ML20027B572
| ML20027B572 | |
| Person / Time | |
|---|---|
| Site: | Crane  |
| Issue date: | 09/02/1982 |
| From: | Hickey C Office of Nuclear Reactor Regulation |
| To: | Collins M NRC OFFICE OF ADMINISTRATION (ADM) |
| References | |
| NUDOCS 8209210297 | |
| Download: ML20027B572 (1) | |
Text
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SEP 2 1982 Docket flo. 50-320 MEMORAllDUM FOR: Michael Collins Document Management Branch Division of Technical Information and Document Control FROM:
Clarence R. Ilickey, Jr., Senior Fishery Biologist Environmental. Engineering Branch Division of Engineering, liRR
SUBJECT:
THREE MILE ISLAND HUCLEAR STATIO!1 - JULY 1982 IA N0ilTHLY REPORT Attached is the monthly report of aquatic studies for July 1982 at Three Mile Island. This document should be placed in the Public Document Room and made available under FOIA.
Clarence R. Hickey, Jr.
Senior Fishery Biologist Environmental Engineering Branch Division of Engineering
Attachment:
As stated h2 DISTRIBUTION:
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GPU Nuclear Corporation 5-U tuclear
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Middletown, Pennsylvania 17057 717 944-7621 TELEX 84 2386 Writer"s Direct Dial Number August 30, 1982 WER-2139 Mr. Clarence Hickey U.S. Nuclear Regulatory Commission Office P-234 Washington, DC 20555 SUBJECT.:, THREE MILE ISLAND NUCLEAR STATION JULY 1982 MONTHLY PROGRESS REPORT (IA)
Dear Mr. Hickey:
Please find enclosed one copy of IA's July 1982 Monthly Progress Report.
If I can be of further assistance, please contact me at (717) 944-2670.
Sincerely, C)N Thomas R. Teitt Environmental Scientist TRT/slw Enclosure cc:
W. C. Ressler (w/o enclosure)
W. E. Riethle (w/o enclosure)
File:
2249.1.6 h"
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c&i 9 2 Mf ( ? C(l h O GPU Nuclear Corporation is a subsidiary of the Genera' r blic Utilities Corporatten u
r-THP.EE MILE ISLAND AQUATIC STbTY MONTHLY REPORT FOR JULY 1982 by Ichthyological Associ.ttes, Inc.
P.O.' Box 223, Etters, PA 17319 George A. Nardacci, Project Leader For j
GPU Nuclear Corporation Ichthyological Associates, Inc.
Edward C. Raney, Ph.D., President 301 Forest Drive Ithaca, New York 14850 i
l l
Q.o m en Dn fr A-- n s 't uv i;j v
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r-IABLE OF CONTENTS Introduction.....................................................
1 Compliance with Environmental Technical Specifications; C.
Nardacci......................................................
2 Macroinvertebrates ; R. Evans, J. Evans, W. Botts.................
2 Ichthyoplankton; B. Lathrop, R.
Evans............................
2 Trapnet; R. Malick...............................................
3 4
Seine; R. Malick.................................................
5 Impingement of Fish; B. Snyder...
6 Electrofishing; H.
Hagerty.......................................
6 Movements of Fishes; H. Hagerty..................................
6 Creel Surveys; B. Snyder, R.
Malick.............
7 Ambient Water Quality; G.
Nardacci...............................
8 Population Estimates of Fishes; H.
Hagerty.......................
1 L
IABLE OF IABLES Table Page 1
_ Sampling conducted in compliance with the Generation Procedures Manual in July' 1982.............................
9 2
Fishes taken by t'rapnet on 7-9 July.1982.near TMINS........
10 3
Fishes taken by trapnet on 23-25 July 1982 near TMINS......
11 4
Fishes taken by seine on 1 July 1982 near TMINS............
12 5
Number of fishes impinged at the Unit 1 Intake during,a 24-hour impingement survey on 14-15 July 1982..............
13 6
Summary of length, weight, reproductive status, and number of fishes impinged,at the Unit 1 Intake on 14-15 July 1982.......................................................
13 7
Number of fishes.... Unit 1...
26-27 July 1982..........
14 8
Sum =ary.... Unit 1...
26-27 July 1982...................
14 9
Number of fishes.... Unit 2.... 14-15 July 1982..........
15 10 Su= mary.... Unit 2...
14-15 July 1982...................
15 11 Number of fishes.... Unit 2...
26-27 July 1982..........
16
.._w.12 Su==arv.... Unit 2...
26-27 Julv'1982...................
16 13 Fishes captured by the AC electrofisher near TMINS in July 1982..................................................
17 14 Creel survey data from the GR for each survey day in July 1982..................................................
18' 15 Creel survey data from the West Dam for each survey day in July 1982...........................................
.18 16 Creel survey data from the East Dam for each survey day in July 1982...........................................
19 17 Creel survey data from the YHGS for each survey day in July 1982..................................................
19 18 Summary of selected physicochemical parameters taken on 10 and 21 June 1982 near the TMINS.........................
20 1A
E;TRODUCT10; The ecology of York Haven Pond near the Three Mile Island Iuclear Station (n112:3) has been under inves tigation since February 1974.
Studies initiated in April 1974 include analysis of achient water quality, ichthyoplankton (far-field), 16hthyoplankton entraic=ent, sacroinvertebrates, fish p'opulation dynamic.;, i=pingement of fishes, creel survey, and ther=al plu=e =apping.
This report discusses the progress of investigations conducted in July 1982.
1
2 COMPLIANCE WITH ENVIRONMENTAL TECHNICAL SPECIFICATIONS (ETS)
Objective:
To determine' compliance with the nonradiological (acuatic) environmental monitoring programs specified in sections j
3.1.1.a. (4), 3.1.2.a., 4.2, and 4.6.1 of the EIS and to insure. that -
f said programs are performed as' detailed in the Generation Procedures 1
Yanual.
Progress:
Compliance with all programs specified in the ETS and detailed in the Procedures Document was achieved in July (Table 1).
1.
The summer, fish population estimate program initiated on 23 June was
,i concluded on 28 July.
j A program by program summary of the progress for July follows.
.MACROIEVERTEBRATES Objective:
To describe the. diversity and distribution of the benthic macroinvertebrates occurring at the five benthos sampling stations in the vicinity of TMINS.
Progress:
Replicate (4) benth6's-samples were taken on 12 and 26 July (Table 1).
Enumeration, determination of dry weights, and identifi-cation of specimens have been completed through 26 July.
2 ICHTHY 0 PLANKTON I
Objectives:
(1) To determine the species composition, abundance, and distribution of ichthyoplankton in York Haven Pond; and (2) To
' nvestigate ichthyoplankton entrained at TMINS Unit 1 and 2 Intakes.
i Tar-Field i
Progress:
Day / night samples were token on 6, 13, 20 and 27 July (Table 1).
A total of 9,217 larval and young fish was collected (1,744 during the day and 7,473 at night)'.
Most fish (4,824) were taken on 20 July.
Species taken included the gizzard shad, comrpn carp, golden i'
shiner, cemely shiner, spottail shiner, spotfin shiner, cimic shiner, i
blun: nose minnow, quillback, channel _ catfish, rock bass, redbreast
?
3 sunfish, pumpkinseed/ bluegill, s=allcouth bass, white crappie, black crappie, tessellated darter, and banded darter.
July day / night water te=peratures averaged 25.7 C and 26.4 C, respectively.
Entrainment Progress:
Ichthyoplankton surveys were conducted at Units 1 and 2 on 6-7 and 20-21 July (Table 1).
At Unit 1, eight ichthyoplanktors (3 surface, 5 oblique) were taken on 6-7 July.
The banded darter was the most co= mon species.
The 20-21 July sample at Unit 1 yielded 105 specimens (67 surface, 38 oblique).
Fishes most frequently taken were the pumpkinseed/
bluegill, spotfin shiner, and mimic shiner.
At Unit 2, six ichthyoplanktors (4 surf ace, 2 oblique) were taket on 6-7 July.
The spotfin shiner and banded darter were collected.
The 20-21 July collection yielded 22 specimens (11 surface, 11 oblique).
The pumpkinseed/ bluegill and spotfin shiner were most abundant.
A computer program was written tc print running tables for the annual report.
This program was tested and found to be operational.
Data for 1982 were coded and proofed through June.
TRAPNET Objectives:
(1) To determine the distribution and relative abundance f
of fishes in the Three Mile Island area vulnerable to trapnet; (2) To providespecgpensformovementsstudies; (3) To monitor the occurrence of diseased fishes; (4) To provide specimens for radiation analysis; and (5) t To determine reproductive status for fishes throughout the vear.
t Progress:
Sa ples were taken on 7-9 and 19-21 July (Table 1).
One I
hundred sixty-four, fish of 12 species were taken on 7-9 July (Table 2).
Most fish (64) were collected at Station 9B2, greatest bic: ass (6.32 kg) at 1A3, and most species (9) at.lA3 cnd 9B2.
Common fishes included the white crappie (34.1% of the total catch), black crappie (26.2%), and
4 pumpkinseed (18.9%).
One Lecomis hybrid (pumpkinseed X bluegill) was collected at 9B2 on 8-9 July.
Leeches parasitized two channel catfish, one rock bass, one pumpkinseed, and one bluegill.
One white crappie was found dead in the trapnet at lA3.
Three channel catfish, one brown bull-head, and one rock bass were sacrificed for radiation analysis.
The following ripe fishes were observed:
eight male and five female pump-kinseed, two male and one female bluegill, and one male redbreast sunfish.
A total of 210 fish of 11 species was taken on 19-21 July (Table 3).
Most fish (103) were taken at Station 932 while greatest biomass (7.28 kg) occurred at llA2.
Stations 11A2, llA3, and 9B2 each recorded seven species.
The pumpkinseed (46.2% of the total catch), black crappie (21.9%), and white crappie (14.8%) were most numerous.
One channel catfish was tagged.
Anchor worms parasitiaed two pumpkinseed and leeches one pumpkinseed.
Five pumpkinseed and two white crappie were found dead in the trapnets.
Over 63% of the pumpkinseed were ripe; the ratio of males to females was 2.6:1.
Other ripe fishes included one' male common carp and eight male bluegill.
Three brown bullhead, three rock bass, and one channel catfish were sacrificed for radiation analysis.
Dead fishes observed in the study area included 8 channel catfish, 3 smallmouth bass, 2 unidentified suckers, 2 walleye, I common carp, 1 northern hog sucker, I shorthead redhorse, and I redbreast sunfish.
No pattern of parasite infection or dead fishes was observed with respect to the location of IMINS in July.
SEINE Objectives:
(1) To determine the species composition of fish upstream and downstream from the TMINS Discharge vulnerable to seine; (2) To determine the relative condition factor for important species; and (3) To determine the reproductive status for fishes throughout the year.
5 Progress:
Collections were made at the 10 stations on 1 and 19 July (Table 1).
A total of 1,652 fish of 17 species was taken on 1 July (Table 4).
Most fish (471) and greatest biemass (123.a g) were taken at Station 10B5 while most species (11) occurred at 4A2.
The spottail shiner and spotfin shiner were'most abundant and comprised 47.9% and 37.0% of the total catch, respectively.
Slight black spot infestations were observed on 59 spotfin shiner, 11 bluntnose minnow, and 2 fallfish. Anchor worms parasitized three'spotfin shiner and leeches one tessellated darter.
One spotfin shiner exhibited scoliosis and one spotfin shiner had necrosis of the caudal fin.
One male bluntnose minnow was tuberculate. No pattern of parasite infection or anomaly was observed with respect to the location of TMINS.
Collections taken on 19 July are currently being processed; results will be presented in the August progress report.
IMPINGEMENT OF FISH Objectives:
(1) To determine the numbers and species impinged on the river water intake screens; (2) To determine day-night differences in impingement frequency; and (3) To determine the extent of mortality of impinged fish.
Progress:
Impingement surveys were conducted on 14-15 and 26-27 July at the TMINS Unit 1 and 2 Intakes (Table 1).
Unit 1 impinged 5 fish of 3 species weighing 4.9 g (Tables 5 through 8).
All fish were young and dead.
Fish numbers and bicmass were highest during the 26-27 July survey.
The estimated impingement for Unit 1 for July was 78 fish weighing 76.0 g (0.2 lb).
Unit 2 impinged 16 fish of 5 species weighing 79.3 g (Tables 9 through 12).
Most fish were young and dead.
Fish numbers and biomass were highest during the 26-27 July survey.
The estinated impingement for Unit 2 was 248 fish weighing 1,229.2 g (2.7 lb).
6 The total estimated impingement at TMINS during July was 326 fish weighing 1,305.2 g (2.9 lb).
ELECTROFISHING Objectives:
(1) To provide specimens for radiard n analysis and movements studies; and (2) To determine the relative abundance of fishes vulnerable to electrofishing in various parts of York Haven Pond.
Progress:
Sampling was conducted on six nights in July (Table 1).
Twenty-four collections in 12 ones yielded 663 specimens of 18 species (Table 13).
The redbreast sunfish (168 specimens), pumpkinseed (132),
quillback (110), and smallmouth bass (84) were most abundant. A total of 14 fish was tagged for movements studies; 33 fish were sacrificed for radiation analysis.
MOVEMENTS OF FISHES Objective:
To determine if fishes in waters receiving the TMINS effluent mix with fishes from other areas.
Progress:
A total of 205 fish was tagged and 11 previously tagged fish were recaptured in July.
Recaptures included 1 broen-bullhead, I channel catfish, 5 rock bass, 3 smallmouth bass, and 1 largemouth bass.
The brown bullhead moved 3.0 km downstream and over York Haven Dam.
The channel catfish moved 0.5 km downstream.
Two rock bass moved 5.0 km and 11.9 km upstream, one moved 3.0 km downstream and over York Haven Dam, and two were recaptured in the same areas in which they were tagged.
One smallmouth bass moved 5.0 km upstream, one made a 0.3 km complex movement, and one was recaptured in the same area in which it was tagged.
The largemouth bass was recaptured in the same area in which it was tagged.
CREEL SURVEYS Objectives:
(1) To determine the extent and success of sport fishing; and (2) Tc determine information on angler residence and use of catch,
7 Progress:
Creel surveys were conducted in all areas on 6, 11, 16, and 31 July (Table 1).
The 454 anglers interviewed fished 738.81 hours9.375e-4 days <br />0.0225 hours <br />1.339286e-4 weeks <br />3.08205e-5 months <br /> and caught 864 fish (Tables la through 17).
The actual harvest was 163 fish or 18.9% of the total catch.
The mean catch per effort (c/e) was 1.17.
Most anglers (190') fished in the General Reservoir.
The largest total catch (310) was recorded in the General Reservoir; most fish kept (83) and most hours fished (305.33) were recorded at the York Haven Generating Station.
The highest c/e (2.55) was recorded at the West Dam.
Smallmouth bass (440 specimens) was the predominant species caught by anglers.
Other species frequently caught included channel catfish (129), walleye (127), rock bass (74), and unidentified sunfish (53).
Approximately 63% of the anglers interviewed lived in York or Dauphin counties.
Most of the anglers reported that they eat some of their catch.
AMBIENT WATER OUALITY Objective:
To determine concentrations of selected water quality parameters in amlient river areas and the TMINS effluent.
Progress:
Water quality samples were collected on 12 and 26 July at the five river stations (Table 1).
Data are currently being analyzed; results will be presented in the August progress report.
The water quality samples collected in June have now been analyzed; results are presented in Table 18.
On 10 June values for sulfate and total and dissolved zine were highest at Station 1Al (located upstream of the TMINS Discharge); dissolved oxygen was highest at 1A2.
Total dissolved solids were highest at Station 11A1 (TMINS Discharge).
On 21 June values for pH, turbidity, and sulfate were highest at Station 1A1; total dissolved solids were highest at 1A2.
Values for dissolved sine (11A1), total zine (11A2), and dissolved oxygen and
E alkalinity (9B1) were highest at stations located at or below the Discharge.
Except for pH and turbidity, parameters for which State water quality criteria have been established were not exceeded at any station on 10 or 21 June.
Values for pH exceeded the upper limit (9.0) of the State criteria at Stations lAl and 11A1 on 10 June.
Values for turbidity exceeded the State criteria (not more than 30 NTU during the period 30 May through 15 September) at all stations on 10 June.
High turbidity values were attributed to the increase in river f1bw in the week preceeding 10 June.
POPULATION ESTIMATES OF TISHES Objectives:
(1) To determine if differences exist in fish populations between areas receiving the TMINS effluent; and (2) To estimate populations in other areas available for recruitment.
Progress:
Summer population estimate sampling was conducted on 11 nights in July (Table 1).
Sufficient recaptures were taken to compute estimates for four species in Zone 16A2 and for three species in Zone 10A3.
Recaptures were too few in the other two zones to compute estir.ates.
Data from summer population estimate samples will be tabulated and results
[
l presented in the 1982 annual report.
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i Table 5 I
i 11uniber of fishes Impfuged at the Unit I lut ke during a 24-hour-impingement survey on 14-15 July 1982.
~iate l
14 15 15 i
Time 2000 0400 1200 l
l Volumetric Flow Rare 3
(m /s) 0.84 0.84 0.84 j
Number of River Water Pumps:
i fluclear Service 1
1 I
Secondary Service 1
1 1
I Ducay lleat 0
0 0
l lutake Veloc!Ly (cm/s)
-9
-9
-9 4
RJver Flow (m3 a) 393.6 393.6 393.6
/
Atr Temp (C) 28.0 23.5 31.0 i
Uater Temp (C) 28.0 27.0 26.5 Total Couditton-of F1sh Alive Dead Alive Dead Alive Dead Alive Dead
[ressellaLed darter 2
2 L
Total 2
2-
}
Table 6 4
Sununary of length, weight, reproductive status, and number of fishes impinged at the Unit 1 Intake on i
14-15.luly 1982.
I Species For'l? I.ength Range Reproductive Status Total Weight Total Number
(_ _'i inm g rt:ups)
(g)
Tessellated darter 26 'l'i 2 Young 0.5 2
3 Total 0.5 2
I t
Table 7 riumher of f t:, hen linpinned at the Unit 1 Intake during a 24-hour impingement survey on 26-27 July 1982.
Date 26 27 27 Time 2000 0400 1200 3
Volumetric Flou Itat e (m /s) 0.84 0.64 0.84 Number of Iliver Water Pumps:
finclear Seivice 1
1 1
Secondary Service 1
1 1
Decay llent 0
0 0
Intake Velocity (cm/s)
-7
-7
-7 River Flow (ml/n) 393.1 366.7 356.8 Air Temp (C) 30.5 27.0 31.0 Uater Temp (C) 29.0 27.0 28.5 Total Condition of Finh Alive Dead Alive Dead Alive Dead
. Alive Dead Shorthead redhorse 1
1 Channel catfJsh 1
1 Tesuellated darter _ _
1 1
Total 2
1 3
Table 8 Sumnuary of length, weight, reproductive status, and number of fishes impinged at the Unit 1 Intake on 26-21 July 1982.
Species Fork I.ength Range Reproductive Status Total Weight Total Number (5 mm groups)
(g)
Shorthead redborse_
61-65 1 Young 3.8 1
Channel catfisli 31-35 1 Young 0.4 1
Tessellated darter 31-35 1 Young 0.2 1
Total 4.4 3
. = _ _
m.
~
1 4
f Table 9
~
Number of fishes impinned at tiie Unit 2 Intake during a 24-hour impingement survey on 14-15 July 1982.
~11 ate 14 15 15 Time 2000 0400 1200 3
Volumetric Flow Itat e (m /s) 1.58 1.58 1.58 Number of Itiver U. iter Pumps:
Nuclear Service 1
1 1
Secondary fiervice 1
1 1
Intake Velocity (cm/n)
-10
-10
-10 I
l(iver Flow (m /s) 393.6 393.6 393.6
. Air Temp (C) 27.5 24.5 30.0 Water Temp (C) 28.0 26.5 27.5 Total Condition ut FIsli.,
Alive Dead Alive Dead Alive Dead Alive Dead C'
Total NO FISil TAKEN Table 10 Summary of length, weight, reproductive status, and number of fishes impinged at the Unit 2 Intake on 14-15.luly 1982, Species Fo rk I.e:ugth llange lleproductive Status Total Weight Total Number (5 mm groups)
(g)
}
_ __ Total NO FISil TAKEN i
D 4
i a
{
,~. -. -
l Table 11 o
Number of fislies impinged.it tlin Unit 2 Intake during a 24-hour impingement: survey on 26-27 July 1982.
Date 26-27 27 Time 2000 0400 1200 3
Volumetric Flow Itate (m /s) 1.58 1.58 1.58 i
Number of River Water Pumps:
Nuclear Service i
1 1
Seconilary Service 1
1 1
r intake Velocity (cm/s)-
-5
-5
-5 l
River Flou (m /u) 393.1 366.7 356.8 j
Air Temp (C) 31.0 27.5 32.0 j
Uater Temp (C) 29.0 28.5 29.0 Total i
Conditjon of l'i til,
Alive.
Dead Alive Dead Alive Dead
' Alive Dead l
Spottall shiner 1
1 Channel catflah 5
4 2
11 Hargined madtom 1
1 i
Rock' bass 1
1 Tessellated darter 1
1 2
F.
Total 75 4
5 16 i
^ Table 12 Summary of length, weight, reproductive status, and. number of fishes impinged'at the Unit 2' Intake on 26-27 July 1982.
Species Fork 1.cngth Range Reproductive Status Total Weight Total Number l
(5 mm_ groups)
(g)
I' Spottati shiner 41-45 1 Young 0.7 L
l Channel catfish 26-45, 181-18S 10 Young, 1 Juvenile 77.0-11 M.irgined mailtom 31 1 Young 0.5 1
Rock basu I6--20 1 Young 0.I 1
Tessellated darter 36-40 2 Young 1.0 2'
i Total 79.3 16 i
l I
L
1#
Table 13
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