ML18040A224
| ML18040A224 | |
| Person / Time | |
|---|---|
| Site: | Nine Mile Point  |
| Issue date: | 12/31/1993 |
| From: | Abbott R, Jinks S, Koeneke M NIAGARA MOHAWK POWER CORP. |
| To: | Colquhoun J NEW YORK, STATE OF |
| References | |
| NUDOCS 9406160235 | |
| Download: ML18040A224 (137) | |
Text
ACCELERATED DI >RIBUTION DEMONST TION SYSTEM h
REGULATORY INFORMATION DISTRIBUTION SYSTEM (RIDS)
DOCKET FACIL:50-220 Nine Mile Point Nuclear Station, Unit 1, Niagara Powe 05000220 50-410 Nine Mile Point Nuclear. Station, Unit 2, Niagara Moha 05000410 AUTH. NAME AUTHOR AFFILIATION JINKS,S.M. Niagara Mohawk Power Corp.
KOENEKE,M.A. Niagara Mohawk Power Corp.
ABBOTT,R.B. Niagara Mohawk Power Corp.
RECIP.NAME RECIPIENT AFFILIATION COLQUHOUN,J. New York, State of
SUBJECT:
"Final SPDES Annual Biological Point Nuclear Station 1993."
'g 940610 r.
Rept Nine Mile DISTRIBUTION CODE: IE25D COPIES RECEIVED:LTR ENCL SIZE:
TITLE: Environmental Monitoring Rept (per Tech Specs)
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7 NIASA A U MQHAlNK NINE MILE POINT NUCLEAR STATION/P.O. BOX 63, LYCOMING, NEW YORK 13093/TELEPHONE (315) 343-2110 June 10, 1994 Mr. James Colquhoun Bureau of Environmental Protection NYS Department of Environmental Conservation 50 Wolf Road Albany, New York 12233
Dear Mr. Colquhoun:
In accordance with Section IV.c of SPDES Permit No. NY-000-1015 for the Nine Mile Point Nuclear Station, enclosed is the 1993 Annual Biological Monitoring Report. This report concerns monitoring requirements for the Unit 1 facility.
Any questions concerning the enclosed report should be directed to Hugh J. Flanagan at (315) 349-2428.
Sincerely, chard B. Abbott Plant Manager - Unit 1
/psc Enclosure (HJ F94.044) pc: J. A. Miakisz H. J. Flanagan J. R. Spadafore Regional Fisheries Manager (NYSDEC, Cortland)
NYSDEC, Cape Vincent T. T. Martin (USNRC)[2]
Document Control Desk (USNRC)[2]
>6OCO3 9406160235 93i23i PDR ADOCK 05000220 7)6 R
PDR l j;
4'e Ontario June 1994 FINAL SPDES Annual Biological Monitoring Report Nine Mile Point Nuclear Station 1993 EA Engineering, Science,
..9406160235 and Technology
1%
12152.01 Final Nine Mile Point Nuclear Station 1993 SPDES Annual Biological Monitoring Report Prepared for Niagara Mohawk Power Corporation Nine Mile Point Nuclear Station Unit 1 P.O. Box 32 Lycoming, New York 13093 Prepared by EA Engineering, Science, and Technology The Maple Building 3 Washington Center Newburgh, New York 12550 teven M. Jin, P, Vice Presi ent Date ary A ice oene e, ProJect anager ate June 1994
CON'ANTS
~Pa e LIST OF TABLES ........................................ ii EXECUTIVE
SUMMARY
................................... ES-1
- 1. INTRODUCTION ...................................... 1-1
- 2. METHODS AND MATERIALS.............................. 2-1 2.1 Schedule (Permit Section IV.B.1) 2 1
~ ~ ~ ~ ~ ~ ~ ~ ~ ~ ~
2.2 Sampling Procedure (Permit Section IV.B.2,3,4,5)..... 2-1 2.3 Laboratory Processing (Permit Section IV.B.4)....... .... 2-2 2.4 Water Quality Determinations (Permit Section IV.B.5) .... 2-3 2.5 Data Presentation (Permit Section IV.C) ........... .... 2-3
- 3. RESULTS AND DISCUSSION .............................. 3-1 3.1 Impingement Abundance and Composition (Permit Section IV.C.3) 3 IV.B.4) .............
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3.2 Length Distributions (Permit Section 3A IV.B.4).....................
~ ~ ~ ~ ~ o 3.3 Biomass (Permit Section 3 5 IV.B.5) ................,
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3.4 Water Quality (Permit Section ~ ~ ~ ~ ~ o 3 6 REFERENCES APPENDIX A: EXCEPTIONS TO STANDARD OPERATING PROCEDURES FOR IMPINGEMENT AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 (PERMIT SECTION IV.B.5)
APPENDIX B: STATION OPERATING CONDITIONS AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 (PERMIT SECTIONS IV.B.5 AND IV.C.9)
APPENDIX C: SCIENTIFIC AND COMMON NAMES OF ALL TAXA COLLECTED IN 1993 APPENDIX D: DAILYIMPINGEMENT COLLECTION TOTALS AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993
LIST OF TABLES Number Title 2-1 Impingement Sampling Dates for Nine Mile Point Nuclear Station Unit 1, 1993.
3-1 Actual Monthly Impingement Collections, Nine Mile Point Nuclear Station Unit 1, 1993.
3-2 Mean Daily Impingement Rate by Species at Nine Mile Point Nuclear Station Unit 1, 1993.
3-3 Monthly Impingement Rate (Based on Flow) at Nine Mile Point Nuclear, Station Unit 1, 1993 ~
3-4 Estimated Monthly Impingement (Based on Daily Average Rate) at Nine Mile Point Nuclear Station Unit 1, 1993.
3-5 Estimated Monthly Impingement (Based on Flow) at Nine Mile Point Nuclear Station Unit 1, 1993.
Length Distribution of Representative Important Species Impinged at Nine Mile Point Nuclear Station Unit 1, 1993.
3-7 Total Biomass of Impinged Organisms Collected at Nine Mile Point Nuclear Station Unit 1, 1993.
3-8 Estimated Monthly Biomass of Collected Taxa (Based on Flow) at Nine Mile Point Nuclear Station Unit 1, 1993.
0 EXECUTIVE SUKGIARY This report, prepared by EA Engineering, Science, and Technology, presents the results of impingement abundance studies conducted during 1993, as required by the State Pollutant Discharge Elimination System (SPDES) Permit No. NY 000 1015,Section IV.C (dated 1 July 1983) for the Nine Mile Point Nuclear Station Unit 1 (NMP Unit 1).
Impingement abundance was monitored between 4 and 20 samples per month, for a total of 78 samples from January through December 1993.
A brief refuel outage occurred from 20 February to 17 April 1993 at NMP Unit 1. Both main circulating water pumps were usually shut off during the outage, though for brief periods, at least one main circulating pump was operating. The seasonal increase in fish impingement diminished during the outage due to the reduction in water volume.
Impingement sampling at NMP Unit 1 in 1993 resulted in the collection and identification of 28 fish taxa. One taxon (sculpin) was identified to the genus level and the remaining 27 taxa were identified to the species level. Crayfish and zebra mussels were the only invertebrates found in the impingement collections in 1993. Alewife was the most numerous (53,592) comprising 96 percent of the total fish catch (55,976 excluding fragments). Alewife, rainbow smelt, and spottail shiner accounted for 98 percent (54,993) of all fish collected
~ ~
(55,976). No rare, endangered, or threatened fish species were collected at NMP Unit 1 in
~
1993.~
Zebra mussels (Dreissena polymorpha) were identified in the Nine Mile Point area in late Summer 1990. Zebra mussels were first noted in the impingement sample collections in late 1991, and their presence (by volume) has been noted on applicable data sheets as part of the regular impingement sample analysis procedure since that time. No Corbicula sp. molluscs were found in the 1993 impingement collections at NMP Unit 1.
- 1. INTRODUCTION Nine Mile Point Nuclear Station Unit 1 (NMP Unit 1) is solely owned and operated by Niagara Mohawk Power Corporation. The station is located on a 900-acre site in Oswego County, New York, and is approximately 6.8 mi north-northeast of the City of Oswego.
The power conversion system utilizes a 1,850-megawatt (thermal) boiling water reactor designed and manufactured by the General Electric Corporation, and a 610,000-kilowatt (net electric) turbine-generator.
NMP Unit 1 has been operational since December 1969. The station is a critical, integral part of the New York State Energy Master Plan, and a cost efficient source of electrical energy within Niagara Mohawk Power Corporation's service area.
NMP Unit 1 utilizes a once-through, non-contact cooling water system to dissipate thermal energy from the main condensers and auxiliary cooling systems. Cooling water is drawn from Lake Ontario by means of two main circulating water pumps rated at 946.25 gal) per minute (total) and two service water pumps which operate at approximately m'250,000 68.13 m'18,000 gal) per minute (total). Usually, one service water pump is operating except during the mid-summer months.
~ ~
The lake intake structure is an open-sided hexagonal concrete structure located in
~ ~
approximately 5.5 m (18 ft) of water (mean lake level) and approximately 259 m (850 ft)
~
~ ~ ~
~ ~
from the existing shoreline. The lake discharge structure is of a design that is similar to the
~
~ ~ ~ ~
intake structure. This structure is hexagonal with open-sided ports and is located
~
approximately 102 m (335 ft) from the shoreline and 3.8 m (12.5 ft) below the surface (mean lake level).
Aquatic organisms, detritus, and other debris enter with the water pumped from the vicinity of the submerged intake structure. These materials flow through trash racks, which are used for removing large items, such as logs, and are impinged on a total of three traveling screens comprised of 9-mm (3/8-in.) mesh, which are used for screening out smaller materials.
Periodically, the traveling screens are rotated and washed 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 NMP Unit 1 have been monitored since 1972 in order to estimate species abundance and composition.
This report presents the results of the biological monitoring program conducted by EA during 1993, as required by the State Pollutant Discharge Elimination System (SPDES) Permit No.
NY 000 1015,Section IV (dated 1 July 1983), covering Niagara Mohawk Power Corporation's NMP Unit 1.
Impingement collections (as required by Section IV.B of the permit) were monitored on a frequency of 4-20 samples per month from January through December 1993 (a total of 78 samples in 1993).
1-1
~
Impingement sampling at NMP Unit 1 in 1993 resulted in the collection and identification of
~
28 fish taxa. One taxon (sculpin) was identified to the genus level and the remaining 27 taxa
~
were identified to the species level. Crayfish and zebra mussels were the only invertebrates found in the impingement collections in 1993. Alewife was the most numerous species (53,592) comprising 96 percent of the total fish catch (55,976). Alewife, rainbow smelt, and spottail shiner (54,993) accounted for 98 percent of all fish collected (55,976 excluding fragments).
Zebra mussels (Dreissena polymorpha) were identified in the Nine Mile Point area in late Summer 1990. Zebra mussels were first noted in the impingement sample collections in late 1991. Their presence has been noted (by volume) on impingement sample data sheets whenever applicable.
As required by correspondence from Niagara Mohawk Power Corporation to the Nuclear Regulatory Commission, all fish impingement samples are checked for the presence of the Asiatic clam (Corbicula sp.). No Corbicula sp. molluscs were found in the 1993 impingement collections, 1-2
- 2. METHODS AND MATERIALS 2.1 SCHEDULE (PERMIT SECTION IV.B.I)
In accordance with permit requirements, 78 impingement collections were scheduled between 1 January and 31 December 1993 as listed below:
Number of Sampling Days Month Scheduled Per Month" January 4 February 4 March 4 April 16 May 20 June 4 July 4 August 6 September 4 October 4 November 4 December 4 Total 78 (a) Days assigned within each month were selected randomly using the formula (1+INT(RAND~31))
from Lotus 1-2-3, Release 2.3.
Samples were collected over a 24-hour period on randomly selected days. As required by the SPDES permit, selected sample dates were scheduled such that no more than 10 days occurred between samples. When rescheduling samples became necessary, every attempt was made to reschedule the samples to accommodate the 10-day requirement. Table 2-1 lists the scheduled sampling dates.
In 1993, a total of 78 impingement samples were successfully collected. One impingement sample had to be rescheduled due to a Clamtrol treatment process in the intake/traveling screen area. The sample was successfully completed on the rescheduled date (Appendix A).
2.2 SAMPLING PROCEDURE (PERMIT SECTION IV.B.2,3,4,5)
Sample collection was initiated at approximately 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 for approximately 5 minutes. The collection basket with a 3.2-mm (1/8-in. stretched mesh) liner was then positioned at the end of the sluiceway. The collection basket remained in place for the duration of the sample period, unless high impingement or debris loads required that it be emptied. For such occasions, it was removed, emptied, and repositioned.
2-1
At the end of the 24-hour period, the traveling screens were rotated and washed for approximately 5 minutes. Impinged organisms were washed into the collection basket; the basket was removed and emptied.
Plant operational data were obtained from station records for each sample date to document cooling water flow rates, intake and discharge temperatures, and power production (Appendix B). When relevant to data analysis, intake water volumes are noted on the report tables. Additionally, volume of water through the intake is apportioned for the time(s) when main circulating water pumps are operating or shut off ("A" and "B" columns on applicable tables).
A subsampling routine was utilized for occasions when high impingement rates or high debris loads were encountered. The subsampling technique was based on volume, and the total 24-hour catch was estimated using the formula:
Volume of Total Sample X No. of Fish in Subsample Estimated No. of Fish in Total Sample ~
Volume of Subsample The total volume of the sample was determined by repeatedly filling a volumetrically graduated container, recording the values, and adding them. The total volume was thoroughly mixed by hand, or with a shovel and spread out evenly over a flat surface.
A subsample volume of at least 25 percent of the total sample volume was mathematically calculated. Aliquots of the sample were randomly selected, removed, and measured to determine their volumes. Aliquots were removed and combined until the required subsample volume was achieved.
When subsamples occurred in 1993, they constituted at least 25 percent by volume of the total sample. Fish and invertebrates contained in the subsample were then processed according to regular laboratory procedures (Section 2.3).
2.3 LABORATORY PROCESSING (PERMIT SECTION IV.B.4)
Once the impingement sample was collected, it was returned to the laboratory and 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 and scientific names is included in Appendix C.
Specimens (to a maximum of 25 individuals) of the following species were analyzed for length and weight: white perch, alewife, and rainbow smelt. All collected specimens of smallmouth bass, yellow perch, and salmonids were weighed and measured. Other species
~
present in the samples were enumerated and weighed to obtain a total count and total weight
~
for each species (or lowest taxonomic level).
2-2
Total lengths were measured to the nearest millimeter. For the purposes of this report, 100 millimeters was used as a determinant of size class differentiation between young-of-the-year (YOY) and adults based on size range information in Scott and Crossman (1973).
Weights were measured 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.
When possible, measurements were recorded with greater accuracy than required (e.g., to the nearest 0.1 gram for specimens between 10 and 2,000 grams) if the scales would allow.
Any unusual conditions, abnormalities, or presence of fish tags were noted on the data sheets.
2.4 WATER QUALITYDE'H<MMINATIONS (PERMIT SECTION IV.B.5)
Intake and discharge temperatures were recorded from the station operating conditions presented in Appendix B.
2.5 DATA PRESENTATION (PERMIT SECTION IV.C)
Data are presented according to the requirements set forth in the SPDES permit:
- a. Monthly and annual total of impingement by species and grand total over all species.
- b. 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 volume of water pumped on sampling days.
- c. Total estimated impingement for each month was calculated using the following formula:
d (x)
C V+
where d = Total estimated impingement c = Number of fish collected during the period v* = Volume of cooling water used during the period
= Based on main circulating water pump(s) operating regime x = Total monthly volume of cooling water used.
The annual impingement estimate was then calculated by adding the 12 monthly impingement estimates.
2-3
- d. Additional tables were calculated for mean daily impingement rate (total number of fishes impinged [by species] on all sampling days in a month divided by the total number of sampling days) and a monthly estimated impingement based on rate (mean daily impingement rate multiplied by the total number of days in a particular month) and are available for comparison of data presentation methods and for historical continuity with past data reports.
- e. Monthly and annual total biomass (grams) by species and grand totals over all species.
- f. Total estimated biomass (adjusted for flow) was calculated in the same manner as estimated impingement.
2-4
TABLE 2-1 IMPINGEMENT SAMPLING DATES FOR NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 Scheduled'i Scheduled" Sampling Scheduled" Sampling Sampling Date Sampling Results Sampling Date Results Sampling Date Results 06 JAN 03 MAY 03 AUG 14 JAN 05 MAY 11 AUG 20 JAN 06 MAY 12 AUG 27 JAN 07 MAY 19 AUG 08 MAY 25 AUG 03 FEB 11 MAY 29 AUG 10 FEB 12 MAY 18 FEB 13 MAY 08 SEP 25 FEB 14 MAY 16 SEP 15 MAY 24 SEP 05 MAR 16 MAY 29 SEP 11 MAR R~C; Completed 22-23 MAR 19 MAY 19 MAR C 20 MAY 07 OCT 26 MAR 21 MAY 13 OCT 22 MAY 19 OCT 02 APR 23 MAY 27 OCT 03 APR 24 MAY C 04 APR 25 MAY C 05 NOV C 05 APR 26 MAY C 12 NOV C 06 APR 27 MAY C 18 NOV C 07 APR 24 NOV 08 APR 03 JUN 13 APR 10 JUN 03 DEC 14 APR 17 JUN 13 DEC 15 APR 27 JUN 23 DEC 20 APR 29 DEC 22 APR 02 JUL 24 APR 09 JUL 26 APR 19 JUL 28 APR 28 JUL 29 APR (a) Sample collection date.
NOTE: C = Completed sample.
R~C = Sample rescheduled and completed on a different date within the confines of a random numbers formula and any remaining available dates in the month (Appendix A) ~
- 3. RESULTS AND DISCUSSION 3.1 IMPINGEMENT ABUNDANCE AND COMPOSITION (PERMIT SECTION IV.C.3)
In 1993, the seasonal patterns of fish species diversity and abundance were evident during the course of impingement sampling at NMP Unit 1. Spring impingement abundance (March and April) are slightly diminished due at least in part to a station refueling outage that occurred from 20 February to 17 April. Both main circulating water pumps were usually shut off during the outage, though for brief periods at least one main circulating water pump was operating. During the outage the volume of water was reduced through the intake as a direct result of the shut down of the main circulating water pump(s). The seasonal increase in fish impingement abundance which typically begins in March and April was diminished until the station restarted in mid-April. Impingement at NMP Unit 1 continues to be less than historically observed and appears to be influenced by record low alewife biomass in Lake Ontario first noted in 1992 (Lange and Smith 1992).
Historically, impingement abundance at NMP Unit 1 increases in the spring, corresponding to the migration of alewife and rainbow smelt inshore. Impingement abundance then decreases for the summer months as adult fish complete spawning and move offshore.
During this time, larval and juvenile fishes have not attained a size susceptible to the impingement process. YOY generally reach an impingeable size in the late summer and autumn. Impingement abundance of YOY then increases sporadically due to the frequency of late summer and fall storms and the inability of YOY to avoid the intake structure during storms.
The collections of impinged fish at NMP Unit 1 for 1993 followed the historical seasonal pattern: April and May impingement collections increased in volume as fish came inshore to spawn followed by a decrease through late spring and summer (Table 3-1). Impingement increased slightly in September and October as a result of storm conditions coinciding with the presence of fish near shore. Samples collected in January and December 199)'also reflect w'inter st'orm conditions and the presence of YOY near shore. The largest fish impingement collections occu'rred in April (22,781), May (30,613), and June (901) .
accounting for 97 percent of the total 1993 fish impingement collections.
Alewife and rainbow smelt continued to dominate annual impingement collections as in most previous years, accounting for 98 percent of the annual fish impingement totals for 1993.
Spottail shiner (231) and trout-perch (199) were third and fourth in abundance (neither are representative important species (RIS). All RIS combined (alewife, rainbow smelt, yellow perch, smallmouth bass, white perch, and lake trout) equaled 54,961 individuals and 98 percent of the annual impingement total. Daily impingement sample results for 1993 are presented in Appendix D.
~ ~ ~
In 1993, fish species diversity occurred in accordance with seasonal abundances and/or behavioral stimuli. Species diversity ranged from a low of 7 species in November to a high
~
of 18 species in December. Low species diversity occurred in March, September, October,
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~
3-1
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and November. ~ Generally, low diversity results from station outages (March) and periods
~
with little meteorological or behavioral influence on fish populations in the vicinity of
~ ~ ~
NMP Unit 1. The highest diversities resulted in January, April, May, and December with
~
the highest diversity occurring in December (17 species). Species diversities in April and May correlate to inshore movements of many species toward their spawning grounds.
Species variety in January and December illustrates the effect of storm conditions on young fish that remain in nearshore areas. When 24-hour impingement collections coincide with storms, the size of the impingement sample may be several orders of magnitude larger than other samples for the same month (e.g., Appendix D - January, February, October, and December).
In previous years, high rates of impingement occurred at NMP Unit 1 when strong winds from the west or northwest resulted in heavy wave action. Lifton and Storr (1977) statistically correlated wave height, water temperature, and wind with impingement at power plants on Lake Erie and Lake Ontario. Wave height was found to be the most significant factor contributing to the correlation. 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 a higher rate of impingement, YOY of most species of fish appear to be most susceptible to meteorological influences (Lifton and Storr 1977). In 1993, storm conditions influenced the size of the impingement collections on several occasions and are described further:
~ An impingement sample collected over the 24-hour period of 26-27 January resulted in the collection of 54 percent of the monthly impingement total. The sample also contained 66 percent of the month's collection of rainbow smelt. Winds were from the northwest at 15 knots with rough water.
~ In February, an impingement sample collected from 2 to 3 February contained 80 percent of the month's impingement total (with both main circulating water pumps operating). Winds were from the northwest and west 15-25 knots. The sample resulted in the collection of 90 percent of February's collection of rainbow smelt.
~ In October, a 24-hour sample collected from 18 to 19 October during 10- to 20-knot northwest winds and 6-ft waves resulted in the collection of 91 percent of the monthly impingement totals and 99 percent of the October total for alewife. All of the alewife collected were YOY.
~ In December, a sample collected over the 24-hour period of 22-23 December contained 89 percent of the monthly impingement total and 81 percent of the total of rainbow smelt YOY. Winds were northwest at 10-20 knots; waves increased to 5-7 ft. This sample was also comprised of the most species for the year: 17 species plus sculpins.
3-2
Temporal presence or absence of species throughout 1993 followed seasonal behavior and meteorological influence. Alewife and rainbow smelt were collected in 7 and 9 months of the year, respectively. Alewife dominated the impingement collections in 5 of those months.
Rainbow smelt dominated the impingement collections made in January and February; months when alewife were nearly absent from the samples. Smallmouth bass and yellow perch, both RIS, were collected in 9 and 8 months, respectively, and their occurrence is considered relatively common in the collections. White perch, also an RIS, were collected during 6 months of 1993. Lake trout, the only salmonid collected in 1993, were found in samples from 6 'months of the year. Non-RIS found commonly and in relative abundance throughout the seasons of 1993 include stonecat, sculpins, spottail shiner, threespine stickleback, and trout-perch.
Rates of impingement were calculated using two different methods. The mean daily impingement rate (Table 3-2) is defined as the average number of fish collected per day per month and is included for comparison. The mean daily impingement rate based on flow (Table 3-3) is defined as the total number of fish impinged on sample days in the month divided by the volume of water pumped in million cubic meters (MCM) during those days.
Each table defines the rate per species per month and the total impingement rate for the month. Impingement rates per MCM on Table 3-3 are further specified into columns "A" for the time period when at least one main circulating water pump was operating and "B" when only the service water pumps were operating.
~ ~
Rates of impingement whether calculated over time (Table 3-2) or volume (Table 3-3) generally demonstrate the same trends detected in the actual impingement collections. In the
~
spring, rates peak as fish migrate inshore then decrease through the summer. In autumn, the rates of impingement increase in response to the occasional influx of YOY during storms.
When the main circulating water pump(s) were operated a portion of the time, the impingement rate per volume was higher when the pumps were operating than when only the service water pumps were running (e.g., February and March). Fish impingement rates may be reflective of meteorological, environmental, and behavioral influences on fish movements near NMP Unit 1 regardless of water volume. However, the volume of water pumped through the intakes will mirror these influences most when both main circulating water pumps are operating (e.g., April impingement rates from 1-18 April and 19-30 April).
The mean daily impingement rate determined by volume (Table 3-3) was highest in April (1,852 fish/MCM), May (1,045 fiish/MCM), and June (154 fish/MCM). These impingement rates are reflective of adult alewife movements to inshore spawning areas. A slight increase in the rate of impingement was seen in October (67 fish /MCM), and December (49 fish/MCM), reflective of the influx of YOY during storm conditions.
The lowest rates of impingement (when at least one main circulating water pump was operating) occurred in August (5 fish/MCM), September (10 fiish/MCM), and November (2 fish/MCM). Weather conditions for the samples were relatively benign with no major storms thereby reducing any meteorological influences on the fish impingement.
3-3
The collection of a particular species on a seasonal basis is also reflected in the daily rate of impingement. The rates of impingement for April, May, and June are a direct result of alewife movements inshore. Rainbow smelt also increased in the impingement in April and May as the result of inshore spawning movements. Several species, including spottail shiner, threespine stickleback, and white perch also increased in rate of impingement in April and May in response to their species specific spawning behavior. Seasonal meteorological events, particularly winter storms, influenced the daily rate of impingement in the manner already addressed for Table 3-1. The effects of storm conditions are particularly evident on the collection of several RIS during 1993: alewife (October), white perch, and yellow perch (December). Non-RIS influenced by winter storms include gizzard shad (January) and pumpkinseed and trout-perch (December). In general, the monthly impingement rates based on flow volume will reflect the collection of fish at times of seasonal abundance and/or under storm conditions seen in Table 3-1.
Calculations of the estimated number of organisms impinged at NMP Unit 1 during 1993 were based on the mean daily impingement rate (Table 3-4) and on the rate of impingement adjusted for flow (Table 3-5). Estimates are similar for both methods of data expression.
Estimates of impingement based on daily average rate (Table 3-4) are given for comparison.
Based on volume, the estimated number of fish impinged was 115,884 (excluding fragments and crayfish). The estimated annual impingement of alewife was calculated as 105,146 equaling 91 percent of the annual total. The number of rainbow smelt estimated impinged in 1993 was 4,607 (4 percent of the total). The RIS fish estimates were impinged in the following numbers: white perch, 675; yellow perch, 170; smallmouth bass, 285; and lake trout, 62. All RIS fish combined (110,945) comprised 96 percent of the annual estimated fish impingement. For 1993, the estimated impingement generally followed the seasonal and meteorological patterns previously discussed.
3.2 LENGTH DISTRIBUTIONS (PERMIT SECTION IV.B.4)
Length-frequency distributions are determined in Tables 3-6a through 3-6f for the following species: alewife, rainbow smelt, white perch, yellow perch, smallmouth bass, and lake trout. Length frequency for species such as alewife and rainbow smelt which are collected throughout the year generally follow a seasonal pattern. Adults and subadults () 100 mm;
) 4 in.) of both species are most often collected during spring months when spawning migrations move adult fish to shallow, inshore waters. Late summer and fall collections are primarily composed of YOY ((100 mm; (4 in.) which are found in shallow inshore nursery areas. (Scott and Crossman [1973] noted the late summer length attained by alewife as 51-75 mm [2-3 in.] and that of rainbow smelt as 51 mm [2 in.].) At times during the year, YOY of both species were collected damaged to an extent that made it impossible to accurately obtain length measurements on individual fish (i.e., August and October).
(During the fall season, some of these fish may have originated from the service water strainers and may not have been collected directly from impingement.)
In 1993, collections of alewife followed the seasonal length distribution pattern as described (Table 3-6a). Alewife collected from March through July were adult and subadult fish.
From August through December, most alewife collected were YOY. Alewife measured from 3-4
samples collected in 1993 were comprised of 94 percent adults and subadults and 6 percent YOY. The minimum length measured was 4.7 cm (1.9 in.); the maximum length recorded was 18.8 cm (7.5 in.).
Rainbow smelt collections in 1993 (Table 3-6b) were dominated by adults and subadults in April and May. The 1992 year class (yearling) rainbow smelt were collected sporadically throughout 1993 but dominated the impingement collections of rainbow smelt in January and February. Overall, YOY rainbow smelt comprised 26 percent of the smelt measured. The minimum length recorded was 4.6 cm (1.8 in.); the maximum length recorded was 18.5 cm (7.4 in.).
White perch (Table 3-6c) measured from the 1993 impingement samples were predominantly YOY (75 percent). Eighty percent of the YOY measured were collected in December; 89 percent (65 individuals) of those were found in one storm-influenced sample.
Adult white perch were collected as individuals and were collected primarily in April and May. The minimum length measured for white perch was 5.7 cm (2.3 in.); the maximum length recorded was 32.0 cm (12.8 in.).
Yellow perch (Table 3-6d) were collected sporadically throughout 1993. One storm-influenced impingement in April resulted in the collection of 13 yearlings (1992 year class).
The yellow perch measured during impingement collections at NMP Unit 1 were comprised of 84 percent adults/subadults. The minimum length measured was 5.0 cm (2.0 in.); the maximum length was 30.0 cm (12.0 in.) Yellow perch appear to have had a successful spawning in 1992 as evidenced by the increased number of YOY in the impingement samples (EA 1993) and the shift to yearling size in the 1993 collections. Preliminary assessment data on yellow perch captured by U.S. Fish and Wildlife Service trawls during 1992 also indicate a successful 1992 spawning (O'Gorman 1993).
Smallmouth bass (Table 3-6e) collected during 1993 were predominantly adult/subadult (53 percent) and were collected sporadically through the year. The minimum length recorded for smallmouth bass collected in 1993 was 4.3 cm (1.7 in.); the maximum length recorded was 44.6 cm (17.8 in.),
Lake trout, the only salmonid species collected in 1993, were found as adults in samples throughout the year. The minimum length measured was 63.6 cm (25.4 in.); the maximum length measured was 81.5 cm (32.6 in.).
3.3 BIOMASS (PERMIT SECTION IV.B.4)
The total biomass (Table 3-7) collected in the 1993 impingement samples at NMP Unit 1 was 1,621,504 grams, excluding invertebrates and fragments. Alewife accounted for 1,474,592 grams (1,475 kilograms) or 91 percent of the annual total biomass. Alewife and rainbow smelt (10,523 grams; 11 kilograms) combined with the other RIS (white perch, 5,059 grams; yellow perch, 1595 grams; smallmouth bass, 18,526 grams; and lake trout, 25,726 grams) comprised 95 percent of the annual total biomass at NMP Unit 1. Biomass is 3-5
~
generally more widely distributed among species collected since a few heavy-bodied fish (i.e., trout, basses, etc.) may weigh more than a more abundant fragile-bodied species such
~ ~ ~
as rainbow smelt.
The estimated biomass (excluding fragments) (Table 3-8) calculated based on flow volume was 3,516,558 grams (3,517 kilograms) of which alewife constituted 76 percent (2,670,455 grams; 2,670 kilograms). Alewife, rainbow smelt, and the other RIS collected in 1993 accounted for 85 percent (2,973,614 grams; 2,974) of the annual estimated biomass (excluding fragments).
3.4 WATER QUALITY (PERMIT SECTION IV.B.5)
Intake and discharge temperatures recorded along with station generating conditions are listed in Appendix B. From the Appendix B tables, intake temperatures ranged from a minimum of 0.0'C on 12 February to a maximum of 23.4'C on 1 September. The discharge temperatures (when the plant was operating at full power) ranged from a minimum of 18.3'C on 20 January to a maximum of 40.9'C on 15 August 1993. Temperatures discussed above may have occurred on additional days, however, the dates given are the first dates of occurrence for minimum and maximum temperatures in the intake and discharge canals at NMP Unit 1 during 1993.
3-6
TA 3-1 ACTUAL MONTHLY IMPINGEMENT COLLEC, NINE MILE POINT NUCLEAR STATION UNIT I, Annual JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total No. of Samples 16 10 78 A B A B A B SPECIES Alewife 22,322 29,823 801 280 5 360 53,592 Rainbow smelt 160 210 264 449 15 63 1,170 Spottail shiner 9 34 40 48 20 3 11 28 2 32 231 Trout-perch 6 4 20 121 16 25 199 Sculpins 16 17 34 2 41 3 139 White perch 18 13 1 65 106 Stonecat 16 35 9 24 95 Threespine stickleback 3 8 19 27 17 2 82 Gizzard shad 32 13 56 Smallmouth bass 13 2 1 12 10 53 Tessellated darter 32 13 48 Emerald shiner 6 21 35 Rock bass 2 1 34 Yellow perch 13 31 Pumpkinseed 29 30 White sucker 20 Bluegill 10 American eel 2 4 NOTE: A = Collected when at least one main circulating water pump was operating; B = Collected when no main circulating water pump was operating; service water only. Dashes ( ) indicate no catches made.
TABLE 3-1 inued)
Annual JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total A B A B A B SPECIES (Continued)
Lake trout 2 2 2 9 Freshwater drum 5 7 Lake chub Largemouth bass Channel catfish Walleye Brown bullhead Lake herring (Cisco)
Sea lamprey Subtotal 244 320 0 0 21 22,764 2 30,597 901 335 42 57 398 15 280 55,976 OTHER SPECIES Crayfish 2 2 12 2 15 3 1 3 40 FISH FRAGMENTS Alewife Spot tail shiner II Tessellated darter Emerald shiner Rainbow smelt Crayfish TOTAL 244 323 0 0 24 22,776 5 30,613 901 338 44 61 400 17 283 56,029
TABLE 3-2 MEAN DAILYIMPIN NT RATE'Y SPECIES AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 Annual JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total No. of Samples 16 20 78 SPECIES Alewife 0.25 1,395.12 1,491.15 200.25 70.00 0.83 90.00 687.08 Rainbow smelt 40.00 52.50 16.50 22.45 3.75 0.25 0.75 1.25 15.75 15.00 Spottail shiner 2.25 8.50 2.50 2.40 5.00 0.75 1.83 7.00 1.00 0.50 8.00 2.96 Trout-perch 1.50 1.00 6.05 4.00 1.00 0.33 0.25 6.25 2.55 Sculpins 4.00 4.25 0.50 2.05 1.25 0.25 2.25 1.50 0.75 0.75 1.78 White perch 1.12 0.40 0.25 3.25 0.25 16.25 1.36 Stonecat 0.50 0.25 1.75 2.25 6.00 0.50 0.50 0.75 1.22 Threespine stickleback 0.75 2.00 1.19 1.35 4.25 0.50 1.50 1.05 Gizzard shad 8.00 3.25 1.75 1.00 0.72 Smallmouth bass 0.50 1.25 0.81 0.10 0.50 0.25 2.00 2.50 1.50 0.68 Tessellated darter 0.25 1.60 3.25 0.25 0.17 0.62 Emerald shiner 1.50 5.25 0.50 0.25 0.25 1.00 0.45 Rock bass 0.50 0.25 1.75 0.06 0.10 0.25 2.00 0.33 1.25 0.25 1.00 0.44 Yellow perch 0.25 0.56 0.15 0.25 0.17 0.50 0.25 3.25 0.40 Pumpkinseed 0.05 7.25 0.38 White sucker 025 0.19 0.10 1.75 0.67 0.25 0.50 0.26 Bluegill 0.25 2.25 0.13 American eel 0.50 1.00 0.50 0.25 0.12 (a) Rate = Average number of fish impinged per day.
NOTE: Dashes ( ) indicate no catches made.
TABLE 3-2 (Co mued)
Annual JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total SPECIES (Continued)
Lake trout 0.50 0.50 0.05 0.25 0.25 0.50 0.12 Freshwater drum 0.25 0.06 1.25 0.09 Lake chub 0.50 0.06 0.05 0.75 0.09 Largemouth bass 1.00 0.05 Channel catfish 0.25 0.50 0.04 Walleye 0.06 0.17 0.03 Brown bullhead 0.25 0.01 0.06 0.01 Lake herring (Cisco) 0.06 0.01 Sea lamprey 0.05 0.01 Subtotal 61.00 80.00 5.25 1,422.85 1,529.85 225.25 83.75 7.00 14.25 99.50 3.75 70.00 717.64 OTHER SPECIES Crayfish 0.50 0.50 0.88 0.75 0.75 0.17 075 0.51 FISH FRAGMENTS Alewife 0.25 0.25 0.08 Spottail shiner 0.06 0.17 0.03
.Tessellated darter 0.05 0.25 0.03 Emerald shiner 0.25 0.01 Rainbow smelt 0.25 0.01 Crayfish 0.25 0.01 TOTAL 61.00 80.7S 6.00 1,423.79 1,530.65 225.25 84.50 7.34 15.25 100.00 4.25 70.75 718.32
TABLE 3-3 MONTHLY IMPINGEME RATE'*'BASED ON FLOW) AT NINE MILE POINT NUCLEAR STATION UNIT I, 1993 Annual JAN FEB APR MAY JUN JUL AUG SEP OCT NOV DEC Total No. of Samples 16 20 78 Sample Volume (MCM) 5.668 3.920 0.051 0.000 0.240 12.296 0519 29.284 5.859 6.041 9.229 6.019 5.951 5.865 5.761 96.703 B A B SPECIES Alcwifc 0.176 1>815.387 1,01&A06 136.713 46.350 0.542 - 60.494 NIA Rainbow smelt 28.229 53.571 21.470 15.333 2.560 0.166 0.504 0.853 10.936 N/A Spottail shiner 1.588 8.673 3.253 1.639 3.414 0.497 1.192 4.652 0.672 0.341 5.555 NIA Trout-perch 1.059 1.020 1.627 4.132 2.731 0.662 0.217 0.166 4.340 NIA Sculpins 2.823 4.337 8.333 2.765 3.854 1.400 0.853 0.166 1.495 1.008 0.512 0.521 N/A White perch 1.464 0.273 0.171 2.185 0.171 11.283 NIA Stonecat 0.510 4.167 1.301 1.195 1.536 3.973 0.325 0.332 0.521 NIA Threespinc sticklcback 0.529 2.041 1345 0.922 2.902 0.331 1.041 N/A Gizzard shad 5.646 3.316 1.176 0.694 N/A Smallmouth bass 0.353 20.833 1.057 0.068 0.341 0.166 1.300 1.661 1.041 N/A Tessellated darter 4.167 1.093 2.219 0.166 0.108 N/A Emerald shiner 1.059 5957 8.333 0.166 0.168 0.694 N/A Rock bass 0.353 0.255 29.167 0.081 0.068 0.171 1.324 0.217 0.&31 0.171 0.694 N/A Yellow perch 0.176 0.732 0.102 0.166 0.108 0.336 0.171 2.257 NIA Pumpkinseed 0.034 5.034 N/A White sucker 4.167 0.244 0.068 1.159 0.433 0.166 0.336 N/A (a) Rate ~ Avcragc number of fish impinged per day by volume.
NOTE: A ~ Collcctcd when at least onc main circulating water pump was operating; B ~ Collected when no main circulating water pump was operating; service water only.
Dashes ( ) indicate no catches made; hIChI ~ million cubic meters; N/A ~ Not applicable.
TABLE 3-3 ( ontinued)
Annual FEB APR MAY JUN JUL AUG SEP OCT NOV DEC Total A B A B B SPECIES (Continued)
Bluegill 0.176 1.562 NIA American eel 0.353 1.020 8.333 0.166 N/A Lake trout 0353 0.510 0.034 0.171 0.166 0.347 N/A Freshwater drum 0.255 0.081 0.868 NIA Lake chub 0.510 0.081 0.034 0.521 N/A Largemouth bass 0.694 N/A Channel catfish 0.176 0.341 N/A Walleye 0.081 0.108 NIA Brown bullhead 0.255 NIA 0.081 N/A Lake herring (Cisco) 0.081 N/A Sea lamprey 0.034 N/A Subtotal 43.049 81.630 0.000 0.000 87.500 1,851.331 3.854 1,044.835 153.7112 55.458 4.550 9.469 66.879 2.560 48.603 N/A OTIIER SPECIES Craylish 0.510 8333 0.976 3.854 0.512 0.497 0.108 0.521 N/A FISII FRAGMENTS Alewife 0.665 0.168 0.171 N/A Spottail shiner 1.927 0.108 N/A Tessellated darter 0.034 0.171 N/A Emerald shiner 0.255 N/A Rainbow smelt 4.167 NIA Crayfish 0.168 NIA TOTAL 43.049 82.395 0.000 0.000 100.000 1,852.307 9.635 1,045.381 153.782 55.955 4.766 10.134 67.215 2.902 49.124 N/A
TABLE 3-4 ESTIMATED
- MONTHLY IMPING T (BASED ON DAILYAVERAGE RATE) AT NINE MILE POINT NUCLEA STATION UNIT 1, 1993 Annual FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total No. of Samples 16 20 78 SPECIES Alewife 41,854 46,226 6,008 2,170 26 2,790 99,082 Rainbow smelt 1,240 1,470 495 696 112 23 38 488 4,570 Spottail shiner 70 238 75 74 150 23 57 210 31 15 248 1,191 Trout-perch 46 28 38 188 120 31 10 194 663 Sculpins 124 119 16 68 64 38 68 46 22 23 596 White perch 34 12 101 8 504 667 Stonecat 14 30 54 68 186 16 15 23 414 Threespine stickleback 23 56 36 42 128 16 46 347 Gizzard shad 248 91 54 31 424 Smallmouth bass 16 39 24 3 15 8 62 75 46 288 Tessellated darter 50 98 169 Emerald shiner 46 147 16 31 Rock bass 16 54 8 62 10 38 31 239 Yellow perch 17 16 8 101 168 Pumpkinseed 227 White sucker 54 21 8 16 116 Bluegill ~
70 78 (a) Estimate = Number of fish impinged per month based on daily average rate (fish impinged per day).
NOTE: Dashes ( ) indicate no catches made.
TABLE 3- tinued)
Annual JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total SPECIES (Continued)
American eel 16 28 16 68 Lake trout 16 14 16 64 Freshwater drum 39 48 Lake chub 14 23 41 Largemouth bass 31 31 Channel catfish 15 23 Walleye Brown bullhead Lake herring (Cisco)
Sea lamprey Subtotal 1,893 2,240 165 42,689 47,428 6,761 2,598 217 430 3,085 114 2,170 109,790 OTHER SPECKS Crayfish 14 16 26 23 23 5 23 130 FISH FRAGMENTS Alewife 30 46 Spot tail shiner Tessellated darter 10 Emerald shiner Rainbow smelt Crayfish TOTAL 1,893 2,261 189 42,717 47,453 6,761 2,621 227 460 3,101 130 2,193 110,006
TABLE 3-5 ESTIMATED 'ONTHLY GEMENT (BASED ON FLOW) AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 Annual JAN FEB hfAY JUN JUL AUG SEP NOV DEC Total No. of Samples 16 20 78 Total Sample Volume (MCM) 5.668 3.920 0.051 0.000 0.240 12.296 0.519 29.284 5.859 6.041 9.229 6.019 5.951 5.865 5.761 96.703 Total hfonthly Volume (MCM) 43.870 26.703 0.321 0.801 1.469 26.434 0.798 45.363 43.717 46.916 47.542 45.751 45.851 43.865 45.128 464.529 SPECIES Alcwifc 47,988 46,198 5>977 2,175 26 2,774 105,146 Rainbow sinelt 1,238 1,431 568 696 112 37 494 4,607 Spottail shiner 70 86 74 149 57 213 31 15 251 1,201 Trout-perch 46 27 43 187 119 31 10 196 667 Sculpins 124 116 12 73 64 37 68 22 24 597 White perch 39 12 675 Stonecat 14 34 54 67 186 24 15 15 415 Threcspinc stickleback 55 41 42 127 16 47 351 Gizzard shad 248 89 54 31 422 Smallmouth bass 15 31 28 15 8 62 76 47 285 Tessellated darter 50 97 166 Einerald shiner 143 12 31 248 Rock bass 15 43 62 10 38 31 226 Yellow perch 19 15 102 170 Pumpkinsecd 227 229 (a) Estimate ~ Number of fish pcr million cubic meters (MCM) of'water pumped per month.
NOTE: A e* Collected when at least onc main circulating water pump was operating; B = Collected when no main circulating water pump was operating; service water only.
Dashes
( ) indicate no catches made.
0 TABLE 3 ontinued)
Annual FEB APR MAY JUN IUL AUG SEP OCT NOV Total A B A B A B SPECIES (Conbnucd)
White sucker 54 21 15 113 Bluegill 70 78 American eel 15 27 12 62 Lake trout 15 14 16 62 Freshwater drum 39 48 Lake chub 14 42 Largemouth bass 31 Channel catfish 15 Walleye Brown bullhead Carp Lake hemng (Cisco)
Sea lamprey 2
Subtotal 1,887 2,183 0 0 128 48,937 3 47,399 6,721 2,603 216 434 3,066 113 2,194 115,884 OTHER SPECIES Crayfish 14 12 26 3 23 23 5 24 130 FISH FRAGMENTS Alewife 30 Spottail shiner 2 Tessellated darter 2 10 Emerald shiner Rainbow smelt Crayfish TOTAL 1,887 2,204 0 0 146 48,963 8 47,424 6,721 2,626 464 3,082 129 2,218 116,098
TABLE 3-6a LENGTH DISTRIBUTION OF REPRESENTATIVE IMPORTANT SPECIES IMPINGED AT NINE MILE POINT NUCLEAR STATION UNIT I, 1993 ALEWIFE Interval Length Interval (cm) JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total 4.0 - 5.9 0 0 0 0 0 0 0 1 0 19 0 20 6.0 - 7.9 0 0 0 0 1 0 0 3 0 11 0 0 15 8.0 - 9.9 1 0 0 7 11 0 0 0 0 0 0 0 19 10.0 - 11.9 0 0 0 23 16 1 0 0 0 0 0 0 40 12.0 - 13.9 0 0 0 17 62 33 6 1 0 0 0 0 119 14.0 - 15.9 0 0 0 38 196 44 25 0 0 0 0 0 303 16.0 - 17.9 0 0 0 64 208 14 24 0 0 0 0 0 310 18.0 - 19.9 0 0 0 1 6 0 3 0 0 0 0 0 10 Total Measured 1 0 0 150 500 92 58 5 0 30 0 0 836 Mean Length 9.6 0.0 0.0 14.7 15.3 14.5 15.8 8.0 0.0 5.9 0.0 0.0 14.8 Length (Minimum) 9.6 0.0 0.0 8.2 7.5 11.5 12.0 4.7 0.0 4.7 0.0 0.0 '.7 Length (Maximum) 9.6 0.0 0.0 18.4 18.4 17.6 18.8 13.8 0.0 7.3 0.0 0.0 18.8
TABLE 3-6b LENGTH DISTRIBUTION OF REPRESENTATIVE IMPORTANT SPECIES IMPINGED AT NINE MILE POINT NUCLEAR STATION UNIT I, 1993 RAINBOW SMELT Interval Length Interval (cm) JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total 4.0 - 5.9 12 3 0 1 3 1 0 0 0 1 1 22 6.0 - 7.9 24 16 0 9 37 9 0 0 0 0 0 97 8.0 - 9.9 7 9 0 9 3 1 1 0 0 1 1 41 10.0 - 11.9 4 1 0 4 9 0 0 0 0 0 1 10 29 12.0 - 13.9 17 3 0 39 129 0 0 0 0 0 1 197 14.0 - 15.9 5 4 0 47 139 0 0 0 0 1 1 5 202 16.0 - 17.9 0 2 0 7 11 1 0 0 0 0 24 18.0 - 19.9 0 0 0 0 1 0 0 0 0 0 0 Total Measured 69 38 0 116 332 12 1 0 0 3 5 37 613 Mean Length 9.0 9.1 0.0 13.1 11.6 7.6 8.3 0.0 0.0 10.0 10.8 11.6 11.3 Length (Minimum) 4.6 5.2 0.0 5.5 5.6 5.4 8.3 0.0 0.0 5.9 5.8 6.8 4.6 Length (Maximum) 15.8 16.8 0.0 17.8 18.5 16.8 8.3 0.0 0.0 15.0 14.8 16.6 18.5
TABLE 3-6c LENGTH DISTRIBUTION OF REP ATIVE IMPORTANT SPECIES IMPINGED AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 WEGTE PERCH Interval Length Interval (cm) JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total 4.0 -5.9 0 0 0 0 0 0 0 0 0 0 0 3 ~ 3 6.0 - 7.9 0 0 0 0 0 0 0 0 0 1 1 19 21 8.0 - 9.9 0 0 0 0 0 0 0 0 0 6 15 10.0 - 11.9 0 0 0 0 0 0 0 0 0 4 12.0 - 13.9 0 0 0 0 1 0 0 0 0 2 0 14.0 - 15.9 0 0 0 0 1 0 0 0 0 0 16.0 - 17.9 0 0 0 3 1 0 0 0 0 0 18.0 - 19.9 0 0 0 1 2 0 0 0 0 0 0 20.0 - 21.9 0 0 0 0 1 0 0 0 0 0 0 22.0 - 23.9 0 0 0 0 0 0 0 0 0 0 24.0 - 25.9 0 0 0 1 1 0 0 0 0 0 0 26.0 - 27.9 0 0 0 0 0 1 0 ~ 0 0 0 0 28.0 - 29.9 0 0 0 0 0 0 0 0 0 0 0 30.0 - 31.9 0 0 0 0 0 0 0 0 0 0 32.0 - 33.9 0 0 0 1 0 0 0 0 0 0 0 Total Measured 0 0 0 6 7 1 0 0 0 13 1 32 60 Mean Length 0.0 0.0 0.0 21.3 18.6 27.7 0.0 0.0 0.0 9.6 7.0 7.6 10.5 Length (Minimum) 0.0 0.0 0.0 16.8 13.1 27.7 0.0 0.0 0.0 6.2 7.0 5.7 5.7 Length (Maximum) 0.0 0.0 0.0 32.0 25.9 27.7 0.0 0.0 0.0 12.0 7.0 10.8 32.0
TABLE 3-6d LENGTH DISTRIBUTION OF REP ATIVE IMPORTANT SPECIES IMPINGED AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 YELLOW PERCH Interval Length Interval (cm) JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total 4.0 - 5.9 1 0 0 0 0 0 1 0 1 0 6.0 - 7.9 0 0 0 0 0 0 0 0 0 0 0 8.0 - 9.9 0 0 0 0 1 0 0 0 0 0 0 10.0 - 11.9 0 0 0 0 1 0 0 0 0 0 0 12.0 - 13.9 0 0 0 2 0 0 0 0 0 0 0 14.0 - 15.9 0 0 0 1 0 0 0 0 0 0 0 16.0 - 17.9 0 0 0 0 0 0 1 0 0 0 0 18.0 - 19.9 0 0 0 0 0 0 0 0 0 1 1 20.0 - 21.9 0 0 0 0 0 0 0 0 0 0 0 22.0 - 23.9 0 0 0 0 0 0 0 0 0 0 0 24.0 - 25.9 0 0 0 0 0 0 0 0 0 0 0 26.0 - 27.9 0 0 0 0 0 0 0 . 0 0 0 0 28.0 - 29.9 0 0 0 0 0 0 0 0 0 0 0 30.0 - 31.9 0 0 0 0 1 0 0 0 0 0 0 Total Measured 1 0 0 3 3 0 1 1 0 2 1 13 25 Mean Length 5.4 0.0 0.0 13.2 17.0 0.0 17.4 5.0 0.0 12.2 18.3 17.4 15.0 Length (Minimum) 5.4 0.0 0.0 12.6 9.8 0.0 17.4 5.0 0.0 5.6 18.3 10.4 5.0 Length (Maximum) 5.4 0,0 0.0 14.3 30.0 0.0 17.4 5.0 0.0 18.9 18.3 21.0 30.0
TABLE 3-6e LENGTH DISTRIBUTION OF REP ATIVE IMPORTANT SPECIES IMPINGED AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 SMALLMOUTHBASS Interval Length Interval (cm) JAN FEB MAR MAY JUN AUG SEP OCT NOV DEC Total 4.0 - 5.9 0 0 8 8 6.0 - 7.9 0 0 1 11 8.0 - 9.9 0 0 0 4 10.0 - 11.9 0 0 0 0 12.0 - 13.9 0 0 0 1 14.0 - 15.9 0 0 0 0 16.0 - 17.9 0 0 0 0 18.0 - 19.9 0 0 1 1 20.0 - 21.9 0 0 0 0 22.0 - 23.9 0 0 0 0 24.0 - 25.9 0 1 0 1 26.0 - 27.9 0 0 0 2 28.0 - 29.9 0 0 0 1 30.0 - 31.9 0 0 0 1 32.0 - 33.9 0 0 0 3 34.0 - 35.9 0 0 ~ 0 1 36.0 - 37.9 0 1 0 6 38.0 - 39.9 0 0 0 4 40.0 - 41.9 1 0 2 4 42.0 - 43.9 0 0 0 0 44.0 - 45.9 0 0 0 1 Total Measured 2 0 5 10 1 2 1 12 10 0 0 6 49 Mean Length 25.3 0.0 32.5 36.4 40.1 30.2 36.1 12.5 10.6 0.0 0.0 12.6 21.3 Length (Minimum) 13.4 0.0 27.1 28.7 40.1 24.4 36.1 4.3 6.0 0.0 0.0 6.7 4.3 Length (Maximum) 37.2 0.0 37.5 44.6 40.1 36.1 36.1 41.5 39.5 0.0 0.0 37.3 44.6
TABLE 3-6f LENGTH DISTRIBUTION OF REPRESENTATIVE IMPORTANT SPECIES IMPINGED AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 SALMONIDS - LAKETROUT Interval Length Interval (cm) JAN FEB MAR APR MAY JUN JUL AUG SEP OCT NOV DEC Total 62.0 - 63.9 0 0 0 0 0 0 0 0 0 0 0 1 64.0 - 65.9 0 0 0 0 0 0 1 0 0 0 0 0 66.0 - 69.9 0 0 0 0 0 0 0 0 0 0 0 68.0 - 69.9 0 0 0 0 0 0 0 0 0 0 0 0 70.0 - 71.9 0 1 0 0 1 0 0 0 0 0 0 0 72.0 - 73.9 1 0 0 0 0 1 0 0 0 0 0 74.0 - 75.9 1 0 0 0 0 0 0 0 0 0 0 0 76.0 - 77.9 0 0 0 0 0 0 0 0 0 0 0 0 78.0 - 79.9 0 0 0 0 0 0 0 0 0 0 0 ~
0 80.0 - 81.9 0 0 0 0 0 0 0 0 0 0 0 1 Total Measured 2 1 0 0 1 1 1 0 0 0 0 2 8 Mean Length 73.6 71.6 0.0 0.0 71.0 73.5 64.6 0.0 0.0 0.0 0.0 72.6 71.6 Length (Minimum) 73.1 71.6 0.0 0.0 71.0 73.5 64.6 0.0 0.0 0.0 0.0 63.6 63.6 Length (Maximum) 74.0 71.6 0.0 0.0 71.0 73.5 64.6 0.0 0.0 0.0 0.0 81.5 81.5
TABLE 3-7 TOTAL BIOMASS OF IM ED ORGANISMS COLLECTED AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 Annual APR MAY JUN JUL AUG SEP OCT NOV DEC Total No. of Samples 16 20 78 A B A B A B SPECIES Alewife 479,764 978,481 11,755 4,336 15 1,474,592 Rainbow smelt 511 3,514 5,277 35 18 41 457 10,523 Spottail shiner 75 342 124 80 10 133 1,419 Trout-perch 42 32 191 984 124 17 113 1,509 Sculpins 48 54 126 6 103 16 19 19 408 White perch 3,651 720 288 119 278 5,059 Stonccat 10 61 911 1,868 616 1,325 104 110 69 5,074 Threespine sticklcback 26 48 27 123 Gizzard shad 26,367 11,926 213 1,848 40,354 Smallmouth bass 567 2,318 9,539 1,565 747 1,845 753 567 18,526 Tcsscllatcd darter < 1(0.5) 85 23 < 1(0.3)
Emerald shiner 33 21 70 Rock bass 291 405 1,038 339 470 529 2,889 589 572 295 540 7,957 Yellow perch 312 76 74 838 1,595 Pumpkinsccd 117 177 White sucker 150 2,310 2,147 3,280 3,109 1,148 1,612 13,756 Bluegill 47 13 American <<cl 406 1,760 330 1,211 3,707 NOTE: A ~ Collcctcd when at least one main circulating water pump was operating; B ~ Collcctcd when no main circulating water pump was operating; service water only.
Dashes (--) indicate no catches made. Biomass recorded in grams.
e TABLE 3- ntinued)
Annual FEB APR JUN JUL AUG SEP NOV DEC Total A B A B A B SPECIES (Continued)
Lake trout 6,680 5,160 2,350 2,975 1,961 6,600 25,726 Freshwater drum 493 393 2,890 3,776 Lake chub 58 45 115 Largcmouth bass 51 51 Channel catfish 980 988 Walleye 2,550 1,550 4,100 Brown bullhead 56 56 18 18 Lake herring (Cisco) 1,260 1,260 Sca lamprey 394 394 Subtotal 36,032 20,915 0 0 3,904 505,191 6 995,269 17,259 15,722 7,244 2,685 2,305 434 14,538 1,621,504 OTHER SPECIES Crayfish 28 4 86 -- ~ 22 10 158 FISH FRAGMENTS Alcwifc Spottail shiner < 1(0.5)
Tcsscllatcd darter < 1(0.4)
Emerald shiner < 1(0.5) 0 Rainbow smelt Crayfish < 1(0.5) 0 TOTAL 36,032 20,916 0 0 3,906 505,219 11 995,357 17,259 15,744 7,254 2,686 2,306 435 14,544 1,621,67tfo (a) The sum of thc Annual Total column when added down may not equal the sum of thc Total row when added across due to rounding off.
TABLE 3-8 ESTIMATED(" MONTHLY BIOMAS COLLECTED TAXA (BASED ON FLOW) AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 Annual JAN APR JUN JUL AUG SEP OCT NOV DEC Total No. of Samples 78 Total Sample Volume 5.668 3.920 0.051 0.000 0.240 12.296 0.519 29.284 5.859 6.041 9.229 6.019 5.951 5.865 5.761 96.703 (MCM)
Total Monthly Volume 43.870 26.703 0.321 0.801 1.469 26.434 0.798 45.363 43.717 46.916 47.542 45.751 45.851 43.865 45.128 464.529 (MChI)
A A SPECIES Alewife 39 1,031,399 1,515,737 87,710 33,675 77 1,818 2,670,455 Rainbow smelt 3,955 4,550 7,554 8,174 261 16 139 307 3,580 28,536 Spottail shiner 580 1,717 774 530 85 124 608 62 75 1,042 6,522 Trout-perch 218 411 1,524 132 26 885 4,454 Sculpins 368 24 271 160 119 22 55 1,713 White perch 7,849 1,115 2,149 917 22 2,178 14,230 Stonecat 68 373 1,958 2,&94 4,596 10,290 536 836 541 22,092 Threcspinc sticklcback 31 54 56 74 201 16 63 495 Gizzard shad 204,079 81,240 1,641 14,476 301,436 Smallmouth bass 4,389 14,188 20,507 2,424 5,574 4,854 9,504 5,724 4,442 71,606 Tcsscllatcd dattcr 132 172 10 319 Emerald shiner 62 12 15 31 165 510 Rock bass 2,252 2,759 6,353 729 728 3,947 22,437 3,034 4,348 2,206 4,230 53,023 Yellow perch 501 466 586 553 6,564 9,166 Pumpkinseed 181 470 651 White sucker 918 4,966 3,326 25,473 16,016 8,726 12,420 71,845 (a) Estimate ~ Number of grams per million cubic meters (MCM) of water purnpcd per month.
NOTE: A ~ Collected when at least one main circulating water pump was operating; B ~ Collcctcd when no main circulating water pump was operating; service water only.
Dashes () indicate no catches made.
TABLE 3-8 tinued)
Annual JAN FEB APR hiAY JUN JUL AUG SEP OCT NOV DEC Total A B A B B SPECIES (Continued)
Bluegill 364 466 American eel 3,142 11,989 2,020 9,405 26,556 Lake trout 51,703 35,150 3,640 22,198 IS,230 51,700 179,621 Freshwater drum 3,358 845 22,638 26,841 Lake chub 395 13 353 770 Largemouth bass Channel catfish 7,585 60 7,645 Walleye 5,482 7,985 13,467 Brown bullhead 381 381 Carp 39 39 Lake hemng (Cisco) 2,709 2,709 Sea lamprey 610 610 Subtotal 278,886 142,472 0 23,891 1,086,063 9 1,541,741 128,777 122,104 37,317 20,409 17,760 3,245 113,884 3,516,558 I
OTHER SPECIES Crayfish 7 6 60 6 133 171 52 47 482 FISII FRAGhIENTS Alewife Spot tail shiner Tessellated darter Emerald shiner Rainbow sin<<lt Crayfish TOTAL 278,886 142,482 0 23,903 1,086,123 17 1,541,877 128,777 122,275 37,372 20,417 17,772 3,255 113,931 3,517,087
EA Engineering, Science, and Technology. 1993. 1992 SPDES Annual Biological Monitoring Report. Nine Mile Point Nuclear Station Unit 1.
Lange, R. and P. Smith. 1992. Signs of Change in the Lake Ontario Ecosystem.
The Lake Ontario Committee of the Great Lakes Fishery Commission, September.
Lifton, W.S. and J.F. 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.
O'Gorman, R. 1993. Assessment of Juvenile Fishes in Northeastern Lake Ontario, 1992.
Presented at Great Lakes Fishery Commission, Lake Ontario Committee Meeting, Niagara Falls, New York. 23-24 March.
Scott, W.B. and E.J. Crossman. 1973. Freshwater Fishes of Canada. Fish. Res.
Bd. Canada, Ottawa, Canada. 966 pp.
Appendix A Exceptions to Standard Operating Procedures for Impingement at Nine Mile Point Nuclear Station Unit 1, 1993 (Permit Section IV.B.6)
APPENDIX A EXCEPTIONS TO STANDARD OPERATING PROCEDURES FOR IMPINGEMPlT AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 (PERMIT SECTION IV.B.5) 10 MAR Void Impingement Sample. The impingement sample scheduled for collection over the period 10-11 March 1993 could not be collected as planned. A Clam-Trol chemical treatment of the intake for zebra mussel control was in process during the scheduled sample collection period.
The sample was rescheduled and successfully collected over the period 22-23 March 1993.
(NOTE: Normally, Clam-Trol treatments do not interfere with impingement sampling.
However, this treatment occurred during the refuel outage. During this time, the station was isolated from the lake in a recirculation mode for the treatment period with no flow to or from the lake. Impingement sampling was not permitted during this treatment while the station's intake and discharge were in this configuration.)
Appendix B Station Operating Conditions at Nine Mile Point Nuclear Station Unit 1, 1993 (Permit Sections lV.B.5 and IV.C.9)
TABLE B-1 STATION OPERATING CONDITIONS AT NINE MILE POINT NUCLEAR STATION UNIT 1, 1993 STATION: Nine Mile Point Unit I MONTH: January 1993 No. of No. of Total Volume Mean Temperature (C)
Circulating Service of Water Electrical Date Water Pum s Water Pum s Pum ed (m') Ou ut (MWe) Intake Discharge I 2 I 1,454,711.76 615 0.9 18.8 2 2 I 1,454,711.76 615 1.3 19.2 3 2 I 1,454,711.76 593 3.1 20.0 4 2 I 1,454,711.76 618 2.7 20.3 5 2 I 1,454,711.76 620 2.0 19.8 6 2 I 1,454,711.76 620 2.6 20.1 7 2 I 1,451,986.56 618 2.6 20.1 8 2 -I 1,451,986.56 617 2.4 19.9 9 2 I 1,451,986.56 619 1.3 18.8 10 2 I 1,451,986.56 617 1.4 19.1 11 2 I 1,453,076.64 615 2.4 20.0 12 2 I 1,455,256. 80 617 2.4 20.0 13 2 I 1,449,806.40 618 2.4 19.9 14 2 I 1,449,806.40 606 1.9 19.2 15 2 I 1,449,806.40 598 3.7 20.8 16 2 I I,449,806.40 594 2.9 19.9 17 2 I 1,362,600.00 598 1.7 18.8 18 2 I 1,371,865.68 594 0.7 18.6 19 2 I 1,345,158.72 591 1.1 19.1 20 2 I 1,389,306.96 594 0.6 18.3 21 2 I 1,382,221.44 611 1.8 19.8 22 2 I 1,382,221.44 615 2.0 20.1 23 2 I 1,411,653.60 618 1.3 19.2 24 2 I 1,426,369.68 618 3.2 20.9 25 2 I 1,401,297.84 610 1.1 18.9 26 2 I 1,396,937.52 246 1.3 5.6 27 2 I 1,392,032.16 0 0.9 1.1 28 2 I 1,392,032.16 111 1.2 4.2 29 2 I 1,338,618.24 489 0.5 16.0 30 2 I 1,295,015.04 575 0.4 18.7 31 2 I I,338,618.24 610 0.5 19.3
TABLE B-1 (Continued)
STATION: Nine Mile Point Unit 1 MONTH: February 1993 No. of No. of Total Volume Mean Temperature (C)
Circulating Service of Water Electrical Date Water Pum s Water Pum s Pum ed (m') Ou ut (MWe) Intake Discharge 1 2 1,309,731.12 608 0.2 19.2 2 2 1,309,731.12 610 0.4 19.6 3 2 1,307,550.96 610 0.2 19.2 4 2 1,307,550.96 608 0.4 19.3 5 2 1,304,825.76 607 0.2 19.0 6 2 1,304,825.76 600 0.3 19.1 7 2 1,338,073.20 598 1.0 19.2 8 2 1,396,392.48 597 1.4 19.1 9 2 1,338,073.20 592 0.6 18.8 10 2 1,338,073.20 587 0.5 18.6 11 2 1,336,983.12 593 1.2 19.4 12 2 1,336,983.12 584 0.0 19.2 13 2 1,336,983.12 581 0.4 18.4 14 2 1,293,379.92 579 0.5 18.8 15 2 1,293,379.92 578 0.7 19.0 16 2 1,293,379.92 574 1.2 19.4 17 2 1,293,379.92 570 0.9 19.2 18 2 1,285,204.32 566 0.3 18.8 19 2 1,236,150.72 555 0.2 18.6 20 2/1 1,079,724.24 2 0.1 0.6 21 1/0 208,205.28 0 0.7 5.2 22 0/1 221,286.24 0 1.1 5.2 23 1/0 65,404.80 0 1.1 9.0 24 0 55,594.08 0 0.9 8.4 25 0 48,508.56 0 0.7 6.2 26 0 44,693.28 0 1.7 6.9 27 0/1 227,826.72 0 1.2 10.4 28 1/0 112,278.24 0 2.1 3.9
TABLE B-l (Continued)
Nine Mile Point Unit 1 MONTH: March 1993 STATION'ate No. of No. of Total Volume Mean Temperature (C)
Circulating Service of Water Electrical Water Pum s Water Pum s Pum ed (m') Ou ut (MWe) Intake Discharge 1 0 47,963.52 0 2.2 9.1 2 0 45,783.36 0 2.0 12.1 3 0 50,143.68 0 1.8 10.9 4 0 89,386.56 0 1.1 7.8 5 0 44,693.28 0 1.4 4.9 6 0 44,693.28 0 2.3 7.0 7 0 89,386.56 0 1.4 9.0 8 0 89,386.56 0 1.1 4.7 9 0/1 361,361.52 0 3.6 4.8 10 1 000<> ~
0 12.6 12.8 11 1 0.00<~ 0 15.7 16.9 12 1/0 49,598.64 0 8.6 10.8 13 43,058.16 0 5.2 7.7 14 43,058.16 0 5.7 4.8 15 44,693.28 0 3.1 11.8 16 44,693.28 0 3.2 18.3 17 43,058.16 0 3.3 22.7 18 86,116.32 0 0.7 10.5 19 43,058.16 0 2.9 12.8 20 40,332.96 0 3.1 15.1 21 40,332.96 0 1.5 12.6 22 61,044.48 0 1.0 5.9 23 61,044.48 0 1.2 5.5 24 0/1 268,159.68 0 1.2 44 25 1/0 70,855.20 0 1.2 1.8 26 0 43,058.16 0 3.1 3.9 27 0 43,058.16 0 3.2 8.9 28 0 43,058.16 0 1.4 6.1 29 0 43,058.16 0 2.8 11.3 30 0 43,058.16 0 1.9 7.4 31 0 43,058.16 0 3.0 10.0 (a) 10-11 March: No flow due to "C" gate closure for zebra mussel treatment of circulating and service water systems.
TABLE B-1 (Continued)
STATION: Nine Mile Point Unit 1 MONTH: April 1993 No. of No. of Total Volume Mean Temperature (C)
Circulating Service of Water Electrical Date Water Pum s Water Pum s Pum ed (m') Out ut (MWe) Intake Discharge 1 0 53,413.92 0 3.2 19.7 2 0 80,665.92 0 3.0 7.9 3 0 80,665.92 0 2.3 8.6 4 0 80,665.92 0 3.2 13.0 5 0 48,508.56 0 3.3 15.2 6 0 97,017.12 0 2.1 6.3 7 0 65,404.80 0 2.6 5.7 8 0 65,404.80 0 2.6 7.3 9 0 65,404.80 0 2.6 6.1 10 0 65,404.80 0 3' 7.2 11 0 65,404.80 0 4.6 8.7 12 0/2 251,808.48 0 3.6 7.9 13 2 1,423,099.44 0 3.2 3.3 14 2 1,423,099.44 0 3.6 3.6 15 2 1,451,986.56 4 3.6 6.7 16 2 1,454,166.72 13 4.0 9.5 17 2 1,454,166.72 181 5.3 11.8 18 2 1,454,166.72 230 6.6 14.3 19 2 1,457,436.96 238 6.8 14.8 20 2 1,463,432.40 428 6.0 18.8 21 2 1,463,977.44 590 6.8 23.7 22 2 1,459,617.12 615 6.8 23.9 23 2 1,459,617.12 619 5.6 22.8 24 2 1,459,617.12 619 5.7 22.9 25 2 1,459,617.12 619 6.6 23.8 26 2 1,463,977.44 619 6.3 23.6 27 2 1,466,157.60 619 6.7 23.8 28 2 1,466,157.60 618 5.8 22.9 29 2 1,466,157.60 618 6.7 23.9 30 2 1,466,157.60 619 6.3 23.6
TABLE B-1 (Continued)
STATION: Nine Mile Point Unit 1 MONTH: May 1993 No. of No. of Total Volume Mean Temperature (C)
Circulating Service of Water Electrical Date Water Pum s Water Pum s Pum ed (m') Ou ut (MWe) Intake Discharge 1 2 1,466,157.60 616 7.4 24.6 2 2 1,466,157.60 618 7.2 24.4 3 2 1,466,157.60 618 5.7 23.0 4 2 1,466,157.60 617 7.1 24.2 5 2 1,466,157.60 617 7.3 24.4 6 2 1,467,792.72 616 8.5 25.7 7 2 1,467,792.72 617 7.7 24.9 8 2 1,467,792.72 615 8.1 25.2 9 2 1,467,792.72 616 8.7 25.9 10 2 1,466,157.60 616 8.8 26.0 11 2 1,466,157.60 615 9.7 26.9 12 2 1,466,157.60 615 9.1 26.3 13 2 1,466,157.60 614 9.3 26.6 14 2 1,467,792.72 615 9.1 26.2 15 2 1,467,792.72 611 8.8 25.9 16 2 1,467,792.72 614 9.7 26.8 17 2 1,467,792.72 614 94 26.7 18 2 1,466,157.60 614 9.4 26.6 19 2 1,466,157.60 614 9.2 26.3 20 2 1,458,527.04 613 10.0 27.2 21 2 1,456,891.92 613 9.7 27.0 22 2 1,456,891.92 611 9.9 27.2 23 2 1,456,891.92 613 9.5 26.8 24 2 1,458,527.04 614 9.2 26.6 25 2 1,458,527.04 612 10.6 28.0 26 2 1,458,527.04 613 10.4 27.8 27 2 1,460,707.20 611 11.3 28.7 28 2 1,456,891.92 613 9.7 27.2 29 2 1,456,891.92 611 11.6 28.9 30 2 1,456,891.92 612 10.8 28.3 31 2 1,456,891.92 614 9.0 26.5
TABLE B-1 (Continued)
STATION: Nine Mile Point Unit 1 MONTH: June 1993 No. of No. of Total Volume Mean Temperature (C)
Circulating Service of Water Electrical Date Water Pum s Water Pum s Pum ed (m') Ou ut (MWe) Intake Discharge 1 2 1 1,456,891.92 612 10.7 28.2 2 2 1 1,456,891.92 613 10.2 27.7 3 2 1 1,454,711.76 612 11.0 28.4 4 2 1 1,454,711.76 612 10.6 28.1 5 2 1 1,454,711.76 612 8.6 26.1 6 2 1 1,454,711.76 607 8.7 26.0 7 2 1 1,454,166.72 613 9.6 26.9 8 2 1 1,454,166.72 613 9.8 27.3 9 2 1 1,456,891.92 611 10.4 27.9 10 2 1 1,460,707.20 609 12.2 29.7 11 2 1 1,460,707.20 611 11.1 28.6 12 2 1 1,460,707.20 608 10.8 28.3 13 2 1 1,460,707.20 611 10.7 28.3 14 2 1 1,465,067.52 595 11.8 29.1 15 2 1 1,460,707.20 607 12.6 30.2 16 2 1 1,462,342.32 607 12.4 30.0 17 2 1 1,455,801.84, 608 11.4 29.1 18 2 1 1,458,527.04 609 11.6 29.2 19 2 1 1,419,829.20 601 12.5 30.0 20 2 1 1,419,829.20 608 12.1 29.8 21 2 1/2 1,463,432.40 603 14.1 31.8 22 2 2 1,497,769.92 601 14.8 32.6 23 2 2 1,486,869.12 601 14.8 32.6 24 2 2 1,491,774.48 601 14.5 32.3 25 2 2/1 1,463,977.44 600 14.3 32.2 26 2 1 1,445,991.12 592 15.4 33.2 27 2 1 1,445,991.12 596 16.1 34.2 28 2 1 1,445,991.12 594 16.4 34.4 29 2 1 1,445,991.12. 594 16.6 34.7 30 2 1 1,445,991.12 593 16.7 34.8
TABLE B-1 (Continued)
STATION: Nine Mile Point Unit 1 MONTH: July 1993 No. of No. of Total Volume Mean Temperature (C)
Circulating Service of Water Electrical Date Water Pum s Water Pum s Pum ed (m') Ou ut (MWe) Intake Discharge 1 2 1 1,431,275.04 591 17.1 35.3 2 2 1/2 1,496,679. 84 593 15.5 33.7 3 2/1/2/1/2 2 1,486,869.12 367 16.1 28.1 4 2/1/2 2 1,465,612.56 379 16.6 30.1 5 2 2 1,496,679.84 512 15.6 31.4 6 2 2 1,513,576.08 582 17.7 35.4 7 2 2 1,513,576.08 564 19.2 36.6 8 2 2 1,513,576.08 570 18.3 35.8 9 2 2 1,513,576.08 581 20.3 38.4 10 2 2 1,513,576.08 570 22.2 40.3 11 2 2 1,513,576.08 572 22.6 40.7 12 2 2 1,513,576.08 576 22.2 40.4 13 2 2 1,513,576.08 575 22.3 40.4 14 2 2 1,513,576,08 578 21.9 39.9 15 2 2 1,513,576.08 577 22.3 40.3 16 2 2 1,511,940.96 574 22.4 40.2 17 2 2 1,511,940.96 575 21.8 39.4 18 2 2 1,511,940.96 578 22.1 39.9 19 2 2 1,521,751.68 581 21.4 39.2 20 2 2 1,529,382.24 577 21.9 39.8 21 2 2 1,529,382.24 578 21.9 39.7 22 2 2 1,529,382.24 579 21.7 39.4 23 2 2 1,529,382.24 581 21.5 39.2 24 2 2 1,529,382.24 578 21.4 39.0 25 2 2 1,529,382.24 580 21.7 39.4 26 2 2 1,528,292.16 584 20.5 38.3 27 2 2 1,528,292.16 581 21.2 39.0 28 2 2 1,528,292. 16 578 21.6 39.4 29 2 2 1,528,292.16 571 21.9 39.6 30 2 2 1,528,292.16 564 22.1 39.6 31 2 2 1,528,292.16 574 21.6 39.3
TABLE B-1 (Continued)
STATION: Nine Mile Point Unit 1 MONTH: August 1993 No. of Total Volume Mean Temperature (C)
Circulating No. of Service of Water Electrical Date Water Pum s Water Pum s Pum ed (m') Ou ut(MWe) Intake Discharge 1 2 1,528,292.16 578 21.6 39.4 2 2 1,516,301.28 578 21.4 39.2 3 2 1,528,292.16 576 22.2 40.2 4 2 1,528,292.16 574 22.2 40.2 5 2 1,528,292.16 575 21.9 39.9 6 2 1,528,292.16 575 21.7 39.6 7 2 1,528,292.16 577 21.0 38.9 8 2 1,528,292.16 578 21.3 39.3 9 2 1,528,292.16 576 21.5 39.5 10 2 1,537,012.80 575 21.4 39.5 11 2 1,514,666.16 572 21.8 39.9 12 2 1,514,666.16 571 21.7 39.7 13 2 1,541,918.16 557 22.2 39.9 14 2 1,541,918.16 561 22.8 40.7 15 2 1,541,918.16 562 22.9 40.9 16 2 1,551,183.84 565 22.5 40.6 17 2 1,541,918,16 568 22.1 40.2 18 2 1,544,098.32 569 22.3 40.5 19 2 1,530,472.32 576 20.3 38.5 20 2 1,541,918.16 565 22.2 40.3 21 2 1,541,918.16 586 14.6 32.6 22 2 1,541,918.16 592 14.8 32.8 23 2 1,522,841.76 579 19.4 37.7 24 2 1,522,841.76 577 20.5 38.8 25 2 1,532,652.48 572 21.5 39.8 26 2 1,535,377.68 564 22.3 40.6 27 2 1,541,918.16 555 22.4 40.4 28 2 . 1,541,918.16 541 23.2 40.9 29 2 1,541,918.16 540 23.1 40.7 30 2 1,532,652.48 551 22.9 40.8 31 2 1,541,373. 12 551 22.8 40.7
TABLE B-1 (Continued)
STATION: Nine Mile Point Unit 1 MONTH: September 1993 No. of No. of Total Volume Temperature (C)
Date Circulating Water Pum s Service Water Pum s Pum ed (m'ean of Water Ou Electrical ut (MWe Intake Discharge 1 2 2 1,534,832.64 550 23.4 41.3 2 2 2 1,534,832.64 558 22.7 40.8 3 2 2 1,534,832.64 559 22.8 40.9 4 2 2 1,534,832.64 558 22.7 40.9 5 2 2 1,534,832.64 558 22.8 40.9 6 2 2 1,534,832.64 566 22.4 40.7 7 2 2 1,544,098.32 569 22.2 40.5 8 2 2 1,541,373.12 569 22.2 40.6 9 2 2 1,540,283.04 570 22.0 40.4 10 2 2 1,540,283.04 571 21.7 40.1 11 2 2 1,540,283.04 574 20.7 38.9 12 2 2 1,540,283.04 575 20.9 39.1 13 2 2 1,537,012.80 577 20.6 38.8
'4 2 2 1,544,643.36 577 20.8 39.0 15 2 2 1,544,643.36 575 20.6 38.8 16 2 2 1,538,102.88 578 20.3 38,4 17 2 2 1,532,652.48 579 20.1 38.2 18 2 2 1,532,652.48 578 20.3 38.4 19 2 2 1,532,652.48 581 20.0 38.2 20 2 2 1,531,562.40 583 19.4 37.6 21 2 2 1,519,571.52 585 18.9 37.1 22 2 2 1,516,846.32 585 18.9 37.2 23 2 2 1,513,031.04 587 18.4 36.6 24 2 2 1,516,301.28 586 18.6 36.8 25 2 2 1,509,215.76 583 18.2 36.3 26 2 2 1,509,215.76 589 18.0 36,3 27 2 2 1,509,215.76 589 17.7 35.9 28 2 2/1 1,469,972.88 593 17.0 35.2 29 2 1 1,469,972.88 594 16.7 34.8 30 2 1 1,467,792.72 593 17.2 35.3
TABLE B-1 (Continued)
STATION: Nine Mile Point Unit 1 MONTH: October 1993 No. of No. of Total Volume Mean Temperature (C)
Circulating Service of Water Electrical Date Water Pum s Water Pum s Pum ed (m') Ou ut(MWe) Intake Discharge 1 2 1 1,465,067.52 594 16.4 34.6 2 2 1 1,465,067.52 590 16.5 34.6 3 2 1 1,465,067.52 595 16.2 34.3 4 2 1/2 1,516,301.28 599 14.8 32.7 5 2 2 1,516,301.28 598 15.1 33.0 6 2 2 1,516,301.28 598 14.8 32.7 7 2 2 1,509,215.76 598 14.9 32.9 8 2 2 1,509,215.76 597 15.2 33.2 9 2 2 1,509,215.76 594 15.4 33.4 10 2 2 1,509,215.76 596 15.3 33.3 11 2 2 1,516,301.28 599 14.3 32.3 12 2 2/1 1,501,040.16 600 14.1 32.2 13 2 1 1,469,972.88 601 13.8 31.9 14 2 1 1,465,612.56 601 13.6 31.7 15 2 1 1,463,977.44 603 13.1 31.2 16 2 1 1,463,977.44 605 12.3 30.4 17 2 1 1,463,977.44 604 13.2 31.3 18 2 1 1,467,247.68 606 12.2 30.3 19 2 1 1,467,247.68 606 11.8 29.8 20 2 1 1,467,247.68 607 11.4 29.5 21 2 1 1,463,977.44 609 10.8 28.8 22 2 1 1,475,968.32 610 10.4 28.2 23 2 1 1,467,247.68 606 10.3 28.1 24 2 1 1,467,247.68 610 10.3 28.2 25 2 1 1,467,247.68 610 10.4 28.3 26 2 1 1,467,247.68 611 10.1 27.9 27 2 1 1,465,612.56 610 10.1 28.0 28 2 1 1,463,977.44 612 9.7 27.5 29 2 1 1,461,797.28 610 9.8 27.6 30 2 1 1,461,797.28 606 9.5 27.2 31 2 1 1,461,797.28 612 9.3 27.1
TABLE B-1 (Continued)
STATION: Nine Mile Point Unit 1 MONTH: November 1993 No. of No. of Total Volume Mean Temperature (C)
Circulating Service of Water Electrical Date Water Pum s Water Pum s Pum ed (m') Ou ut (MWe) Intake Discharge 1 2 1,461,797.28 611 9.2 27.1 2 2 1,463,977.44 610 10.0 27.8 3 2 1,471,608.00 610 9.9 27.7 4 2 1,471,608.00 611 9.6 27.3 5 2 1,467,247.68 612 9.1 26.9 6 2 1,467,247.68 611 7.7 25.4 7 2 1,467,247.68 '613 7.7 25.4 8 2 1,462,887.36 614 7.8 25.6 9 2 1,462,887.36 613 8.2 26.1 10 2 1,462,887.36 614 8.2 26.1 11 2 1,462,887.36 614 8.1 25.9 12 2 1,461,797.28 614 7.5 25.4 13 2 1,461,797.28 610 8.4 26.2 14 2 1,461,797.28 614 8.0 25.9 15 2 1,465,612.56 614 8.1 26.1 16 2 1,461,797.28 614 7.8 25.7 17 2 1,461,797.28 614 8.1 26.1 18 2 1,461,797.28 614 8.2 26.1 19 2 1,461,797.28 611 8.1 25.9 20 2 1,461,797.28 609 6.2 23.8 21 2 1,461,797.28 617 6.1 23.9 22 2 1,461,797.28 617 6.6 24.4 23 2 1,461,797.28 616 7.4 25.2 24 2 1,461,797.28 616 6.6 24.4 25 2 1,461,797.28 616 5.7 23.4 26 2 1,461,797.28 616 6.4 24.2 27 2 1,453,076.64 613 6.9 24.6 28 2 1,453,076.64 616 6.7 24.4 29 2 1,453,076.64 618 4.8 22.6 30 2 1,453,076.64 616 6.7 24.4
TABLE B-1 (Continued)
STATION: Nine Mile Point Unit 1 MONTH: December 1993 No. of No. of Total Volume Mean Temperature (C)
Circulating Service of Water Electrical Date Water Pum s Water Pum s Pum ed (m') Ou ut(MWe) Intake Discharge 1 2 1,453,076.64 615 7.1 24.8 2 2 1,457,436.96 616 6.9 24.7 3 2 1,453,076.64 617 5.8 23.6 4 2 1,453,076.64 612 6.8 24.4 5 2 1,453,076.64 616 6.8 24.6 6 2 1,455,256. 80 616 6.3 24.1 7 2 1,453,076.64 617 5.8 23.7 8 2 1,458,527.04 616 6.2 23.9 9 2 1,453,076.64 616 7.0 24.8 10 2 1,453,076.64 616 7.0 24.8 11 2 1,453,076.64 524 5.9 21.3 12 2 1,453,076.64 609 6.3 24.1 13 2 1,453,076.64 616 5.9 23.7 14 2 1,450,896.48 616 6.2 24.0 15 2 1,450,896.48 616 6.5 24.3 16 2 1,450,896.48 617 4.6 22.4 17 2 1,457,436.96 618 4.6 22.4 18 2 1,457,436.96 616 4.8 22.6 19 2 1,457,436.96 618 44 22.3 20 2 1,457,436.96 619 4.5 22.3 21 2 1,457,436.96 617 5.4 23.2 22 2 1,457,436.96 619 3.2 20.9 23 2 1,457,436.96 618 3.8 21.4 24 2 1,457,436.96 618 49 22.6 25 2 1,457,436.96 618 2.6 20.3 26 2 1,457,436.96 621 0.2 18.7 27 2 1,457,436.96 620 1.9 20.1 28 2 1,457,436.96 620 2.3 20.3 29 2 1,459,617.12 618 4.9 22.8 30 2 1,462,342.32 620 0.7 18.9 31 2 1,462,342.32 622 0.8 18.9
Appendix C Scientific and Common Names of all Taxa Collected in 1993
0 APPENDIX C SCIENTIFIC AND COMMON NAMING OF ALL TAXA COLLECTED IN 1993 Scientific Name Common Name Alosa pseudoharengus Alewife Ambloplites rupestris Rock bass Anguilla rostrata American eel Aplodinotus grunniens Freshwater drum Cambaridae Crayfish Family Catostomus commersoni White sucker Coregonus artedii Lake herring (Cisco)
Cottus spp. Sculpins Couesius plumbeus Lake chub Cyprinus carpio Carp Dorosoma cepedianum Gizzard shad Etheostoma olmstedi Tessellated darter Gasterosteus aculeatus Threespine stickleback Ictalurus nebulosus Brown bullhead Ictalurus punctatus Channel catfish Lepomis gibbosus Pumpkin seed Lepomis macrochirus Bluegill Micropterus dolomieui Smallmouth bass Micropterus salmoides Largemouth bass Morone americana White perch Notropis atherinoides Emerald shiner Notropis hudsonius Spottail shiner Noturus flavus Stonecat Osmerus mordax Rainbow smelt Perca flavescens Yellow perch Percopsis omiscomaycus Trout-perch Petromyzon marinus Sea lamprey Salvelinus namaycush Lake trout Stizostedion vitreum Walleye
Appendix D Daily Impingement Collection Totals at Nine Mile Point Nuclear Station Unit 1, 1993
TABLE D-1 DAILYIMPINGE COLLECTION TOTALS AT NINE MILE POINT S ON UNIT 1, 1993 JANUARY FEBRUARY MARCH 6 14 20 27 3 10 18 25 5 19 23 26 SPECIES Alewife Rainbow smelt 19 14 21 106 190 9 11 Spottail shiner 5 3 18 14 2 Trout-perch 3 3 2 2 Sculpins 1 3 9 3 5 10 2 White perch Stonecat Threespine stickleback 1 2 8 Gizzard shad 19 9 9 2 2 Smallmouth bass Tessellated darter Emerald shiner 3 3 21 Rock bass 1 1 Yellow perch Pumpkinseed White sucker Bluegill American eel 1 1 Lake trout 1 1 NOTE: Dashes ( ) indicate no catches made.
TABLE D ntinued)
JANUARY FEBRUARY MARCH 6 14 20 27 3 10 18 25 5 19 23 26 SPECIES (Continued)
Freshwater drum Lake chub 2 Largemouth bass Channel catfish Walleye Brown bullhead Lake herring (Cisco)
Sea lamprey Subtotal 28 19 65 132 258 41 21 0 16 1 0 4 OTHER SPECIES Crayfish 2 2 FISH FRAGMENTS Alewife Spottail shiner Tessellated darter Emerald shiner Rainbow smelt Crayfish TOTAL 28 19 65 132 260 41 22 0 16 3 0 5
TABLE D ntinued)
APRIL 2 3 4 5 6 7 8 13 14 15 20 22 24 26 28 29 SPECIES Alewife Rainbow smelt Spottail shiner 3
1 7
1 1
354 18 2
138 34 8
8,400 40 '0 16 10,716 12 1,291 47 1,423 94 Trout-perch Sculpins 9 1 4 6 2 White perch 12 Stonecat 12 1 Threespine stickleback 12 Gizzard shad Smallmouth bass 6 1 1 Tessellated darter Emerald shiner Rock bass Yellow perch Pumpkinseed White sucker 2 1 Bluegill American eel Lake trout Freshwater drum NOTE: Dashes ( ) indicate no catches made.
TABLE D ntinued)
APRIL 2 3 4 5 6 7 8 13 14 15 20 22 24 26 28 29 SPECIES (Continued)
Lake chub
.Largemouth bass Channel catfish Walleye Brown bullhead Carp Lake herring (Cisco)
Sea lamprey Subtotal 2 0 0 0 0 0 0 35 13 8 385 185 8,496 10,776 1,343 1,523 I'
OTHER SPECIES Crayfish 1 1 5 1 2 FISH FRAGMENTS Alewife Spottail shiner Tessellated darter Emerald shiner Rainbow smelt Crayfish TOTAL 3 0 0 2 0 0 0 40 13 9 387 185 8,496 10,780 1,343 1,523
TABLE D-1 (Continued)
MAY 3 5 6 7 8 11 12 13 14 15 16 19 20 21 22 23 24 25 26 27 SPECIES Alcwifc 3,730 1,653 1,635 824 2,135 6,842 1,594 1,894 3,091 1,076 699 491 376 608 670 626 844 341 207 487 Rainbow smelt 27 44 37 34 31 70 33 30 27 13 11 15 8 15 11 8 3 11 7 14 Spottail shiner 1 1 1 1 2 2 3 3 3 3 2 3 9 Trout-perch 3 1 12 5 7 13 8 4 4 2 2 42 Sculpins 1 2 5 2 3 4 White perch Stonccat 1 3 3 2 1 Thrcespinc sticklcback 3 1 I 3 1 Gizzard shad Smallmouth bass Tessellated darter 1 I 1 4 3 6 4 2 2 Emerald shiner Rock bass YcHow perch Pumpkinseed White sucker Bluegill American ccl Lake trout Freshwater drum
TABLE D-1 (Continued)
MAY 3 5 6 7 8 11 12 13 14 15 16 19 20 21 22 23 24 25 26 27 SPECIES (Continued)
Lake chub Largcmouth bass Channel catfish Walleye Brown bullhead Lake herring (Cisco)
Sca lamprey Subtotal 3,768 1,713 1,683 865 2,174 6,934 1,644 1,939 3,133 1,096 719 521 403 646 706 646 858 363 225 561 P
OTHER SPECIES Crayfish 1 1 1 1 2 1 2 1 2 1 2 FISH FRAGMENTS Alewife Spottail shiner Tcsscllatcd darter Emerald shiner Rainbow smelt Crayfish TOTAL 3,769 1,714 1,683 865 2,174 6,934 1,645 1,939 3,133 1,096 719 522 405 647 708 647 85$ 365 227 563
TABLE D- ntinued)
JUNE JULY AUGUST 3 10 17 27 2 9 19 28 3 11 12 19 25 29 SPECIES Alewife 222 256 306 17 116 100 63 1 1 Rainbow smelt 3 6 6 1 Spottail shiner 6 11 2 1 2 Trout-perch 10 1 2 Sculpins 3 2 1 White perch Stonecat 4 2 3 15 7 2 1 1 Threespine stickleback 9 6 1 1 Gizzard shad Smallmouth bass 2 1 3 9 Tessellated darter 4 8 1 Emerald shiner Rock bass 1 3 2 3 1 1 Yellow perch Pumpkinseed White sucker 1 2 2 2 1 2 1 Bluegill American eel Lake trout
TABLE D- ntinued)
JUNE JULY AUGUST 3 10 17 27 2 9 19 28 3 11 12 19 25 29 SPECIES (Continued)
Freshwater drum Lake chub Largemouth bass Channel catfish Walleye Brown bullhead Lake herring (Cisco)
Sea lamprey Subtotal 262 295 319 25 140 117 74 4 2 4 3 1 6 26 OTHER SPECIES Crayfish 1 2 1 FISH FRAGMENTS Alewife Spottail shiner Tessellated darter Emerald shiner Rainbow smelt Crayfish TOTAL 262 295 319 25 141 119 74 4 2 4 3 2 7 26
TABLE D- ntinued)
SEPTEMBER OCTOBER NOVEMBER DECEMBER Annua 8 16 24 29 7 13 19 27 5 12 18 24 3 13 23 29 Total SPECIES Alewife 355 5 53;592 Rainbow smelt 2 I 2 I I I I 51 11 1,170 Spottail shiner 27 I 3 2 I 30 I 231 Trout-perch 25 -- 199 Sculpins 3 6 I 2 I 2 2 3 -- 139 White perch I 2 10 58 6 106 Stonecat I I 2 I 95 Threespine stickleback 6 82 Gizzard shad I 6 . 4 56 Smallmouth bass 10 5 I 53 Tessellated darter 48 Emerald shiner 4 35 Rock bass I 3 3 34 Yellow perch 12 I 31 Pumpkinseed 29 30 White sucker I I 20 Bluegill 7 10 American eel Lake trout I 9
TABLE D- ntinued)
SEPTEMBER OCTOBER NOVEMBER DECEMBER Annua 8 16 24 29 7 13 19 27 5 12 18 24 3 13 23 29 Total SPECIES (Continued)
Freshwater drum 3 Lake chub Largemouth bass Channel catfish 1 1 Walleye Brown bullhead Lake herring (Cisco)
Sea lamprey Subtotal 2 0 6 49 3 4 363 28 7 1 5 2 7 2 249 22 55,976 OTHER SPECIES Crayfish 1 2 40 FISH FRAGMENTS Alewife Spottail shiner Tessellated darter Emerald shiner Rainbow smelt 1 Crayfish 1 TOTAL 2 0 6 53 3 6 363 28 7 1 5 4 8 2 251 22 56,029