ML20087P553
| ML20087P553 | |
| Person / Time | |
|---|---|
| Site: | Oyster Creek, 05000363, 05000000 |
| Issue date: | 04/02/1984 |
| From: | Fiedler P GENERAL PUBLIC UTILITIES CORP. |
| To: | Crutchfield D Office of Nuclear Reactor Regulation |
| Shared Package | |
| ML20087P554 | List: |
| References | |
| NUDOCS 8404090156 | |
| Download: ML20087P553 (34) | |
Text
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GPU Nuclear Corporation Nuclear
- u?388 Forked River, New Jersey 08731-0388 609 971-4000 Writer's Direct DialNumber:
April 2, 1984 Mr. Dennis M. Crutchfield, Chief Operating Reactor Branch #5 Division of Licensing Docket No. 50-219 U.S. Nuclear Regulatory Commission Washington, DC 20555
Dear Mr. Crutchfield:
Subject:
Oyster Creek Nuclear Generating Station (OCNGS)
Full Term Operating License (FTOL) Conversion Environmental Review Enclosed are the responses to the questions contained in your letter of March 7, 1984. A number of the responses provide projected dates by which GPUN presently anticipates completing certain activities. The dates presented represent only ou" present projection based upon the information available and are not meant to be construed as final commitment dates for completi'ng the various activities. Shelld you or your staff have any additional questions or require any addit.ional information, please do not hesitate to contact me or Mr. Douglas r. Moore of our Environmental Licensing staff at (609) 971-4630.
Would you please advise Mr. Moore of the date selected by your staff to conduct the site visit of the OCN3S so that arrangements may be made to have representatives of our Corporate Environmental Controls Department available to assist with the tour and to answer any questions that may arise.
Very truly yours,
,as K E 1lin Vice President / Director Oyster Creek dis:0440f:0012f
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- l B404090156 040402 PDR ADOCK 05000219 R
PDR GPU Nuclear Corporation is a subsidia 'y of the General Public Utikties Corporation
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- 290.1 QUESTION Have there been studies conducted,'since the~ plant went online, on
' terrestrial ecology or on waterfow1? If yes,' provide copies of the report..
RESPONSE
Yes, a copy of the following report is provided:
Terrestrial Environmental Program, Forked River Nuclear-Station Annual Report, March 1978 - February 1979. 251pp. Terrestrial Environmental. Specialists,ulnc. Phoenix, NY 290.2 QUESTION.
Environmental Report, Appendix C' Table A12-1 lists chemicals used to
' control vegetation. Update this table with list of chemicals presently.used for control of vegetation onsite and in R-0-W.
Also indicate method of application and specify whether application is controlled by! federal regulation.
. RESPONSE
' Table 1 ' lists the chemicals currently in use in the Jersey Central
-Power & Light and GPU Nuclear vegetation management programs for
. Oyster Creek Nuclear Generating Station.
s
.The concentration of the ch'emicals applied are quite low and are
.always applied selectively. The types of chemicals in use, methods of application and concentration used are such that residual
-persistance is relatively short and these chemicals neither bio-accumulate.nor create a hazard to the environment.-
290.3 QUESTION
.If there have been times when icing land fogging from the intake or p
.-discharge canals;have~ caused traffic problems on Route 9 provide the following information: number of times this problem has occurred, p
the average length of. time that fog or. ice was'a problem, the number of~ accidents that occurred while fog or ice was-present on Route 9.-
and any action.taken to mitigate this problem, if it is one.
RESPONSE-
~
GPUN has not' received'nor are we aware'of any complaints of traffic
-problems on U.S. Route-9~as a~ result'of icing and/or fogging from the
) intake or discharge canals.
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11 290.4 ' QUESTION Provide a copy of the following reference:
W. R. Clark, R. Rogers and L. J. Wolgast, The Effects of Salt Drift on Land Dwelling Vertebrates, Mineo, p. 86, Jersey Central Power and Light, 1971.
RL'PONSE -
A copy of the' requested document is attached.
290.5 : QUESTION The FES, page 11-50, item 2, states that a Mrs. Anita Linck claims there have been problems with livestock.end honey bees in the vicinity of Oyster Creek. Have any problems of this type been.
reported to you since publication of the FES in 1974? Is yes,
. provide complete details.
. RESPONSE GPUN has not received nor.are we aware of any complaints of problems of the type reported by Mrs.:Anita Linck since the publication of the FES in 1974.
290.6 QUESTION Refer to attachment of letter. dated March:21, 1983, to D. M.
Crutchfield from P. B. Fiedler. -Item 3e response states that Oyster
_ ' Creek was dredged in 1978-79. When is the next scheduled dredging?
Item 3e further states that Forked River was to be dredged in o
1983-84.. Has this. work been completed? -If'not, give percent completion. -Also include on an aerial photograph or map the location
.of the area where spoil from both the.1978-79 and 1983-84 dredging
-was and/or.is to be deposited, the. total: acres over.which the spoil
- will'be deposited and-detailed plans to revegetate.the areas..-
Provide copies of any environmental reyfew done in conjunction with
'the dredging.
' RESPONSE
. Sounding-data collected by GPU' Nuclear indicate that Oyster Creek
~
will not: require dredging for'8-12 years.
The contract for the Forked River dredging project will be awarded.in
. March'or April.of 1984.. Since our permit prohibits us from dredging between May'1;and November 30, it is-anticipated that'only'a small i portion'of the' dredging can be accomplished during the spring of c1984. The majocity of.the dredging. activity will probably take place sin Decsmber'of 1984~and January of.:1985.
l A map showing the location of ~the spoil disposal site for the:1984-85 i
Forked. River dredging project.is attached (Figure 2-A, & 2-B). The
-same'22 acre site was used for the 1978-79 Oyster Creek-dredging
. project.
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The construction of the dredge spoil disposal basin will require the development of a soil erosion and sediment control plan which must be
~
certified by the Ocean County Soil Conservation District. That plan will include the' details of all proposed nonstructural methods of soil, stabilization such as-revegetation.
Environmental reviews of the dredging project will be performed by the U.S. Army Corps of Engineers (AC0E) and the New Jersey Department of Environmental Protection (NJDEP), the regulatory agencies requiring permits'for the dredging project. The AC0E. permit
' application number is NAPOP-R-830241; the docket number for the NJDEP Waterfront Development Permit / Water Quality Certification is 83-0492.
290.7 QUESTION.(Para 1)
E
_ Refer to same attachment as in question 290.6. Item K1, p. xii.
~
. Mention is made of " material storage areas" that do not need
'revegetation.
Is the material stored on these-areas required for station operation or result from station operation? -If the answer is
.yes for both types of material, will these areas be needed for the duration of.the plant's operational life? Also indicate their location on an aerial photograph or map.
If the answer is no, how
.long will these areas be required for storage and what are the plans for restoration of these areas?
RESPONSE.
Material storage areas (Level D Storage Area) will be needed presumably throughout the station's life for outdoor storage of materials required for station operation (or repair) and also for storage of RCRA material prior to shipping.
-Location is indicated on' attached Figure No. 1.
If taken out of 5
service at a later date; and not otherwise used, it will be seeded with grasses and natural successional development will be encouraged.-
L QUESTION (Para 2) l L
On an eerial-. photograph or map-indicate the location of the 12 acres that "has since been-disturbed and requires revegetation?.Also include.'the. program and the schedule of restoration.
RESPONSE
L o
E The following is a list with photograph reference of areas, which l.
require.revegetation. The area ~ size and date of revegetation is
- provided.
(Refer to Figure.No. 1)
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Size Revegetatton p
- Location (Acres) Program Date
. Sandblaster Area (F2) 0.3 ~
Lime. Fertilize, 1984 seed with grasses and legume.
South of So Pcrking Lot (F9).1.7 Grade, place top 1985 soil (local), lime fertilize, seed as above.
South of Helistop (F10) 0.1 Same as F2 1985 East bank, trestle area (F7) 0.5 Same as F9 1984-5 Emergency Office ~B1dg (F8) 0.8 Aggregate and base soil 1984-5 North of No Parking Lot (R4) 8.6 Regr'ade as.necessary 1983-4 to handle increased
- runoff due to cons-truction, lime, fer-tilize & seed'as F2.
i
- QUESTION.(Para 3)
. Item K1, p. states that updates of-the status of revegetation is provided in three letters to NRC..These. letters discuss specific
-locations where revegetation has or is scheduled to take place..
Indicate on an aerial photograph or map the location of each of these areas. Also indicate the'present status of each of these areas.
~
I
- RESPONSE
.The following areas are those described.in the three referenced letters:
Area Description
- Status-
.1.. (R1) ? Dredge Spoil slope
- Revegetation completed June 15, 1983 north of firepond
!y -
'2.
!(RS)'
Barge ~ unloading Revegetation and slope stabilization cornpleted-m facility- ~ '
December 10, 1982.
3.
(FS,-F6): 10ysterCreek To be revegetated 1984-1985; permits.pending.
i banks'between So Access Rd & Discharge Canal-
[
' - 4..(R2)-
Nest of Energy ~
Revegetation completed.
. Spectrum & North of
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. Sediment Basin'#2' 25.-i(R8)' -Proposed natural.
Revegetatfon completed.
- draft cooling tower-site c
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6 (Fil) Backfill Stockpilo Border near treeline was haybaled in 1982; Stockpile to be used as fill to backfill Forked River excavation site; pile site to be revegetated following removal of pile.
- Alphanumeric designations refer to Figure 1 locations.
. QUESTION (Para 4)
The areas discussed in the above-mentioned letters do not. appear to include all-the denuded areas discussed'in ER' Amendment 2, question E4, fpp. E4-1 to E4-6 and Figure E4-1.
Provide the present status of all denuded areas discussed in question E4 if not already provided in answers to previous questions. Identify each area on an aerial photograph or map.
RESPONSE.
Question E4 Fig E4-1 Pres. Fig 1 Status
-Main Disposal Area Area #9 R7, D3 R7 naturally revegetated; D3 2 attempts failed - site too dry to establish new growth.
Disposal Area #1 Island Area R6, D2 R6 bank revegetated; D2 to be revegetated 1986.
Unnumbered
-Same R5 Revegetated and slopes
~~,
. Disposal Area stabilized.
' West of Rt 9 Oyster Creek 'F1 Revegetated.
Station
'F2, 3 To be revegetated, 1984 F4 To be revegetated, 1986 R3, R3a Revegetated D1 Dirt road and Transmission r-Line R-O-W for Atlantic City Electric Co.
t South Branch of Wilbert Area D4 Private Property - no plans Forked River Canal to revegetate IEast of Rt 9 Pearl DS Same as D4 JC Area D6 Natural revegetation in progress -
Pearl (East Revegetated or developed of County road and bridge)
~ Club area Same as D4 Area.6; Developed and/or naturally revegetated i
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29141
~ QUESTION s
H la) ' Provide a' ccuparison of all cooling system design specifications
~
6:
.(relative to terrestrial and aquatic resources and water quality
~
impacts) as;they now exist with those that were:
1)-. evaluated in the 1974 FES; and E) analyzed in the 316(a) and (b)-demonstrations 2
submitted for OCICS.
' RESPONSE' The cooling system design specifications that. relate to terrestrial and aquatic environmental inpacts,.as analyzed in the 1978 316(a) and
-(b). demonstrations, were identical to those evaluated in the 1974 FES witn the exception'of the rerouting of the screen-wash flume, organisms and debris washed off the traveling screens were originally
-passed into the condenser discharge.via the screen-wash flume. In order to-reduce the stress associated with inpingement followed by-
~
'tenperature shock, the flume was rerouted so that impinged organisms would be passed.into the ambient tenperature dilution pump disenarge flow.. This modification was coupleted during the sunmer of 1977.
Since the submission of the 316(a)Jand (b) demonstrations in 1978, all six traveling screens have been replaced with Ristroph type' screens. -During the present outage,.the screen-wash punp associated
' piping are being replaced and a new fish handling system is being installed. Tne details of these modifications are described in the response to questions 291.1.(b).
291.1-
' QUESTION
- (b) ~ Provide, also, the design (diagrammatic) and operational characteristics of the new intake traveling screen-fish handling system.
' RESPONSE i;
E Traveling Water Screens F
Tne'six (6) loops-of traveling water screens serve to screen out-debris and marine life. 'This function is performed by a' loop'of-
. screen panels propelled over-a pair of head sprockets. Tne loop is.
O xanchored by foot sprockets which rotate' freely'on the fixed:
s
~ -
footshaft.' Tne head sprockets are keyed-in pairs to'the head shaft L
and driven by an: outboard driven sprocket..A conceptual sketch of a; travelingiscreen is presented in Figure 3..
.The. screen panels ~are end mounted between'two strands of-carrier a
Lchain. The fit between adjacent panels is sufficient to provide a -
c
? seal. -In the boot, guiding and edge ~l sealing are acconplished Dy the
- fit;between thefend plates of the screen panels and the side _ face of f
the boot'. track bars.- The bottom edge of each screen panel is fitted J
Iwith~a' fish. bucket capable of holding.3-4' inches of water.'
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Each trr.veling watsr screen is powered by a 460 volt, 1 horsepower
, p*
. motor. Each screen is centrolled by a 4-position
[,.
' FAST-S wl4-OFF-REVERSE control switch.
A cathodic protection system is_ installed on each traveling screen to s
increase corrosion protection.
We=High. Pressure and Low Pressure Screenwash systems are comprised e
l'.
of two independent pump and piping systems designed to automatically
~
remove debris-and marine-organisms from the traveling water screens l
as they are rotated from their submerged positions, Low Pressure Screenwash System s
The Inw Pressure Screenwash system has two (2) 100% capacity pumps of the vertical wet pit turbine type powered by 460 volt, 40 horsepower 1 motors. : Wese punps draw suction from the intake structure downstream of the traveling water screens and discharge to a ccannon
-header. The main' discharge flow passes througn a duplex strainer ibefore branching out to the individual. screen-spray headers at each t
- screen. The.in-line-strainer prevents any debris from entering the
. spray headers and plugging the nozzles. Pressure indication at the L
pump discharge-and screen spray headers ~and_ differential pressure-indication.at the strainer are provided. 'This is to ensure that N
p spray pressure is maintained, the pumps are running at rated capacity and to indicate if the strainer is plugged and requires cleaning.
d iAt each of the six-(6) traveling water screens there are two (2).
n spray headers, one internal header and one external header. The
- M
-external spray which operates at a lower pressureL(10-15'psig), and flow rate (25-35 gpm), provides a' moist environment for the marine organisms at the start of the reflex of the screens and aids'in
~
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beginning.the flow mecnanics of' sliding off the mesh.- The internal header--which operates at a higher pressure-(20-30 psig) and flow rate
-(141-185 gpm) provides the. continuing hydromechanic action of
. floatation'and flowing of the' marine. organisms and" easily loosened debris. '%ese marine 1 organisms are' flushed into the fish trougn i' ~
which will return them to the environment. A flap seal' prevents the organisms from bypassing the fish trough..
High Pressure:Screenwash System l' Die.High Pressure -Screenwash system has two (2).100% capacity pumps
~~
of the_ vertical wet pit turbine _ type' powered by 460 volt 150 horsepower motors.. These punps draw suction from the intake
- atructure downstream of the traveling water screens and discharge to
- a' coranon header..' Wel main discharge flow passes through a duplex :
3.
' strainer'before' branching out_to the= Individual screen spray headers at each! screen. The in-line-strainer prevents any debris from-entering the spray-headers'and plugging the nozzels. Pressure
- indication at the pump l discharge and' differential pressure indication
'at_the strainer are provided. This issto ensure that the pumps are runningTat' rated capacity and to indicate if.the strainer is plugged'
_'and requires cleaning.'.
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.At each of the six (6) trtysling watar screens, ths High Prersure Screenwash Header is locEted at a lower elsvation than the low
- pressure spray. As the screen descends past the fish trough, the dense,ilodged debris is loosened by the high pressure spray (70-90 peig) and is cascaded into the debris trough. A-flap seal ensures the debris cannot bypass the trough.
p Fish Trough and Fish Sampling Pool
- The fish trough and fish sampling pool consists of a new trough
~
-.arrangemeet.and a new fish sampling pool with building enclosure and accessories.
The new trough consists of a fish trough and a debris trough which
~~
y converge with the: fish and' debris trough from the traveling water-2 screens. The new fish and-debris troughs join into a common trough-which returns to the existing screen wash. discharge trench. A sluice gate 'in the new common trough ' allows the diversion of the screen wash 1
discharge to the new fish sanpling pool forl sampling of marine.
1 organisms.
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.The fish sampling pool, located on the northeast corner of the intake structure,'is a concrete basin equipped'with an overflow and drain.
It is enclosed by pre-fabricated metal building provided with neating'
-and lighting.~ The pool is divided by a manually movable screen.-
i There is.a metal' walkway spanning the pool with 1 adder to the pool 1
floor. Conceptual' sketches of.the' fish trough and sampling pool are
, presented in Figures ~4-A through 4-J.
All fish trough and fish sanpling pool-surfaces are smooth to avoid abrasion.--The fish troughs are constructed with glass fiber reinforced polyester material. A design objective was to minimize
.the projection into the. flow stream which might'cause eddies.or
- inpact; surfaces. The maximum water velocity.with the troughs full is
.10 feet per second. Tne fish-sanpling pool is isolated from the
~ '~
normal discharge flow.
System Operatilonal 'Sunnary The. traveling water screens are located at the inlet of the intake structure and serve tozprevent debris and marine life from' entering the circulating water and service water systems' water' supply.
- Should~the traveling screens become clogged with debris or organisms-
.J
-_to the extent that flow across the screens is in-iM, a high idifferential~ pressure signal. activates the Hign Pressure and Low 4
~
' Pressure Screenwash systems. LWhen the~ discharge ' pressure of the high pressure screenwash' header. reaches 85 psig, the traveling water
! screens ~ automatically begin rotating forward atLtheir slow speed.of E
r2.5 feet per minute (FPM). -Should the' pressure differential across' r
ithe, screens ~ continue-to rise,.the screens'can"be manually switched to
. fast' forward,~10 FPMr The screens also can be rotated in reverse for.
3
-maintenance purposes.'
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6 /
iThe traveling water screens.can also operate on a pre-set cycle
~'
ttimer; LOn a. signal from the timer, the High Pressure and Inw
~
I'
' Pressure Screenwash systems activate.and the' screens operate as
' idescribed'above.
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v Shutdown of'the traveling water screens and the screenwash systems occurs on' low differential. pressure across the center of the j
traveling water screens;-electrical. failure of both high pressure '
?-
screenwash pumps; or if the cycle timer coupletes the preset cycle.
Since each. case described above results in the shutdown of the high pressure.screenwash pumps, the subsequent pressure-decay in the high pressure spray header trips the traveling water screens.
~.Undernormal[operatingconditions,asthescreenflexesacrosstne head sprocket, the external-low pressure spray, which is at
. approximately 10-15 psig,-moistens and loosens the marine life and
-loosely held debris.. The marine life and loose deoris is washed into the' fish trough by the internal low pressure spray headers operating
.at'about 20-30 psig.. A flap seal-prevents bypassing the fisa.-
c trough. The screen rotates past the fish ~trougn and is washed by the high pressure spray at about 70-90 psig which will remove any densely H
ilodged debris. The washdown cascades into a debris trough which also has.a flap seal to ensure all materials are carried off in the. trough.
' The fish a'nd debris troughs merge to form a single discharge trough to carry away both the fish and the debris.~ This flow can be diverted to the new fish. sampling pool by use of a manually operated 4
~
gate..-The collected discharge sample is then examined to determine the species-composition, abundance and survival rates of the fin and
- shellfish impinged on the traveling water screens.
291.2'
. QUESTION
.(a) Provide a b'ibliographic~1isting of all' journal and professional conference proceedings, publications and' abstracts (by licensee
~_
and. licensee's consultants) that have resulted from aquatic
~
studies and monitoring of the OCNGS site vicinity.
RESPONSE
-'See Attached' Table 2' l291.2
. QUESTION
' (b) - Provide a bibliographic listing of all technical papers that
- have been prepared'by state and federal agencies and private
~
. organizations on the aquatic; resources associated with the OctGS site vicinity..
RESPONSE
See' Attached Table 3'
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TABLE 1 VEGETATION MANAGEMENT PROGRAM CHEHICALS APPROVED FOR USE AT OYSTER CREEK NUCLEAR GENERATING STATION Name Form Application Method Substation /R-0-W Use Ammate X-NI Water-soluble Crystal Hydraulic and/or low pressure backpack Amizol, Amitrol T.
Wettable. Powder Hydraulic an'd/or low pressure backpack Roundup Liquid Hydraulic and/or low pressure backpack
- Tordon 101,.Amdon 101 Liquid Hydraulic and/or low pressure backpack
- Tordon 10K-Pellets Manual-Spot Treatment Krenite Liquid Hydraulic and/or low pressure backpack Banvel-520 Liquid Hydraulic'and/or low pressure backpack Garlon 3A Liquid
-Hydraulic and/or low pressure backpack
~0ust Liquid Hydraulic and/or 10W Pressure backpack Karmex Wettable Powder Hydraulic and/or low pressure backpack
- Tordon 101--
Liquid Hydraulic and/or low pressure backpack 10ust
-Dispersible Granule Hydraulic and/or low pressure-backpack Amitrol;T Liquid Hydraulic and/or low pressure backpack
- Roundup.
. Liquid Hydraulic-and/or' low pressure backpack.
- NOTES:
All Chemicals'are subject to the N. J. Pesticide Control Act
- Restricted-Use Pesticides No R-0-W'use since 1978 east of Garden State Parkway; none planned
~forLfuture.
==,
A t
,' TABLE 2
==
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BIBLIOGRAPHIC LIS'1ING OF ALL JOURNAL AND PROFESSIONAL CONFERE' ICE PROCEEDINGS, PU3L12ATIONS, AND ABSTRACTS BY LI,CENSEE AND LICENSEE'S CONSULT \\NTS Ih Browne, M. E. 1979. Prellsinohengineeringandenvironmehtalevaluationof
. tine-mesh profile wire as powerplant intake screenin's. Passive Intake
'3 55
' SJrcen Workshop, Johnson Division VOP Inc., New Brighton, Minnesota, p..
11-38.
$=
'Ch i raadia, ' F.. A., M. J. Kennish, and V. L. Ohori. 1984. Physical Description
==
\\ of Barnegat Bay, in Kennish, M. J. and R. A. Lutz, eds., Ecology of
' 'Barnegat Bay, New Jersey. Springer-Verlag, New York, 1-28.
==
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Cunliffe, J. E. and M. J. Kennish.1974. Shell growth patterns in the is hard-shelled ~ clam. Underweter Naturalist, 8:20-24.
E_
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Danila, D. J. and M. J. Kennish. 'i?81. A tagging study of the winter flounder jg (Pseudopleuronectes americyr.us) in Barnegat Bay, New Jersey. Proc. Oceans 81, p. 759-764.
e-nn Eg Hib.lman.
R. E. 1978..The occurrence of Minchinia cp. (Haplosporida,
-r
,haplosporidiidaet in species of the molluscan borer, Teredo, from h
IBarnegat Bay, N'ew Jersey'. J. Invert. Path., 31i263-266.
c' RE Hillaan, St. E.1979.OccurrencedhMinchiniasp. in species of the molluscan
\\
[i bor'er, Teredo. Mar FJsh. Rkv., 14:21-24.
4 L_
n
(
[-
- Hillman, R.'E. 1979 Encystment of the ciliate Boveriet Yeredinidi in the tissues of the molluscan woodborer Bankia gouldi in Barnegat Bay, New Jercey.
J. Invert. Path., 34 :78-83.
'y Hillman, R.ti. 1980. Life cycle stages of Minchinia sp'..in Teredo navalis.
gg j$
Amer. '2ool., 20 (4) :961 ( Atatr.).
E
~
.n i
EI Hillman, R.
E., N. J. Maciolek, J.'~I. Lahey, anb C. I.\\$slmore. 1982.' tffects
=
of a haplosporidian parasite, haplosporidium sp., on species of the molluscan woodborer Terodo in Barnegat Edy, New Jers'c'. J. Invert. Path.,
y 40:307-319.
m Hillman, R. J. and M. J. Kennish. 1984. Commercial and sport fisheries, in T; Kennisi, M. J. and R. A. Lutz, eds', Ecology of Barnegat Bay, New Jersey., Springer-Verlag, New York,' 281'-201.
~
Kennish, M. J.J2974. The effects of thyrmal addition on the microstructural growth of Mercenaria mercenaria'.'Ceologic01'd(fclety of America (Northeastern Sectional Meeting), abstracts w$th progroms, 5:43.
~
s e
+
~ y Kennish, Ma J.
1975. Growth increment analysis of Mercenaria 'mercenaria from artificially-heated coSstal marine waters a practical monitoring method..
(XII Annual Chronobiology Conference), abst'racts with programs,12:38.
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(g TABLE 2 continued p
Kennish,'M. J.'1976. Monitoring thermal discharges: a natural method.
Underwater Naturalist, 9:8-11.
~
Kennish, M.- J.1977. Growth increment analysis of Mercenaria mercenaria from
. artificially-heated coastal marine waters. Proceedings of the XII
. International' Chronobiology Conference (Washington, D. C.), p. 663-669.
Kennish, M. J. 1977. Effects of thermal discharges on mortality of Mercenaria mercenaria in Barnegat Bay, New Jersey. Paleontological Society (National
, ' Meeting), abstracts with programs, Journal of. Paleontology, 51 (Suppl. to
' No. 2) p. 17.
- Kennish, M. J.1978. Effects of thermal discharges on mortality of Mercenaria
-mercenaria in Barnegat Bay, New Jersey.-Environmental Geology, 2:223-254.
"Kennish, M. J. -1980. Shell microgrowth analysis: Mercenaria mercenaria as a typa example for research in population dynamics, in Rhoads, D. C. and R.
A..Lutz, eds., Skeletal Growth of Aquatic Organisms, Plenum Press, New York, p. 255-294.
.Kennish, M. J. 1982. Trophic relationships.in Barnegat Bay, New Jersey.
Atlantic Estuarine Research Society Meeting (Baltimore, Maryland),
abstracts ~ with ; programs.-
Kennish,.M.'J. 1984. Introduction, in,Kennish, M. J. and R.,A.
Lutz, eds.,
n i
Ecology of Barnegat Bay, New Jersey. Springer-Verlag, New York.
1Kennish, M. J. 198f. Summary.and Conclusions, in,Kennish, M. J. and R. A.
Lutz, eds., Ecology of Barnegat Bay, New Jersey.~ Springer-Verlag, New York, 339-353.
.Kennish,-M. J. and R. K. Olsson. 1975. Effects of thermal discharges on the microstructural growth of Mercenaria mercenaris. Environmental' Geology, 1:41-64.'
Kennion, M. J. and R. E..Loveland. 1977. Mathematical modeling of growth in the northern. quahog, Mercenaria mercenaria. Geological Society of America'
.(Northeastern Sectional Meeting),' abstracts with programs, 9:282.
Kennish,iM. J;iand. R. E.- Loveland.1980. - Growth models of the northern quahog,
' Mercenaria mercenaria (Linne). Proc. Natl. Shellfish.. Assoc'., 70:230-239.
-Kennish, M. J.~and R. J. Hillman. 1983. Commercial fisheries of Barnegat Bay,'
New Jersey: ' ;results' of a thirty-year, study (1950-1980). Estuaries, 6, 288.c JKennish,'M..J. and R.~E..Loveland. 1984. Trophic Relationships, in.
x
-Kennish,;M.-J. and'R.oh. Lutz, eds., Ecology:of Barnegat Bay, New
-Jersey.1. Springer-Verlag,'New York,~ 302-317.
+ ' '
~
4 lc-3a w
1 j
,[
TABLE 2 continued t
' Kennish,. M. J. and R. A. Lutz (editors).1984. Ecology of Barnegat Bay, New Jersey. Springer-Verlag, New York,:396,pp.
Kennish,* M. J., D. J.'Danila, R. J.-Hillman, and M. B. Roche. 1980. Assessment
~ of the bl'ue crab, Callinectes sapidus Rathbun, in Barnegat Bay, New QJersey. Atlantic Estuarine.Research Society Meeting ' (Annapolis,
" Maryland), abstracts with programs.
Kennish, M. J., - R. ~ A.' Lutz, and D. ' C. Rhoads.1980. Preparation of acetate O'f, peels'and fractured sections for observation of growth patterns within H'
the bivalve shell,Ljn Rhoads, D. C. and R. A. Lutz, eds., Skeletal Growth j of Aquatic Organisms, Plenum Press, New York, p.. 597-601.
1 9
Kennidh, M. J.,'R."J.3 Hillman, and D.;J..Danila. 1982. Assessment of the
' blue crab, callinectes sapidus.Rathbun, in Barnegat Bay, New Jersey.
1
~
' Bull. N.J.' Acad. Sci.', 27:59-71.
1 Kennish, M.'J.,iM. B. Roche,:and T.'R. Tatham. 1984. Anthropogenic Effects on Aquatic Communities, h Kennish, M. J. and.R. A. Lutz, eds., Ecology of Barnegat Bay, New Jersey. Springer-Verlag, New York, 318-338.
Kennish,. M.
J., J. J. Vouglitois, D. 'J.
Danila,- and R. A. Lutz.1984.
Shellfishi Jn,Kennish, M. J. and R.' A. Lutz, eds., Ecology of Barnegat Bay,-. Hew. Jersey. Springer-Verlag,'New York, 171-200.
- Loveland, R.' E. an J.J.Vouglitois.'$984.Benthicfauna,j_nKennish,M.J.
n and _R. A, Lutzb eds., Ecology of z Barnegat Bay, New Jersey.
- Springer-Verlag, New York,-135-170.
I
- Loveland, R.
E., J. F. Brauner, J. E. Taylor and M. J. Kennish. 1984.
Macroflora, in,Kennish,-M. J. and R. A. Luts, eds., Ecology of Barnegat Bay, New Jersey. Springer-Verlag, New York, 78-94.
Richards, B.1R., M. J.'Kennish, Land M. B..Roche. 1979. The composition, distribution, and abundance of shipworms ~in Barnegat Bay, New Jersey.
J American: Society of Limnology'and Oceanography (National Meeting),
. abstracts with programs.
Richards,'B.
R.', R. E.'Hillman,-and N. J. Maciolek. 1984.. Shipworms,,i_n
~Kennish,-M. J.'and R. A. Lutz,'eds., Ecology of Barnegat Bay, New Jersey.
-/
Springer-Verlag, New York,.201-225.
Sandine,EP.' H.r1984.;sooplankton, in Kenn'ish, M..J. and R. A.'Lutz, eds.,
1 Ecology;of-Barnegat Bay, New Jersey."' Springer-Verlag, New York, 95-1J4.
g Tatham, T.iR., D.<L. Thomas,=and'G. J. Miller. 1978.-Survival of fishes'and.
Inacroinvertebrates, impinged at; Oyster Creek Generating Station, jn, 1 Jensen, L.~'D., Led.,' Fourth National; Workshop on~Entrainment.and
^
? Impingement, EA Communications,~ Melville4 New York, 235-243.
gg s
~
g
,s
-3_.
'Ai,*
4.g m
4
'I',
% n 2
ia
~
TABLE 2 continued Tatham, T.
R., D. L. Thomas, and D. J. Danila. 1984. Fishes of Barnegat Bay, in Kennish, M. J. and R. A. Lutz, eds., Ecology of Barnegat Bay, New Jersey. Springer-Verlag, New York, 241-280.
Thomas, D. L. and G. J. Miller. 1976. Impingement studies at the Oyster Creek Generating Station, Forked River, New Jersey, from September to December 1975, in Jensen, L.
D.,
ed., Third National Workshop on Entrainment and Impingement, Ecological Analysts, Inc., Melville, New York, 317-341.
vcuglitois, J. J. 1976. The application of SAS to the analysis of five years of benthic invertebrate data collected in the vicinity of the Oyster
' Creek Nuclear Generating Station. Data Management Workshop, Society of f
Power Industry Biologists, 1976.
Vouglitois,'J. J. 1983. Life history and environmental distrubance-responses of temperate estuarine fishes during a five year period, 1976-1980.
Northeast Fish and Wildlife Conference, abstracts with programs.
Vouglitois, J. J. and M. J. Kennish. 1980. Setting of Mercenaria mercenaria (Linne) relative to environmental factors and the occurrence of adults in Barnegat Bay, New Jersey. Northeast. Fish and Wildlife Conference, abstracts with programs.
Vouglitois, J. J. and R. E. Loveland. 1973. Growth of oysters in the thermal outfall of a nuclear power plant. Bulletin of the New Jersey Academy of Science 18:18.
TABLE 3 BIBLIOGRAPHIC LISTING OF ALL TECHNICAL PAPERS THAT HAVE BEEN PREPARED BY STATE
'AND FEDERAL AGENCIES AND PRIVATE ORGANIZATIONS ON THE AQUATIC RESOURCES
-ASSOCIATED WITH THE OYSTER CREEK NUCLEAR GENERATING STATION SITE VICINITY Asarovitz, T., W. Norse, and M. Silverman. 1971. Wind and tide effects on a thermal plume:in Barnegat Bay, New Jersey. Unpublished manuscript prepared for National Marine Fisheries Service, Highlands,'New Jersey.
'Blanchard, R. L.
1980. Present practices and future requirements for monitoring the-aquatic environment at nuclear facilities, in Effluent and Environmental Radiation Surveillance, ASTM STP 698, J. J. Kelly, Ed.,
American Society for Testing and Materials, 139-149.
L-
- Blanchard, R.'L., W. L. Brinck, H. E. Kolde, H. L. Krieger, D. M. Montgoa.ery, S. Gold, A. Martin, and B. Kahn.
1976.<' Radiological surveillance studies at the Oyster Creek BWR Nuclear Generating Station. Rept.
EPA-520/5-76-003 (PB-257, 952/2GA), Environmental Protection Agency, NTIS, Cincinnati, Ohio.
Blanchard,-R.' L. an'd B.'Kahn.
1979. Abundance and distribution of radionuclides discharged from a BWR nuclear power station into a marina bay.. Nuclear Safety, 20:190-205.
Campbell, R.
1965. Effect of effluent from an atomic power plant on the adjacent portion of Barnegat Bay, New Jersey. Special interim report to the U.S. Department of HEd, Public Health Service, Bureau of State Services', Division of Environmental Engineering and Food Protection, Shellfish Sanitation Branch,! Northeast Research Center, Narragansett,
,~
1 Campbell,'R.
1966. Effect of effluent from an atomic power plant on the-adjacent. portion of Barnegat Bay, New Jersey..Special interim report to the-U.S.-Department of HEW,,Public Health Service, Bureau of State services,. Division of Environmental. Engineering and Food Protection, Shellfish Sanitation Branch, Northeast Research Center, Narragansett, Rhode Island.
Campbell,1R. '1969.
Effect 'of ef fluent from an' atomic power plant on the adjacent portion of Barnegat Bay,'New' Jersey. Special interim; report to
.the U.S.l Department of, HEW,.Public, Health Service, Bureau of State-Services, Division'of Environmental Engineering and Food Protection, Shellfish Sanitation Branch, Northeast'Research Center,.Narragansett,
,Rhode Island.-
. Carpenter,'J. H.
1963. Concentration-distribution for material discharged into Barnegat Bay.. Pritchard-Carpenter, Consultants and The Johns Hopkins
' Univ.,;Unpub. Tech.-Rept.,-13 pp.
~
. Evans,LC.'A.
1977. -The possible effects of thermal' pollution on benthic-
~ lgae'in Oyster Creek,'Barnegat Bay, New Jersey. Rutgers Univ., Unpub.
D' a
M.S. Thesis,.40 pp.
2,.
L-l
' - i
- e,-
- 7. -
TABLE 3 continu:d
,Hein, M.'K.
1977. Effects of thermal discharges on.the structure of periphytic diatom communities. Rutgers Univ., Unpub. M.S. Thesis, 106 pp.
.'Hein, M. K.:and J. D. Koppen. '_1979.
Effects of thermally elevated discharges
' on'the structure and composition of estuarine periphyton diatom aassemblages.'Est. Coastal Mar.. Sci., 9:385-401.
~
Hoagland, K. E.
1983.~-Ecological studies of.woodboring bivalves in the vicinity of.the Oyster Creek Nuclear Generating Stations fin 41 raport September 1976-December 1982. Rept.'to U.S. Nuc. Reg. Comm.,
NUREG/CR-3446, 173 pp.
+.
Hoagland, X.'E...1982._ Ecological studies of woodboring bivalves and fouling organisms in the vicinity of the Oyster Creek Nuclear Generating Station.
Rept. to U.S. Nuc. Reg. Comm., NUREG/CR-2727, Vol. 4, 38 pp.
- Hoagland, K. E. and L. Crock't.
1979.; Analysis of populations of boring and e
4
~
. fouling organisms.in the vicinity of the Oyster Creek Nuclear Generating i
' Station: September'1, 1977-August 31', 1978. Rept. to U.S. Nuc. Reg.
?
Comm., NUREG/CR-0634, 114 pp.
i Hoagland, K.. E.'and L. Crocket.
1979. Analysis of populations of boring and fouling organisms in the vicinity of the. Oyster Creek Nuclear Generating
~ Stations September 1978-November 1978.
Rept. to U.S. Nuc. Reg. Comm.,
NUREG/CR-0812, 64 pp.
.Hoagland, K. E. and:L. Crocket.
1980. Ecological studies of woodboring i
bivalves in.the vicinity of the Oyster Creek Nuclear Generating Station.
Rept; to.U.S. Nuc. Reg.,Comm., NUREG/CR-1795,-31 pp.
Hoagland, K. E. and R. D. Turner. 1980. Range extensions of teredinids
/(shipworms)' and polychaetes in the vicinity of a temperate-zone nuclear generating station. Mar. Biol.,'58:55-64.-
- ;Hoagland, K.
E.' and L. Crocket. :1981.. Ecological studies of woodboring m bivalves.in the vicinity of the Oyster Creek Nuclear Generating, Station.
Rept; to U.S.-Nuc. Reg. Comm., NUREG/CR-1855,'48.pp.-
' Hoagl'and, - K., E. 'and L.' Crocket.
1981. ' Ecological studies of-woodboring N.
bivalves'in the vicinity of the Oyster Creek Nuclear Generating' Station.
~
i Rept.'to U.S.:Nuc. Reg. Comm.,'NUREG/CR-1939,-Vol. 3, 38 pp.
Hoagland,-K. E. andlL. Crocket.
1981. Ecological studies of woodboring
,sbivalves'in the' vicinity of the Oyster Creek Nuclear Generating Station..
- Rept. to U.S.. Nuc. Reg. ~ Comm., NUREG/CR -1939, Vol. 4, 4 4 - pp.~
LHoagland, K. EN-and R.--D.' Turner.
1981'. -Evolution and adaptive radiation of woodboring bivalves (Pholadacea). -Malacologia,- 21:111-148.
s s
T 1
t, Q
C 1
I k
[
f'
. I t
~
s
, r - 9,.
y -
,re
-..~r
+,
n w+
,,,,,,,m-sa.,.
,,ws e,--,.n
- w.,-,n
-w,-m
, ~. - y me,r--,.
c.:.
-TABLE 3 continu:d m i.
Hoagland,lK.
E., M. Rochester, and R. D. Turner. 1977. Analysis of boring and fouling organisms in the vicinity of the Oyster-Creek Nuclear Generating Station with discussion of relevant physical parameters over 4.
period: March 1-May 31, 1977. Rept. to U.S. Nuc. Reg. Comm., 26 pp.
t i Hoagland, K.
E.,.M. Rochester, and L. Crocket. 1977. Analysis of boring and fouling organisms in the vicinity of the Oyster Creek Nuclear Generating
, Station with' discussion'of relevant physical perameters over the period:
~
June 1-August 31, 1977.. Rept. to U.S. Nuc. Reg. Comm., 48 pp.
Hoagland,~K.
E.,
R.,D. Turner, and'M. Rochester.
1977. Analysis of. boring and fouling organisms.in the vicinity,of the Oyster Creek Nuclear Generating Station with discussion of relevant physical parameters over the period: April 30-November 30, 1976. Rept. to U.S. Nuc. Reg. Comm., 61 pp.'
1 Hoagland, K.
E.,'R. D.' Turner,;and M. Rochester.- 1977. Analysis of boring and fouling organisms in'the vicinity of the Oyster Creek Nuclear Generating Station with discussion of relevant physical parameters over
'the period: December 1,'1976-February 28, 1977.
T-Cosa., 61 pp.
Rept. to U.S. Nuc. Reg.
r
- Hoagland, K.-E.,
L. Crocket, and M. Rochester.
1978.- Analysis of boring and
. fouling organisms in the vicinity of the Oyster Creek Nuclear Generating.
}
' Station with discussion of relevant! physical parameters ove:; the period:
September 1-November.30,-1977.- Rept.-to U.S.~Nuc. Reg. Comm., a pp.
~
y
. Hoagland, K.?E.,.L. Crocket, and M.' Rochester.
1978. Analysis of populations'
.of boring and fouling organisms in the vicinity of the Oyster Creek Nuclear Generating Stations' December _l,'1977-February 28, 1978. Rept. to-
-U.S. Nuc. Reg. Comm., NUREG/CR-02?3,,44'pp.
Hoagland,'K.
E., L. Crocket, and M. Rochester. ^1978.
Analysis of boring f
ana fouling organisms in the vicinity of the Oyster Creek Nuclear
' Generating Station with discussion of relevant physical parameters over the periods March 1-May 31, 1978. Rept.,to U.S.-Nuc. Reg. Comm.,
j J
NUREG/CR-0380, 42 pp.7 Hoagland,;K.
E.,
L.' Crocket,1 and J.. Harms.
1979. ' Analysis of populations of boring and fouling organians in the vicinity'of the Oyster Creek Nuclear.
l Generating Station. Rept. to.U.S. duc. Reg. Comm., 52 pp.
i Hoagland,_K.(E.,~L.' Crocket,'and R.=D.' Turner. 1980. Ecological studies of
~
j woodboring bivalves ~.in the vicinity'of the Oyster Creek Nuclear Generating
= Station. - Rept. to U.S. Nuc.' Reg. Comm., NUREG/CR-1517, 65'pp.
- LMarcellus,'K.;L. 21972.
~
l Fishes of Barnegat Bay, New-Jersey, with particular
[.jt
- reference: to' seasonal: influences and possible affects. of thermal :
- - discharges..Rutgers Univ.,-Unpub. Ph.D.' Thesis,'190 pp.,
p4
+
.~
s l
y 4
6 i
t
- f L
8 4
t
- 4. ~
i
[q a
V.[
2
' TABLE'3:continu:d
- r..-
4 T
McCurdy,'D[ E. ~ 1971.. Environmental radiation levels in the state of New
< Jersey.- New Jersey State, Department of ' Environmental Protection Rept.,
Trenton,'New' Jersey.
f, McCurdy, D.'and J. Ross. 1972.. Temporal variations of the Oyster Creek water s
temperature downstream from the Oyster Creek Nuclear Generating Station during 1973 and 1974. New Jersey State Department of Environmental Protection Rept.,-Trenton, New Jersey.
- McCurdy, D. E. and'J. J.'Russo.
1972 and 1973. Environmental radiation surveillance of the Oyster Creek Nuclear Generating Station. New Jersey Department of' Environmental Protection Repts., Trenton, New Jersey.
RMoskowitz, M. R.
1971. Thermal addition and the diversity of the benthic H
'macroinvertebrate community in Barnegat Bay. Rutgers Univ., Unpub. M.S.
Thesis,'ll7 pp.
~
Mountford, K.
1967. The occurrence of Pyrrhophyta in a brackish cove -
Barnegat Bay, New Jersey at Mantoloking, May through December,1966.
hC Bull. N.J. Acad. Sci., 12: 9-12.
Mountford, K.
1969. A seasonal plankton cycle for Barnegat Bay, New Jersey.
' Rutgers ~ Univ., Unpub. M.S. Thesis, 66 pp, u
Mountford, K.
1969.
Plankton sur'vey data for.Barnegat Bay,'New Jersey,
- 1964-1965 (abs. ). Bull. N.J. Acad.' Sci., 14 3.15.
Mountford, K.
1971., Plankton studies in Barnegat Bay. Rutgers Univ., Unpub.
Ph.D.' Thesis, 147 pp.
Mountford, K.-.
1980. Occurrence and predation by Mnemiopsis leidyi in Barnegat Bay,'N.J. Est.' Coastal-Mar. Sci., 10: 394-402..
~
.New Jersey Department of Environmental Protection. 1973. Studies of the
-upper'Barnegat Bay' system. Final Rept. Proj. 3-137-R-2, Mis. Rept.1No.
-5<
'lDM, Trenton, N.J.
3
- New Jersey Department of Environmental Protection', Division of Environmental" Quality, Bureau of Radiation Protection. Undated report. Temporal variations of the Oyster Creek. Nuclear Generating Station during 1973 and
.1974. - Table;6: Reported Fish Kills.in Oyster-Creek.
-1.p..
- =Ohori,~V. L..J1982. 'The d'istribution, abundance, and importance of the-seagrass, Zostera marina.L., in the vicinity of Oyster Creek Nuclear Generating Station, Barnegat Bay, New Jersey, 1979-1980. Rutgers Univ.,.
. Unpub. M.S.LThesis, 62 pp.
y Olsen, C.'R.,
P. E. Biscaye, H. J. Simpson, R.' M. Trier,.N. Kostyk, R. F.
Bopp,-Y.-H. Li, and H. W. Feely! 1980. Reactor-released radionuclides
'and fine-grained sediment' transport and: accumulation patterns in Barnegat
..~-
Bay, New Jersey and adjacent shelf waters. 'Est. Coastal Mar.. Sci.,
110:119-142.-
f
'F
~ - ~
W W
c 3
1
.j.--i---.
rir-i=
TABLE 3.continu:d
- 4.
'Phillips, F.
X'.
.'1972..The ecology of the benthic macroinvertebrates of Barnegat Bay, New Jersey. Rutgers Univ., Unpub., Ph.D. Thesis, 156 pp.
'Sandine, P. H.'~1973. _ Zooplankton of Barnegat Bay:
the effect of the Oyster Creek Nuclear Power Plant. Rutgers Univ., Unpub. M.S. thesis, 73 pp.
- Shafto, S.'S.
1974.- The marine boring and fouling invertebrate community of Barnegat Bay, New Jersey. Rutgers Univ., Unpub. M.S. Thesis, 235 pp..
Taylor,.J. E.
1970. The ecology and seasonal periodicity of centhic marine algae from Barnegat Bay, New Jersey. Rutgers Univ., Unpub. Ph.D. Thesis, 194 pp.
Turner,. R..D. - 1971-1976. Reports on panels removed from Oyster Creek and
-adjacent stations. Monthly. unpublished reports available from the archives, Acad. Nat. Sciences Dept. of Malacology, Philadelphia, Pa..
Turner, R. D..
1973. Report on marine borers,(Teredinidae) in Oyster Creek, Waretown, N.J.
Report.to marina owners and AEC:
30 pp.
Turner, R. D.
1973.
In the path of a warm, saline effluent. Bull. Amer.
Malac. Union., 36-41.
, Turner, R. D.
1974. The introduction of Teredo furcifera von Martens into Oyster Creek, Waretown, New Jersey.
app:
3 pls.
- Report to marina owners and AEC.
4 Turner,.R. D.
1974. Report'on panels removed Aug. 27, 1974, from Oyster Creek, Stout's Creek and' Holly Park. Report-to marina owners and AEC.
16 pp, 11 pis.-
- Turner, R.;D.
1975. Report on panels removed from Oyster Creek, Forked River Beach, Stout's Creek, and Holly Park on January 26, 1975.. Report to marina owners and AECs. 12 pp, 6.pls.
U.S. Atomic Energy-Commission..1974. -Final environmental statement related
'to operation of the Oyster Creek Nuclear Generating Station.
AEC Docket No. 50-219.
~
~
Reacte sensing study of electric-U.S. Environmental Protection Agency.. 1973.
igenerating station thermal' discharges to Barnegat Bay and Great Egg
~
H Harbor, New Jersey. Technical report prepared by the National Field Investigation Center, Denver and Region II, New York.
Young, J. _ S.' and A. B. Frame.
1976. Some effects of a power plant' effluent on estuarine epibenthic organisms.. Int. Revue ges. Hydrobiol., 61, 37-61.
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