ML20082R343

From kanterella
Jump to navigation Jump to search
Study of Woodborer Populations in Oyster Creek Generating Station,Progress Rept for 34th Quarter,830721-1020
ML20082R343
Person / Time
Site: Oyster Creek
Issue date: 11/30/1983
From: Belmore C, Hillman R
BATTELLE NEW ENGLAND MARINE RESEARCH LABORATORY
To:
Shared Package
ML20082R340 List:
References
15207, NUDOCS 8312130132
Download: ML20082R343 (24)


Text

.

I PROGRESS REPORT FOR THE THIRTY-FOURTH QUARTER l

On STUDY OF WOODBORER POPULATIONS IN RELATION TO THE OYSTER CREEK GENERATING STATION To GPU NUCLEAR CORPORATION November 30,1983 by R.E. Hillman and C.I. Belmore REPORT NO.15207 July 21,1983 to October 20,1983 BATTELLE New England Marine Research Laboratory Duxbury, Massachusetts 02332 Battelle is not engaged in research for advertising, sales promotion, or publicity purposes, and this report may not be reproduced in full or in part for such Purposes.

8312130132 831202 PDR ADOCK 05000219 l

R PDR

TABLE OF CONTENTS Page EX EC UTIVE SU M M ARY.....................................................

1 INTRODUCTION...........................................................

2 PROCEDURES AND INTERIM D ATA.........................................

3 Exposure Panels.......................................................

3 Water Quality.... -....................................................

3 Teredmid Gonadal Development Studies...................................

3 LIST OF TABLES Table 1.

Geographical Locations of Exposure Panel Arrays in Barnegat 5

Bay, New Jersey.

Table 2.

Incidence of Teredinidae in Panels Removed August 1-2, 198 3..........

9 Table 3.

Incidence of Teredinidae in Panels Removed September 6-7,1983.......

10 Table 4.

Incidence of Teredinidae in Panels Removed October 4-5, 1983.........

11 Table 5.

Incidence of Limnoria in Panels Removed August, September and 12 October,1983.........

Table 6.

Water Quality at Exposure Panel Stations, August 1-2, 1983............

13 Table 7.

Water Quality at Exposure Panel Stations, September 6-7,1983.

14 Table 8.

Water Quality at Exposure Panel Stations, October 4-5, 1983...........

15 Table 9.

Condition of Gonads of Teredinid Borers Removed from Exposure Panels in Barnegat Bay from July through September,1983.............

16 LIST OF FIGURES Figure 1.

Outline of Barnegat Bay Showing Geographical Locations of Exposure Panels..................................................

4

1 EXECUTIVE

SUMMARY

This progress report presents data from field and laboratory work during the period July 21,1983 to October 20,1983.

All field work during this quarter was carried out by GPU Nuclear personnel.

Temperature,calinity, dissolved oxygen and pH were measured and recorded at each of the 20 stations during the three periods of exposure panel exchange.

Shipworm damage has increased this year as compared with 1982, particularly at Stations 13 and 14. Bankia gouldi is responsible for the increase. One specimen of Bankia gouldi was found in the long-term exposure panel remove! from Station 17 in October,1983. The last time any Bankia were found in long-term exposure panels from this site was 1978. Teredo navalis continues to be active there also.

Two Limnoria tunnels were found in the long-term exposure panel from Station 5 at the mouth of Oyster Creek in September,1983. There were no tunnels in the panels examined from this site in October,1983.

No Teredo bartschi have been found in any of the exposure panels in Barnegat Bay as yet this year.

For the most part, the gonads of both B. gouldi and T. navalis were in typical mid-to late-summer condition, with most being in the late active to partially spawned stage. No unusual conditions were noted in the gonad histology.

2 PROGRESS REPORT FOR THE THIRTY-FOURTH QUARTER on STUDY OF WOODBORER POPULATIONS IN RELATION TO THE OYSTER CREEK GENERATING STATION to GPU NUCLEAR CORPORATION November 30,1983 by Robert E. Hillman and C.I. Belmore REPORT NO.15207 July 21,1983 to October 20,1983 from BATTELLE New England Marine Research Laboratory Duxbury, Massachusetts 02332 INTRODUCTION Battelle's New England Marine Research Laboratory is conducting an investigation to determine whether the generating station is affecting the resident ti;crine berer population in Oyster Creek to the extent that that population is contributing significantly to marine borer-caused damage in Barnegat Bay.

A description of the program and procedures used may be found in the seventh annual report titled, " Study of Woodborer Populations in Relation to the Oyster Creek Generating Station", dated May 15,1983.

This report presents data for the thirty-fourth quarterly period from July 21 to October 20,1983.

i PROCEDURES AND INTERIM DATA Exposure panels The long-term and short-term exposure panels were retrieved and replaced with new untreated pre-soaked (for two weeks) panels at the 20 exposure sites in Barnegat Bay and adjacent waters (Figure 1) during the periods of August 1-2, September 6-7, and October 4-5, 1983. I.cag-term and short-term panels at 211 stations were retrieved and replaced by personnel from GPU's Oyster Creek Nuclear Generating Station.

Table 1 describes the geographical locations of the exposure sites. Data from the laboratory exarr.ination of the panels are presented in Tables 2 through 5.

Water Quality Salinity, water temperature, dissolved oxygen and pH were taken at each site by the GPU Nuclear field team. Results for August, September, and October,1983 are presented in Tables 6 through 8.

Teredinid Gonadal Development Studies Table 9 shows the gonad condition of teredinid borers collected in July, August, and September,1983. Included are results from panels exposed for periods ranging from 6 to 12 months.

4 G,@

MANASQUAN INLET BDELLE 0

4,3 POINT d

PLEASANT INTA ACOASTAL #

WATERWAY CAN AL MANTOLOKING 15 KETTLE CREEK 0

D Q

<f SEASIDE 16

/ 7' SLOOP CREEK ATLANTIC OCEAN HOLLY PARK C

qr STOUTS CREEK

[

108 SEDGE to ISLAND

($10A o

p 5$

OYSTER 6

BARNEGATINLET OYSTER CREEK NUCLEAR GENERATING 1 BARNEGAT gg STATION C TY WARETOWN 4

BARNEGAT BEACH CONKLIN

$ PANEL ARRAY ISLAND h

0 2

3

- MILES g

sARNEGAT iNtET. NEW JERSEY Latsude 39 45 8 N y

Lonqrtu6e 74 060 W g

2 I 5 1

4 L

FIGURE 1. OUTLINE OF BARNEGAT BAY SHOWING GEOGRAPHIC LOCATIONS OF EXPOSURE PANELS

TABLE 1.

GEOGRAPHICAL LOCATIONS OF BATTELLE NEW ENGLAND MARINE RESEARCH LABORATORY'S EXPOSURE PANEL ARRAYS IN BARNEGAT BAY, NEW JERSEY Structure to be used for Nearest Previous Approximate Latitude i

Site No.

Site Suspension of Rack Data Stations and Longitude l

l 1.

Barnegat Coast Guard Finger Pier WC1 Lat. 390 45.8'N l

l Station, Barnegat Inlet Bulkhead WFCL 19' 8-1967 Long. 740 06.5'W 4

2.

Ashton Marina Bulkhead WC 13,14 Lat. 390 40'N 1450 Bay Ave.

Long. 740 13'W Manahawkin u,

3.

Iggie's Marina Bulkhead WC 16,17,18,19 Lat. 390 45'N East Bay Ave.

Long. 74012.5'W Barnegat (Conklin Island) 4.

Liberty Harbor Marina Bulkhead WC 21 Lat. 390 47'N Washington Ave.

R. Turner Long.740ll'W Waretown Rutgers U.

4-A *.

Holiday Harbor Marina Bulkhead WC 21 Lat. 390 48'N Lighthouse Drive R. Turner Long. 740 ll'N Waretown Rutgers U.

5.

Mouth of Oyster Creek, Dock WC 29,30 Lat. 390 48.5'N Lot 4, Compass Road Rutgers U.

Long. 74010.3'W Offshore End 6.

Oyster Creek 1 Dock Lat. 390 48.5'N Lagoon, Inshore End Long. 740 10.35'W 37 Capstan Drive

TABLE 1. (Continued)

Structure to be used for Nearest Previous Approximate Latitude Site No.

Site Suspension of Rack Data Stations and Longitude 7.

Private Dock End of Dock WC 27,28 Lat. 39o 48.5'N Dock Ave.

R. Turner Long. 74011.1'W Oyster Creek Rutgers U.

Sands Pt. Harbor Waretown 8.

Oyster Creek-R.R.

Cross Member WC 26 Lat. 390 48.7'N Bridge Bridge Rutgers U.

Long. 74012'W Discharge Canal 9.

Forked River Cross Member WC 31 Lat. 390 49.2'N m

South Branch R.R. Bridge Long. 740 12.2'W Intake Canal 10.

Teds Marina Pier WC 33,34 Lat. 390 50.I'N Bay Ave.

Long. 740 11.6'W Forked River 10 A *.

Private Dock Under Dock Lat. 390 49'N 1217 Aquarius Ct.

Long. 74010'W Forked River 10B*.

Private Dock Under Dock Lat. 390 49.4'N 1307 Beach Blvd.

Long. 74010.I'W Forked River 11.

Forked River Bulkhead We 35 Lat. 390 49.7'N (near mouth)

Rutgers U.

Long. 74010'W 1413 River View Drive i

TABLE 1. (Continued)

Structure to be used for Nearest Previous Approximate Latitude Site No.

Site Suspension of Rack Data Stations and Longitude 12.

Stouts Creek Bulkhead WC 38,40,41 Lat. 390 50.5'N 1273 Capstan Drive R. Turner Long. 740 08.8'W Wurtz Rutgers U.

l l

13.

Rocknak's Yacht Basin End of Pier WC 46 Lat. 390 52'N Seaview Ave.

Long. 740 09'W Lanoka Harbor Cedar Creek 14.

Dicks Landing Pier WC 49 Lat. 390 54'W y

Island Drive R. Turner Long. 740 08.1'W Bayville (Holly Park)

Nelson 15.

Winter Yacht Basin Inc.

Pier WC57 Lat. 400 02.5'N Rt.528 Long. 740 04.9'W Mantoloking Bridge 16.

Berkely Yacht Basin Pier WC 60,61 Lat. 390 55.9'N

3. Street Long. 740 04.9'W Seaside 16 A *.

Municipal Dock Pier WC 60, 61 Lat. 390 56.6'N Seaside Heights Long. 740 04.9'W 16B*.

Bayside Boats Pier WC 60, 61 Lat. 390 56.6'N State Highway 35 and Long. 740 04.9'W Bay Boulevard Seaside Heights, N3

TABLE 1. (Continued) l Structure to be used for Nearest Previous Approximate Latitude Site No.

Site Suspension of Rack Data Stations and Longitude l

17.

Island Beach Pier WC 68 Lat. 390 47.I'N State Park Long. 740 05.9'W (Sedge Island)

All exposure panel racks suspended in a minimum water depth at mean low water of at least three feet. Racks hung with nylon line from existing structures so the bottom panels are close to, but not touching the bottom. Racks at Forked River railroad bridge and Oyster Creek railroad bridge suspended with wire rope.

WC = Woodward-Clyde m

WFCL = William F. Clapp Laboratories Site 4-A installed April,1977.

Sites 10A,10B installed April,1978.

Site 16 discontinued November,1981.

Site 16A installed December,1981 - discontinued June,1982.

Site 16B installed June,1982.

9 TABLE 2. INCIDENCE OF TEREDINIDAE IN PANELS REMOVED AUGUST l-2,1983.

No.of Percent Size Range Station Pane!

Specimens Filled in mm.

Species Identification Remarks 1

P 900 5

<1-16 10 T. navalis, 890 Te7edinidae*

C 1100 4

<l-7 1100 Teredinidae*

2 P

0 C

1

<1 2

1 Teredinidae*

5 P

1

<1 30 1 B. gouldi C

0 7

P 1

<1 2

1 Teredinidae*

C 0

8 P

2

<1 13-30 2 B. gouldi C

1

<1 1

1 Teredinidae*

10A P

2

<1 14-45 2 B. gouldi C

0 10B P

2

<1

<1 2 Teredinicae*

C 0

11 P

46 60 35-110 43 B_. gouldi, 3 T_.

Ripening gonads navalis C

0 12 P

2

<1 13-20 2 B, gouldi C

1

<1

<.1 1 Teredinidae*

13 P

O C

2

<1

<!-3 2 Teredinidae*

14 P

59 40 20-110 59 B_. gouldi Ripening gonads C

28

<1

<!-4 28 Teredinidae*

Stations 3-4A, 6, 9,10,15 No Teredinidae present.

P = Long-term panel submerged February 8-9,1983.

C = Short-term panel submerged July 5-6,1983.

o = Not speciated due to size.

10 TABLE 3. INCIDENCE OF TEREDINIDAE IN PANELS REMOVED SEPTEMBER 6-7,1983.

l No.of Percent Size Range Station Panel Specimens Filled in mm.

Species Identification Remarks 1

P 850 98

<1-50 650 T. navalis,200 Ripening gonads Teredinidae*

C 1040 5

<!-18 40 T_. navalis,1000 Teredinidae*

3 P

1 3

180 1 B. gouldi C

0 5

P 2

8 230-240 2 B. gouldi C

0 7

P 3

5 60-220 3 B_. gouldi C

0 8

P 7

8 25-180 6 B. gouldi,1 T.

Teredo-ripening navalis gonads C

0 10A P

1 4

250 1 B_. gouldi C

0 11 P

37 95 50-190 36 B_. gouldi,1 T.

Teredo dead navalis C

0 12 P

1 3

160 1 B. gouldi

~

C 1

<1 28 1 B. gouldi 13 P

6 17 140-250 6 B. gouldi C

0 14 P

47 90 20-190 47 B. gouldi C

0 15 P

1 2

130 1 B. gouldi C

1

<1 4

1 Teredinidae*

17 P

7 1

<l-27 4 T. navalis,3 Teredinidae

  • C 8

<1

<1-3 1 Teredo spp,7 Teredinidae

  • Stations 2,4,4A,6,9,10,10B, and 16B - No Teredinidae present.

b 5 b80ff*t'ed"[tMel's"uk*m*Ed.edS*fghs['l '2,N3.

E*"*

  • = Not spect ue to size

11 TABLE 4. INCIDENCE OF TEREDINIDAE IN PANELS REMOVED OCTOBER 4-5,1983.

No. of Percent Size Range Station Panel Specimens Filled in mm.

Species Identification Remarks 1

P 400 99 30 T. n_avalis, 370 None live Teredinidae*

C 85

<1

<l-3 85 Teredinidae*

6 P

1 2

140 1 B. gouldi C

0

~

7 P

4 8

95-200 4 B. gouldi 3 live, I dead C

0 8

P 3

7 130-170 3 B_. gouldi C

0 10A P

1 7

360

15. gouldi C

0 10B P

2 5

140-180 2 B_. gouldi 1 live, I dead C

0 11 P

48 98 25-190 11 B_. gouldi, 37 37 empty tubes Teredinidae*

C 0

12 P

1 2

165 1 B. gouldi C

0 13 P

23 95 75-225 23 B. gouldi C

0 14 P

120 98

<!-120 1 T_. navalis, 46 65% of specimens B. gouldi 73 dead Teredinidae*

C 0

15 P

1 5

285 1 B_. gouldi C

0 17 P

24 5

<!-140 1 B. gouldi, 6 T.

-n valis,1 Teredo spp*,8 Teredinidae*

C 0

Stations 2-5,9-10,16B - No Teredinidae present P = Long-term panel submerged April 5-6, 1983.

C = Short-term panel submerged September 6-7, 1983.

  • = Not speciated due to size or condition.

12 l

TABLE 5. INCIDENCE OF LIMNORIA IN PANELS REMOVED

AUGUST, SEPTEMBER, AND OCTOBER,1983.

August September October No.of No. of No.of No.of No. of No.of Station Panel Tunnels Specimens Tunnels Specimens Tunnels Specimens i

P 7

12*

26 12**

19 3

C 7

8*

10 12**

10 7

2 P

1600 1500**

4000 3800**

2000 1500**

C 31 23*

38 47*

2 0

3 P

20 16*

155 170**

150 130***

C 0

0 0

4 P

14 19**

290 375**

205 205***

C 0

1 0

0 4A P

4500 6000**

7200 6000**

7500 5500**

C 260 380*

59 73**

10 10 5

P O

2 2*

O C

0 0

0 Stations 6-17, no Limnoria present.

P = Long-term panel, submerged 6 months.

C = Short-term panel, submerged 1 month.

  • = Gravid females present.
    • = Gravid females and juveniles present.
      • = Juveniles present.

13 TABLE 6. WATER QUALITY AT EXPOSURE PANEL STATIONS AUGUST,1983 Depth in Salinity Temperature 02 Station Date Time Feet 0/00 (oC)

(mg71) pH I

8/1/83 0905 4.0 25.2 21.7 6.1 7.7 2

8/1/83 0950 3.0 23.4 27.0 5.0 7.6 3

8/1/83 1025 1.0 21.1 28.2 4.4 7.5 4

8/1/83 1048 1.5 21.8 29.0 5.2 7.7 4A 8/1/83 1106 1.0 21.8 28.8 5.6 7.8 5

8/1/83 1125 0.8 15.2 28.7 6.2 7.8 6

8/1/83 1140 2.0 16.8 27.5 6.2 7.8 7

8/1/83 1706 1.5 19.0 30.0 6.2 7.9 8

8/1/83 1356 4.0 17.8 28.5 6.5 7.8 9

8/1/83 1325 4.0 17.8 28.8 6.0 7.4 10 8/1/83 1521 3.0 12.5 28.9 5.8 7.5 10A 8/1/83 1425 1.5 19.3 29.6 5.2 7.8 10B 8/1/83 1443 3.0 18.9 29.5 6.0 7.9 11 8/1/83 1500 2.0 17.8 29.2 5.6 7.9 12 8/2/83 1250 2.0 18.3 28.7 6.0 7.6 13 8/2/83 1220 2.5 13.0 28.5 6.3 7.4 14 8/2/83 1152 3.0 17.8 28.2 5.6 7.7 15 8/2/83 0908 3.5 13.0 26.5 5.8 7.2 16B 8/2/83 0942 4.0 12.3 26.8 5.0 7.2 17 8/2/83 1030 1.0 23.3 27.0 7.6 8.0

I 14 TABLE 7. WATER QUALITY AT EXPOSURE PANEL STATIONS SEPTEMBER,1983 Depth in Salinity Temperature O2 Station Date Time Feet 0/00 (OC)

(mg/1) pH 1

9/6/83 0910 6.0 24.8 23.7 5.6 7.4 2

9/6/83 0955 1.5 24.5 27.7 5.0 7.5 3

9/6/83 1028 1.5 22.8 27.9 4.4 7.3 4

9/6/83 1102 3.0 22.6 28.0 3.2 7.2 4A 9/6/83 1123 2.0 22.3 29.0 5.6 7.6 5

9/6/83 1142 2.0 18.1 28.7 6.3 7.5 6

9/6/83 1155 2.0 19.1 28.0 5.0 7.3 7

9/6/83 1213 1.2 17.5 29.0 6.0 7.3 8

9/6/83 1340 4.0 20.2 27.9 5.4 7.3 9

9/6/83 1323 4.0 19.0 28.7 6.0 7.2 10 9/6/83 1512 4.0 16.0 28.7 5.7 7.3 10A 9/6/83 1406 2.2 20.2 28.9 5.8 7.6 10B 9/6/83 1425 3.0 20.0 29.0 6.0 7.6 11 9/6/83 1442 1.5 19.0 29.2 6.0 7.6 12 9/7/83 1324 2.5 19.4 28.8 5.2 7.5 13 9/7/83 1256 3.0 16.1 28.8 5.3 7.4 14 9/7/83 1220 4.0 17.9 29.0 4.8 7.4 15 9/7/83 0852 3.0 15.2 26.7 6.3 7.3 16B 9/7/83 0930 4.0 13.8 27.6 5.0 7.2 17 9/7/83 1055 1.5 23.9 28.7 3.9 7.6

15 TABLE 3. WATER QUALITY AT EXPOSURE PANEL STATIONS OCTOBER,1983 Depth in Salinity Temperature O2 Station Date Time Feet 0/00 F)

(mg70 pH 1

10/4/83 0900 5.5 20.9 19.6 6.6 7.8 2

10/4/83 0938 2.0 20.9 19.8 6.9 7.7 3

10/4/83 1026 2.0 20.5 20.2 6.3 7.6 4

10/4/83 1053 2.2 20.8 19.9 5.8 7.6 4A 10/4/83 1112 2.2 21.1 20.7 6.8 7.8 5

10/4/83 1131 1.2 16.6 20.5 8.8*

7.9 6

10/4/83 1148 2.5 18.0 20.0 7.4 7.8 7

10/4/83 1205 1.6 16.9 21.7 8.4 8.0 8

10/4/83 1401 4.0 20.2 20.6 9.0 8.0 9

10/4/83 1340 4.0 18.8 21.7 7.2 7.4 10 10/4/83 1535 4.0 18.2 21.0 7.3 7.7 10A 10/4/83 1430 1.5 19.0 22.3 7.1 7.7 10B 10/4/83 1450 3.2 19.4 21.6 7.8 7.9 11 10/4/83 1508 2.5 18.5 21.7 7.8 7.9 12 10/5/83 1250 2.5 19.6 21.6 7.6 7.9 13 10/5/83 1225 3.0 19.6 21.6 8.0 8.0 14 10/5/83 1140 4.0 17.9 21.5 7.4 7.8 15 10/5/83 0928 4.0 17.6 20.6 7.3 7.7 16B 10/5/83 1000 5.0 14.0 20.7 7.8 7.9 17 10/5/83 1054 1.5 22.3 21.6 a.2 7.7

  • Value may be too low, DO meter may have needed to be recalibrated.

TABLE 9a CONDITIOri OF GONADS OF TEREDINID BORERS REMOVED FROM EXPOSURE PANELS IN BARNEGAT BAY FROM JULY THROUGH SEPTEMBER,1983.

EA=Early active; LA= Late active; R= Ripe; PS= Partially spawned; S= Spent; M= Male; F= Female; H= Hermaphrodite Month No. Months Gonad Specimen No.

Station Removed Exposed Species Sex Condition Comments I

1247 a 7

Jul 83 12 Teredo navalis M

R Special panel i

b Teredo navalis F

R l

c Teredo navalis F

R d

Teredo navalis F

R e

Teredo navalis M

R 1248 a 17 Jul 83 12 Teredo navalis F

R Special panel b

Teredo navalis M

PS c

Teredo navalis M

PS d

Teredo navalis M

PS 1249 11 Jul 83 12 Bankia gouldi F

R Special panel 1250 11 Jul 83 12 Teredo spp.

F R

Special panel 1251 a 11 Jul 83 12 Teredo navalis H

S Special panel b

Teredo navalis F

PS l

]

1252 a 11 Aug 83 6

Bankia gouldi M

LA b

Bankia gouldi M

PS c

Bankia gouldi H

R d

Bankia gouldi H

PS l

e Bankia gouldi F

PS f

Bankia gouldi F

PS g

Bankia gouldi M

R l

h Bankia Qouldi H

PS i

i Bankia gouson M

PS l

j

_Bankia gouldi M

PS i

i TABLE 9.

(Continued)

Month No. Months Gonad Specimen No.

Station Removed Exposed Species Sex Condition Comments k

Bankia gouldi No discernable gonad 1

Bankia gouldi M

LA m

Bankia gouldi F

PS Bankia gouldi M

PS l

n l

1253 a 12 Aug 83 6

Bankia gouldi No discernable gonad b

Bankia gouldi No discernable gonad 1254 a 14 Aug 83 6

Bankia gouldi F

R b

Bankia gouldi F

PS c

Bankia gouldi F

PS d

Bankia gouldi F

PS Bankia gouldi M

PS e

N f

Bankia gouldi M

PS Bankia gouldi No discernable gonad g

h Bankia gouldi M

LA i

Bankia gouldi M

PS j

Bankia gouldi F

PS k

BankTa' gouldi F

PS 1

Bankia gouldi F

PS m

Bankia gouldi M

LA n

Bankia gouldi F

PS Bankia gouldi F

PS o

1255 8

Aug 83 6

Bankia gouldi No discernable gonad 1256 a 1

Aug 33 6

Teredo navalis No discernable gonad b

Teredo navalis No discernable gonad 1257 a 10A Aug 83 6

Bankia gouldi M

LA b

Bankia gouldi M

R 1258 5

Aug 33 6

Bankia gouldi M

R

TABLE 9.

(Continued)

Month No. Months Gonad Specimen No.

Station Removed Exposed Species Sex Condition Comments i

1259 11 Aug 83 6

Teredo navalis No discernable gonad 1260 a 11 Aug 83 12 Bankia gouldi H

LA Special panel b

Bankia gouldi M

PS c

Bankia gouldi M

R d

Bankia gouldi No discernable gonad e

Bankia gouldi M

R f

Bankia gouldi F

R g

Bankia gouldi M

PS h

Bankia geSuldi M

R 1261 17 Aug 83 12 Teredo navalis Special panel, no discernable gonad g-1262 15 Sep 83 6

Bankia gouldi No discernable gonad 1263 12 Sep 83 6

Bankia gouldi No discernable gonad 1264 12 Sep 83 6

Bankia gouldi M

EA 1265 a 8

Sep 83 6

Bankia gouldi No discernable gonad b

Bankia gouldi M

PS c

Bankia gouldi M

R d

Bankia gouldi M

PS e

Bankia gouldi M

S f

Bankia gouldi M

PS 1266 8

Sep 83 6

Teredo navalis F

R 1267 10A Sep 83 6

Bankia gouldi M

LA 1268 a 14 Sep 83 6

Bankia gouldi M

S b

Bankia gouldi F

R

TABLE 9. (Continued)

Month No. Months Gonad Specimen No.

Station Removed Exposed Species Sex Condition Comments c

Bankia gouldi F

S d

Bankia gouldi F

S e

Bankia gouldi F

PS f

Bankia gouldi F

S g

Bankia gouldi M

PS h

Bankia gouldi M

PS i

Bankia gouldi M

S j

Bankia gouldi M

R k

Bankia gouldi M

S 1

Bankia gouldi F

S m

Bankia gouldi M

S 1269 a 5

Sep 83 6

Bankia gouldi M

S b

Bankia gouldi M

S 1270 a 7

Sep 83 Bankia gouldi No discernable gonad b

Bankia gouldi M

R c

Bankia gouldi M

R 1271 3

Sep 83 6

Bankia gouldi M

S 1272 a 1

Sep 83 6

Teredo navalis No discernable gonad b

Teredo navalis F

R Teredo navalis F

R c

d Teredo navalis F

R Teredo navalis F

R e

f Teredo navalis F

R Teredo navalis F

R g

h Teredo navalis M

R i

Teredo navalis No discernzMe gonad j

Teredo navalis F

R k

Teredo navalis F

R

TABLE 90 (Continued)

Month No. Months Gonad Specimen No.

Station Removed Exposed Species Sex Condition Comments 1

Teredo navalis F

R Teredo navalis F

R m

Teredo navalis F

R n

Teredo navalis No discernable gonad o

Teredo navalis F

R p

1273 a 17 Sep 83 6

Bankia gouldi No discernable gonad b

Bankia gouldi No discernable gonad Bankia gouldi No discernable gonad l

c d

Bankia gouldi M

EA 1274 a 11 Sep 83 6

Bankia gouldi M

PS b

Bankia gouldi F

S ro c

Bankia gouldi M

PS d

Bankia gouldi M

PS Bankia gouldi M

PS e

f Bankia gouldi F

S g

Bankia gouldi M

R h

Bankia gouldi M

LA i

Bankia gouldi M

LA j

Bankia gouldi M

PS k

Bankia gouldi M

R 1

Bankia gouldi M

S m

Bankia gouldi M

R n

Bankia gouldi F

PS 1275 a 13 Sep 83 6

Bankia gouldi M

R b

Bankia gouldi F

S c

Bankia gouldi F

S d

Bankia gouldi M

S e

Bankia gouldi F

R f

Bankia gouldi No discernable gonad 1276 7

Sep 83 12 Bankia gouldi F

R Special panel

l m

TABLE 9. (Continued)

Month No. Months Gonad Specimen No.

Station Removed Exposed Species Sex Condition Comments 1277 12 Sep 83 12 Bankia gouldi M

PS Special panel 1278 a 11 Sep 83 12 Bankia gouldi M

S Special panel b

Bankia gouldi M

PS c

Bankia gouldi M

S d

Bankia gouldi M

S e

Bankia gouldi M

S f

Bankia gouldi M

S 15ankia gouldi M

S g

h Bankia gouldi No discernable gonad 1279 a 17 Sep 83 12 Teredo navalis M

S Special panel ro

~

b Teredo navalis M

PS Teredo navalis H

S c

d Teredo navalis M

S e

Teredo navalis F

R f

Teredo navalis No discernable gonad g

Teredo navalis M

S h

Teredo navalis No discernable gonad i

Teredo navalis F

EA j

Teredo navalis F

S k

Teredo navalis M

S 1

Teredo navalis M

S Teredo navalis M

S m

1280 17 Sep 83 12 Teredinidae M

R Special panel

22 D

1 8

,.3p M

l e

.o b

.E.

M iT

=L z

5 88

  • e 8z h

8 E

V aw Battelle New England Marine Research Laboratory 397 Washington Street Duxbury, Massachusetts 02332 Telephone (617) 934-5682 4

_ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _