 2 2,158,358.4 761 6.4 21.7 29 3 2 2,158,353.4 817 6.3 22.4 30 3 2 2,158 358.4 830 5.8 21.9 STATION 1 James _&_fitzfairick NONTH: December _1285 No. of No. of Circulating Service Total Voluna (e3) of Mean Electrical __Inseeratures_IC).
Data Water _Euses Water _Euses ____ Water _Eummed Duteut_1MWe)_ lotske Discharse 1 3 2 2,158 358.4 832 4.8 20.9 I 2 5
3 4
3 3
3 3
2 2
2 2
2,093 607.6 2:093 607.6 2,115,191.2 2e115,191.2 035 832 833 833 5.7 5.2 6.4 4.6 22.1 22.1 23.2 23.2 i 6 3 2 2,093 (47.6 830 6.0 22.6 7 3 2 2,093,607.6 332 6.8 23.3 8 3 2 2,093 607.6 832 5.8 22.4 9 3 2 2,tt5,191.2 832 4.1 22.7 10 3 2 2,093 607.6 832 5.5 22.2 I 11 12 13 14 3
3 3
3 2
2 2
2 2,093,407.6 2,093 607.6 2,093 407.6 2,093,607.6 830 831 027 5.6 5.6 5.9 22.2 22.1 22.4 830 5.6 22.1 I 15 3 2 2,072,024.1 830 4.4 20.9 16 3 2 1,964,106.1 832 4.2 20.8 17 3 3 1 942,522.6 833 3.4 20.2 10 3 2 1:099,355.4 832 3.3 20.2 19 3 2 1,8??.355.4 831 4.3 21.1 20 3 2 1,077,771.8 826 4.4 20.9 21 3 2 1 899 353.4 832 5.8 22.3 22 3 2 1,856,108.2 832 5.0 21.5 23 3 2 te834 404.6 831 5.3 21.8 24 3 2 teR34 604 4 831 5.3 21.7 25 3 2 1,356 133.2 833 5.1 21.6
- .. 4 s e o.w e em .o e.v. g., ev.y 27 3 2 1,813 021.1 830 5.1 21.5 29 3 2 1,013,021 1 833 4.4 20.8 i
I 29 30 31 3
3 3
2 2
2 1 813 021.1 1 013:021.1 1,877,771.8 832 833 833 4.4 4.3 4.8 20.9 20.7 21.2
I I
I I
I APPENDIX C I SCIENTIFIC AND COMMON NAMES OF ALL TAIA COLLECTED IN 1985 I
I I
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I
!I I
I I
I I
t
APPENDIX C SCIENTIFIC AND COMMON NAMES OF ALL TAXA COLLECTED IN 1985 Scientific Name Common Name Alosa eseudohnreneus Alewife )
I Ambloolites runestris Anouilla rostrata C.1mb arid ae Rock bass American eel Crayfish family 1
Catostomus commersoni White sucker I Cottus spp. (non-ricei)
Couesius olumbeus Sculpins Lake chub Cvorinidae Minnow / Carp family Egyosoma cenedianum Gizzard shad Etheostoma olmstedi Tessellated darter Gasterosteus aculeatus Threespine stickleback I Ietalurus nebulosus Lenomis cibbosus Lecomis machrochirus Brown bullhead Pumpkinseed Bluegill Microoterus dolomieui Smallmouth bass Mollusca Clam Morone americana White perch Morone chrvsons White bass Notronis atherinoides Emerald shiner Notronis hudsonius Spottail shiner Noturus flavus Stonecat Osmerus mordax Rainbow smelt Perca flavescens Yellow perch Percoo ia omiscomaveus Trout perch Petromszon marinus Sea lamprey Rhinietthys cataractae Longnose dace Salmo gardneri Rainbow trout Salmo crutta Brown trout Salvelinus namaveush Lake trout Umbra limi Central mudminnow I_
C-1