ML20210A351
| ML20210A351 | |
| Person / Time | |
|---|---|
| Site: | Seabrook  |
| Issue date: | 07/31/1986 |
| From: | NORMANDEAU ASSOCIATES, INC. |
| To: | |
| Shared Package | |
| ML20210A285 | List: |
| References | |
| R-210, NUDOCS 8705050069 | |
| Download: ML20210A351 (303) | |
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i SEABROOK ENVIRONMENTAL STUDIES
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1 1985 DATA REPORT.-
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. TECHNICAL REPORT XVII-1 j.
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Prepared fo'r i PUBLIC SERVICE COMPANY OF NEW HAMPSHIRE NEW HAMPSHIRE YANKEE DIVISION I
Prepared by i
NORMANDEAU ASSOCIATES, INC.
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Bedford, New Hampshire
! R-2IO i- July 1986
. 8705050069 870430 l PDR ADOCK 05000443 R PDR ,
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'b TABLE OF' CONTENTS PAGE-
1.0 INTRODUCTION
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2.0 FINFISH. . . . . . . . . . . . . . . . . . . . .. 3 2.1 ICHTHYOPLANKTON . . . . . . . . . . . .. . . . 3 2.1.1 Methods. . . . . . . . . . .. . . . . . 3 -
2.1.1.1 Field Methods. . . . . . . . . 3 2.1.1.2 Laboratory Methods . . . . .. 4 2.1.2 Results. . . . . . . . . . . . . . . . . 5 2.2 ADULT FINFISH . . . . . . . . . . . . . . . . . 9 2.2.1 Methods. . . . . . . . . . . . . . . . . 9 2.2.1.1 Otter Trawls . . . . . . . . . 9 2.2.1.2 Gill Nets. . . . . . . . . . . 9 2.2.1.3 Sample Analysis / Data Com-pilation . . . . . . . . . . . 10
. 2.2.2 Results. . . . . . . . . . . . . . . . . 10 1
i 3.0 PLANKTON . . . . . . . . . . . . . . . . . . . . . . 15, 4
3.1 BIVALVE LARVAE. . . . . . . . . . . . . . . . . 15 3.1.1 Methods. . . . . . . . . . . . . . . . . 15 l 3.1.1.1 Field Methods. . . . . . . . . 15 3.1.1.2 Laboratory Methods . . . . . . 15 4
3.1.2 Results. . . . . . . . . . . . . . . . . 16 j 3.2 NONARUS AMERICANUS (LOBSTER) LARVAE . . . . . . 17 3.2.1 Methods. . . . . . . . . . . . . . . . . 17?
1 I 3.2.1.1 Field Methods. . . . . . . . . 17 3.2.1.2 Laboratory Methods . . . . . . 17 3.2.2 Results. . . . . . . . . . . . . . .. 18 i
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PAGE 4.0 BENT 90S. . . ... . . . . . . . .. . . . ... . . 19 4.1 MACR 0 ALGAE. . . . . . . . . .. . . . . . . . . 19 4.1.1 Methods. . . . . . . .. . . . ... . . 19 4.1.1.1 Field Methods. . . . .. . . 19 4.1.1.2 Laboratory Methods . . .. . . 21 4.1.1.3 Data Analysis. . . . . . . . . 22 4.1.2 Results. . . . . . . . . . .. . . . . . 23 4.2 MARINE MACROFAUNA . . . . . . . . .. . . . . . 29 4.2.1 Methods. . . . . . . . . .. .. . . . 29 4.2.1.1 Field Methods. . . . .. . . . 29 4.2.1.2 Laboratory Methods . . . . . 30 4.2.2 Results. . . . . . . . . . . . . . . . 31 4.3 SELECTED BENTHIC SPECIES. . . .. . . . . . . . 35 4.3.1 Methods. . . . . . . . . . . . . . . . . 35 4.3.1.1 Field Methods. . . . . . . . . 35 4.3.1.2 Laboratory Methods . . . . . . 35 4.3.2 Results. . . . . . . . . . . . . . . . . 36 4.4 EPIBENTHIC CRUSTACEANS. . . . . . . . .. . . . 41 4.4.1 Methods. . . . . . . . . . .. . . . . . 41 4.4.1.1 Field Methods. . . . .. . . . 41 4.4.1.2 Laboratory Methods . . . . . . 41 4.4.2 Results. . . . . . . . . . . . . . . . . 42 4.5 MYA ARENARIA. . . . . . . . . . . . . .. . . . 45 4.5.1 Methods. . . . . . . . . . . . . .. . . 45 4.5.1.1 Spat Surveys . . . . . . . . . 46 4.5.1.2 Adult Surveys. . . . . . . . . 46 4.5.1.3 Temperature and Salinity . . . 47 4.5.1.4 Clam Digger Coants . . . . . . 47 4.5.1.5 PSP Toxicity Levels. . . . . . 46 iv 1
PAGE 4.5.2 Results. . . . . . . .. . . . . . . .. 49 5.0
SUMMARY
. . . . . . . . . . . . . . . . . . . . . .. 53 5.1 ICHTHYOPLANKTON . . . . . . . .. . . . . . . 53 5.2 ADULT FINFISH , . . . . . . . . . . . . . .. 56 5.2.1 Otter Trawl. . . . . . . . . . . . . . 56 5.2.2 Gill Nets. . . . . . . . . . . . . . . . 57 5.3 #YA ARENARIA (SOFT SHELLED CLAM)
AND MYTILIDAE (MUSSEL) LARVAE. . . . . . . .. 58 5.4 RONARUS ANE,?ICANUS (LOBSTER) LARVAE . . . . . . 59 5.5 MACR 0 ALGAE. . . . . . . . . . . . . . . . . . 61 5.6 MARINE MACROFAUNA . . . . . . . . . . . . . 65 5.7 SELECTED BENTHIC SPECIES. . . . . . . . . . . . 67 5.8 EPIBENTHIC CRUSTACEANS. . . . . . . . . . . .. 71 5.9 #YA ARENARIA. . . . . . . . . . . . . . . . 73 6.0 LITERATURE CITED . . . . . . . . . . . . . . . . .. 77 7.0 APPENDICES l
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LIST OF FIGURES PAGE 2.1-1 Plankton sampling stations. . . . . . . . .. . 7 i
- 2.2-1 Finfish sampling stations .. . . .. . . . . . 12 4.1-1 -Benthic marine sampling stations. .. .. . . . 25 4.4-1 Locations of lob' ster, rock and green crab trapping. . . . . . . . . . . . .. . .. . . 43 I 4.4-2. Ilampton-Seabrook Estuary salinity and tempera-ture, soft-shell clam (hys arenaria) and l
j green crab (Carcinus maenas) sampling stations. . . . . . . . . . . . . . . . . . . . 44 4.5-1 Size class distributions and standard deviation of Mya arenaria in Hampton-Seabrook Estuary in October 1985 . . . . . . . . . . . . .. . . 51 i
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LIST OF TABLES PAGE 2.1-1 FINFISH SAMPLING METHODS, JANUARY THROUGH DECEMBER 1985 . . . . . . . . . . . . . . . . . 8 2.2-1 DESCRIPTION OF FINFISH SAMPLING STATIONS. . . . 15 4.1-1
SUMMARY
OF METHODS FOR SUBTIDAL AND INTERTIDAL MACR 0 ALGAL STUDIES. . . . . . . . . . . . . . . 26 4.2-1 BENTHIC STATION LOCATIONS AND DESCRIPTIONS. . . 32 4.2-2
SUMMARY
OF METHODS FOR MARINE SUBTIDAL BENTHIC SAMPLES . . . . . . . . . . . . . . . . . . . . 33 4.3-1
SUMMARY
OF ANALYSES OF SELECTED BENTHIC SPECIES . . . . . . . . . . . . . . . . . . . . 39 4.5-1 NUMBER OF #YA ARENARIA SAMPLES COLLECTED DURING THE ANNUAL FALL SURVEY IN HAMPTON AND SEABROOK ESTUARY, 1985. . . . . . . . . . . . . 52 i
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LIST OF APPENDIX TABLES PAGE ICHTHY 0 PLANKTON APPENDIX TABLE 1-1. ABUNDANCE (NO./1000 CUBIC METERS) 0F FISH EGGS BY STATION, SPECIES AND DATE . . . .. A-3 APPENDIX TABLE 1-2. PERCENT COMPOSITION (NO./1000 CUBIC METERS) 0F FISH EGGS BY STATION, SPECIES AND DATE . A-6 APPENDIX TABLE 1-3. ABUNDANCE (NO./1000 CUBIC METERS) 0F FISH LARVAE BY STATION, SPECIES AND DATE . . . . A-8 APPENDIX TABLE 1-4. PERCENT COMPOSITION (NO./1000 CUBIC METERS) 0F FISH LARVAE BY STATION, SPECIES AND DATE. . . . . . . . . . . . . . . . . .. . A-11 APPENDIX TABLE 1-5. COUNTS OF AMERICAN SAND LANCE LARVAE, AMNODYTES ANERICANUS, BY STATION, 0.5-mm LENGTH CLASS AND DATE . . . . . . . . .. . A-13 APPENDIX TABLE 1-6. COUNTS OF k'IhTER FLOUNDER LARVAE, PSEUSO-PLEURONECTES AMERICANUS, BY STATION, 0.5 mm LENGTH CLASS AND DATE . . . . . . . . . . . A-14 APPENDIX TABLE 1-7. COUNTS OF YELL 0k' TAIL FLOUNDER LARVAE, LINANPA FERRU6INEA, BY STATION, 0.5-mm LENGTH CLASS AND DATE. . . . . .. . . . . .. . . A-15 APPENDIX TABLE 1-8. COUNTS OF ATLANTIC COD LARVAE, CABUS #0RNUA, BY STATION, 0.5-mm LENGTH CLASS AND DATE. . A-16 APPENDIX TABLE 1-9. COUhTS OF ATLANTIC MACKEREL LARVAE, SCONBER SCONBRUS, BY STATION, 0.5-mm LENGTH CLASS AND DATE. . . . . . . . . .. .. . . A-17 APPENDIX TABLE 1-10. COUNTS OF CUNNER LARVAE, TAUTOCOLABRUS ADSPERSUS, BY STATION, 0.5-mm LENGTH CLASS AND DATE. . . . . . . . . . . ... . A-18 APPENDIX TABLE 1-11. COUNTS OF HAKE LARVAE, UROPHYCIS SP., BY STATION, 0.5-mm LENGTH CLASS AND DATE . . . A-19 APPENDIX TABLE 1-12. COUhTS OF ATLANTIC HERRING LARVAE, CLUPEA HARENGUS HARENGUS, BY STATION, 0.5-mm LENGTH CLASS AND DATE . . . . . . . . . . A-20 APPENDIX TABLE 1-13. COUNTS OF POLLOCK LARVAE, POLLACFIUS VIRENS, BY STATION, 0.5-mm LENGTH CLASS AND DATE. . A-22 l
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s PAGE APPENDIX TABLE 1-14. HYDROGRAPHIC DATA COLLECTED ON ICHTHYO-PLANKTON CRUISES FOUR TIMES A MONTH AT THE NEARFIELD (P2) AND FARFIELD (P7) SITES. . . A-23 ADULT FINFISH APPENDIX TABLE 2-1. MONTHLY CATCHES AND MONTHLY PERCENT COMPOSITION, (REPLICATES SU? DIED), OF FISH COLLECTED BY OTTER TRAWLS OFF HAMPTON-SEABROOK. . . . . . . . . . . . . . A-49 APPENDIX TABLE 2-2. OVERALL CATCH AND PERCENT COMPOSITION BY STATION FOR FISH COLLECTED IN OTTER TRAWLS OFF HAMPTON-SEABROOK. . . . . . . . . . . . A-57 APPENDIX TABLE 2-3. NUMBER OF INDIVIDUALS AND SPECIES (REPLI-CATES SUPDIED) COLLECTED PER MONTH BY OTFER TRAWLS OFF HAMPTON-SEABROOK . . . . . . . . A-58 APPENDIX TABLE 2-4 OTTER TRAWL CATCH PER UNIT EFFORT FOR SIX FINFISH SPECIES COLLECTED IN 1985 . . . . . A-59 APPENDIX TABLE 2-5. FISH SPECIES COLLECTED IN GILL NETS (SUM OF WO DAYS) FISHED MONTHLY AT SURFACE AND OFF-BOTTOM DEPTHS OFF HA'IPTON-SEABROOK. . . A-60 APPENDIX TABLE 2-6. FISH SPECIES COLLECTED IN GILL NETS (SUM OF WO DAYS) FISHED IN FEBRUARY, JUNE AND OCTOBER AT SURFACE, MID, AND OFF-BOTTOM DEPTHS OFF HAMPTON-SEABROOK . . . . . . . . A-64 APPENDIX TABLE 2-7. TOTAL CATCH AND PERCENT COMPOSITION OVER ALL DEPTHS, STATIONS AND SAMPLING PERIODS FOR FISH SPECIES COLLECTED IN GILL NETS OFF HAMPTON-SEABROOK. . . . . . . . . . . . . . A-68 APPENDIX TABLE 2-8. NUMBER OF SPECIES AND INDIVIDUALS COLLECTED MONTHLY OVER ALL DEPTHS AT EACH GILL NET STATION OFF HAMPTON-SEABROOK. . . . . . . . A-69 APPENDIX TABLE 2-9. CATCH PER UNIT EFFORT (C/E=24 HOUR SET) FOR FIVE FINFISH SPECIES COLLECTED BY GILL NETS IN 1985 . . . . . . . . . . . . . . . . . . A-70 ix
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APPENDIX TABLE 2-10. CATCH PER UNIT EFFORT (C/E=24 HR. SET) FOR FIVE FINFISH SPECIES. C/E BASED ONLY ON MONTHS WHEN MID NETS WERE SET: FEBRUARY, JUNE AND OCTOBER. . . . . . . . . .. . . . A-71 1 ,
APPENDIX TABLE 2-11. VOLUME (LITERS) 0F MACR 0 ALGAE COLLECTED IN OTTER TRAWLS DURING 1985 . . . . . . .. A-72 [
i BIVALVE LARVAE APPENDIX TABII 3-1. DENSITIES (NO./ CUBIC METER) 0F SOFT-SHELL
- CLAM (NYA ARENARIA) AND BLUE MUSSEL j (NYTIEUS EDUEIS) UMBONED VELIGERS i AT STATION P2 . . . . . . . . . . . . . . . A-74 4 .
i 4 EONARUS ANERICANUS (LOBSTER)-LARVAE APPENDIX TABLE 4-1. TOTAL NUMBERS COLLECTED OF LOBSTER (EONARUS 2
ANERICANUS) LARVAE BY LIFESTAGE FOR
< EACH STATION AND DATE AND SUMMED OVER STATIONS. . . . . . . . . . . . . . . . . . A-76
! APPENDIX TABLE 4-2. ABUNDANCE (NO./1000 SQUARE METERS) AND PER-i CENT COMPOSITION OF LOBSTER (FO#ARUS ;
AMERICANUS' LARVAE BY LIFESTAGE FOR i EACH STATION AND DATE AND SUMMED OVER STATIONS. . . . . . . . . . . . . . . . . . A-79 l
MACR 0 ALGAE
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APPENDIX TABLE 5-1. MEAN BIOMASS (GRAMS DRY WEIGHT PER SQUARE l
METER) 0F MACR 0 ALGAL SPECIES AT SUBTIDAL AND INTERTIDAL STATIONS DURING 1985 . . . . A-83 J APPENDIX TABLE 5-2. STANDARD DEVIATION OF BIOMASS (GRAMS DRY ~
WEIGHT PER SQUARE METER) 0F MACR 0 ALGAL SPECIES AT SUBTIDAL AND INTERTIDAL STATIONS'DURING 1985. . . - . . . . . . . .. A-91 1
j APPENDIX TABLE 5-3. PERCENT COMPOSITION OF BIOMASS (GRAMS DRY
- WEIGHT PER SQUARE METER) 0F MACROALGAL l
SPECIES AT SUBTIDAL AND INTERTIDAL STATIONS DURING 1985. . . . . . . . . . . . A-99 1
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PAGE APPENDIX TABLE 5-4. -STATISTICS (SUM,MEAN, STANDARD DEVIATION, NUMBER OF SPECIES) 0F MACROALGAL SPECIES BIOMASS (GRAMS DRY WEIGHT PER SQUARE METER)
AT SUBTIDAL AND INTERTIDAL STATIONS DURING 1985. ................... A-107
- APPENDIX TABLE 5-5. THE OCCURRENCE OF MACROALGAE FROM GENERAL COLLECTIONS AT ALL SUBTIDAL AND INTERTIDAL DESTRUCTIVE STATIONS DURING 1985. . . . . . A-108
' APPENDIX TABLE 5 -6. A. THE NUMBER OF UNIQUE TAXA RECORDED FROM ALL DESTRUCTIVE SUBTIDAL AND INTERTIDAL SAMPLES AND GENERAL COLLECTIONS BY STATION, 4 B. THE NUMBER OF TAXA AT SELECTED SUBTIDAL AND IhTERTIDAL STATIONS AND C. THE NUMBER OF TAXA PRESENT IN GENERAL COLLECTIONS IN MAY, AUGUST AND NOVEMBER. . . . . . . . . . A-112 APPENDIX TABLE 5-7. MEAN, MEDIAN AND RANGE OF PERCZhT COVER OF
, KELP SPECIES FROM TRANSECT STUDIES AT j SUBTIDAL STATIONS OVER THREE SAMPLING PERIODS. .......... . . . . . . . A-114
! APPENDIX TABLE 5-8. MEAN, MEDIAN AND RANGE OF THE NUMBER OF KELP
- SPECIES FROM TRANSECT STUDIES AT SUBTIDAL STATIONS OVER THREE SAMPLING PERIODS. . . . A-115 4
APPENDIX TABLE 5-9. A. MEAN PERCENT FREQUENCY OF DOMINANT "UNDERSTORY" ALGAE, B. TOTAL AND NUMBER PER METER SQUARE OF STRONGYLOCENTROTUS DROEBACEIENSIS AND C. MEAN PERCENT COVER i 0F SUBSTRATE TYPE FROM TRANSECT STUDIES AT SUBTIDAL STATIONS DURING 1985 . . . . . . . A-116 L
APPENDIX TABLE 5-10. PERCENT FREQUENCY AND PERCENT COVER PER 0.25 mr OF A. PERENNIAL, B. " EPHEMERAL" MACR 0 ALGAL SPECIES AND C. PRESENCE OF EPIPHYTES ON FUCOID ALGAE AT FIXED l INTERTIDAL NON-DESTRUCTIVE SITES. . . . . . A-118
- i. APPENDIX TABLE 5-11. PERCENT FREQUENCY OF SELECTED INTERTIDAL FAUNA IN THE FIXED 0.25 m* NON-l DESTRUCTIVE SITES AT STATIONS IMSL AND 4
SMSL. ..... . ... . . . . . . . . . . A-121 4
APPENDIX TABLE 5-12. FREQUENCY OF FUCOID ALGAE AT 'lVO FIXED TRANSECT SITES IN THE MEAN SEA LEVEL ZONE . A-122 !
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p-PAGE MARINE BENTH0S A?PENDIX TABLE 6-1. MEAN DENSITY (PER METER SQUARED) AND STANDARD DEVIATION OF SELECTED MACROFAUNAL SPECIES BY SAMPLING PERIOD AND STATION. . . A-124 APPENDIX TABLE 6-2. MEAN DENSITY (PER METER SQUARED), STANDARD DEVIATION AND COEFFICIENT OF VARIATION OF SELECTED MACROFAUNAL SPECIES BY STATION AND SAMPLE PERIOD . . . . . . . . . . . . . A-132 APPENDIX TABLE 6-3. MEAN DENSITY (PER METER SQUARED), STANDARD DEVIATION AND COEFFICIENT OF VARIATION OR PRESENCE OF COLONIAL MACROFAUNAL SPECIES COLLECTED IN AUGUST, 1985 . . . . . . . . . A-153 APPENDIX TABLE 6-4. MEAN DENSITY (PER METER SQUARED), STANDARD DEVIATION, COEFFICIENT OF VARIATION AND NUMBER OF SPECIES FOR STATIONS SAMPLED IN AUGUST, 1985. . . . . . . . . . . . . . . . A-168 APPENDIX TABLE 6-5. SURFACE TYPE AND ESTIMATED PERCENT COVER OF MACR 0 ALGAE (PER 0.0625 m") FOR MARINE SUBTIDAL AND INTERTIDAL BEhTHIC STATIONS FOR MAY, AUGUST AND NOVEMBER. . . . . . . . A-169 2
APPENDIX TABLE 6 6. MEAN DENSITY (No./m ) AND STANDARD DEVIATION OF #0BIOLUS #0BIOLUS OBSERVED AT MARINE SUBTIDAL TRANSECT STATIONS. . . . A-170 APPENDIX TABLE 6-7. ABUNDANCE OF SPIR 0RBID POLYCHAETES LIVING ON THE ALGA PEYLLOPEORA SP COLLECTED IN AUGUST 1985 AT MARINE SUBTIDAL STATIONS . . A-171 BENTHIC SELECTED SPECIES APPENDIX TABLE 7-1. MEAN ABUNDANCE (NO.PER SQUARE METER) AND STANDARD DEVIATION OF THE SELECTED SPECIES AT STATIONS IMLW, SMLW, 17, 35, 19 AND 31 . A-173 APPENDIX TABLE 7-2. MEAN SIZE (MM), STANDARD DEVIATION AND THE NUMBER OF INDIVIDUALS OF JASSA FALCATA MEASURED AT STATIONS 17 AND 35. . . . . . . A-177-APPENDIX TABLE 7-3. NUMBER OF JASSA FALCATA WITH EGGS OR BROOD AND PERCENT OF THESE FEMALES COMPARED TO TOTAL NUMBER MEASURED . . . . . A-178 xti
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PAGE APPENDIX TABLE 7-4. SIZE CLASS DISTRIBUTION (MM) 0F JASSA PALCATA INDIVIDUALS MEASURED AT STATIONS ,
17 AND 35 . . . . . . . . . . . . . . . . . A-179 APPENDIX TABLE 7-5. MEAN SIZE-(MM), STANDARD DEVIATION AND THE NUMBER OF INDIVIDUALS OF PONTO6ENEIA INERNIS MEASURED AT STATIONS 19 AND 31. . . A-180 APPENDIX TABLE 7-6. NUMBER OF PONTOCENEIA INERNIS WITH EGGS OR BROOD AND PERCENT OF THESE FEMALES COMPARED TO TOTAL NUMBER MEASURED . A-181 APPENDIX TABLE 7-7. SIZE CLASS DISTRIBUTION (MM) 0F PONT06ENEIA INERNIS INDIVIDUALS MEASURED AT STATIONS 19 AND 31 . . . . . . . . . . . . . . . . . A-182 APPENDIX TABLE 7-8. MEAN SIZE (MM), STANDARD DEVIATION AND THE NUMBER OF INDIVIDUALS OF A#PITROE R7BRICATA MEASURED AT STATIONS IMLW AND 5MLW. . . . . A-183 APPENDIX TABLE 7-9. NUMBER OF A#PITHOE RUBRICATA WITH EGGS OR BROOD AND PERCENT OF THESE FEMALES COMPARED TO TOTAL NUMBER MEASURED . A-184 APPENDIX TABLE 7-10. SIZE CLASS DISTRIBUTION (MM) 0F ANPITROE RUBRICATA INDIVIDUALS U.ASURED AT STATIONS 1MLW AND SMLW . . . . . . . . . . . . . . . A-185 APPENDIX TABLE 7-11. MEAN SIZE (MM), STANDARD DEVIATION AND THE NUMBER OF INDIVIDUALS OF NUCELLA LAPILLUS MEASURED AT STATIONS 1MLW AND SMLV. . . . . A-186 APPENDIX TABLE 7-12. SIZE CLASS DISTRIBUTION (MM) 0F NUCELLA LAPILLUS INDIVIDUALS MEASURED AT STATIONS IMLW AND SMLW . . . . . . . . . . . . . . . A-187-APPENDIX TABLE 7-13. MEAN SIZE (MM). STANDARD DEVIATION AND THE NUMBER OF INDIVIDUALS OF CANCER IRRORATUS MEASURED AT STATIONS 17 AND 35. . . . . . . A-188 i
APPENDIX TAlLE 7-14. SIZE CLASS DISTRIBUTION (MM) 0F CANCER i IRRORATUS INDIVIDUALS MEASURED AT STATIONS 17 AND 35 . . . . . . . . . . . . . . . . . A-189 l
APPENDIX TABLE 7-15. MEAN SIZE (MM), STANDARD DEVIATION AND THE l NUMBER OF INDIVIDUALS OF ASTERIIDAE MEASURED AT STATIONS 17 AND 35 . . . . . . . . . . . A-191 i
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PAGE APPENDIX TABLE 7-16. SIZE CLASS DISTRIBUTION (MM) 0F ASTERIIDAE INDIVIDUALS MEASURED AT STATIONS 17 AND 35. A-192 APPENDIX TABLE 7-17. MEAN SIZE (MM), STANDARD DEVIATION AND THE NUMBER OF INDIVIDUALS OF MYTILIDAE MEASURED AT STATIONS IMLW, SMLW, 17, 35, 19 AND 31 . A-194 APPENDIX TABLE 7-18. SIZE CLASS DISTRIBUTION (MM) 0F MYTILIDAE MEASURED AT STATIONS IMLW, SMLW, 17, 35, 19 AND 31 . . . . . . . . . . . .. . . .. A-195 APPENDIX TABLE 7-19. MEAN SIZE (MM), STANDARD DEVIATION AND THE NUMBER OF INDIVIDUALS OF STRONCYLOCENTROTUS BROEBACRIENSIS MEASURED AT STATIONS 19 AND 31. . . . . . . . . . . . . . . . .. A-197 APPENDIX TABLE 7-20. SIZE CLASS DISTRIBUTION (MM) 0F STRONGYLOCENTROTUS DROEBACRIENSIS INDIVID-UALS MEASURED AT STATIONS 19 AND 31 . . . . A-198 EPIBENTHIC CRUSTACEANS APPENDIX TABLE 8-1. MONTHLY CATCH PER UNIT EFFORT (15 TRAPS PER TRIP) AND PERCENT COMPOSITION OF MALES, FEMALES AND OVIGEROUS FEMALE RONARUS ANERICANUS AT STATIONS L1 (DISCHARGE) and L7 (RYE LEDGE). . . . . . . . . . . . . . . A-200 APPENDIX TABLE 8-2. MONTHLY CATCH PER UNIT EFFORT (15 TRAPS PER TRIP) AND PERCENT COMPOSITION OF LEGAL AND SUBLEGAL-SIZED RONARUS ANERICANUS AT STATIONS L1 (DISCHARGE) AND L7 (RYE LEDGE) . . . . . . . . . . . . . . . . A-201 APPENDIX TABLE 8-3. MONTHLY CATCH PER UNIT EFFORT AND PERCENT SIZE CLASS DISTRIBUTION OF RONARUS ANERICANUS. . . . . .. . . . . . . . . .. A-202 APPENDIX TABLE 8-4. MEAN SIZE (CM) AND RANGES FOR MALES, FEMALES AND OVIGEROUS FEMALES FOR CANCER IRRORATUS AND CANCER BOREALIS AT STATIONS L1 (DIS-CHARGE) AhT L7 (RYE LEDGE). . . . . . . . . A-203 i
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APPENDIX TABLE 8-5. OVERALL CATCH PER UNIT EFFORT AND PERCENT COMPOSITION OF t; ALES, FEMALES AND OVIGEROUS FEMALES OF CANCER IRRORATUS AND CANCER BOREALIS AT STATIONS L1 (DISCHARGE) AND L7 (RYE LEDGE) . . . . . . . . . . . . . . . . A-204 APPENDIX TABLE 8-6. MONTHLY CATCH PER UNIT EFFORT OF CARCINUS
- AENAS AND SEX RATIO INCLUDING FEMALES WITH EGGS . . . . . . . . . . . . . . . . . A-205 SOFT-SHELL CLAM APPENDIX TABLE 9-1. MEAN DENSITIES (PER SQUARE FOOT) AND STANDARD DEVIATION OF SOFT-SHELL SPAT CLAMS IN HAMPTON-SEABROOK ESTUARY . . . . . A-207 APPENDIX TABLE 9-2. MEAN DENSITIES (PER SQUARE FOOT) AND STANDARD DEVIATION OF JUVENILE AND ADULT
. SOFT-SHELL CLAMS IN HAMPTON-SEABROOK ESTUARY . . . . . . . . . . . . . . . . . A-208 APPENDIX TABLE 9-3. STANDING CROP ESTIMATES OF SOFT-SHELL CLAM NYA ARENARIA IN THE HAMPTON-SEABROOK ESTUARY FOR OCTOBER 1985. . . . . . . . . . A-210 APPENDIX TABLE 9-4.
SUMMARY
OF STANDING CROP ESTIMATES OF ADULT
- YA ARENARIA IN HAMPTON-SEABROOK ESTUARY, 1967-1985 . . . . . . . . . . . . . . . . . A-211 APPENDIX TABLE 9-5. SIZE CLASS DISTRIBUTION AND STANDARD DEVIATION OF #YA ARENARIA IN HAMPTON-SEABROOK ESTUARY IN OCTOBER, 1985 . . . . . A-212 APPENDIX TABLE 9-6. SEA WATER TEMPERATURE AND SALINITY ON SELECTED DATES IN HAMPTON HARBOR AND BROWN'S RIVER . . . . . . . . . . . . . . . A-214 APPENDIX TABLE 9-7. PARALYTIC SHELLFISH POISONING (PSP) T0XICITY LEVELS IN #YTILUS EDULIS FROM HAMPTON HARBOR. . . . . . . . . . . . . . . . . . . A-217 APPENDIX TABLE 9-8. DISTRIBUTION OF CLAM DIGGER NUMBERS AND PERCENT OF TOTAL ON EACH FLAT AND ESTIMATED NUMBER OF BUSHELS REMOVED . . . . . . . . . A-218 XV
SEABROOK ENVIRONMENTAL STUDIES 1985 DATA REPORT TECHNICAL REPORT XVII-1
1.0 INTRODUCTION
This report presents data collected in 1985 as part of the preoperational environmental studies for Seabrook Station. It includes a synopsis of field and laboratory methods, followed by tabular listings of the data. Simple statistics such as mean abundance and standard deviation are used to show data trends. A summary of findings for each section is also presented.
In 1985, as in previous years, plankton, finfish and benthic comm:inities were monitored in the Hampton-Seabrook estuary and nearshore marine environment. Because of the length and adequacy of the preopera-tional database, some sampling programs were reduced or suspended in 1985 with a subsequent focus on certain key programs. These studies are a continuation of preoperational studies which began in 1975 and were modified in July 1977. In 1982, further refinements in certain programs were made with respect to sampling frequency and location in order to improve the data base for the formal preoperational period which began January 1982. In March 1983, ichthyoplankton sampling was increased to four times monthly. Both spatial and temporal distributional patterns were the focus of all programs, with certain important selected species monitored most intensively.
1
2.0 FINFISH 2.1 ICHTHYOPLANKTON 2.1.1 Methods 2.1.1.1 Field Methods Ichthyoplankton samples were collected four times monthly during January through December 1985, (Table 2.1-1). The four sampling dates in each month were distributed among these four quarter-month periods:
1st quarter dates 1-8 2nd quarter dates 9-15 3rd quarter dates 16-23 4th quarter dates 24-31 Sampling dates in successive quarter-month periods were scheduled to be at least five days apart and no more than 10 days apart, weather permit-ting. In 1985, the fourth sampling period for July was collected one day early, giving the third quarter two sampling periods instead of one, and none in the fourth quarter.
In each sampling period, four samples were collected at each of two sites: nearfield and farfield (Stations P2 and P7, respectively; Figure 2.1-1). Samples were oblique tows taken at night with a 1-m diameter 0.505-mm mesh net. The net with depressor was set off the stern and towed for 10 minutes while varying the speed, allowing the net to sink to approximately 2 m off the bottom and to rise obliquely to the surface at least twice during the tow. The standard 10-minute tows were reduced to 5 minutes on 4 April and 17 April at Station P7 during high-plankton density to minimize net clogging. The volume filtered was estimated with a calibrated General Oceanics@ digital flowmeter mounted in the net mouth. Volume filtered ranged from 181 to 643 m3 and aver-3'
a 4 2 a e a a s
- -- 4+ pp+ su P- m.
aged 471 -3m . Upon retrieval, the net was washed down from mouth to cod end and the contents were preserved in 5% formalin buffered with borax.
At both stations, temperature, conductivity, and salinity profiles were made with a Beckman thermistor / salinometer (Model RSS-3).
~
l Duplicate dissolved oxygen samples and a salinity sample were also collected subsurface and near bottom. Dissolved oxygen samples were
- fixed in the field with manganous sulfate and alkaline iodide-azide.
Upon returning from sample collection, the fixed samples were
- immediately processed. Sulfamic acid was added and the dissolved oxygen I concentration (mg/t) was then determined titrimetrically by the azide modification of the Winkler Method (Strickland and Parsons, 1972).
. 2.1.1.2 Laboratory Methods L
i During 1985 only two of the four samples collected at the nearfield station (P2) were analyzed. The remaining six samples, two
, from the nearfield and four from the farfield station (P7), were held for possible processing at a later time. Sampics were subsampled with a l Folsom plankton splitter and sorted for fish eggs and larvae using a i dissecting microscope. Successive aliquots were analyzed until a minimum of 200 eggs and 100 larvae were sorted or until 200-400 m1 settled plankton volume was sorted. All eggs and larvae were identified to lowest practical taxon (usually species) and' counted. Some eggs, I
difficult to identify to species, were grouped with eggs of similar l appearance [e.g., cunner (Tautogolabrus adspersus) and tautog l (Tautoga onitis) were grouped with yellowtail flounder (Licanda l /errugines) and terced Labridae/Limanda eggs] .
f 4
l
d Notochord lengths were measured to the nearest 0.5 mm for nine
-selected species:
Ammodytes americanus, American sand lance Pseudopleuronectes americanus, winter flounder Limanda ferruginea, yellowtail flounder Gadus morhua, Atlantic cod Scomber scowbrus, Atlantic mackerel Tautogolabrus adspersus, cunner-
. Urophycis sp., hake Clupea harengus harengus, Atlantic herring Pollachius virens, pollock 1
Up to 20 larvae per species were measured from each sample.
An additional 10 larvae were measured for a species in a sample if the
! third highest length was more than twice the third lowest length, an j indication of higher than normal variation among the initial 20 measure-ments. This subsampling procedure assures that the number of larvae j measured is enough in about 95% of the cases (based on variances observed j in actual samples) to detect a 20% difference in mean length between stations or dates 80% of the time (power = 0.80) with 95% confidence (significance level = 0.05). .
2.1.2 Results
]
4 1
APPENDIX TABLE NO. DESCRIPTION l
1-1 Fish eggs, abundance by station, i species and date l 1-2 Fish eggs, percent composition by species and date 1-3 Fish larvae, abundance by station, i species and date i
1-4 Fish larvae, percent composition by species and date l
! 5 l
i
i i
l I
i I
l APPENDIX TABLE NO. DESCRIPTION 1-5 American sand lance larvae, lengths by date 1-6 Winter flounder larvae, lengths by date 1-7 Yellowtail flounder larvae, lengths by date 1-8 Atlantic cod larvae, lengths by date 1-9 Atlantic mackerel larvae, lengths by date 1-10 Cunner larvae, lengths by date 1-11 Hake larvae, lengths by date 1-12 Atlantic herring larvae, lengths by date 1-13 Pollock larvae, lengths by date 1-14 Hydrographic data collected on ichthyoplankton cruises 6 ,
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- ; = ICHTHY 0 PLANKTON STATIONS Q=LOBSTERLARVAESTATIONS Figure 2.1-1. Plankton sampling stations. Seabrook Environmental Studies, 2.985.
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TABLE 2.1-1. FINT ISil SAMPLING METHODS, JANUARY THROUCil DECEMBER 1983. SEABROOK ENVIRONMENTAL STUDIES, 1985.
PHOGRAM CFAR CHARACTERISilCS SAMPLE DESIGN SAMPLING SCHEDULE Ichthyo- 1-m d iameter, 0.505-mm 2 stations offshore, plankton mesh plankton net with 4 oblique tows per sta.(a) Jan-Dec, 4 times monthly, night depressor Ades i t Otter 9.8-m trawl 3 stations, offshore Monthly, night; yea r round l aruf Trawl 3.8-cm mesh body 4 replicates per sta.
- Juvenile 1.3-cm mesh cod end liner
! Tinrish Gill 30.5 by 3.7 m nets 3 sta tions, of f shore Monthly, two 24-hr periods, Net mesh sizes: 2.5, 5.1, 2 nets per sta. year round 10.2 and 15.2 cm ( I nea r-surface, ca 1 near-bottom)(b)
(a) Only two tows analyzed f rom Nearfield Station P2. fairfield Station PT samples not analyzed.
(b) One additional mid-water net used per station in February, June and October 1985, i
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i 1
2.2 ADULT FINFISH 2.2.1 Methods 2.2.1.1 Otter Trawls The offshore groundfish community was sampled monthly by trawling at night along Transects T1, T2 and T3 (Figure 2.2-1; Table 2.1-1) with a 9.8-m shrimp trawl (3.8-cm nylon stretch mesh body; 3.2-cm stretch mesh trawl bag; 1.3-cm stretch mesh cod end liner). Four replicates were taken at each transect. Transect areas are described in Table 2.2-1. The net was towed at approximately 1 m/s (engine operating l
at 900 rpm) for 10 minutes, with successive tows taken in opposite directions. The amount (volume) of drift algae caught in the trawl was recorded. Large volumes of macroalgae in the net make sampling very difficult and interfere with sampling efficiency; therefore, when this
[
situation occurred in two successive tows at one transect, sampling was
, terminated at that transect.
I s
2.2.1.2 Gill Nets Gill nets were set for two consecutive 24-hr periods monthly at three stations, G1, G2. and G3, shown in Figure 2.2-1 and described in Table 2.2-1. Sampling methods are shown in Table 2.1-1. Nets are 2 30.5 m x 3.7 m and are composed of four panels having stretch mesh dimensions of 2.5 cm, 5.1 cm, 10.2 cm and 15.2 cm. One net array, consisting of near-surface and near-bottom nets, was set at each station. All nets were set perpendicular to the isobath (Figure 2.2-1),
1 Additionally, one gill net per station was set at mid-depth in February, June and October. The nets were positioned on permanent buoys and tended daily by SCUBA divers.
l 9
2.2.1.3 Sample Analysis / Data Compilation catch data from each type of fishing gear used in this study were standardized to catch per unit effort. For the otter trawls, one unit was equated to 10 minutes of trawling; for the gill nets, a 24-hour set of one net (i.e., surface or bottom net) constituted one unit. Each transect or station was considered separately, as were the surface, mid-depth and bottom sets for the gill nets.
2.2.2 Results In five instances (March 21, May 23, June 20, July 19, October
- 24) the large volume of macroalgae made further otter trawl collections prohibitive at Transect T2, so only two tows were completed at that site on each of those dates. Also at Transect T2 two tows were not taken in August and all 4 tows were cancelled in September because of large concentrations of lobster gear in the area.
i APPENDIN TABLE NO. DESCRIPTION OTTER TRAWLS 2-1 Monthly catch by species 2-2 Overall catch and percent composition 2-3 Total catch and number of species collected monthly 2-4 Catch per unit effort for six selected species 2-11 Volume of macroalgae caught i
I 10 1
f L_________________._____________________._
APPENDIX TABLE NO. DESCRIPTION GILL NETS 2-5 Monthly catch, surface and off-bottom nets, by species 2-6 Catch in February, June and October; surface, mid-water and off-bottom nets, by species 2-7 Overall catch and percent composition over all depths l 2-8 Total catch and number of species collected monthly 2-9 Catch per unit effort for five selected species 2-10 Catch per unit effort for
- five selected species in February, June and October, mid-water nets l
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12 l
TABLE 2.2-1. DESCRIPTION OF FINFISH SAMPLING STATIONS. SEABROOK ENVIRONMENTAL STUDIES, 1985. I OTTER TRAWLS TRANSECT TOW DEPTH BOTTOM TYPE REMARKS T1 20-28 m sand Transect begins .5 mile southeast of Breaking Rocks Nun, 150-200 m 1 from rock outcrops. 1 T2 15-17 m sand, drift algae Scoured by tidal cur-with shell debris rents; large quanti-ties of drift algae, 100 m from inner sunk rocks. T3 22-30 m sandy; littered Located north of Great with shell debris Boars Head; just seaward of a cobble area (rocks 15-50 cm in diameter). j GILL NETS BOTTOM STATION NET DEPTH BOTTOM TYPE REMARKS I G1 20 m sand Seaward from rocky out-crop off Seabrook, G2 1* m sand Seaward of Inner Sunk Rocks. G3 17 m rock / cobble Offshore from Great Boars Head, I l 13
3.0 PLANKTON 3.1 BIVAINE LARVAE 3.1.1 Methods 3.1.1.1 Field Methods To monitor temporal distribution of the soft-shell clam #ya arenarla and the blue mussel #rtflus edulls, duplicate oblique or vertical not tows were made weekly from April 18 through October 15 at the nearfield (intake, Station P2; Figure 2.1-1) and farfield (north site, Station P7) stations. Sample collection continued until densities 3 of #ra arenarla fell below 1/m . The normal sampling procedure was a two-minute oblique tow using a 0.5 m diameter 0.076 mm mesh net, with a 15 lb. depressor attached. The net, towed at approximately 1/4-1/2 knot, was lowered to a depth of approximately 15 m (49 feet) in the first minute and returned to the surface during the second minute. The volume filtered, estimated with a General Oceanicas flowmotor, ranged from 7.5 to 13.0 m3and averaged 10.2 m3per tow. When not clogging occurred, vertical tows were taken using the same apparatus as for the oblique tows. The not was lowered to the bottom (approximately 15-18 m) and returned to the surface. Volume filtered, calculated by multiplying distance travelled up and down by not mouth area (0.196 m 2), ranged from 5.9 - 6.5 m3and averaged 6.2 m3. Upon recovery, net contents were thoroughly rinsed into a 1/2-gallon container and preserved with 2*. borax buffered formalin (with sugar added to enhance color preservation). Samples were kept refrigerated until processing. 3.1.1.2 Laboratory Methods Samples collected at Station P2 were analyzed for the umboned larvae of #ra arenarlo and #rt/lus cdults, those collected at Station P7 were concentrated and stored. When the total umboned larvae caught 15 w- + -_ _ - . - ___m _ _ _ _ _ _ - _ _
i ranged from 1-300, the entire sample was processed; when total numbers exceeded 300 the sample was split. The bivalve larvae were concentrated by a swirling motion and split from one to four times to arrive at a randomly selected fraction containing 200-600 umboned bivalvo larvae for 4 Adentification and enumeration. TWo sample fractions were enumerated { from each sample, each fraction originating 'f rom dif ferent halves of the i sample. 1 i 3.1.2 Results i j APPENDIX TABLE NO. DESCRIPTION 3-1 Densities (No./ cubic meter) of soft-
- shell clam (#ya arenaria) and blue mussel (Mytilus edulls) umboned veligers collected at the nearfield site (Station P2) i i
i l t i I 1 l 1 16 4
3.2 HOMARUS AMERICANUS (IDBSTER) LARVAE 3.2.1 Methods 3.2.1.1 Field Methods To monitor temporal distribution of Nomarus decr/canus larvae, neuston tows were made weekly from !!ay 20 through October 15 along horseshoe shaped transects approximately 1/2 mile (800 m) on a side, centered on the nearfield (intake; Station P2) and the farfield (Station P7) (Figure 2.1-1) stations. Collections were made with a rectangular, 1 mm mesh not (dimensions: 1 m x 2 m x 8 m) fitted with a General Oceanics3 flowmeter and a 40 lb. depressort tow speeds of approximately 1 m/sec (2 kn) were maintained. Effective sampling area of the not was 1.0 m2 . Town were made from the side of the boat in water clear of the boat's wake; the bottom of the net mouth was approximately 0.5 m below surface. Tow duration was 30 minutes; area sampled averaged 3578 m2 (ranging from 3301 to 4146 m ). Upon retrieval, the not was washed down from month to cod end and the contents emptied into five-gallon buckets. All debris was thoroughly rinsed before discarding and the remainder was concentrated to approximately one gallon. The samples were transported, at ambient seawater temperature, to the laboratory. 3.2.1.2 I,aboratory_ Methods Samplen were totally sorted for lobster larvae Stages I IV either by scanning the contents of the sample in a white enamel pan or by examining it under a starconcopic dissecting microscope at approxi-mately 10X magnification. I.obster larvae were staged and enumerated. 17 l
i 3.2.2 Results APPENDIX TABLE NO. DESCRIPTION 4-1 Total number of lobster (Nomarus americanus) larvae collected by station, date and lifestage and summed over stations 4-2 Abundance (No./1000 m ) and percent composition of lobster (Nomarus americanus) larvae by station, date and lifestage and summed over stations e 18 i
4.0 BENT 110S 4.1 MACROALGAE 4.1.1 Methods 4.1.1.1 Field Methods l Quantitative Sampling
- Quantitative sampling of subtidal and intertidal macroalgae were collected at six permanent stations during May, August, and l November; four of the stations (17, 19, 31, and 35) were subtidal and two were intertidal (IMLW. 5MLW) (Figure 4.1-1). General collections of macroalgal species (including fucolds and kelps) were compiled for subtidal and intertidal stations in May, August and November of 1985.
l In addition, macroalgan from MSL (mean sea level), and from tido pools j in the flLW (mean low water) and !!SL zones, were collected at each , intertidal station. In August, general collections also included crustose algal species. A summary of methods for macroalgal studies for 1
; 1985 is shown in Tabic 4.1-1.
Subtidal In-Situ Sampling Dominant subtidal "understory" algae were sampled non-j destructively at Stations 17, 19, 31 and 35 in April, July and October. 1 Six replicate band transects (1 m x 7 m) were surveyed along randomly selected compass azimuths radiating from the center of each station. Along each trannect line were 20 equally spaced markings (total number i por station = 120) under which the occurrence (e.g. presence / absence) of the dominant "understory" macroalgae (Chondrus cr/spus, Thyllophora sp. or Ptllota serrata) was noted. The substrate type (rock, cobb1c or I mixture) was also noted for each of the six transects at a given station. l 19
4 i All kelp species within each 1-m quadrat along the transects were identified, counted and percent cover was recorded; any Laninaria , sp. less than six inches and Agarun cribrosun less than threo inches were categorized as " juvenile" and not recorded. Based on the results , 2 of a power analysis (to detect a 50*. chaage in the mean, m = .95), only 12 one-m quadrats (2 per transect) at Stations 19 and 31 were
; sampled for Agarun cr/brosun. The number of urchins (Strongylocentrotus i
i droobachtens/s) present in each 1-m quadrat sampled was also noted. . Intertidal In-Situ Sampling Two permanent sites (0.25 m ) at It!SL and $?!SL (ono " baro" rock, one Fucus sp. covered) at each intertidal station were sampled non-destructively during April, July and December. The presence / absence of I fucold algal holdfasts (Fucus sp. and Ascophyllun nodosun) and
- gastropods (Acnaca tostudinalls, Littor/na sp. (Juvenile}, L. littorca, L. obtusata, L. 'saxatills and Nucella lap /11us) was recorded for each ;
} - of 16 subdivisions of the fixed 0.25-m' quadrat. The overall percent cover of the fuccid algae (prior to disturbance) within the quadrat was also noted. General observations over the sampling area were recorded and photographs taken of each tidal zone and permanent (?!!N, !!SL, ?!LW)
! o 0.25-m' site, j
The occurrence of "understory" algan (Chondrus cr/spus, C/gart/na sec114ta and " ephemeral" algau), Balanus sp. and ttytilidao
- within the 0.25-m2quadrats was determined by laying a 2.5-m line within J
j the fixed quadrat and the presence / absence of organisms under each of 50 points on the line was recorded. The line was laid three timos for a total of 150 records por quadrat. The percent frequency of opiphytes on the fucoid algao was also determined (before any algae was disturbed) within each quadrat by the " point contact" method. In this case, the 1 l 2.5-m line was laid within the 0.25-m quadrat once and the prosonce of epiphytes on the fucold algan under each of the 50 points on the line l was recorded. i ! 20 i- . _ _ _ _ _ _ - _ _ - _ _ _ - - _
Intertidal transects were also sampled in April, July and December to record the frequency of the fucold algae (Fucus sp. and Ascophyllun nodosun) over a larger band of the t!SL zone. A 9.5-m line was laid between two fixed points in the t!SL zone and the occur-rence of plants under each of 20 points on the line was recorded. Three ] replicate transects were recorded. i i i 4.1.1.2 Laboratory tiethods Quantitative samples were initially separated into plant and animal fractions (see Section 4.2-1). The macroalgal portion of each sample was preserved by freezing. Sample analysis included sorting, ! identification and dry weight biomass determination of each species (to
; 0.01 gms); plants were dried at 105 C for approximately 24 hours.
I f Species list > were compiled from collections (general and f destructive) in Play, August and November. The presence or absence of f crustoso algae was also recorded from general collections in August. l All crustose algal species, along with any other unknown species, were j identified by Dr. Arthur flathieson at the t'niversity of New ilampshire. j Voucher specimens are filed in the University of New flampshire lierbarium. In quantitative samples, taxonomic " lumping" was necessary in some cases: algae identified as Chaetonorpha sp. is a complex of l C. aerca, C. brachygona and C linun, Phyllophora sp. includes P. pseudoceranoides and P. truncata. Cystoclonjun purpureun v. cirrhosun was reported in the appendix tables as Cystoclonfun purpureun, since this is tho only variety reported in this locale and in fact may l be an ecotype. 1 4 I l 21
4.1.1.3 Data Analysis Quantitative Data i . The biomass value for each algal species from all destructive i j sampics was converted to biomass per square motor before any calculations I were mado. The mean, standard deviation and percent composition of biomass por square mater was determined for each algal species at each I station during each sampling period. The overall mean biomass por square mater (all species combined), standard deviation, sum and the f j number of species was computed for each station for each samplo period. I i A list was compiled of all macroalgal species identified from i general collections at both intertidal and subtidal stations sampled in 1 ! 1985. The total number of taxa at subtidal and intertidal destructivo I stations (combined) and for general collections was datormined for cach sample period and overall for 1985. i i Subtidal in-Situ Sampling i The mean, median and range of the number of plants and porcent i cover for each kelp species from non-destructivo subtidal stations was datormined based on a total of 42 one m2 quadrats at nach station. The total number of urchins and the number por one m quadrat was computed i j for each station. The mean porcent frequency of dominant "understory" l algal spectos was calculated for nach station; the number of marks along thn six transects under which a given specion was found was expressed as j a percentage of the total number of marks (120) at each station. The f mean percent cover of substrato typo (rock, cobble or mixture) was also i calculated based on a total of 42 onn m quadrats per station. i I 22
Intertidal In-Situ Sampling Intertidal non-destructivo data were tabulated separately for each 0.25-m samplo. The following values woro calculated:
- Porcent frequency (*. F) for fucold algae and gastropods a the number of subdivisions in which species <
occur divided by lo, multiplied by 100.
- Percent frequency (*. F) for opiphytes on fucold algao = the number of points under which epiphytes occurred divided by 50, multiplied by 100.
- Porcent frequency (*. F) for "understory" algan, Balanus sp. and Mytilldin a the averago number of points (of three replicaten) under which the species occurred divided by 50, multiplied by 100.
i
- Percent cover (*. C) = cntimato for tho entirn 0.25 m namplo.
j 4.1.2 Results APPENDIX TA!!!.E No. DECHIPTION GENERA!, C0!.f.ECTIONHi _DESTRl'CTIVES 51 Mean biomann by specion, station and sample period 52 Standard deviation of apocion biomaan by station and samplo period 53 Percent composition of npocios biomann by station and namplo period i 23 l
APPENDIX TABLE NO. DESCRIPTION CENERAI COLLECTIONS. DESTRUCTIVES i 5-4 Sum, overall mean biomass and standard deviation and number i of species J 5-5 List of species occurrence in 1985 5-6 Total numbers of taxa in 1985 SUBTIDAI, TRANSECTS 5-7, 5-8 Knips; mean, median and range of percent cover and number of plants j 59 Understory algan; mean percent 1 frequency of occurrence Urchins total number and number per
, o 1 one-m 1
j Substrate typo; mean percent cover I ' i
!NTERT!DA! NON DESTRUCTIVES 1 '
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l'igure 4.1 -1. !!cnthic marino sampling strtions. Seabrook Environmental Studien,19M. 25
TABLE 4.1 1.
SUMMARY
OF MEJ10DS FOR SUBTIDAL AND INTERTIDAL MACROALGAL STUDIES. SEABROOK ENVIRONMENTAL STUDIES, 1985. METHOD STATION MONTHS SAMPLED Destructive Subtidal Three 0.0625 m' quadrats 17, 19, 31, 35 May, August, November General collections 17, 19, 31, 35 May, August, November Intertidal Three 0.0625 m' quadrats 1HLW, 5MLW Hay, August, November General collections' 1MLW, 1HSL Hay, August, November SMLW, SMSL Hay, August, November Non Destructive Subtidal transect study b gpj,,, April, July, October Kolpa . cover) 17, 19, 31, 35 Dominant understory 17, 19, 31, 35 April, July, October algae" (*. frequency) Urchins (total #, #/m 8 ) 17, 19, 31, 35 April, July, October d April, July October Substrate type 17, 19, 31, 35 (*. cover) Intertidal Transects Dominant fucold algae 1HSL, SMSL April, July, December (*. f requency) a 26
1 i 4 TABLE 4.1-1. (Continued) i 1 HETHOD STATION MONTHS SAMPLED l i Non-Destructive (Continued) Intertidal Sampling Two 0.25-m 8 fixed IMSL, SMSL April, July, December quadrats yucold algae * (*. cover, IMSL,5HSL April, July, December j
. frequency)
Epiphytes on fucoid 1MSL, SMSL April, July, December j algae (*. f requency) i j All other algae present 1MSL,SMSL April, July, December l (*. frequency) l t 1 a l samples from tido pools also collected at each height. Agarun cribrosun, Alaria esculenta, Laminaria digitata, Laninaria saccharina. j
'Chandrus crispus, Phyllophora sp. (P. truncata/P. pseudoceranoides), Ptilota serrata.
j d rock, cobble, mixture.
*Ascophyllun nodosua, Fucus sp. (F. vesiculosus, T. distichus esp. edentatus, i 7. distichus esp. evanescens).
i i i l 1 I i l 1 27 l I,
4.2 MARINE MACROFAUNA 4.2.1 Methods 4.2.1.1 Field Methods Quantitative (destructive) sampics were collected at six permanent benthic stations during May, August and November; four of the stations (17, 19, 31, 35) were subtidal and two were intertidal (1MLW, SMLW) (Figure 4.1-1. Table 4.2-1). These stations represented three nearfleid (17, 19, 1MLW) and three farfield (31, 35, SMLW) stations. The sampling program for May and November was designed to provide greater resolution of temporal patterns of the dominant benthic taxa. In August, stations were sampled to provide an examination of the entire community (Table 4.2-2). 9 During the sampling program three 0.0625-m' replicate samples were taken at Stations 17, 19, 31, 35, IMLW and SMLW. All subtidal benthic stations were permanently marked by a large granite mooring block with an attached surface buoy. Subtidal sampling sites were randomly preselected by determining azimuth and distance (within 10 m) from the station block. Replicate samples were taken at randomly selected sites by placing the 0.0625 m frame on a horizontal rock surface (samples were stratified to horizontal hard substrate to reduce variability introduced by other substrate types). Epifauna and flora were scraped from rock surfaces and drawn through a diver-operated airlift into a 0.79 mm (1/32") mesh bag. The mesh bag was placed in a labeled plastic bag, brought to the surface, and sent to the laboratory for preservation and processing. All intertidal samples were collected in the Chondrus (mean low water) zone at Stations IMLW and SMLW. l 29 l
During August, all non-colonial organisms were identified to the lowest possible taxon and counted. When parts of animals were found; only heads, echinoderm central discs, hinged bivalves or gastropods with animals were counted. Colonial taxa were identified from destructive samples and listed as present with a count of zero. The abundance of spirorbid polychaetes at Stations 19 and 31 was estimated from 4 gram algal (Phy11ophora sp.) subsamples from each of the three replicates. The spirorbids present on the algae were counted and identified and the density was converted to an areal estimate based on the dry weight of the algal subsamples. 4.2.2 Results APPENDIX TABLE NO. DESCRIPTION DESTRUCTIVE SAMPLING 6-1 Mean density and standard deviation of dominant species by month and station 6-2 Mean density, standard deviation and coefficient of variation of dominant species for all months by station 6-3 Mean density or presence of colonial species, standard deviation and coefficient of variation at stations in August 6-4 Mean density, standard deviation, coefficient of variation and number of species at stations in August 6-5 Surface type and percent cover of macroalgae at benthic stations by month l 6-7 Abundance of spirorbid polychaetes on Phyllophora sp. in August 1 SUBTIDAL TRANSECTS 6=6 Mean density of Hodiolus modlolus 31
J 1 1
- Field notes were recorded concerning substrate type, percent i
cover of macroalgae inLthe frame and substrate microtopography within ). the frame. A general collection of macroalgal species was made within
! the station area during May, August and November collections (see I Section 4.1 on Macroalgae).
i j In situ Sampling C At Stations 17, 19, 31 and 35 (Figure 4.1-1; Tables 4.2-1, 4.2-2), six replicate 1-m x 7-m band transects were surveyed along I randomly selected compass azimuths radiating from the station's center in April, July and October 1985. Adult #odfolus modlolus were counted in each 1 m area along each 7-m transect. At Stations 17 and 35, l' 7 samples / transect were taken, whereas at Stations 19 and 31, because of consistently high' densities, only two 1-m 2 areas on each transect were I I
! surveyed.
I i 4.2.1.2 Laboratory Methods i I j All marine subtidal destructive samples were washed over a l 1.0-mm sieve prior to preservation. Organisms collected in all hard t substrate samples were first separated from the algae collected as part t of the sample. Faunal samples were then preserved in 6% buffered I formalin; algal samples were frozen. i During the May and November sampling periods, dominant species were identified and counted. Animals not designated as dominants were , left in the samples and archived for future reference. The dominant 4 species were determined from previous studies to be those taxa which are j ! the most useful as indicators of overall community type in the study area. i 30 l
TABLE 4.2-1. BENTHIC STATION LOCATIONS AND DESCRIPTIONS. SEABROOK ENVIRONMENTAL STUDIES, 1985. h DEPTH"' LOCATION a ft STATION LONGITUDE LATITUDE HARD SUBSTRATES 4 4.6 15.0 17 70 47'37" 42 54'00" Algae covered ledge (87%) and Corelline covered ledge (13%) i i 6.1 20.0 35 70 46'07" 42 57'22" Algae covered ledge (85%) and boulders (15%) 9.1 31.0 31 70 47'37" 42 58'04" Algae covered rocks (27%) mussel beds (60%) i and cobble (13%) l ! 12.2 40.0 19 70 47'13" 42 53'40" Algae covered ledge and boulders (60%) and I mussel beds (40%) 0.3 1.0 1MLW 70 47'41" 42 53'56" Algae covered ledge (100%) mussel bed (15%) mussel mat (90%) l 1.3 4.2 1MSL 70 47'46" 42 53'50" Algae covered ledge- . (100%) 1 0.3 1.0 SMLV 70 45'36" 42 58'19" Algae covered ledge (85%) boulder (15%) mussel mat (90%) mussel bed (10%) 1.3 4.2 SMSL 70 45'44" 42 58'12 Algae covered ledge
- (100%)
i i a depth below mean low water subtidal station. b depth above mean low water intertidal station. l 32
TABLE 4.2-2.
SUMMARY
OF METHODS FOR MARINE SUBTIDAL BENTHIC SAMPLES. SEABROOK ENVIRONMENTAL STUDIES, 1985. a SAMPLE TYPE STATION MONTH AMJA0ND Destructive Abundance of all taxa IMLW, SMLW, 17, 19, 31, 35 X or presence of colonial . species Abundance of unisort IMLW, 5MLW, 17, 19, 31, 35 X X X species O Abundance of Spirorbids , on Phyllophora 19, 31 X In Situ Non destructive Intertidal 1MSL, SMSL, X X X Intertidal Transects 1MSL, SMSL X X X Abundance of Nodiolus modiolus 17, 19, 31, 35 X X X a Sampling Months: April, May, July, August, October, , November, December.
. . ~
33
1 4.3 SELECTED BENTHIC SPECIES 4.3.1 Methods 4.3.1.1 Field Methods The selected species program was conducted as part of the marine benthos study to collect information about the structure of populations of important taxa in the study area. Nine taxa were selected for study in this program: the decapods cancer irroratus and Cancer borealis, the amphipods Pontogeneia inermis, Jassa falcata and Ampithoe ruoricata, the echinoderms Strongylocentrotus droebachiensis and Asteriidae, and the-molluscs Nucella lapillus and Mytilidae (includes Mytilus edulis and nodiolus modiolus). These animals were obtained from the destructive samples collected from subtidal Stations 17, 19, 31 and 35; and intertidal Stations IMLW and SMLW (See Section 4.2.1). Each species was analyzed at the depth where they are generally most abundant, including a nearfield (experimental) and a farfield (control) station. Three 0.0625-m repli-l cate samples wera taken at each station in May, August and November. 4.3.1.2 Laboratory Methods In the laboratory, animals were separated from the algae, washed over a 1 mm sieve and then identified and counted. A predetermined number of individuals for each species were then measured (according to methods specific to each species) to the nearest 0.1 mm. Female amphipods with eggs or brood were recorded as such to indicate potential recruitment to the populations, though actual egg or brood counts were not made. A summary of the stations sampled, number of individuals processed and method of measurement for each species are presented in Table 4.3-1. Damaged specimens were not included in the 1985 selected species data, i i Cancer borealis, found at Station 17, were-damaged and none occurred ! l at Station 35; therefore, selected species statistical data for C. borealis and Cancer spp. are not included for 1985. Abundances 35
4 2 for the 0.0625-m replicates were converted to number per square meter for all species studied in the selected species program before calcula-tions of mean and standard deviation were performed. Size-class data.is presented without transformation using the following guidelines: size-class <1 includes all animals less than 1.0 mm; size-class 1 includes animals between 1.0-1.9 mm; size class 2 includes animals between 2.0-2.9 mm, etc. 4.3.2 Results APPENDIX TABLE NO. DESCRIPTION 7-1 Selected species: mean abundance and standard deviation by species, station and month 7-2 Jassa falcata: mean size, standard deviation and number of individuals measured by station and month 7-3 Jassa falcata: number and percent of adults, juveniles and females with eggs or brood by station and month 7-4 Jassa falcata: size-class distribution (sum and percent) by station and month-7-5 Pontogencia inermis: mean size, standard deviation and number of individuals measured by station and month 7-6 Pontogeneia inermis: number and percent of adults, juveniles and females with eggs or brood by station and month 7-7 Pontogeneia inermis: size-class distribution (sum and percent) by station and month i 36 l
i APPENDIX TABLE NO. ' DESCRIPTION I. 7-8 Ampithoe rubricata: mean size,
. standard deviation and number of individuals measured by station.
and month 7-9 Ampithoe rubricata: number.and percent of adults, juveniles and females with eggs or brood by station and month-7-10 Ampithoe rubricata: s'ize-class
~
distribution (sum and percent) by
-station and month 7-11 Cancer irroratus: mean size, I standard deviation and number of individuals measured by station.
and month 4 7-12 Cancer irroratus:' size-class distribution (sum and percent) E by station and month 7-13 Mytilidae: mean size, standard deviation and number of individuals measured by station and month i { 7-14 Mytilidae: size-class distribution (sum and percent) by station and
; month 7-15 Nucella lapillus: mean size, standard deviation and number of individuals measured by station and month I ~
7-16 Nucella lapillus: size-class distribution (sum and percent) by station and month
, 7-17 Asteriidae: mean size, standard-1 deviation and number of individuals i measured by station and month 1
7-18 Asteriidae: size-class distribution (sum and percent) by station and month t 1 1 37 f
- APPENDIX TABLE NO. DESCRIPTION 7-19 Strongylocentrotus- .
droebachiensis:~mean size, standard deviation and numbe'r of individuals measured by station i and month 7-20 Strongylocentrocus droebachiensis: size-class I distribution (sum and percent) by I station and month t i l-l I I /> l 1 i. 1 38
TABLE 4.3-1.
SUMMARY
OF ANALYSES OF SELECTED BENTHIC SPECIES. SEABROOK ENVIRONMENTAL STUDIES, 1985. NUMBER a SPECIES STATIONS MEASURED PER STATION MEASUREMENT Pontogene/a /nermis 19, 31 50 individuals randomly length ( rostrum to selected f rom splits or telson), remale with replicate A (8,C as brood or eggs noted needed) Jassa ra/cata 17, 35 25 individuals randomly length ( rostrum to selected from splits of telson), female with replicate A (B,C as brood or eggs noted needed) Amp /thoe rubr/cata IMLW, SMtw all individuals measured length ( rostrum to in replicates A,B,C telson), female with brood or eggs noted Strongy/ocentrotus d' droebachiens/s 19, 31 all individuals measured length (test diameter) in replicates A,B,C Asteriidae I T, 35 all in.fividuals measured length (tip or longest in replicates A,B,C arm to disc center) Nuce//a tap ///us 1MWL, 5HLW 100 individuals selected length (spire tip to from replicate A (B,C as canal tip) needed) Mytilidae 17, 35, 19, 200 individuals randomly length (umbo to frontal 31, 1HLW, selected f rom replicates ma rg in) 5MLW A,B and C combined Cancer /eroratus all individuals measured width of carapace (outer Cancer borea/Is(b) 17, 35 in replicates A,B,C tooth to outer tooth) a Number or individuals required based on a power analyses of the data to achieve a statistically valid comparison between years, b Cancer bores //s did not occur at Station 35 and were damaged (therefore not measured) at Station 17.
4.4 EPIBENTHIC CRUSTACEANS 1 l 4.4.1 Methods 4 4.4.1.1 Field Methods The epibenthic crustaceans, Homarus americanus, Cancer borealis f and Cancer irroratus were collected at two areas from 1 June to 30 November 1985. Fifteen-trap trawls were fished approximately three times a week, weather permitting, near the discharge site (Station L1) and off Rye Ledge (Station L7) (Figure 4.4-1). Green crabs, Carcinus noenas, were collected at four locations, two traps per location, on j the perimeter of Flat 2 in Hampton Harbor (Figures 4.4-1, 4.4-2). The traps were fished biweekly except in February and March when historically no crabs have been found. e i , 4.4.1.2 Laboratory Methods i All Nomarus americanus and Cancer spp. crabs caught were enumerated, sexed and measured. In addition, egg-bearing females of each species were recorded. Cancer crab carapace width measurements were recorded to the nearest millimeter. Lobster carapace lengths were l l entered into 1/2" size classes ranging from 2" to 4-1/2" such that the 2" size class includes lobsters of carapace length <2-1/8", the 2-1/2" l size class includes 2-1/8" - <2-5/8" carapace length, the 3" size class i includes 2-5/8" - <3-3/16" carapace length 3-1/2" size class includes 3-3/16" - <3-5/8" carapace lengtl,:, 4" size class includes 3-5/8" - l <4-1/8" carapace length, 4-1/2" dize class includes carapace length i j . 4-1/8" and greater. The green c(abs, Carcinus maenas, were I enumerated, sexed and measured add egg-bearing females were recorded, t .
, e I
?
! 41
J 4.4.2 Results APPENDIX TABLE NO. DESCRIPTION AMERICAN LOBSTER , 8-1 Lobsters, catch per unit effort; percent composition by sex and reprcductive condition 1 8-2 Lobsters, catch per unit effort; i legal versus sublegal size classes 3 i , 8-3 Lobsters, catch per unit effort; percent composition by size
- class ROCK CRABS 8-4 Cancer spp., mean. size by sex and reproductive condition 8-5 Cancer spp., catch per unit
- effort; composition by sex and reproductive condition 1
GREEN CRABS f 8-6 Carcinus maenas, catch per unit effort; percent composition d by sex and reproductive condition l 4 4 'l 1
;t 1 ! 42 l
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@=CLAMFLATS X = GREEN CRAB TRAP STATIONS h h = ESTUARINE SALINITIES Figure 4.4-2. Hampton-Seabrook Estuary salinity, temperature, soft-shell clam (A'yc crev.cric!
and green crab (Ccroir.us mcer.cs) sampling stations. Seabrook Environmental Studies, 1985. .
- - - -- . -~ _ - .. -. -- , --
o. 5 4.5 MYA ARENARIA t 1 J
- Information on th'e larval stage of Mya arenaria is-
- contained in Section 3.1 (Bivalve Larvae) of this report. Similarly, j information on the principal non-human predator on Nya arenaria, the l green crab, Carcinus maenas, is contained in Section 4.4 (Epibenthic 1
l Crustaceans). i i j 4.5.1 Methods l j As in past years, the five largest flats in the
- Hampton-Seabrook Estuary (Figure 4.4-2) were surveyed in the late fall to obtain information on #ra arenaria spat and adult clams. Aerial 3
photographs taken of the flats in September,1984 at mean low water were used to construct sampling maps. Using those maps, flat acreages were 3 calculated using an electronic planimeter with digital readout. l l A statistical power analysis (Sokal and Rohlf, 1969) was l performed on log transformed 1984 data (NAI 1984) to determine the l number of randomly chosen sampling stations needed on each flat to adequately characterize soft-shell clam populations. Adequacy was l ! initially defined as the ability to detect a real 50% change in the log i mean of clam density per flat with 90% confidence (50*. AX,a = 0.10). l To meet this confidence level for spat, forty-five stations were 1 i sampled on Flat I and twenty-five each on Flats 2,3,4 and 5 (Table 4.5-1). , The number of stations sampled for adults was sixty-five on Flat 1, j forty on Flat 2 and twenty-five on Flat 4. Flats 3 and 5 were not ! sampled for adults. Low densities of adult clams coupled with lack of 3 use by recreational clammers led to the decision to drop these stations. After the initial sampling was complete, another power analysis was f performed on the 1985 data. Because of high within-flat variability in ! clam density, additional samples were collected, in early November, to meet the sampling adequacy criteria (Table 4.5-1). I I 45
l l l l To select the sampling stations, the intersecting points of rectangular (x,y) coordinates (chosen from a random numbers table) were plotted on charts of each flat until the final quota of stations was attained. Stations which fell in areas known to be occupied by dense mussel beds or flooded at mean low water were disqualified and replaced by other coordinate generated stations. Stations were located in the field by compass bearing and distance from a permanently marked central reference point. 4.5.1.1 Spat Surveys During the annual Hampton-Seabrook clam flat survey, spat samples were collected at the above described stations using a four inch, inside diameter, PVC pipe corer. At each station three replicate 4 inch deep cores were extracted from the sediment within the confines of the adult sample area. The samples were placed into a plastic bag with an identifying tag, and transported to the field laboratory. There they were washed through a 1 mm mesh sieve, and the Nya arenario spat were removed from the remaining sediment, enumerated and measured to the nearest 1 mm. The annual sampling program, due to the randomization of sampling ef fort, provided a representative quantitative estimate of spat densities for the Hampton-Seabrook flats as a whole, which included areas both favorable and unfavorable to spat settlement. 4.5.1.2 Adult Surveys Adult #ya arenaria samples were collected in conjunction with the spat samples during the annual late fall clam flat survey on flats 1, 2, and 4 To delineate the adult sample area, a frame, two feet by one foot, outside dimension, was placed on the substrate, outlined, and dug to a depth of 18 inches. Juvenile and adult soft-shell clams (shell length > 26 mm) found during excavation were put into a plastic bag with an identifying tag and transported back to the 46
field laboratory. There the clams were enumerated and measured to the nearest 1 mm. From these measurements, length class distributions were generated (Figure 4.5-1). Based on sizes, individual sample counts were converted'to biomass estimates (bushels per acre) using a table of clam volumes provided in Belding (1930). To express results in terms of standing crop (bushels of clams on the entire flat), the biomass estimate was multiplied by flat surface area (acres). (Appendix Table 9.3). 4.5.1.3 Temperature and Salinity At high and low slack water, temperature measurements and salinity readings were taken weekly in Hampton Harbor and Brown's River, (Figure 4.4-2). Salinities were determined from the refractive index of the samples using an American Optical @ refractometer. Temperatures were taken with a laboratory grade thermometer, reading to 0.1'C. I 4.5.1.4 Clammer Counts The impact of human predation on the #ra arenaria habitat was gauged every Friday by recording the number of clam diggers on each flat approximately one half hour before low slack tide. Counts were taken at this time based on data obtained in 1984 which showed the 1 i highest numbers of clammers were on the flats just before low tide. Some Saturday counts have also been made over the years. The total number of digger trips in a season is the sum of Friday trips plus a Saturday estimate based on the relationship between Friday and Saturday counts. I I ! 47 l
-_-__a - - _ - _ _ - - _ _ _ . _ _ - _ - _ - _
4.5.1.5 PSP Toxicity Levels Paralytic shellfish poisoning levels in #rtilus edu11s in Hampton Harbor were acquired from the New Hampshire Division of Public Health Services. 48
4.5.2 Results APPENDIX TABLE NO. DESCRIPTION 9-1 Mean densities and standard deviation (per sq. ft.) of spat Nya arenaria in i Hampton-Seabrook Estuary October, 1985 9-2 Mean densities and standard deviation (per sq. ft.) of juvenile and adult Nya arenaria in Hampton-Seabrook Estuary October, 1985 9-3 Standing Crop estimates of soft-shell clams (#ya arenaria) in Hampton-Seabrook Estuary October, 1985 9-4 Summary of Standing Crop estimates of adult Nya arenaria, 1974-1985 in Hampton-Seabrook Estuary October, 1985 9-5 Size-class distribution of #ya arenaria in Hampton-Seabrook Estuary October, 1985 l 9-6 Seawater temperatures and
; salinities in Hampton Harbor and Brown's River, January-December, I 1985 9-7 Paralytic shellfish poisoning (PSP) toxicity levels in l Nytilus edulis from Hampton Harbor, 1985 9-8 Distribution of Clam Diggers- i numbers and percent of total on each flat, and estimated number of bushels removed, from January ,
through May and September I through December, 1985 in ( Hampton-Seabrook Estuary l , 1 t l l 49 I l
FIGURE NO, DESCRIPTION 4.5-1 Size class distribution of Nya arenaria in Hampton-Seabrook Estuary, log transformed density i f I l 50
1
+6 19 1
. +2 _
Y - 9 R ! A + 8 U !8 T , S5 - E8 ! 9 +14 K1 t8 O , l OS !0 RE BI ! 8 AD ! EU 16 ST !7 S 1 N ! OL , 2 IA !1 PT MN ! AE ! HM 8 16 ) N NO ! M
.IR 1 M 1 I 4 (
AV !6 S
- IN
- 5. R E !
S A 50 - 4 A NK I6 l C EO 5 E R AR RO 5 6 / F U D I5 l S GAA l
}
I YE F MS l2
] $
f , l OY l l8 T NI loS N l I} is e iE ri UD I f T I UD I BE Io s IM I i RR I TO $ SF $6 IS I3 DN I A I SR $2 S1 - 3 A - LG - CO + 8 L . 2 E Z I. I + 4 S - 2
+ 0
_ 2 I
}6
. 1 I.
+ 2 I1 I.
}8 I
I o is 4
+ 0 i + I1IIIl1l1IlI liI h' ,u +,llI l ggi 0 0 0 "
0 0 1 0 1 1 9 8 I' R 5* UMion
=
f
m TABLE 4.5-1. NUMBER OF #YA ARENARIA SAMPLES COLLECTED DURING THE ANNUAL FALL SURVEY IN HAMPTON-SEABROOK ESTUARY, 1985. SEABROOK ENVIRONMENTAL STUDIES, 1985. SPAT ADULT Flat orig. add'tnl. total orig. add'tnl. total 1 45 26 71 40 65 105 2 25 - 25 40 11 51 4 3 25 - 25 - - - 4 25 - 25 25 11 36 5 25 8 33 - - - All 145 34 179 105 87 192 o 52
1 5.0
SUMMARY
5.1 ICHTHY 0 PLANKTON 8
- 1. Overall abundances (annual mean of 8566/1000 m for all species combined) of fish eggs in the nearshore waters off
' Hampton, N.H. in 1985 were 67*. higher than those observed in 1984 (5131/1000 m'), the lowest abundance in the nine-year period 1976-1984. The 1985 abundances however were still 27*. Iower than the average for 1976-1984 (11709/1000 m').
- 2. The three taxa which contributed the highest numbers of eggs in 1985 were cunner /yellowtail flounder (Labridae/Limanda),
hake (Urophycis sp.), and Atlantic mackerel (Scomber scombrus), together accounting for 89% of eggs collected during the year. These three groups have consistently been dominants in past years. Cunner /yellowtail flounder egg abundances increased 76*. (from 2562 to 4506/1000 m'), hake eggs increased 61% (from 1508 to 2442/1000 m'), and Atlantic mackerel eggs increased 95% (from 468 to 916/1000 m3 ) over 1984 abundances.
- 3. Windowpane flounder (Scopthalmus aquosus) eggs. more abundant in 1985 than in any of the previous nine years (189/1000 m 3 ), increased 171*. over the 1984 abundance of 69/1000 m' This increase coupled with the increases in cunner /yellowtail flounder, hake, and Atlantic mackerel eggs accounted for the increase in total abundance over 1984. Other species were present in numbers within previously observed ranges.
- 4. Overall abundance of fish larvae was lower than average in 1985. Although 1985 abundances (699/1000 m') increased 15% over 1984 abundances (608/1000 m'), they were still
< 56*. Iower than the average for 1976-1984 (1601/1000 m 2).
I 53
d
- 5. The most abundant larvae were Atlantic mackerel (Scomber scombrus), American send lance (Ammodytes amcricanus),
and winter flounder (Pseudopleuronectes americanus), together accounting for 47% of the larvae collected during the year. Atlantic mackerel larvae, the most variable during the past ten years of sampling, was the most abundant species in 1985, with an abundance of 128/1000 m'. Only once within the past ten years was the abundance higher. This was in 1980 when the abundance was 600/1000 m'. Cunner (Tautogolabrus adspersus) typically one of the three most numerous larvae ranked fifth l in 1985 with an abundance of 63/1000 m', down 55*. from the I 1984 abundance of 145/1000 m'.
- 6. The seasnail (Liparts atlanticus), usually found in low abundances in the Hampton, N.H. area, was the fourth ranked species in 1985, with an abundance of 64/1000 m'. At no time during the past ten years was the abundance higher.
- 7. There were no species of eggs or larvac new to the study area identified during the 1985 sampling year.
- 8. The season of occurrence and time of peak abundance were similar to previous years for all species except one. For Atlantic cod (6adus morhua) larvae, the time of peak abundance has normally been in June or July. Peak abundance in 1985 occurred in early December.
j
- 9. Temperatures were vertically homogeneous at both stations frcm January through late April and late October through December.
A thermocline first occurred in March, dissipated, and then re-developed in late April, attaining its steepest gradient in mid July (averaging 6.75'C difference between surface 54
, ~. . . - . - - . -. - -. - - . . . --
A 4-f and bottom depths [maan of 17.5 m) at the two stations on l July 10) and in mid August (averaging 7.1'C difference on ' August 12). The'thermocline continued through October, j
- 10. Salinity levels at Stations P2 and P7 were spatially j similar throughout the year. However, surface salinities i were lower than bottom salinities between July and i
j mid-November, in contrast to 1983 and 1984 when this j salinity profile occurred between January and September. A maximum surface-to-bottom differential occurred in ] I September and October (1.1 ppt) at P2 and in July (2.2 ppt) at P7. Minimum surface salinities occurred in l September at P2 (30.7 ppt) and in July.at P7 { (29.4 ppt). Maximum surface salinities occurred in February 7 i at P2 (33.5 ppt) and in February and March at P7 (33.3 ppt). 4 i
- 11. Highest values of dissolved oxygen (up to 12.0 mg/1) at I
j Stations P2 and P7 were observed in January through April, ; I whereas lowest values (down to 6.3 mg/1) occurred in August . l through October at P2 and August through December at P7. ! } These values represent perce't n saturation levels ranging 1 j f rom a low of 69*. to a high of 116*.. k'hile dissolved oxygen surface to bottom distributions were homogeneous during the winter and spring, they exhibited greater f variation during the summer and fall with both stations ( showing their greatest surface to bottom differences in : September (reaching an average difference of 2.25 mg/l ! over 17 m for the tw stations on September 25)'and 6 October (reaching a 2.65 mg/l difference on October 21). !
; t
} t 55 * ! 6 i i
5.2 ADULT FINFISil 5.2.1 Otter Trawl
- 1. Total otter trawl catch (5443 individuals) decreased 23*.
from the 1984 value (7083 individuals). Overall CPUE
- (42.5) dropped below the lowest previously recorded value (50.0) which occurred in 1977. Catches were lowest during the winter months and greatest in spring and j summer as in 1984. Total number of species in 1985 was i low in January and February and high in October and November. Numbers of' taxa were seasonally more variable
- than in previous years.
- 2. Yellowtail flounder, longhorn sculpins, and hake species dominated the trawl catches with 64*. of the total catch; this was similar to prior years. Skates, winter flounder and windowpane flounder comprised another 25?.. Similar distributions of dominant species have been recorded in previous years.
- 3. As in previous years, trawl catches for yellowtail flounder, hake species and cod were higher at Transects T1 and T3 while catches for winter flounder and rainbow smelt were greater at Transect T2.
- 4. The catches per unit effort for yellowtail flounder, hake species and winter flounder were similar to previous years. Overall CPUE for Atlantic cod was lower than previous years and most similar to 1977. Catches for 1
I rainbow smelt was noticeably lower than any previous ! years sampled. I l 56
1 3 5.2.2 Gill Nets i i' j 1. Total 1985 gill net catch (496) was less than half the 1984 total (1246), primarily because nets were fished monthly instead of twice per month. Similar to previous years, i i total number of species was highest spring through early l i winter when most of the pelagic fish were in the area. Total number of species was 23% lower than 1984. Overall j catch was down during the past two years (1984-85) mainly
! because of reduced Atlantic herring catches.
i i 1
; 2. Atlantic herring and pollock dominated gill net catches, j together comprising 47*. of the total catch. Atlantic 1
mackcrol, blueback herring and menhaden comprised another l 25%. The low relative contribution of Atlantic herring , (25%) was similar to levels in 1984; because of these low l. relative values, pollock increased in relative'contribu-
]
a tion to its highest level (22%) recorded since the beginning of the study in 1976. No' substantial station difference in CPUE was observed for the dominant pelagic species in gill nets in 1985, as observed previously. t
}.
l 1' i f i i i 1 i I I I r l l l
\
! 57 i I j
5.3 FlYA ARENARIA (SOFT SHELLED CLA51) AND ?!YTILUS EDULIS (BLUE
?!USSEL) LARVAE
- 1. Nytllus edulis was more abundant than Nya arenaria throughout the 1985 bivalve larvae sampling program (conducted weekly,18 April-15 October) until late September when nya arenarla became only slightly more abundant. #rtflus edu11s had three strong pulses within one sustained peak during the sampling period: late June (10,870 umboned larvae per m'), mid-July (8,096 per m') and late July (7.788 per m 8). Nya arenaria first appeared in mid-June but d:d not peak until mid-August. This peak was sustained until late September; the maximum mean density (63 umboned larvae per cubic meter) was recorded on August 12th.
Numbers of #ya arenaria umboned larvae fell sharply the last two weeks of the program, 7 October and 15 October, to below one per cubic meter. Abundances of Mytilus edu11s were still over three per cubic meter at this point.
- 2. The minor early summer peak of #ya arenaria larvae observed in 1978-1981 and 1984 did not occur in 1982, 1983 or 1985. Major pulses in 1985 occurred in mid to late summer. The earliest nya peak recorded was on 8 June 1978 (296 umboned larvae per m') while the heaviest early summer peak l
recorded occurred on 2 July 1979 (481 per m'). The lowest yearly population mean of Nya larvae occurred in 1985 with 9 per m 3, followed by 1984 (30 per m ) and 1983 3 (52 per m ). The highest recorded yearly mean occurred in 1982 with 243 umboned larvae per cubic meter. 58
1 , i 5.4 HOMARUS AMERICANUS (LOBSTER) LARVAE-
- 1. Total numbers of lobster larvae collected (all stages l
combined) in 1985 were 68 larvae at Station P2 and 143
- larvae at Station P7, for a total catch of 211 larvae.- During-
! the eight years of collection at P2, only 1980 showed a Icv:.r l total abundance (No./1000m2 ) than was observed in 1985 (18.6/1000mm ). In the four years of collection'at-Station P7, only 1984 showed lower total abundances of l lobster larvae than did 1985 (42/1000m 2 ).- Station P7 has shown slightly higher abundances than Station P2 < consistently during the four year period when both stations were collected (1982-1985). 1 i
- 2. All four planktonic stages of lobster larvae were collected in 1985 as in 1979, 1981, 1983 and 1984. At Station P2 Stage IV
{ l larvae predominated in. 1978, 1981, 1982,~1984 and 1985, while j Stage I larvae predominated in 1979 and 1980 and Stages I.and II predominated in 1983. At Station P7, Stage IV was the most l dominant stage from 1982-1985, although Stage I was only i slightly less abundant than Stage IV in 1983. In 1985, a f total of 63 Stage IV larvae were collected at Station P2, l comprising 92.6*, of the total catch at Station P2. Stage IV l zoea comprised 88.8*. of the total catch at Station P7, with 127 larv'ae. i
- 3. Lobster larvae abundances (No./1000 m 2 ), both stations l combined, showed only one significant peak'in 1985. On August 5 all stages of larvae were collected, Stage IV predominating,
- with a total of 36/1000 recorded. 8 A secondary pulse of Stage IV zoea occurred on September 9. Maximum abundances at l
each station were recorded on the same date. I
- 4. Peak larval abundances of Noearus americanus have his-torically occurred from as early as June in 1983 (primarily 59 l
Stage I) to as late as September 8, 1981 (primarily Stage IV). Peak abundances have most frequently occurred in July, as in 1979, 1980 and 1982 and in August, as in 1978, 1984 and 1985.
- 5. In 1985, lobster larvae were collected on 41% of the sampling dates at Station P2 and on 54*. of the sampling dates at Station P7. In 1984 the percentages were 44?. at Station P2 and 47% at Station P7.
60
5.5 MACR 0 ALGAE
- 1. The total numb'r e of taxa identified in May, August and November general collections was 42 at.subtidal stations (17, 19, 31 and 35) and 62 at intertidal stations (IMLW, 5MLW). The subtidal stations were composed of 19%
Chlorophyta, 21% Phaeophyta and 60% Rhodophyta. In comparison, the community composition was 23% Chlorophyta, 29% Phaeophyta and 48% Rhodophyta at intertidal stations. These trends are consistent with those observed in 1984. i
. 2. At subtidal stations (17, 35, 19, 31 combined) the I highest overall mean dry-weight biomass (a11' species combined) occurred in August, while the lowest biomass i was observed in November. The highest mean dry-weight biomass was recorded at Station 17 (in August) while_the-lowest mean dry-weight biomass was found at Station 19 (in May).
- 3. At intertidal Stations 1MLW and SMLW, sampled in.1985, f the highest mean dry-weight biomass was recorded in August and May respectively. The lowest mean dry-weight biomass occurred in November at Station 1MLW while at-Statica 5MLW the lowest mean dry-weight biomass was I observed in August, t
- 4. Chondrus crispus and Phyllophora sp. had the highest and second highest mean dry-weight biomass at subtidal stations in 1985. As in past years, a general trend of decreasing dry-weight biomass with increasing depth was observed. Chondrus crispus was the dominant algal species at both Stations 1HLW and SMLW. Cigartina stellata 61
and Co rallina officinalis had the second and third highest mean dry-weight biomass respectively at intertidal sta-tions in 1985. l
- 5. In the subtidal transect survey, Laminaria saccharina was most abundant.at shallow subtidal Stations 17 and 35.
Laminaria digitata was also. common at Stations 17 and 35; however, it was most abundant at the mid-depth sub-tidal Station 31. Agarum cribrosum was the most pro-lific at deeper Stations 19 and 31. -Alaria esculenta was the least abundant of the kelps, present only at Station 31. The overall abundance of Strongylo-centrotus droebachiensis recorded in the subtidal transect survey was-very low.
- 6. Based on frequency of occurrence, dominant "understory" algae in the subtidal transect surveys showed depth-related differences. Consistent with previous years, Chondrus crispus was most common at the shallow subtidal stations (17, 35). The percent frequency of Phy11ophora sp. was highest at the mid-depth (31) and (19) stations.
The highest percent frequency for Ptilota serrata occurred at subtidal Station 19.
- 7. Of the fuccid algae examined in the mean sea level zone, Ascophy11um nodosum had the highest percent frequency in April and July at Stations 1MSL and SMSL respectively.
Fucus vesiculosus reached the highest percent fre-quency in December at Station IMSL, while at Station SMSL the percent frequency of F. vesiculosus was relative-ly consistent during the three sampling periods in.1985. Fucus distichus ssp. edentatus and Fucus sp. were only noted at Station IMSL and the percent frequency for these species was substantially lower than A. nodosum and F. vesiculosus at the same station.
! 62 1
(
---n - - c..,
V 4 T
- 8. Two fixed quadrat samples (one " Bare" rock and'one T
"Fucoid" algad covered) in the mean sea level zone (MSL) kere monitored for seasonal and spatial differences. The following observations were made:
Spring (April) - The number-of " ephemeral" macroalgal I species observed was high, with most species present at Station IMSL. Balanus sp. had set.at:both stations.
.w Several gastropods at both Stations IMSL and SMSL were sti1Il in crevices and not actively foraging. The frequency of Mytilidae was con,siderably higher at Station '
iMSL. ? Summer (July) - There were no " ephemeral" algal species 1
- present at Station SMSL in July. The overall abundance of the' dominant perennial algal species was higher at Station SMSL. The abundance of Fucus vesiculosus was substantially higher in July than'in April at Station I 1MSL.
The percent frequency of Mytilidae at Station IMSL "Fucoid" algae covered site decreased in July while the percent frequency at the " Bare" rock site increased. There were no Mytilidae observed at Station SMSL. Most gastropods were more active at the " Bare" rock site at both stations, however, Nucella lapillus, was only present at tlin "Fucoid" algae cove' red r.bic. ,
. 4 4
Late Fall (December) - There were only three ephemeral species recorded in December (two at Station IMSL and one- , at Station SMSL). The percent frequency of the dominant 1- perennial alga Fucus vesiculosus decreased substantial- J ly at Station IMSL, while the percent frequency of-F. vesiculosus at the " Bare" rock site at Station SMSL reached 100*4 in December. The abundance of I
- i 63
.w . . . .
3; .;
*s;.. g a w s '
, 1 .
+
s s
, MV t
_ /
-i ,
Balanus sp. was substantially lower at the " Bare" rock site at Station ~1MSL. Balanus sp was still x
. abundant at Station SMSL. There was an. increase in the
- i - frequency.of Mytilidae at the "Fucold" algae covered site
*z at Station IMSL, however, there were no Mytilidae
, observed at the " Bare" rock site. LThere were no Mytilidae noted at the "Fucoid" algae covered site at Station SMSL and only a small percent frequency noted at the " Bare" rock site. The overall percent frequency of
. gast'ropods was higher at the " Bare" rock site for both s .- .-
g . Stations 1MSL and SMSL. , i b i
^r e
ax . s. i
'9 5
t , B 4 N 'k.
/
D 6 1 l r i ( p , , i .. 64
-. _-w . -w e -
yw-- v 1v ye p,a-.4-- e.- e - .?gi . .w. - , +., 4-w.
5.6 MARINE MACROFAUNA
- 1. In samples collected in August 1985, the most abundant taxon subtidally was Mytilidae. It had the highest mean density at each station except at the shallow stations, 17 and 35, where Pontogencia inerals and Lacuna vincta, respectively, had the highest densities. At the shallow subtidal stations, 17 and 35, Ischyrocerus anguipes (17), Jassa falcata, Idotea phosphorea, Idotea balthica (35), L. vincta (17)
~
and P. inermis (35) were also dominant. At mid-depth stations, 19 and 31, Anomia sp., Elate 11a sp., L. vincta (31), P. inermis (31), Achclia spinosa (19) and Molgula sp. were important numerically.
- 2. At intertidal Stations 1MLW and SMLW the abundant taxa were Mytilidae, Turtonia minuta, Nucella lapillus, Lacuna vincta, Niatella sp., Jaera marina, Oligochaeta, Anomia sp. (1MLW),
Fabricia sabella (SMLW), Gammarellus angulosus (1MCW), Gammarus oceanicus (SMCW) and Littorina littorea (SMCW).
- 3. The dominance of Mytilidae at all stations was consistent with previous years. With the exception of Station 31, densities were lower than in 1964. Mytilidae were most abundant at the mid-depth subtidal Station 31 and represented not only a dramatic increase (94%) in density from 1984, but also the greatest density of Mytilidae recorded at any station. Intertidal Stations 1MLW and SMLW supported the next highest densities of Mytilidae followed by mid-depth subtidal Station 19. Shallow subtidal Stations 17 and 35 had the lowest densities of Mytilidae.
i 65 t
- 4. During August all species encountered were enumerated. A total of 190 taxa were identified which is considerably less than in previous years. In 1984, 245 taxa were identified , 272 in 1983, 284 in 1982, and 293 taxa in 1981. Overall, the greatest number of taxa were identi-fled at Station 19 (124) and the least at Station 35 (66).
- 5. In previous years, the overall density from the August samples has been highest at intertidal Stations 1MLW and SMLW and lowest at Stations 19 and 31. This was the pattern in 1985 as well, except for Station 31 where densities were substantially higher than previous years and greatest over all sta-tions. The variability in total density as measured by coefficient of variation was less than 22% except at Stations 17 and 1MLW; variability was highest at Station 17 in 1984 G
- 6. From transect surveys, average Nodiolus modiolus densities were very low at Stations 17 and 35, as in 1982 through 1984 As in 1984, mean densities at Stations 19 and 31, across all sampling periods (April, July, October), were consistent with the exception of Station 19 in July where mean densities were approximately half those at Station 31.
- 7. The abundances of the two dominant epiphytic spirorbid polychaetes were lower in 1985 than in 1982 and 1984 but much higher than in 1983. Circels armoricana continued to be the most abundant species: Pfleolaria sp. was only found at Station 19 in 1985 and 1982 and in very low numbers; this species was not found at either Station 19 or 31 in 1983 and l l 1984.
l l l 66
i i 4 .l I 5.7 SELECTED BENTHIC SPECIES
- 1. As part of the marine benthos program, abundance information was collected in May, August and November at Stations 1MLW,-
SMLV, 17, 35,~19 and 31 for selected species. Size data for ).
- each species were also collected at's subset of these l
! stations. i l 2. Jassa falcata was most abundant over the three sample periods at Stations 17 and 35. This pair of stations has historically been studied for selected species data for this amphipod. J. falcata was also observed in i moderate levels at IMLW and SMLW during all periods, and i
- only incidentally at Stations 19 and 31. Greatest f abundances occurred during the spring sample period (May) j at both stations. There was no seasonal pattern to size-class distributions at either station. The highest j percentage of individuals occurred in the 4 mm size-class for all months at both stations except in May at Station l
j 17 when most occurred in the 5 mm size-class. Female l Jassa carrying eggs or brood were most numerous in-4
- August at Station 35 and in November at Station 17.
1 J
- 3. Pontogenela inermis was more abundant at the shallow subtidal stations (17 and 35) than in deeper subtidal stations (19 and 31); none were collected at intertidal j stations. At the deeper subtidal stations where-the l
selected species study was done, P. inermis was more abundant at Control Station 19 than at Farfield Station 31, except in August. Mean size varied only slightly (4.5 mm-6.2 mm) across months at both stations. In May l and November, the 4 mm and 5 mm size-classes predominated j while in August a greater percentage of P. inermis ! individuals were 5 mm to 7 mm in length. The number of I - l juveniles (4 mm and less) measured in May was notably 67 l u______
lower than in 1984. Fewer females with eggs or brood were collected in 1985 at Station 19 than in 1984. None of the P. inermis measured at Station 31 were reproductive.
- 4. Ampithoe rubricata abundances have declined since 1982.
Although this amphipod most commonly occurs in intertidal and shallow water habitats, its occurrence was as great or greater at the subtidal stations (especially Station 19) in 1985. A. rubricata was not recorded at Station SMLW this year. Occurrence was low at Station 1MLW and therefore no temporal pattern was observed in size-class distribution, nor was recruitment of juveniles in the population observed. Similar to previous years, females with eggs or brood were not encountered in 1985.
- 5. Nucella lapillus was present at intertidal Stations 1MLW and SMLW almost exclusively. Densities were consistently higher at Station 1MLW over the three sampling months; however, length data were similar for both stations. The greatest percentage of individuals measured occurred between the 2 mm and 5 mm size-classes for Stations 1MLV and SMLW. An increase in small individuals (1 mm to 2 mm size-class) occurred in August at both stations, similar to that observed in 1984.
- 6. Cancer spp. were identified as either Cancer 1rroratus or Cancer borealls in 1985 as in 1984 and 1983.
l , C. frroratus, the most prevalent Cancer species, was abundant at the two stations chosen for selected species measurements (17 and 35) as well as Station 1MLW. Only three C. borealis were collected for measurement; however, these were damaged and therefore were not included in the ! selected species data. Mean sizes for C. frroratus I ! were smaller for each month sampled in 1985 compared to
- 1984. .C. Irroratus was most abandant in August, 68
during which time the greatest percentage of individuals occurred in the 3 mm size-class. In 1984, a similar temporal abundance pattern was observed.
- 7. Asteriidae were most abundant at shallow subtidal Stations 17 and 35. A temporal abundance pattern was observed in 1985 with decreased densities occurring in the fall. This pattern differs from 1984 when densities increased in the fall. Mean size ranged from 5.9 mm to 9.2 mm at Station 17 and from 8.8 mm to 14.1 mm at Station 35; slightly smaller ranges than recorded during the same months in 1984. The greatest percentage of Asteriidae were distributed between the 5 mm and 11 mm size-classes at both stations. Recruitment of small juveniles occurred in August (most notably at Station 17).
similar to 1984 and 1983.
- 8. Mytilidae were the most abundant of the selected species at most stations, especially subtidal Station 31 and intertidal
- Stations 1MLW and SMLW. Mean size ranged from 1.8 mm to 3.5 mm at Stations 1MLW and SMLW and from 1.5 mm to 4.4 mm at Stations 17, 35, 19 and 31. Although mytilids occurred as
, large as 31 mm. the majority collected for each month at each station were in the 1 mm to 3 mm size-classes. These observations are consistent with results from previous years (1984 and 1983).
- 9. Strongylocentrotus droebachiensis was most abundant at the i deepest subtidal station (19). No distinct seasonal abundance pattern was exhibited at either of the selected Stations, 19 or 31. Most individuals measured occurred in the l
69 )
1 mm and 2 mm size-classes. In transect surveys, very few adult S. droebachlensis were' recorded at the four stations surveyed (17, 35, 19, 31); densities were always less than one per square meter in 1985 except at Station 17 in April where four per square meter were recorded. I 70 i
5.8 EPIBENTHIC CRUSTACEANS
- 1. Lobster catches were greatest at both Station L1 and Station L7 during September, October and November with the highest values in October. This pattern is similar to previous years.
Historically, catches at L7 have been higher than at L1; however, in 1985, catches were similar. Mean catch per unit effort was somewhat lower than 1984 values, which were the highest reported over the 10-year period, but consistent with earlier years. Female lobsters were more abundant than males for all months at both stations. Berried females comprised a small proportion, less than I?., of the total female population with peak catch occurring in October at Station L1 and November at Station L7. Historically, the catch of ovigercus females reached a maximum during September and October at Station L7 and during October and November at Stucion Lt. Legal-sized lobster catch was 7.5*. of the total catch at each site, averaging approximately 6.6 per 15-trap trawl, similar to 1984 levels but substantially less than previous years. This decrease is, in part, due to the increase in the legal size limit from 3-1/8" to 3-3/16" in 1984. The largest percentages of legal lobsters were caught during July at both stations. Size class three (2-5/8" - <3-3/16") consistently represented the greatest catch over all months at both stations with highest numbers caught in October and November.
- 2. Catches of Cancer borealls were substantially higher than in previous years, averaging 14.3 per 15-trap effort. This was higher than catches from the previous three years, but still lower than catches from 1975-1981. The greatest number of, crabs were caught in August at both Station L1 and Station L7 as has been true in previous years. The proportion of females, which averaged approximately 74%, increased dramatically from June through September and decreased in October and November at both stations. This is in agreement I
71
~
with earlier years. Berried females, comprising 1ess than 1*. of the population, were collected in June only at Station L1 and from June through August at Station L7. Males were generally slightly larger than females as noted in previous years.
- 3. Cancer irroratus catches were slightly higher than those in 1984. More than twice as many crabs were caught at Station L1 in comparison to Station L7. 'In fact, catches of Cancer irroratus, at the discharge, are the highest recorded since 1975 and have shown a steady increase since 1982. Peak catches occurred in August at both stations followed by the ,.
Iowest catches in September. No females were collected in June, August and September at Station L1 nnd in July and September at Station L7. As in recent years, no egg-bearing females were caught. Males were generally larger than females.
- 4. Catches of Carcinus maenas in 1985 were substantially I lower than in 1983 and 1984-at four locations on Flat.2 in Hampton Harbor, but similar to 1982 values. Catches had been steadily increasing from 1981 through 1984.
Peaks occurred in April and again in late fall, agreeing.with data from recent years. Females outnumbered males in all ! months except April. Ovigorous females were caught from April through August, and were most abundant in May when 9.3*. of the total catch were gravid. ' 72 i
_ . . . ._ _ _ ~ . _ _ _ _ _ _ .. . .. __ . _ . - . _ _ i 1
! 5.9 MYA ARENARIA '
i ~ ! .1. The mean density of Mya arenaria spat (shel1 length 1 mm- ' 4 . to 25 mm) at all flats declined 73% from 1984 and by 51% 3 - from 1983. Flat 1 showed the sharpest decrease in spat, ' with densities 91% lower than in 1984. Flats 2 and 5 t j showed only slight decreases in 1985, while Flats 3 and 4 showed 62% and 80% decreases, respectively. There were i no 18 mm to 25 mm Nya arenaria spat found, and those 1 i from 6 mm to 16 mm in length were rare, found only on ! Flats 1 and 3. Overall spat densities in 1985 were the j lowest recorded in ten years, with 1979 and 1982 being i ranked second and third lowest, respectively. n j The 1985 spat population (all flats combined) was 2% of l I the 1976 population and 3*. of the 1981 population, the I two largest spat set years recorded since 1976. , + Distribution of newly settled clams (1-6 mm) was fairly even between the flats in 1985, with the highest mean i density being found on Flat 2,'followed by Flats 4, 5, 3 1 i and 1, respectively. In 1984, Flat 4 had the highest { mean density of 1-6 mm clams, followed by Flats 1, 3, 2 l and 5. Plat 4 also had the highest density in.1983. In ) I 1982, Flat 5 showed the heaviest set. i i 2. The 1985 population of adult Nya arenaria also showed i substantial decreases from 1984. The mean densities (number per square foot) on Flats 1, 2 and 4 were 68%, 79*4 and 53% lower than in 1984. Flats 3 and 5 were.not i sampled for adults in 1985. The highest recorded mean density overall of adult #ra arenarla in the ten year i period between 1976 and 1985 occurred in 1980 and the 1 )- l 1 I i i 73
i Iowest occurred in 1977. The second and third lowest
.mean densities were recorded in 1976 and 1985, respectively.
- 3. Coincident with low numbers of-spat clams in 1985 were the low concentrations of #ya arenarla larvae recorded in 1985 (see Section 3.1). A major contributing factor to low spat densities is likely the green crab, Carcinus esenas. Although a sharp decrease in CPUE was observed in 1985 in comparison to 1984, the number of green crabs captured in 1985 was still the third highest since sampling began in 1976.
- 4. Standing crop estimates for Nya arenarla decreased in all size groups on all flats in 1985. Flat 2 density estimates decreased 85*. (all sizes combined) from 1984, while Flats 1 and 4 showed decreases in standing crop ,
estimates of 69% and 54%, respectively. Flat 1 contained' 66*. of the harborwide standing crop; Flat 2 contained 11% and Flat 4 contained 23%. This pattern of harbor-wide -i distribution was similar to the past six years of data.
- 5. PSP (paralytic shellfish poisoning) toxicity levels measured in #rtflus edulls were above acceptable ,
limits for human consumption from mid-August through early September.
- 6. Salinities in Hampton Harbor and the Brown's River were somewhat higher in 1985 than in 1983 and 1984 but were comparable with earlier years. In Hampton Harbor, mean low tide salinities (29.1%) and mean high tide salinities (32.2%) were between 2 and 3.3 parts per thousand higher than in 1985. As has been the trend,lBrown's River salinities were lower at their respective tides, with 74
mean low tide salinities (21.7*.) averaging 3.6 parts per thousand higher and high tide salinities (30.6*,) averaging 2.3 parts per thousand higher than in 1984. Temperatures in Hampton Harbor for both winter (January to March) and summer (July to September) seasons were the highest yet recorded (2.9*C and 18.6'C at low tide, respectively), continuing the trend of increasing winter temperatures. Brown's River temperatures were comparable to previous years with only summer high tide values (18.4*C across three months) being greater than those recorded in 1984. 1 4 1 i t i 75 l
1 i 6.0 LITERATURE CITED 4 Belding, D.L. 1930. The soft-shelled clam fishery of Massachusetts. Commonw. Mass. Dep. Conserv. Div. Fish Game. Har. Fish. Ser. 1:65 pp. Normandeau Associates, Inc. 1984. Seabrook Environmental Studies, 1983 l 1 Data Report. Technical Report XV-1. Prepared for the Public Service Company of New llampshire, Manchester, Nil. 178 pp + 654 App. pp. I Sokal, R.F. and F.J. Rohlf. 1969. Biometry. V.!!. Freeman Co., San Francisco. 776 pp. Strickland, J.D.H. and T.R. Parsons. 1972. A handbook of seawater analyses. Fish. Res. Bd. Can. Bull. No. 167 (2nd ed.). i 310 pp, i 5 I i i J l J } } l l 77
l0 APPENDICES I I l l I I 1
APPENDIX 1.0 ICHTHYOPLANKTON
<1 = <0.5 (values > 0.5 and <1.0 are rounded to 1)
ALL (Dates, in Tables 1-1 and 1-3) = mean of 12 monthly means, i ALL (Dates, in Tables 1-2 and 1-4) = percent within ! column of mean abundance of 96 samples. j
?
5 i a 1 i }
. .- - - . . - _ . . - . _ _. . -. =-
CES8D1 DM8DI APPENDIX TABLE I-1. ABUNDANCE IN0/1000 CUBBC METERS) 0F FISH ECCS AT NEARTIELD STATION IP2] BY SPLCIES AND DATE. MEAN Of IWO IDWS. SEABROOK ENVIRONMENTAL STUDIES,1985. l Jl Jl J l J l F l F I I I F l M M l Ml Ml A l A A I A l Mi Mi l A l A I A l A l E I E I E l [ l A A l A l A I P 1 P ' P l Pl A I A l l f4 l N l N l N I B l B l B l BI R R I R l Rl R I R i R l R l YI Yl i I I I . I I I I i 1 I I I I l l 0 l 1 1 2 1 2 1 0 l 1 1 2l 21 0 1 1 2 1 2 1 0 1 1 ' 1 1 2 0 l 1 1 1 3 1 0 1 3 l 9 5h 1 l 0 1 8I 8 3 1 0 1 7 1 4i O I 71 4 h 1 1 31 BLABRIDA[/LIMANDA l l l l l l l l 4 l l l H I l l l l 65 luROPflVCIS SP. l l l l l l l l h l I l l l l l l lSCOMBER SCOMBRUS I l 1 l l l H l l l l l l H I i 144 l f NClif t YOPtlS/UROP18YCIS l l l l l l l l l l , I l H I l H ISCOPilillALMUS AQUOSUS l l l l l . I H H I l t l l l l Il 210 1 ITNCalELYOPUS CIMBRIUS ll 1 I I l i I I I l l 21 51 31 . 1311 3101 4'68h l I CAD I DAf /CLYPT OCE PilALUS l l l l l l . I I H I I IIIPPOGIOSSotDES PL ATESSotDES I l 11 1 1 1 26h 1 2 . 221 3 51 114 176l 291 44 101 2681 45 ; Y IPOLLAClflUS VIRENS l l 51 671 9 l l 108 : l l l l l 1 l l l l w lMERIUCCIUS BILINEARIS I l l l H l . I i l l l H ' i l l l l l GADUS /MELANOCRAMMUS I l l l l l l l 231 21 l 201 61 9h 291 71 171 81 401 581 IGADIDAE I l I l I l l l I l l l l l l l l l l l GADUS MORHUA 1 361 24l 361 408 241 1321 31 1 11 1 11 Il 21 51 1 2 21 21 lCLYPTOCEPilALUS CYNOCLOSSUS l l l l 1 l l l l l 1 l l I I h I liAUIOGA ONITIS l l I I I l l I I l I I l l . l l ltlMANDA FERRUGINEA l l l l l l l l l l l 21 l 24 l 81 801 89 lIAUlOCOL.ABRUS ADSPIRSUS l l l l l l l l i l I l l l l l lRROSMF BROSME I l l l l l l l l l l l l l l l l l 80ST E ICillllYE S $ l 21 2I I I 21 l l I II I Il l l i 11 lHREVOORilA IYRANNUS l l l l l l l l l l l l 1 1 IMELANOGRAMMUS AECLEFINUS I l l l l 1 l l l l l i l I i 1l 1 6 lLABRIDAE I I l l l l l l l l I I I ll l l l . lALL l 36l 311 1061 Sol 241 2681 31 251 45l 241 121 231 2121 461 117 2521 703110671 4
- _ _ _ _ _ . - _ _ . _ _ _ . . . _ _ ~ . _. _ _
QE38D1 DM8DI i i i , APPLNDix TABLE 1 1. ICONilNUED)
- ABUNDANCE (NO/1000 CUBBC ME1ERS) OF FISil ECCS AT NEARFIELD STAllON (P2) BY i SPECIES AND DATE. MEAN OF TWO TOWS. SEABROOK ENVIRONMENTAL STUDIES.1985.
H M l M i J l J l J J l J J l J l J l A l A I A l A 1 Sl S l A I A 1 uI u l u u I u u I u 1 u l u l uh u ' U 1 E I E I Yl Y l N I N I N N l L L l L l L I C l C C Gl Pi P l u 1 I I I I I I I H I l 1 21 2 1 o1 1 1 1 2 1 0 1 1 1 1 1 2 1 0 l 1 2 H 2 0 1 1 1 , j OI 9 1 4 1 1 1 9 L 5 l 2 1 0 1 6 1 3 1 5 1 3 1 1 8 3 l 1 l IIABRIDAE/LIMANDA l 2301 3451l12321212481250101 837711169861304481 49101180571 7258:19561 4171 391 I I IUROPilYCIS SP. l l l l 6131 11231 131371 90881 1173110779l 4915' 10620 4442115555 6363 :17411 161851 lSCOMHER SCOMBRUS 125731344921 1521 33681 19821 134 ' 8121 3221 l I l [ NCllE LYO PUS /UNOPHYC I S I 1 l l 19101 2721 4689 L 28131 7931 175 l 340 1 1 162 107 ISCOPitTilALMUS AQUOSUS I 1901 2451 118 8591 621 2813 l 4061 5171 64 . 691 10671 441 632 ;233 : 949 46 lENCllELYOPUS CIMBRIUS l 3591 28468 105 ; 3011L 110L i 1211 1 105 l l l 8 l il l 101 l lCADIDAE/CLYPTOCEPHALUS I l l 408l 1446l 187l 29481 1 4601 249' 698 291 l l i 3, l i l l lHIPPOGLOSSotDES PLATESSotDES I 3111 33881 868 368 I I I I l H a l l l l l l l l h I POLLACillUS VIRENS l l l l l l 1 l IMfRluCCIUS BILINEARIS I I I 41 3411 5031 1 1921 l I l l H I 241 22 l 461 IcADUS/MELANOCRAMMUS 1 1711 1591 1 1 5871 l l l l l l H I l ICADIDAE l l 1 l l l 1 I l I l l l l IcADUS MORilUA I 91 1418 41 l l l l l l l a IGLYPTOCf PilALUS CYNOGLOSSUS I l l l 681 1 1341 711 2071 , I 58l 329 l ITAutocA ONITIS I I l l l l l l l H I ' 58 311 i ILIMANDA [ERRUCINEA 1 24l l l l l l l l l l l l l l I T AulOcOL AHRUS ADSPERSUS I I I I i .I 1 l 291 1 l l 197; I I l lBROSME BROSME I l l l l l 134 l l 291 l l l l l 1 l L OSIE ICHillYE S I I 351 I l i I I I I l 1 I l i I HDREVOORilA TYRANNUS 1 ll l l l ll l l ! I I ll l l l j ' MEl.ANOCRAMMUS AEGLEFINUS I l l l l l l l l l l Ili l
~
LABRIDAE I I l l l I I I I I I l I l I lALL 1386814475612110133232129895110776013049013392011639812344911891417009117130 6659127911165231 i w
RESCD1 DM801 APPENDIX TABLE 1-1. (CONTINUED) ABUNDANCE (NO/lOOO CUBBC METERS) OF F ISH ECCS AT NEARF IELD STAT ION ( P2) BY SPECIES AND DATE. MEAN OF TWO TOWS. SEABROOK ENVIRONMENTAL STUDIES,1985. l Sl SI Ol 0 l 0 1 O H N I NI N l N 1 Dl D l Dl DI l l E I E I Cl Ci Cl C Ol 0 1 0l 0 I EI EI EI E l l l P l Pl T l TI T I T , VI Vl Vl Vl Cl Cl Cl Cl l I I i 1 1 I I h l I I i 1 1 l 1 1 1 1 2 i O I 1 1 2 1 3 1 0 1 1 1 1 2i OI 1 1 1 1 2 1 1 1 8i 5l 21 0 1 1 1 01 7 31 9l 4 1 4 1 01 7l 7 l ALLI ILABRIDAE/LIMANDA 1 l l l l l . l l l l l l l l44821 IUROPilVCIS SP. l 67018747l 11 l 301 5 ; 21 l l l l l l 121921 ISCOMBER SCOMBRUS l l l l l 1 1 l l l l l l 9161 l ENCll[LYO PUS /UROPHYCI S l 81 8181 , i 191 l l l l l l l l 2521 ISCOPHIHALMUS AQUOSUS I 1411 1 6 ; I l I l l l H l l 1891 IENCHELYOPUS CIMBRIUS I l 29h 21 1 11 , I l l l l l 1618 IcADIDAE/CLYPTOCEPflAL US I I l l , l l l 1 , i 1211 lHIPPOGLOSSOIDES PLAi[SSOIDES I I l l l l l l l l l . 1021 Y, I Pott ACalluS vlRENS l l H l H 31 1 11 l 21 208 671 756l 200 261 u IMERLUCCIUS BILINEARis l 188 1 151 3ll 31 31 1 I i l l l l H 251 IcADUS/MELANOCRAMMUS I l l l l l l l l l 1 l l l 24l IcADIDAE l l l l l l l 821 1031 Ill 691 7691 l l l 221 ICADUS MORilUA l l l l 11 311 1431 291 191 41 231 471 69 791 15 ' 191 IcLYPIOCEPHALUS CYNOCLOSSUS l I I I I I I i i l l l l 10h ITAutocA ONITIS I l l Il l l l l l l l l l ' 10h ILIMANDA FERRUGINEA I l l l l l l l l l l l l l , 51 l ITAutocOLABRUS ADSPERSUS I I I I I I I I l l l l l l 5' l IBROSME BROSME l l l I I I I I l l l l l l 3 l IOST E ICilif fYE S I l l I l l l l 8 l l l l 11 II l lBREVOORilA TYRANNUS l l l l l 301 9; , I l l l 1 ll l Il i IMEIANOGRAMMUS AEGIEFINUS l l l l l l l l 1 i l l l ' ll <18 ! ILABRIDAE I I i l 11 Il Il i I l l l I l <11 I lALL I 836195951 351 51 1471 1611 1141 1228 158 941 8361 1361 835 217 85661 l r I s I 1 i I
[E S8D1 DM801 APPENDIX TABLE 1-2. PERCENI COM POS I T I ON (N0/1000 CUBIC HETERS) OF F ISH ECCS AT NEARF IELD STAT ION ( P2) BY SPECIES AND DATE MEAN OF 1WO TOWS. SEABROOK ENVIRONMENTAL STUDIES.1985. 1J lJIJIJIF l Fl F lFlMlHIMIM1AlAlAlAlMIMIMIMIJ1JiJIJIJIJiJiJ1AlAlAlAl lA l Al Al Al E I El E l El Al Al ;AlR1RlRIRlRlR1RIYIYlY1YlNINININ1LlLi Al Pl Pl Pl Pl Al Al Al Al UI UI UI UILlL1GlClClGI Ul UI UI UI UI Ul UI Ul IN l NI NI NI B I Bl B 1 81 R i I I I i i 1 1 1 1 1 1 1 I I I I I I i 1 1 I I 1 l l 1 1 1 I I I I I I o I 11 21 21 o I il 2 1 21 oh il 21 21 of 11 11 21 og 11 21 21 of 11 11 21 01 11 Il 2I ol il 21 28 13 101319151110 I 81 81 31 01 71 41 01 71 41 11 31 01 91 41 11 91 51 21 01 61 31 51 31 11 81
--..._..... ___.---....... ........___ .. ...........===-- =-- ....... _..-..__... -..-...______ .-___....__....
l ItAnRIDAE/LIMANDA I I l l l l I I I l l I l l .I l l l 61 61 8158164184 781561901301771381281 2 Il IUROPilYCIS SP. I l l l l l l l l l l l l l l l l I l l l l 28 4 l12l301 3 66121156163191 961 ISCOMBER SCOMB9US l l l l l l l l l 1 l l l l l l l 1141671771 71101 7 <11 3l 1 I I l l i i l E NCHE LYOPUS/UROPlfYCl 3 l l I l l 1 l l l 1 l l l l l l l l 1 I I l 61 11 41 91 2 l 11 Il l 2H l l lSCOPfliHAl.MUS AQUOSUS l I l 1 l l l l l l l l l l l l l<11201 SI 11 61 31<11 31 11 2H<11<11 61 61 41 31 l[NCHELYOPUS CIMBRIUS I l 1 l l l l l l l l l l 11101271521441421 91 61 51 91<11 l<11 1 11 l l<11 l l lGADIDAf tt.l YPIOCE PHALUS I I I I I I H l l I l I l l l l l l l l 1191 41 Il 31 1 Il 21<18<11 I i 1 IIllPPOGLOS<nl9ES PLATESSOIDES I l l 11 21 110 : I 81491131451501831641381401381 41 81 81 41 Il l l l 1 1 l l l l l T I pot l AClf s w *sRENS 1 1171631181 140, I l l l l l l l l l l l l l l l l l l l l l l l l l Os IMERLUCCIUs BILINEARIS I l l l l 1 l l l l l l l l l l l l l l l<11 Il 21 l 11 l l l l 1 l<11 ICADUS/M[tANOCRAMMuS I I I I I I i 192148183846140114: 161151 31 61 51 41<11 1 I 21 I I I i 1 l I i l IcADloAE I I I I I I I I I i 1 1 1 I I I I I i 1 1 I i 1 I I I I I I I I I IcADUS MORitUA l100176134180110014911001 1 31 1 91 51 11101 1 11<11<18<11<1 <11 1 1 1 1 I I I I I i l ICLYPIOCEPilALUS CYNOGLOSSUS l l l l l l l l l l l l l l l l l l l l H l<18 l<11<11 11 l l l l l 1 liAUTOCA ONiilS l I I l l l l l l l I l l l l l l I l l l l l l l l l<11 l l l 21 l ltiMANDA FERRUCINEA l l I 1 1 I l l l l l l l 11 1201 3l111 81 Il l l l l 1 l l l l l l l l liAUTOCOLABRUS ADSPERSUS I l l l l l l l l l l l l l l l l l l l l l l l l 1 l<11 l l l Il l IBROSME BHOSME l 1 1 l l l l l l l l l l l l l l I I I l l l l<11 I l<11 l l l l l loSIE ICIIT HYE S I I 71 21 1 I il i I I 41 I Si I I i l<11 I l<11 1 I I I 11 I I I I I I I IBREVOOHilA TYRANNUS I l l l l l l l l l l l l I l l l l l l l l l l l l l l l l I I I IME LANOGRAMMUS AEGLEFINUS l 1 l l l l l l l l l l l l l l<11 1 Il l l l l l l ; I l 1 l l l l lLABRIDAE I l l l l l l l l l l l I I I l l l l I l l l 1 l l l l l l l l l.
RES831 DM801 APPENDIX TABLE 1-2 (CONilNUEDI PFhCENT COMPOSITION IN0/1000 CUBIC METERSI or FISH ECGS AT NEARFIELD STATION I P2) BY SPECIES AND DAIE. MEAN OF TWO TOWS. SEABROOK ENVIRONMENTAL STUDIES.1985. I SI SI SI S1 01 01 Of Of Nl NI Ni Ml Of D1 Dl DI I l El El El El Cl Cl CI Cl 01 01 Of of El El El El l l Pl Pl Pl Pl Il Il Tl 11 VI Vl VI VI Cl Cl Cl Cl l I l l l l t i I I I I I l I l l l Al l 01 11 Il 21 01 11 21 31 01 11 11 21 Of 11 11 21 Ll I 31 11 81 51 21 of 1l 01 71 31 91 41 41 01 7l 74 LI lLABRIDAE/LIMANDA I l 1 l l l l l l l l l l l l l l$2I IUROPflVCIS SP. 162198180191831l 1211 31 21 l l l I l l 1261 ISCoMBER SCOMBRUS l l l l l l l l l l l l l l l l l111 I E NCHE LYOPUS/UNO PHYCI S l l 11 Il 91 l 413l l 1 l l l l l l l 3l lScorHillAL MUS AQUOSUS 134l<18178 l178 l l l l l l l l l l l 21 IENCHttvoruS ClMBRIUS l<1l 11 l<11 61 l TI l l l 1 l l l l l 28 IcAoloAE/ctYPiocE PflALUS I I I l l l l 1 I l l l l l l l l il I lHIPPOGtOSSOIDES PL ATES50lDES I i l l l l l l l l l l l 1 l l l 11 > l l Pott AcHluS VIRENS I l l l l 1 l 21 1 11 l l 21 2150190l921<11 b l lMERtuCCIUS DILINEARIS l 11<11'21 143160121l 21 l l l l l l l l<11 l IcADuS/MrtANocRAMMuS I I I l l l l l l l l l l l l l l<11 ! IcADIDAE l l l l l l 1 1 1721851721731921 l l l<11 IcADuS MORituA l l l l l 1201211881251151281241 61501101 71<11 IcLYProcEPilALUS CYNOCLOSSUS l l l l l l l 1 l I l l l l l l l<1l ITAutocA ONITIS I 21<11 I l 31 l l I I I l l l l l l<1l lLIMANDA FERRUGINEA i l 1 l l 8 I I I I I I l l l I l<11 ITAutocotAERUS ADSPERSUS l l l l l l l l l l l l l l l l l<1l lBROSME BROSME I I l l l l l l l l l l l l l l l<11 IOSTEICHTHYES I l l l l l l l l l l l l l l l<1l<11 IBREVOORilA TYRANNUS l l l l l l l201 61 l l I l l l 1 l<11 IMELANocaAMMuS a[ctErINUS l<11 l l l l l l 1 l l l l l l l I<11 ltAnalDAr l 1 I l i 1201 Il 18 I I I l l l t l<1l
.. ----- ..--.------------- ----............=__ _ _ ------------.--------... --
CES8D3 DM803 APPENDIX TABLE 1-3. ABuMDANCE (NO/1000 CUBIC METERSI OF FISH LARVAE AT MEARFIELD STATION (P2) BY SPECIES AND DATE. MEAN OF TWO TOWS. SEASRDOK [NVIRONMENTAL STUDIES,1985.
........ .. _==........--......--..........--...................--......................
I J l J l J l J l F I F I F l F 1 M I M t M l M I A l A l A l A l M ] M) i A l A l A l A l E I E$ El [ l Al A l Al A l Pl P l P i PI A l A l il NII NII N l N I l 8lI Bll 8i BlI Rl Rl R I R l R l RI RI R 1 Yl Yl I 8 I I I I I I i l l l I oI il 21 2 I oI i l 21 2I oi 1 1 21 2I oi 1 1 1 8 2I oi 1 1 1 3I o1 31 9I 51 1 I oI 8 I 8 I 3 I oI 73 4I oI 7 i =1 1 l 3l
... .. .=====
IScoMa[R SconsRus I I I I I I I I I I I I I I I I l I I l B AMMODYTES AMERICANUS l 178 18 40114521 2818 611 6391 4121 322119121 1781 1421 41 51 131 81 148 1121 l IPStuport tuRoNECTES AMER CAmus i I I I I I I I I I I I I I I I 91 11 1021 l IllPARIS ATLANTICUS I l l 1 1 I I I I 21 1 11 1 1 98 Tl 871 32112971 ITAutocotAaRuS ADSPtRSUS I I I I I I I I l l I I I I I I I 3 l ItNCHEtVOPUS CIMBRIUS I l l l I I l l l l l l l l l l l l l lut VARI A SUBBit uRCATA B l l l l l 1 I I I I i 1 l l l 38 71 2481 3, IP0ttACHluS VIRENS l 1101 621 3741 1831 821 2801 561 141 325 l 11 I l 1 I I I I e Bruot:5 cuMNEttuS I I I I I 31 121 271 671 1791 4618 1918 1261 1 16l 41 131 21 1 C3 IMERtUCCIUS BILINEARIS l l l 8 I l I I l I l l l l l l l 1 I luporuvC S SP. I I I I I I I I I I i 1 I I I I I I I lC10 PEA HARENCUS HARf MCUS l l 81 101 81 1 83 21 8 241 1 71 151 1 128 1 11 18 ICtvPTOCtPHALUS CYMOCLOSSUS I 1 l l l l l l 1 $ $ l l l l l l l l lScornIHatMuS AouoSUS I I I I I I I I I I I I I I I I I l l IHIProC10SSOIDES PLATES 3OIDES I i i 18 I I I I e l I l 51 28 I l 31 l al ICADUS MORHUA l 178 I41 Ill I 71 71 48 8 4l 1 31 31 1 l l l l l It MANoA ttRRuctNEA I I I I l i I l I I I l i I I I I I I IllPARIS COHENI I I I 28 1 348 51 41 331 71 ISI 261 81 21 1 I 91 18 I IMf0A0CEPHALUS AENAEUS I I I l l l 8 73 21 41 1 371 78 68 l l 41 11 151 ! IMYoxoCtruAtuS oCioOECENSPINOSUS I I I 21 l l 1 71 21 81 461 181 11 I I I I l l l IASPIDOPHOROIDES MONOPitRYCIUS I i l I I I I I I 28 351 31 141 l l 28 21 1 I ISVNCMATHUS FUSCUS 1 I I I l .I l I l 1 1 1 I I I l l I l l loSit CutHvts 1 I I I I 48 I I 61 21 1 21 11 I I I I I I l ItOPHIUS AMERICANUS I I I l l 1 l I I I I I I I I I I l 1 I Pi rR s t uS IR ACANT HUS I I I I i i I I I I I i i 1 I i I I i 11AUTOCA 04818S I I I I I I l l I 1 I l 8 I I I I l l ICYCLOPIERUS LUMPUS I l l l ? I I I I l I l l l I l l I 48 BCAoinAt i 28 1 51 I I 41 I I I I I I I I I I I I IMyoxoCEPHAtuS SCoRPauS I I I I I I I I i 41 I 31 I l 1 I I I I losMtRuS MoRnAx I I l i I I I I I i i i I I i 1 1 1 1 18PoSME BRoSME I I I I I I I I I I I I i 1 I I I I I lt: PARIS SP. I I l I l i l l I Sl I I I l ?! l l l IAmCusttA ROSTRATA I I I I I I I I I 41 I I I I I I I I IMYOMOCtPHALUS SP. I I I l l I I I I I I I I I I 3I I I l IMttANoCRAMMuS AtCLEFINUS I I I I I I I I I 28 I I I I I I I I I lSrnASitS SP. I I I I I I I I I I I I I I I I I I I ItUMPfNuS LAMPRETAETORMIS l l l l l I 13 3 I I I I I I I I I I I tcRyrTACAN! Hoots MACutATuS I I I I I I I I I I I i 11 I I I I I I It uMrt NuS MACUt ATUS I I I I i I I I I I I i 13 3 I I I I I IAtt i 1478 851 447116431 4128 3781 7461 5361 601124691 471! 3241 141 431 291 1391 60117851
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__ _._ _ ... __._ _. .. _ . _ _ - - _._.- - ___._ . . ~ . . - . . _ - - - - . -- --~ -_. -- REs8D3 DM603 Arr[NDIX TA8tE 1-3. IcostilssUEDI AButsDANCE INo/1000 CuBsC ME1ERs) 0F FISH LARVAE AT NEARFIELD sTAitom 1r21 BY srECIEs AND DATE. MEAN cf TWo TOWS. stA8 ROOK ENVIRONMENTAL sTUol[s,1985. I Ml MI J l Jl J l J l J l J l Jl J l Al Al Al Al sI sI sI sI I Al A l UI U I ul UI UI UI UI UI uI UI U I U l EI E I EI EI I y I Yl NI N l N I N l Ll Ll L 1 tl C1 CI Cl CI ri rI ri ri I I I I I I I i 1 I I i 1 I I I I I I I 28 2 I oI il il 21 0l 1 1 1 1 2I oi I I 2I 2 I oi I I 1 1 21 I oI 9I 4 1 1 1 9I 51 2I oI 61 3I 51 31 1 1 8 I 31 1 1 81 51 IsCOMBER scoMBRUs l l 51 1 27114601 126139201 661 601 4558 11 I I I I I I I I AMMPOviEs AMERICANUS I 91 13 511 I 9) 41 l 1 I l t 1 1 I I $ 1 Irstuport tuRONtcits AMERICANUS $16611 10117961 1161 2581 751 488 561 178 I I I I i 1 1 1 1 Itsraans AT ANiscus 1 8578 121 6921 31I 181 311 I I 7I I I I I I I l l l (TAutoCotA8Rus ADsetRsus l I I I l 91 385 9428 2T51 211 781 391 2601 5041 4918 3341 461 21 31 Itsecutivorus c:MeRius I I il 81 388 1061 488 412I 9941 781 751 51 28 I I 21 41 mi i lutvAR A sussitUncATA I 1521 431 6521 2TI 3041 651 68 1141 221 451 11 l I I l l I I y trottACHIus VIRENs l l 1 l 1 l l l l l l l l l 8 l l 1 I s tructss cussNEttus I I I I I I I I I I I I I I I I i 1 IMERtuccsus asteNEAass i I I I i 161 48 6371 1148 I I I i i 248 1 1888 11 201 luRortsycas sr. I I I I I I I I SI l I I 21 368 6438 401 1441 141 591 IcturrA nARisscus nAntsecus I l l l 1 1 I I I I I I I I I I i l l ) IctvrioctretALUs cyteoctossus i I I I i 161 8I I 4731 51 Ill 18 I I I 21 I I I IscorninAinus Aouosus l I I I I I 231 771 3231 191 1 71 11 21 1 48 81 101 91 IntreoctossotDts rtATEssosots I 781 51 1011 51 1241 tot 361 331 28 I I I I I I I I I IcAous MoRuuA I 91 11 81 21 8 151 1 81 Si I i I I i I I l l It manor ttnaucisstA l I I 181 191 611 361 1 241 St I i l l I I I I I lterARes cositNs I 91 I I I I I I I I I l i I I I I I I BMYoMcCt ritAtus AtNAtus I 188 1 188 Il l I I I I I I I l I I 1 l I tenoxoctruAtus ocicotctMsressosus i I I I I I I I I I I I I I I I I I I IAseDornoRosots secesorTERycius i 1 1 I I I I I I I I I I I I I I l i IsynecasAistus FUscus ! I I I l 1 l l l 11 1 61 61 101 278 31 I I 11 lositicutnyts I I II I I I 41 1 251 il i I I I I I I I il ILOrHlus AMERICAS 0us l I I I I I I I I I I I I I 48 l 151 I l letrRitus TRsACANTHUs l l l l l t I l I I I I l l 121 41 41 l Il IIAUlocA ofi Tis l l l l l I I I I I I I I I 4l 14l l l l l ICYctoritRus tuMeus I l i I I I I I SI I i 11 I I I 41 1 1 1 ! IcAoinat i I l i I I I I I I I I I I I I I I I IMyomoctrnAtus scoRr:Us 1 I I I I I 21 I I I I I I I I I I I i l losMtRus McRoAx I I l 1 I I I I 81 I i 11 I I I I I I i l IsmosMt esosME I I I I I I I I I 71 I I I I I i 1- 1 I lasrAnas sr. I I I I I I I I I I I I I I I I I I I I ANcusttA RosIRATA l 1 l t l I I I l I I l l l l l I I I IMroxoctenAtus sr. 1 I I 'I I I I I I I I I I I I I I I I IMrtANocaArnus Atcttressus ! I -l i I I I I I I I I I I I I i i I I I I I I I I I I il 1 18 I I I I I I I Istarsits sr. I I l litMrtNus t AMrRETAEFoRMis I l l I l l I l I I I I I I l l IcavriAcAMinoots MAcutAius i I I I I I I I I I I I I I i I I i l
! I I I i I I I I I I I I I I I I I IttmrtNus MAcut Atus 1 lat t 12T948 8083342l 266123821 52816079125291 ?521 6641 631 2711 552112061 4061 4081 311 941 1
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RES8D3 DM803 APPE NCIX TABLE 1 3. ICoWTINutD) A8uhDANCE INO/1000 CUBtc METERSI OF FISH LARVAE AT NEARFIELD STATION (P2) BY SPECsES AND DATE. MfAN OF Two TOWS. SEABROOK ENVIRONMEMTAL STUDIES,1985. l l OI OI OI OI NI N l N I N I DI DI DI Dl I l CI Cl Cl Cl O l 0 1 01 Dl EI E i El E l l I T I T I T l T I vI vi vi vi Cl Ci C1 CI i 1 1 I i 1 1 I I I I I I I I I oI 1 1 21 3I oI 1 1 1 1 21 01 1 1 1 1 2I l i 2I oI i 1 01 ---- 7I............. 38 9I ........................... 4 1 4 I oI 71 7 I Atti IScoMeta SConeRUS I I I I I I I I I I I I I 1281 , IAMMoDviES AMERICANUS I I I I I I I I I I 161 51 21 1191 l t rStuoorttunoWE Cit S AMERICANUS I I I I I I I I I I I I I 86l I t t rAR e s AT LAN T ICuS I I I l l l l l l l l l l 641 ITAutocotAaRUS ADSPERSus ! Il i I I l l l l l l I l 631 IENCH[tv0 pus CIMBRluS I i 11 61 Il 18 I I I 11 I I l 378 lutVARIA SuBBIfuRCATA l l l l 1 l l l l l l l l 351 3, IPottACHlus VIRINS I I I I i 11 Il l l 91 71 91 2181 301 e Irnot:5 cuMNtttuS 1 l i I I I I I I I I I I 231 C3 (MERtuCCluS 88tINEARIS I l l Il i 21 31 l l l l l l 211 luROrtivCl3 Sr. 1 il l 41 I I I l l l l l l 201 BCturtA nARENcus HARINCuS I l 2451 11 2491 601 161 538 601 1211 211 21 41 191 lctyProCErstAtuS CvNoctoSSuS I I I I I I I I I I I I I til ISCorninAtMuS AouoSuS I 11 I I I I I I I I I I I tot in:ProctoSSotDES et ATESSol0ES I I I I I I I I I I I I I 98 i I IcADuS MonstuA I I I I il 151 341 41 51 bal ill 41 101 Si It MANDA FERRUGINEA I l l l l l l 1 l l l l l 31 IttPARis COHtMt i I I I I I I I I I I I l 31 IMv0XoCEPHAtuS AfMAfuS I I l l l l I I l l 1 I I 21 IMv0xoCtrnAtuS oCiootCtMSr NoSuS I I I I I l i I I I I I I 21 lASelDOPHoROIDES MONOPTERvCluS I l l l l l l l l l l l l 11 ISvMcMAinuS RUSCUS I 11 1 I I I I I I I I I i 18 l loSTERCHIKv[S 1 l l l l l l l l Il l I I Il l ltOPHILS AMERICANUS l Il 13 l Il l l I l l l l l <11 i trErnitus TR ACANTituS l I l l 1 I I I I I I I I <tl I jiAuToCA ONITIS I 18 I I l l l I l l I I l <11 l lCvCtoPTERuS LuMPUS I l I I l l l l l l l l l <1I IcADIDAE I I l l I I l I l l l l Il <1l
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! IBROSME BRoSME I I l I I I I I I I I l l <1l ItIPARIS Sr. I I I I I I l l l I l l l 411 I ANculttA RoSTRATA I I i l l l l l I l 11 l l <1I pecomoCt rnAtuS Sr. I I I l l l 1 l I I I I I <11 Int t ANocRAMMuS At ct t r :NuS I I I I I I I I I I I I I <ff IStnASitS Sr. 1 I I I I I I I I I I I I <11 It unrt NuS L AMPet T At s oRMIS 1 I I i i I l l l l l l 1 <ll ICRYPTACANTHOo[5 MACutATUS I I I l l l l l l t I l l <Il ItuMPtNuS MACutatuS I I I I I I I I I I I i 1 <11 IAtt I 61 2471 128 2531 791 551 571 651 1801 551 201 2351 6991
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CES8D3 DM803 APPEN0lx TABLE 1-4. PERCENT COMPOSIT ION (NO/1000 CUBBC METERS) OF F ISH LARVAE AT NEARFIELD STATION l P2) BY SPECIES AND DAIE. MEAN OF TWo TOWS. SEABROOK ENVIRONMENTAL STUDIES,1985, IJIJIJIJIFIFlFIFIMIMIMi HIAlAlAlAlMIMIMIMIJIJIJiJIJlJlJIJiAlAlAlAl i Al Al Al Al El El El El Al Al Al Al Pl Pl Pl Pl Al Al Al Al UI UI UI UI UI Ut UI UI Ul Ut Ul Ul INININIMlBlBlBl81RlRlRIRIRtRlRlR1YlYIYlYlN NINIMlLILlLlLlClClGlGI I I I I I I I I I I I I I I l i I I I I I I I I I I I I I I l l 1 of il 21 21 01 il 21 21 of Il 21 21 of 11 11 21 01 11 21 21 0 11 11 21 of 11 11 21 01 il 21 21 1 31 of 31 91 51 18 01 81 of 31 01 71 41 01 71 41 11 31 01 91 41 11 91 51 21 01 61 31 51 31 II 81 , ISCOMBER SCOMBRUS I l l l l 1 I I I l l l 1 I l l l l l 1 71 1101611241641 31241691 Il I 1 l l IAMMoDYTES AMERICANUS 1128 11 9188168116186177l543778381441305111451 61241 61<11 Il 21 l<11 11 l l l l l l l l l leStuoortEURONEC1ES AMERICANUS l l l l 1 l l l 1 l l l l l l l 71 21 6859112154144111114l Il 21 78 I I l l l l lLIPARIS ATLAMitCUS l I l l l l l l l<11 l<11 l 1201241631541731311151211121 11 61 l l 31 1 1 l l l ITAutoCOLABRUS ADSPERSUS 1 1 I l l l l l l l l 1 l l l l l l l 1 l l l<11 71161111 81121621961911411 l lENCHELYOPUS CIMBRIUS I l i I i l l l 8 I I I I I I I I I I i 11<11141 41 91 71391311111 of 11 l l i lutvARIA SUB8tfURCATA I I I I I I i 1 1 1 1 1 1 I I I 21121141 51531201101131121<11 41 91 71 21 1 I I IPottACHIUS VIRENS 1751731841111201741 71 31 Si l<11 1 I l 1 l l l l 1 1 I l l 1 l l l t l l l y IPHOtlS cuMNEttUS l l l l l 11 31 4112l301191411398 1361151101 31 l l l l l l 1 1 I l l l l l l p. IMERtuCCluS BILINEARIS I I l l I l I I I l l l l l l l l l l l l 8 l Il 11101 51 l l l l l 21 M IUROPHYCIS SP. I I I I I I I i 1 I I I I i 1 1 I I I I i l 1 I i l<11 1 I I il 61531 ICtuPtA HARENGUS HARENGUS I l 91 21 11 l 21<11 1 41 l 11 51 1288 l Il 21 l l l l l l l 1 l l l l l 1 l IcLvPioCE PHALUS CYNOCLOSSUS I I i 1 1 I I I I l l i I l I I I I I l I l l 11 21 1191 2 21 21 l 1 1 I SCOPHIHAt MUS AQUCSUS I I I I I I I I I I I I l l I I I I l i I I I I 41 11131 8 1111<11<11 I tillProctOSSoIDES PLATESSotDES I I l<11 I I l l l l l l 11151 l i 21 l<1l 31 71 31 21 51 91 11 11 11 I I l l l l GADUS MORHUA 1128161 31 1 21 21 Il l El I 11 il l I I I I l<11 11<18 11 1 31 l<11 21 l l 1 I I lLIMANDA FERRUGINEA 1 l l 1 I l i I l l l l l l i I I I l l l Il 71 38 71 l Il 21 l l l l l ItlPARIS COHINI I I l<11 1 81 Il 11 61 Il 11 61 21151 l l 61 21 l<11 l l l l 1 l 1 1 I ( l i I IHv0xoCEPHALUS A[NAEUS l l l I l l I 11<11 Il I 81 21401 I i 31211811 1 11<11 l l l l l l l l 1 1 I MyoxoCE ruAL US oCTOoECE MSPI NoSuS I I I il l I I il<ti il 21 41<18 I I I I I I I I I I I l l 1 I I I I I I IASPIDOPHoROIDES MONOPTERYGluS I I I l l I I I l<1l 11 Il 48 l l 71 Il l I l l l l l l l l l l l l l l lSYNCMATHUS FUSCUS I I I I I I I I I I I I I I I I I l I l i I I I I I l<11 l 91 21 21 21' IOST[lCHTHYES I l l I l 18 l l Il<II I<1I<1l I I I 1 l l l Il l l l Il l Il<1l l l l l l ItoPHIUS AMERICANUS I I I I I I l l I I l l l l I l l I I l l l l l l l l l l l l l<11 lPfPRitUS IRIACANTNUS I l l l I l l l l 8 I I I I I I I l l l I l I l I l l I I l I l Il ITAutocA oNITIS I I I I I I I I I I I I I I I I I I I I I I I i 1 1 I I i 1 I l<11 ICYC10PIERUS LUMPUS I I I l l l I l I l I l l I I I I I<11 l I I I I I l<1l l l Il l i I scADIDAE I 18 I 13 I I Il l l l I I I I I I I I I I I l I l I I l l l I I I l IMyoxoctrHAtuS ScoRPlUS I I I I I I I I i 11 8 11 I I I I I i l I I i l l<11 1 1 I I I I I I loSMtRuS MoRDAx i I I I I I I I I I I I I I I I I I I I i 1 1 I I l<11 1 1 Il i I 1 lBROSME BROSME I I I I l l l l l I I I l l I l l l l l l l l I I l l 3l I I l l l It PARIS SP. 1 I I I I I I I I il i i 1 1 Si l i I I I I I I i i I I I i 1 1 I I I Ancultt A ROSTRATA I I I l l l l I I Il l l l l l I I I I I l l I I I I I l l l l l l IMv0xoCtruAtus SP. I I I I I I I I I I I I I I I 91 1 I I I I I I I i 1 1 I I I I I I IMitANoCRAMMUS AFCLEFINUS l l 1 I l l I I l<11 l l I I l I I l l l l 1 I I I l I I l l l l l IstBASirS SP. 1 I I I I I I I I I I I I I I I I I I I I i i i I I l<11 1 21 I I Il uMPtNUS L AMPRETAEFORMIS l l I l l l<Il l ! l l l l I I I l l I I I I l I I I I l l I $ l ICRvri ACANTHooES MACutAtus l I I I I l i I I I I l<11 I I I I I I I I I I i 1 1 1 1 I I I I I ItuMrt NuS MACut ATuS I I I I I I I I I I I I<11 1 I I I I I I I I I I I I I I I I I I I 7
CES803 DM8D3 i APPENDIX TABIE 1-4. (CONTINUEDI PERCENT COMPOSITION IMO/1000 CUBIC METERS) OF FISH LARVAE AT NEARFIELD STATION (P2) BV SPECRES AND DATE. MEAN OF TWO TOWS. SEABROOK ENVIRONMENTAL STUDIES,1985. 1SISIS1SI01010101 NI NI NI NI D l Of DI DI l l El El El El Cl Cl C1 Cl 01 01 01 01 E I El El El l l Pl Pl Pl PI Tl il il Tl VI VI VI VI Ch Cl Cl Cl I i I i l i I i 1 1 I I I I I I I Al 1 01 11 Il 21 OI 11 21 31 01 11 11 21 Ol 1 Il 21 LI l31118151210111017131914148 Of It il L1 ISCOMnER SCOMnRuS I I I I I I I I I I I I I l l l 188 lAMMODYTES AMERICANUS l 1 l l l l l l l l l l l 129125) 1117 i IPSEUDOPLEURONECT[$ AMERICANUS l l l l l l l l l l l l 1 l 1 l l12l lLIPARIS ATLANilCUS l l I l l l l l l l l l l l l l l9 , ITAuTOcOLABRUS ADSPERSUS 1821111 71 31171 l l l l l l l l l l l 9 ' IENCHEtVOPUS ClHRRIUS l<1l 1812l 1 l<11511<11 11 l l l Il l I I 51 IULVARIA SUBBITURCATA l l l l l l l l l l l l l l l l h Si p IPOtlACHauS VIRENS l l 1 I I I I l I 11 21 I i 5112145173i 41 s H I Pilot lS CuMNELLUS l l l l l l l l l l I l l l l l . 31 IMERLUCClus BILINEARIS l 1461 3121l I l 81 1 3l 61 l l l l l l 31 luROPityCIS Sr. 1101351441631171 1321 1 1 I I I I i 1 l 31 lCLUPEA HARENCUS HARENGUS I 1 I l i 1991 91991751301931931671371101 2 31 t ct VPIOCE PHALUS CYNOCLOSSUS l<11 i l i l l ! l l l l l l l l 21 ISCortlIHALMuS AouOSuS I 11 21341101171 1 I I I I I l l l l il IHIPPOCLOSSOIDES PLATESSotDES l l l l l l l l l l l l l l l l 11 I I I I I l l l<18191628 71 7127120 20 . 41 1 IcADuS HORHuA lLIMANDA l[RRUCINEA l l l l l l l l l l l l l l l , (<1 ; ILIPARIS COHENI l l l l l l l l l l l l l l h I l<1H INYOXOCEPHAIUS AENAEUS l l l l l I I I l l l l 1 I I l<11 lMYOXOCE PHALUS OCTODECEMSPINOSUSl l l l l l l l l l l l l l l l<11 lASPIDOPilOROIDES MONOPTERYCIUS l 1 l l l l l l l l l l l l l l<1l ISYNGNATHUS FUSCUS l 11 l l 18171 l l l l l l l l l l l<1l IOST EICilillVES I l l l 11 l l l l l l l l Il l l l<ll ILOPitsuS AMERICANUS l l 41 l 1171<18 l<11 l l l 1 l l l l<11 IPEPRILUS TRIACANTHUS l 11 Il l 11 l l l l l i l l l l l i<11 ITAufOcA ONITIS 1 31 1 1 1171 l l l l l l l l l l <11 ICYCLOPTERUS LUMPUS l Il l l l l l l l l l l l l I h<1 IGADIDAE I I l l I I l I I l l l l l l<1 <1 IMYOXOCEPHAtUS SCORPIUS l l l l l l l l l l l l l l l l <1: lOSMERUS HORDAX l l l l l l 1 l l l l l l l l l <1 : lBROSME BROSME 1 I l l l I i l l l I l l l l l l<1 lllPARIS SP. 1 l l l l l l l l l l l l l l I<1 IANCulltA ROSTRATA l l l 1 l l l I l i l l l 2) h l<1
- IMYOxOctPilALUS SP. l l l l l l 1 l l l l l l l l<1 IMFLANOCRAMMUS AECLEFINUS I l l l l l l l l ' l l l l l<1l IS[nASI[$ SP. l l l 1 I l I i l l l l l H l l <1l ItuMPENUS BAMPRETAEFORMIS I I l 1 I I l l l l l l l l ' I <1' lCRYPIACAN1HODES MACUtATUS l l l l l l l l l l l l l l l l : <1 It uMrE NuS MACut AiuS I I I l l t i l i I l I I I H I
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CES8AA DM8AA 1 l APPENDIX TABLE 1-5. COUNTS OF AMERICAN SAND LANCE LARVAE, AMMODYTES AMERICANUS, AT THE NEARFl[LD STATION (P21 BY 0.5 MM LENGiH CLASS AND DATE. SUM OF LARVAE MEASURED IN TWO 10WS. SEABROOK ENVIRONMENTAL STUDIES,1985. 1J lJ lJ lJ lF llI IF lFiMi M iMlM llAlA IA lAIM M ,MlM J lJ J J D D llDl DI IA IA l A 1A l E ll E IE IE IA l A l A l A ll P 1Pl P1P 1: A A A lA U lU U U E E E E lNlN lNINlB ,Bl bib l R lR R ll R R R l R IR 1;Y Y Y Y NIN N N C C C C I I I I I I I I I l . ll t I ll 1 I
......-l o 1 1 1212 1oI1 12 l 21ol 1 'I2 2ll0 ll1 11 12 0 ,1 2 2 ol 1 1 2 l 011 1 2 l lLENGTHl 3 1 0 ..___........_______.........__........__....._
1 3 l9I5l1 1O l8I8 I3-10 1714 10 1714 1 l3 0 9 I4 11 I, 9I5I4 10 7 7! ALL I t l_____________.____ ...____ ..___. _________....._____..________________.__. I 4.5 l il 1 11 I 21 1 ti i 11 11 1 , I I- l l ll 1 I I I I I I l 81 1 5.0 1 13 ; I 61 161 141 11 31 41 141 1 3 ' 1 - l 1 ll 1 l l l 8 , 1 2 861. > I 5.5 I i i 101 191 158 1 151 III 141 131 5'l Il i 1!I ll 1 I l 7 1 4 1151 l I 6.0 l ll l 71 51 1 l 91 141 41 111 4 1 l l :I l 54 l l 6.5 l 11 1 St I 31 4 . 41 31 I 01 6 l 1, 1 I I I , 1: 33 i T.0 I i i 21 1 31 2 41 41 31 31 61 . , 1 1 11 1 'l ll l l 29 : I 7.5 I Il I 41 1 21 5 l l 21 31 61 61 1 2 1 1 11 1 Il l 33 p l 8.0 l l l Il i 11 81 2.1 1 11 Il 21 71: I i 11 l . l , 2:a l 8.5 I I I l l l 41 ll 11 1 1 ' 31 31' I I , 11 l I l l 13 [ i i t 9.0 l I I I I l 51 2 l 1 , l . 11 41 I 21 I I 15 . 11 2 9 I 9.5 l l 11 11 1 I I: 1 1 l 11 1:1 1 ' 110.0 l l 1 1 1 1 1 l l 1 ll 11 4 , i 3ll 3 ; I 12 110.5 1 l 1 l l l 1 l ll 1: l l 1 2 1 ll l 1 1 2 1 10- , 111.0 l l l l l l 3 ll l 1: 11 1 4 ' l 1 1 1 5 1 : 1 L i 17 1 111.5 l l l 1 l l l l l 1 il I 1. 3 , l 'i ! l l 5 ; 112.0 1 I I I l l 11 I I I 2 1 l 11; I I i 1; , 4 2 112.5 l l l l ll l l l 1 : I . I 11 . :1 1 i 3 113.0 I L l l ll l i 1 1 2 : l ll l 11 2 , I l 5 113.5 l l l l ll l 1 l l l , i l 1 1 I I I ( L 2 : . 4 l i te . o l l l l ll l l l l l 1 1 I l l t I I I i . I 114.5 1 1 1 1 1 ; I I I I I I I I I I ,I i 1 - 1 I i 1, 1 ; 115.o i I I I i 1 1 1 1. I I I I I l 1 - 1ll 1 1 I I I I ' I l l - 21 115.5 I I i 1 I ll 1 I I I I I I I . I I I I . I I 116.0 l I I I I I I i i I I l 1 2 1 1 I I I 2-l 1 1 I l! 1; 116.5 I I I I I I I I ll ll 1 . ll ll 117.0 I I I I I I I I ll ll 1 I I I I i 1 I i i ! I I 1 . i 117.5 I I l l l l l 1 11 I I I I i 11 1 I I il 118.0 l l l 1 1 1 I I I I I I I I I I I l I l l 118.5 l l l l t i I I I I i 1 I i 1 -l 119.0 1 I I I I I I I I I I I I I ' i I 119.5 I I i 1 l l l l l I I l II I ll I l 'l I I' 1 120.0 1 I I I I I I l I' ' I l 1 l I I I l ' l ' I 121.0 I I I I I I I I I ll ll l l I I I I l 1 1 122.0 I I I I I i 1 I I l l I l I I I I 1 1 12t .5 l i l 1 1 I I I I I I I' l I 'l "I 1 1 , l; I I I Il 1 l l 1 1 il , 1 126.5 I I ll 1 1 I I l' I I I I I I I I I 1 4 L 129.5 I I I I I I I I I I I l l I I I I 11 -' -. ' I i 1l I l i I I I I I l . 21 1 I I I I 2l' 130.0 I I , I I I I ll 1 i 11 21 1 15; 51 21495': IALL I 161 il 371 401 401 381 40ll tool 401 t:01 401 t ol 21 21 31 91 121 2r I 1 i 11: til
i CES8WF DM8WF l l
~
l l APPENDIX TABLE 1-6. _ l COUNTS OF WINTER ftOUNDER IARVAE, PSEUDOPLEURONECi[S AMERICANUS, AT THE NEARFIELD STATION ( P2) BY 0.5 t MM LENGTil CLASS AND DATE. SUM OF LARVAE MEASURED IN TWO TOWS. SEABROOK ENVIRONMENTAL STODIES,1985.
----------....----___-------------- --............ a.--._----_-----, ,,
- 1A '
A IA IA IM i M iM MlJ l J ~l J l J lT !J J 1 [J . ) - 4 [ lP P lP l PIA lA IA A l U lU d iU l U lU U lU l' h IR R l R l R IY IY Y Y IN lN N IN i Ll L lL1Li l l l 1 I I . m H I . I l I i [ -------I o I 1 1 1 2 Ioi1 12 ie oI 1 i1 12 0 11 l 1 12 I I i lLENGTill 4 IO I7l 4 11 13 10 9 4l 1 I9I5 12 10 16 13 1.-_..__....--- .-_--..... ----....1 .....- .......... -----....--.._--...... lALLI 12.5 1 1 I I I I 21 1 I I I I I I I I 21 13.0 l I I I 3' I l il L I 11 I I I I I 51 l 13.5 I l l l 5 1 21 81 fu 2h 2 ' i 1 1 1 I I 21 i 14.0 l l t 1 2 I I 51 101 1: Su 9 ' Si ! -1 l I 37 _ l 14.5 i L l i l 21 131 li 81 9 ' 41 1 11 39 - l 15.0 l H I :I 1' 61 31 61 4 I 6' 3 I l l 29 15.5 l H H I l 1 11 61 5 l l ' 2 1 1 17 ! y, 16.0 l ll l l 2 1 7 I 5 : 5 $ l 1 1 261 a 16.5 I I 4 l 2 l 1h . 2 3 . 11 4 1 1, 2 . 1 , l 17' _4 H 17.0 l l L I I I 2h 31 21 21 91 1 : 3 i 6 1 28 ' " 17.5 l l 1 , 1 I I I I H 2' 6 . , 4: 12 18.0 1 l l l- 1 I . 1 . Il i 1 l 4 7 - 18.5 I I I I l.. 'l ~ l I I l l 1 il 2 - , IALL l 1 l l Ill i 171 401 9 ll 401 401 26 l 311 3 1 71 181 l242 9 v A wm 0
RES8LF DH8LF i APPENDIX TABLE 1 7. COUNTS Of YELLOWTAIL FLOUNDER LARVAE, LIMANDA FERRUGINEA. AT Tit [ NEARFIELD STATION (P2) BY 0.5 MM LENGill CLASS AND DATE. SUM OF LARVAE MFASURED IN TWO TOWS. SEABROOK [NVIRONMENTAL STUDIES.1985. lH H H11M lJ J ll J'IJllJ lJ lJ lJ l l A A A A l U U U U llU lU lU lU l l Y l Y Y YlN N N N 'I Li LIL L 1, I I I , l l I 1oi1 2 2 I o .I 1 1 i2 i oi1 1 2 , I LENGilll 1 13 ,0 ,9l411 l9I5 12iO 6 3 , i_______________________._______________________________'ALLI ____
- I 3.0 I I I I ll l 31 3 1: I 611 3.5 I I I i 11 71 6 3 1 17ll 4.0 1 1. I I i 61 11; 31 2 12ll 4.5 l l 21 3ll 21. ll 11 ,
8 I 5.0 l l . I 2'l l' I 2' . 5.5 l I l li 1 1 1 6.0 I l l I I I l' I il I 6.5 I I i 1 11 , 11 Y I 7.0 1 I ll 1 I 11 I e m 7.5 I i 11 . l ti
~ . 8.0 1 I ll l 8.5 I I I 9.0 1 .
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N { .( APPENDIX TABLE 1-8. COUNTS OF ATLANTIC COD LARVAE, GADUS MORHUA, AT THE NEARFIELD STATION ( P2) BY 0.5 MM LENGTH CLASS AND DATE. SUM OF LARVAE MEASURED IN IWO TOWS. SEABROOK ENVIRONMENTAL STUDIES.1985. 1 J' J' JI JI F , F l F F M I MI M M l MI: M 'J J' JI J. J' J'lJ 01 N NI N N D! D D Di l l A' A' A A E E ' E E A L Al A A A A U U ' UI U U U U Cl 0 01 0 0 E E E E IN N N N B B B B R tRI R R Y Y N N N N L 'l L Tl V VI V V C C C C
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------- 0 1 2 2 0 1 2 2 0 Il 2l 2 -2 2 0 1 ' 1 -2 0 1 1 3 0 1' 1 2 0 11 1' 2 l LENGTH. 3 0 3 9 5 1 01 8 8. 31017 01 9 4 : 1 9 5 2 : 0 6 0 7 3 l9 4 4 01.7 l 7. ALL g--_-.. .....-___ ----...-_-...............-- ......................-....---..........----.....__---..
3.0 l l l 'I l l l 1 l .I l l1 l 2 l 1ll 1l611 11 I 1: 131 3.5 1 l l l l 1 ; 1 2 l2 9 131 3 3 '10 l 1 '1 1 l 4811 2 1' 2: 2 18 2 ll 4.0 4 1 1 1 Il I 'l 5 III I 3 4 59 4.5 5 2 3 1 Il 1 1 4 4 ; 1: 3: 25 s 1 5.0- 3 3 1 l 1 1 I i 1 1 . I 3 ; 1 l 14 ; 5.5 1 2 5 1 l l ' 21 10 ! 6.0 2 1 1 1 1 1 I l 6l , p
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RES8SS DM8SS APP [NDIX TABLE 1-9. COUNTS OF ATLANTIC MACKERAL LARVAE, SCOMBER SCOMBRUS, AT Tile HEARFIELD STATION (P2) BY 0.5 MM LENCTH i CLASS AND DATE. SUM OF LARVAE MEASURED IN TWO 10WS. SEABROOK ENVIRONMENTAL STU01ES,1985. M M M M J ! J l J I J J J J J A l A l'A A d A A A ,A U U U U U U U U UlU U U I Y Y Y Y N N N N L L L L ClC C C
, I 0I1 2 2 0 1 l 1 2 0 1 1 2 0 1 212 .
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- 5.5 8 4 2 8
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_ _ _ _ . _ _ _ _ _ _ _ _ _ _ _ , . _ . _ _ , _ _ _ _ ___ _.m - _ _ . _ _ _ _ _ _ _ . _ . _ . . . . . _ . _ i. RES8TA DM8TA APPENDIX TABLE 1-10. 3 COUNTS OF CUNNER LARVAE, T AUTOGOLABRUS ADSPERSUS, AT THE NEARF IELD STAT ION ( P2) BY 0.5 MM LENGTH CLASS AND DAIE. SUM OF LARVAE HEASURED IN TWO TOWS. SEABROOK ENVIRONMENTAL STUDIES.1985. e 1 ..................____........................_ .............___ .................... J IJ J J J ' J J -J A A A A S S S .S1O O O O I O U U U U U U U U U U U E E E E ' C C C C i N N N N L L L L G G G G P P P P T. T T T
------- 0 1 1 2 0 1 l 1 2 0 1 2 2 0 1 1 2 0 1 2 3. .
LENGTH is 1 , 9 5 2 016 3 5 3 1 8 3 1 8 5 2 0 1 0 ' ALL 2.0 I . Il 4 'l i I 1l J 2.5 15 4 2 2 1 24' 6 2 3.0 1 8 3 3 1 2 84 3.5 8 9 to 3h . 5 3 2 3 1 44 4.0 2 2 4 5 1 6 12 8 12 1 2 i 55 4.5 3 1 4 2 3 11 13 4 11 1 53 5.0 2 3 is 3 6 5 2: 10 - ?! Il 38 y 5.5 1 2 to 1 6 3 ! 7 8 1 39 s 6.0 6 3 4' 6 3 . 6 1 29 1 P 6.5 4 3 4 1. 3 15 1 7.0 3 1 1 1. 2 8 I 1.5 l' 1 '1 1 1 51 l 8.0 4 1 5 I 8.5 1 4 1 , 1 1 7 ?. 9.0 1 3. 2 1 7
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. . ~ _ . . . . _ , . , . -. - -
RES80S'DM8US !- ~ APPENDIX TABLE 1-11. COUNTS of HAKE LARVAE. UROPHYCIS SP..AT THE NEARFIELD STAT ION ( P2) BY 0.5 MM LENGTH CLASS AND DATE. SUM Of LARVAE MEASURED IN TWO TOWS. SEABROOK ENVIRONMENTAL STUDIES,1985. J J J J A A .A A S S S S 'O O O O , U U U U U U U U E E E E C C C C L l L L L G G G G P P P P T T T T l
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RES2PV DM8PV APPENDIX IABLE 1 13. COUNTS OF POLLOCK LARVAE, POLLACHluS VIRENS,AT THE NEARFIELD STATION (P2) BY 0.5 MM LENGTH CLASS AND DATE. SUM OF LARVAE MEASURED IN IWO TOWS. SEABROOK ENVIRONMENTAL STUDIES,1985. J lJ ! J J F F F IF M M M M N N Nl N ' D D D D l A l A A A E E E I E A A A A O O O l 0 E E E E NIN N N B B B B R R R R V V V'V C C C C 1 I ...-... ;O 1 2 2 0 1 2 2 0 1 2 2 0 1 1 2 0 1 11 2 LENGTH l 3 0 3 9 5 1 0 8 8 3 0 7 7 3 9 is 4 10 7 17 ALL l 3.0 l 11 l , L l' I .11 1 .
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1 ' I ' 2 1 9 75 5.0 ? 6 12 1 3 1 12 i I 1 3 f4 5.5 3 1 5 1 . I 11 12 6.0 1 is . 1 . 1 . 1 I 8 : y 6.5 1 1 .. 1l 2 ' 5 l e 2 l 2 M 7.0 . l M 7.5 1 1 . 2 8.0 l 1 l . I "ALL 40 : 391 f 0!, 18 40 40 ' 25 7 184 Il 1 1 1 I 9 ; 6 9 84 0 330 l ) i
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Z Ee e eme e =meme m o em ee n ee n n ee n - em =eweeeeweee em em om em se em em e. em em em .E =a s oe eeseemeeemee O to u -e----o----e- e - en - - - - - o- e - e. i w- eamea.e =ee- eeeee w e e. e- - e e- = e- o- a -- U v e. e. ens e = anena. as sees ema. =====.=ene enen es e= ens em um ., enseene. - en - emao == == am e= emum a a e l f e@ E E ,.,4 O O == se se ce en ce se se ce se ce em em en em en om en om em en em == es es se se ce se se se se se em em em em em em em em en em eo ! em $= ca as at tue b= A4 em e.2 g ceneceneen cececce. nee ecepececen ececepecece a. e enemmeneem Gemememomme a. e e e ee m en o m at e s mesomemessee , {- p ene > . .......... ........... M . eel ...es se ,. . . . . . . se ........... NO - .e en - en - - e.e..-e.-- 40 e ee ee ee es se re ec ce se ee s se e. se ee ss ee / e g; M O **==-----e====. - = = = = = = = = = = = - = = =====.==.= O =====.=====e=m ===.==e===*-==== ee E ===a===.===e - E ======e .. - -. .=======ee== C i Z ' l W Ce C < l i .s* l l I i l a l i 1 APPENDIX TABLE l-14. (CONTINUED) iU DATE STAil0N RFF TIME Tlft PROJ SANFtt INST DEFTN HD DT TR IST STAct e TEMPERATURE CONDUCTIVITT SAtlNITT SICMA-T DISS DITCIN e O O FEET MtitRS CD F C CD MMH 0fCM CD FFT CD CMFCM3 MCfL %B4T Co 13 9 I5 3 1 4547 M 388 08554 8051 0.5 8.9 44.9 4.4 A 33.8 A 33.5 A 35.5 f.0 te & II 4 85 I i 4547 H 108 18554 8411 3.3 3.8 14.9 4.4 4 33.8 4 38.5 A 15.5 9.4 8 13 4 45 1 I 3547 N ISO 84334 3453 4.5 3.0 44.0 4.4 A 33.7 A 33.9 4 35.5 0.0 e i St t OS 3 8 1547 H Its 98354 8451 13.8 4.0 44.9 4.4 A St.7 A St.t & 35.5 0.0 0 , II 4 05 3 I 4547 N 200 80554 3458 19.4 4.0 44.0 4.4 A 33.8 A 33.5 & 35.5 0.0 0 It t 85 3 8 1547 H 148 40554 3453 34.3 8.0 14.0 4.4 A 31.9 A 38.4 A 35.4 0.4 6 II 4 85 3 8 1547 N ISO 88334 5453 33.0 36.0 99.8 4.7 A 33.9 A 31.4 A 35.5 0.8 0 ] II 4 OS 1 l 1547 H ISO 88554 9458 39.3 83.0 44.5 4.9 4 33.3 4 St.7 A 15.4 4.8 4 II 4 SS 3 8 1547 H ISO 88334 3453 45.9 10.0 44.3 4.7 4 33.8 A 33.8 A 35.7 8.0 0 13 4 05 I i 1547 H tot 80534 5953 31.5 84.0 44.0 4.7 A 33.9 A 58.7 4 15.4 0.8 9 13 4 85 3 8 1547 N ISB 89554 5451 55.7 17.0 44.8 4.7 A 33.9 A 33.7 A 25.4 f.3 ft A Il 4 45 7 9 1435 C 198 19557 5458 0.0 8.0 44.3 7.9 A 33.5 4 33.3 4 15.1 0.4 Of A II 4 05 7 I I435 E 388 00557 9453 3.3 8.8 45.4 7.4 A 33.5 A 33.4 A 15.5 9.9 9 it 4 05 7 I 1435 t ISO 90357 9951 4.5 2.0 45.4 7.0 & 53.5 4 St.4 A 35.5 9.8 9 13 4 05 7 8 1835 t 200 98557 3453 13.9 4.8 45.4 7.9 A 33.5 A 33.4 A 15.5 0.0 0 II 4 85 7 8 1435 t 388 00537 3453 89.4 4.0 45.4 7.4 A 33.5 A St.4 A 35.5 0.g 0 II 4 85 7 1 1835 E 390 08537 3453 24.3 0.0 05.4 7.4 A 33.5 A 32.4 A 35.5 0.0 0 Il 9 85 7 t 9435 C 200 08537 3451 33.0 19.9 13.4 7.5 4 13.5 & 38.5 & 35.4 e.0 0 63 4 85 7 I 1435 t 300 80557 8953 39.3 13.0 45.4 7.9 A 33.5 4 33.4 & 35.5 0 0 0 13 4 45 7 8 1435 t les .I8357 3453 45.9 49.0 43.4 7.4 A 33.5 A 31.4 4 35.5 0.0 t it 4 05 7 1 1435 t 300 00357 3453 53.5 14.0 44.3 7.9 A 34.1 A 31.0 A 35.4 0.0 0 ft t al 7 8 1835 t 188 80557 3453 59.8 88.0 44.4 8.8 A 34.3 A 33.9 A 35.4 7.8 ft A >I D= , Ln i I DATE STATION Rtr TIME TIDE FROJ SAMFLE INST DEFTH YtMPERATURE CONDUCTlvlTT sat!NITT SICHA-T DISS OSTCtN d MO 07 TR 8 EST STACE B 4 0 Ftti METERS CD F C CD MMH 0fCM CD FFT CD CMfCM3 MCFL % SAT CD 4 ft is 95 1 3 1555 F ISO 85478 3451 0.0 0.0 45.4 7.4 A 33.3 A 33.3 A 15.3 9.0 93 A II I6 83 3 8 ISSS F 199 48470 8451 3.1 1.0 45.7 7.4 4 33.3 4 33.3 4 35.3 9.9 9 13 le 35 3 3 1555 F 200 88470 9453 4.5 3.0 45.7 7.4 A 33.3 A 33.3 A 25.1 0.0 e il 10 SS 1 1 1555 I Ile 88470 0458 13.8 4.0 45.7 7.4 A 53.4 A 32.3 4 15.3 0.9 9 la le 85 t I 1555 t ISS 90470 B453 19.4 4.0 44.4 8.0 A 33.9 A 33.5 A 35.3 0.0 0 83 39 05 3 8 1555 F Its 08470 5451 14.1 0.8 14.4 8.8 4 34.8 A 31.4 A 15.4 0.0 0 13 le 85 3 I 1555 f 180 08470 8453 23.8 10.0 44.4 8.8 A 34.0 A 33.5 & 35.3 0.0 e it 19 05 I l 4555 F Itt 80479 9451 39.3 31.9 94.0 0.4 A 34.8 4 33.4 & 35.4 0.0 0 33 30 45 3 I 1555 t 398 SO470 5453 95.9 14.5 44.5 7.0 A 33.8 A 33.4 A 35.4 0.9 0 4 II IO 35 1 5 1555 F ISS 08479 8453 49.1 15.0 44.3 7.9 A 30.0 & 33.7 4 15.5 7.9 03 & II 19 05 7 9 1835 F 308 00477 3453 8.0 0.9 44.0 4.4 A 33.4 A 33.3 A 35.4 0.7 87 A It 18 SS 7 8 1835 F tes 40477 5433 3.3 1.8 45.0 7.1 A 53.3 A 33.4 4 15.5 0.9 9 13 IS 35 7 t 1835 F Its 00477 3453 4.5 3.0 95.0 7.3 4 33.4 A 33.7 A 35.4 c.3 e 33 le OS 7 8 3435 F Its 89477 3451 13.8 4,9 45.4 7.0 4 33.4 A 31.5 & 35.4 0.0 0 13 ID 05 7 I 1435 F 398 58477 5453 19.4 4.9 43.4 7.9 A 33.0 A 33.5 A 35.4 0.0 0 It It 85 7 I till F 380 88477 3432 84.3 8.0 15.3 7.3 4 33.4 4 31.4 A. 15.5 0.0 0 ! 18 le 05 7 8 1435 t Ice Stoff 8453 33.8 10.0 45.4 7.4 A 33.3 A 33.3 A 33.3 9.8 e , it le 65 7 I 1435 F tes 88477 8453 39.3 88.0 St.7 7.0 4 33.3 4 38.4 A 15.5 9.0 e il 50 05 7 I 1835 F III 88477 Belt 45.9 84.0 95.7 7.4 A 33.7 A 33.7 A 35.5 c.e e it le SS 7 I 1835 F 308 88477 3453 53.5 14.0 44.0 8.3 A 34.4 A 33.0 A 15.5 7.1 7t A m . . ____ , . _ _ _ _ _ _____l1 I i A-46 1 1 I i l l 4 IO *E at et 4 IO as 4 se at ese W es y i U l => Weeeeeeeeep Woesa. eeeeem U. e meGemees, e .e .e ., eeeeee e en j ** at em en a e se og m en e o O em O ag We es es en en sm. e e. e. e. e. e. e. e. e.o*se. . .
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< w ceneecec e e ve nececcenceem a c e n c e m e wo ne vo we e we n c e n c e pm e e es e e e e e e e ED h eeeeeSDeeeeee en eeeeeeeeee e e e e e e e op = en one W w = = = .* * = = .m m % em . . . . .m m . .m . s. w ..mem.**..** .m===.m.. N at O eme emenmeeeam . em ammen emaus e. e= mea = es ** st O 8e se se se 8e se 8e se se se se se se ye se ye ao se se ye E G M8 O g g ***e".**a.**=**e**.aas" = ee == = =.e- ***B . = .s.e aa=*=e.*e- ame =.==.m== ** 8e ** *e a O *e*******="***es E so .e = = e. e.e ** e. =m *e=*e e. sees se= **a. ** = e*e *e a. Z id APPENDIX TABLE 1-14. (CONTINUED) A = DATA OK. B = BECKMAN INSTRUMENT FIELD CIIECK EXCEEDED ACCEPTABLE TOLERANCE LEVELS. D = DIFFERENCE BETWEEN DISSOLVED OXYCEN REPLICATE SAMPLES WAS >0.5 mg/1. Il = IIICII WATER (15 MINUTES EITIIER SIDE OF SLACK). E = EBB TIDE. L = LOW WATER (15 MINUTES EITIIER SIDE OF SLACK). F = FLOOD TIDE. I C APPENDIX 2.0 ADULT FINFISH NSPE = number of taxa C/E = catch per unit effort CPUE = catch per unit effort N (in column head) = number of samples N (in table body) = no samples collected O i RES801 DM8D1 SUM APPENDIX TABLE 2 1. MONTHLY CATCHES AND MONTHLY PERCENT COMPOSITION; (REPLICATES SUMMED); 0F FISH COLLECTED BY OTTER TRAWLSf 0FF HAMPTON-SEABROOK. SEABROOK ENVIRONMENTAL STUDIES.1985. i )- J F I M A I M i J I J A S I O l N D A E I A P l A l U U U E C l O E N B R R i Y l N L C P T V C ' 1 , l 2 2 2 1 2 l 2 1 1 1 2 2 2 1- -MONTHLY CATCH 4 5 1 8 3 1 0 l 8 I 5 1 5 4 ! 5- 9 I ALL ITI ALOSA PSEUDOHARENCUS l 1 l 41 1 4 u I ENCllELYOPUS CIMBRIUS l . l 1 3 4 j l CADUS MORHUA 3L 25 9 4 6 2 1 1 7 2 3 62 I .CLYPT0CEPHALUS CYNOCLOSSUS 1 3 11 i S : I .HEMITRIPTERUS AMERICANUS 1 2 3 ! l HIPPOCLOSSotDES PLATESS01 DES . 1 3 4 . I LIMANDA FERRUClNEA I 56 20 59 III 127:m 109 100 ' 114 49 9 .63 43 860' ,LOPHlUS AMERICANUS I I 1 l 1 l 2 8 MACROZOARCES AMERICANUS 4 2. 4 41 3 3 l 6 1 3 3 3 36 $$ MERLUCCIUS BILINEARIS , f 2 8 5 ' 1 2 3 21 l MYOXOCEPHALUS OCTODECEMSPINOSUS 3 3 5 67 58 43 28 84 11 99 28 42 4711 l MYOXOCEPHALUS SCORPlUS 1 . I 2 I OSMERUS MORDAX- , 7 9' 11 l . 4 21 I LPARALICHTHYS OBl.ONCUS i 1 l 8 9 11 . 11 3 43 I HPEPRILUS TRIACANTHUS I I 1 2 3 I POLLAClllUS VIRENS I 11 1 I l 8 20 ' 'l PRIONOTUS CAROLINUS I l i 2 2 lPSEUDOPLEURONECTES AMERICANUS 9 31 8 6 2 15 ; 18 I 57 l- 17 29 13 25 l 202: RAJA SP. 3' 51 12 241 to 8 30 261 28 38 11 18 213' SCOPHillALMUS AQU0 SUS 4 5: 3 14 ; 14 4 8 18: 9 9 11 .14 113' , ;SPHOEROIDES MACULATUS I 1 1 l lSTENoiOMUS CHRYSOPS . . 3 2 5 - I UROPHYCIS SP. 1 8 ' 78 88 123 35 35 . 2 11 381 l ALL 87 73 . 101 246 238 ; 280ll 297 . 444 161 ; ~239 138 174' 2478 1 4 --.__.____ _ _ _ _ _ _ _ _ _ _ . _ , _ _ . . <_ . _ _ . . _ . _ . . -.- . - ~ _ . - ._m _ . . . . _,. RES801 DM801 SUM APPENDIX TABLE'2-1.'(CONTINUED)- MONTHLY CATCHES AND MONTHLY PERCENT COMPOSITION; (REPLICATES SUMMED); OF FISH COLLECTED BY OTTER TRAWLS OFF HAMPTON-SEABROOK. SEABROOK ENVIRONMENTAL STUDIES,1985. J F ! M A -l M J J A S O- N I D l A E A P i A U U. U E C 0 E N B R R Y N .L C P T V C-1 2 l 2 2 l 1 2 2 1 1 1 2 2 2 l 1 MONTHLY CATCH 4 1 5 1 1 8 1 3 0 I 8 5 5 4 1 5 l 9 ALL IT2 lALOSA AESTIVALIS l 1 ! Ni l l l l l (ALOSA PSEUDOHARENGUS ll 2 N 11 '3 l ALOSA SAPIDlSSIMA 1 N l '
- 1:
( AHMODYTES AMERICANUS 1 l N 1 1 CLUPEA HARENGUS HARENCUS ' N l [NCHELYOPUS CIMBRIUS -1 1 N 21 GADUS MORHUA 5 1: j' l I i N -1 71 p, - LCLYPTOCEPHALUS CYNOGLOSSUS . N l
- HEMITRI PTERUS AMERICANUS I 2 l 21 8 .1 1 N 3 1 181 us
! HIPPOGLOSSOIDES PLATESSOIDES I I C) N l 1 IllMANDA FERRUCINEA i Sh 30 29 I 481 6 1 4 3; N 12 l 10. 151 lLIPARIS ATLANTICUS I 1 I l- N 1 1 3 , ILOPilluS AMERICANUS L N l , -I MACROZOARCES AMERICANUS i l 19 1 19 N 10 50 MELANOGRAMMUS AEGLEFINUS l . N i MENIDIA MENIDIA 1 N 1 l MERLUCCIUS BILINEARIS 9 N 9 l MYOXOCEPHALUS OCTODECEMSPINOSUS 6 1 21 7 1 2 N , 4 : 22 9 73 , I MYOXOCEPHALUS SCORPIUS 5 . 1 1 1 N 1 2 10 11 lOSMERUS MORDAX 1 18 I '68 7 N 4 2 8 29 IPARALICHTHYS OSLONCUS I I N IPEPRILUS TRI ACANTilUS H I , N l i - POLLACHlUS VIRE NS I I 3 :N .11 15 19 , PRIONOTUS CAROLINUS ' N : 1 1 i HPSEUDOPLEURONECTES AMERICANUS 19 : 20 l 10 17 9 30 3 . 49 N . 14 l 33 6 . 210 i RAJA SP. I 1 1 1 3 4 : 11 2; 2 Ni 2 5 31
- SCOPHTHALMUS AQUOSUS 21 4 2 2 6' l : 331 : 4 4 ;
-N 5 3 84 l lSPHOEROIDES MACULATUS N I (STENOTOMUS CHRYSOPS N 4 4 i SYNGNATHUS FUSCUS I; I I N 1 1 .TAuTOcOLABRUS ADSPERSUS I . 1 N 1 I 2 UROPHYCIS SP. l . .2 1 .18 13 5 N 3 21 44 < ,ALL, l 64L 87 . 47 136 .35 89 29 . 81 N 36 1071 . 44 755 1 _- -__.- _ _ _ _ ~ _ .RES801 DM8D1 SUM . APPENDIX TABLE 2-1. ICONTINUED) MONTHLY CATCHES AND MONTHLY PERCENT COMPOSITION; (REPLICATES SUMMED); OF EISH COLLECTED BY OTTER TRAWLS' OFF HAMPTON-SEABROOK. SEABROOK ENVIRONMENTAL STUDIES 1985. J ll F l M l .A M i .J- J l 'A l S l O' i N I D l A E i A I P -A. U U U: 1 E C' ' 0 i E 1 N R I R I R Y N L C P T V C l I 1 2 2 2 1 1 2 2 I 2 2 2 1 1 MONTHLY CATCH I 4 l 5 h I l' 8 3 0 h 8 .1.I5 5 4 .....------l' 5 9 i ALL IT3 "AtOSA PSEUDOHARENGUS I i 1 71 1. l l I l 7 l l ,CLUPEA HARENCUS IIARENGUS : 11 l l l I 1 i
- GADUS MORHUA l 1: 3 4 3 38 8 4 2 IHEMITRIPTERUS AMERICANUS 1 3 31 69 l l .
3' il 1 1 6 l I HIPPOCLOSSOIDES PLATESSotDES l 1 1 1 LIMANDA FERRUGINEA l 19 35 14 102 . 21 54 54 57 531 -24 26 15 474 I . MACR 020ARCES AMERICANUS l 1 ti l 1: 28 3 l 14 1 2 .I I MELANOGRAMMUS AEGLEFINUS I I 31' Il 1 '63 ' 3 8 l l MENIDIA MENIDIA l I MERLUCCIUS BILINEARIS 61 4 : 1 1 . 11 1 l MYOXOCEPilALUS DC10DECENSPINOSUS 81. 3 .17 : 89 14 173 93 591 40 95 '11 l OSMERUS MORDAX 61 5 $ ' 53 ~655 l l 1 3 4 23 1 IPARALICHTHYS DBLONCUS l , l 1 4 1 3 . 10 3' 211 l lPOLLACHlUS VIRENS l I I 1 . I l' 1 i PRIONOTUS CAROLINUS h 1 i l' - I 1 4 5 i PSEUDOPLEURONECTES AMERICANUS l l 3 11 1 . 10 5 : 11 .17 16 6 1 71 i RAJA SP. 8 l 11 : 7 13 2 16 26 46 136 60 3 ~ 15 343 l SCOPHTHALMUS AQU0 SUS 8 l 2 3 9 2 1. Il 13 19 . 9 3 70 STENOTOMUS CHRYSOPS- . I 5 3 ~.8 ISYNCNATHUS FUSCUS I 1 3 'I l 4 I IUROPHYCIS SP. 1 -1 1 . ' 32 66 74 . 92 ' .75 l 171 151 373 i lALL- l 50 : 72h - 55: 256l 47 345' 256 270 362 303 l 1261' 681 22108 a o - c-- - . -. , _.. - -- - ..~. .- - - - . . .- , . ~ CES8D1 DM8D1 1 l l SUM 1 APPENDIX TABLE 2 1. ICONTINUED) MONTHLY CATCHES AND MONTHLY PERCENT COMPOSITION; l REPLICATES SUMMED); OF FISH COLLECTED BY OTTER TRAWLS OFF HAMPION SEABROOK. SEABROOK ENVIRONMENTAL STUDi[S,1985. l J F l M A I M J J A S I 0 N D l l A E A P l A U U U E C O E l l N 8 R R I Y N L C P- T V C- l i~ l I 4 2 2 2 1 2 2 1 1 2 _2 l 2 1 l MONTHLY CAICH 4 5 1 L 8 3 .O , 8 5 i 5 4 l____..___9 5 ALL l lALL lALOSA AESTIVAllS H i I l l l l IH l lALOSA PSEUDOHARENCUS 13 : 1 l 14 l lALOSA SAPIDISSIMA ' r 1 , l 1 , l IAMMODYTES AMERICANUS 1 1 l l 1 4 1 CLUPEA HARENCUS HARENCUS 1 ; I H 1 . }' .ENCHELYOPUS CIMBRIUS J , l i 1 : 1 3: 6 , GADUS MORHUA 3 26l 12 13 10 ; 40 9 4 9 5 7 138 i l ,
- CLYPTOCEPHALUS CYNOCLOSSUS p.
l 1 . 3 : 1 5 IIEMITRIPTERUS AMERICANUS 2 5 8 1 . 1 l 2; .6 2 27 ut I l HIPPOCLOSSOIDES PLATESSOIDES 2 3 - 5 " l HLIMANDA FERRUCINEA 83 85 102 261 154 164 158 174 102 33 101 68 14851 1 l ILIPARis ATLANTICUS 1 l 1 1' 3 I lLOPHluS AMERICANUS l .1 1 2 l MACROZOARCES AMERICANUS 1 16' 3 51 1 8' 36 4 of 2 4 13 .3 .149 l MELAMOCRAMhuS AEGLETINUS 3 . 3 1 l ; MENIDIA MENIDIA 1 1 1 1 2 l lMIRLUCCIUS Bit.INEARIS l l I 2 8 20 1 6 1 3 41 , l i IMYOXOCEPHAtUS OCTODECEMSPINOSUS' 17H 6 1 23 : 177 79 217 121 145 51 198 103 62 . 1199 6 l lMYOXOCEPHALUS SCORPIUS l , .1 ' .1 1 3 . -12 l OSMERUS MORDAX 14 15 6 i 6 7 7 4 2 12 73 l 'PARALICHTHYS OBLONCUS I 1 9 131 14 21 6 64 ) l PEPRILUS TRIACANIHUS I I I 1 2 3 l lPOLLACHlUS VIRENS. I 12 1 4 1 15 .8 40 l lPRIOMOTUS CAROLINUS I l . 3 5 8 I 4 l lPSEUDOPLEURONECTES AMERICANUS 28 26l 19 24 11 ~ 55 . 26: 117 348 59 52 32 483 1
- RAJA SP. 12 178 19 40 16 .
35 58 . 74 164 -98 16 . 38 587 lSCOPHIHAtMUS AQUOSUS '34 39h 10 25 ,18 ' 9 14 23 22 28 25 20 267 ISPHOEROIDES MACULATUS l- i' i 1 ,1 i SIENOTOMUS CHRYSOPS 12 5 i~' 17 SYNCNAIHUS FUSCUS 11 ~l . _3 1 5 TAUIOGOLABRUS ADSPERSUS h 1 l l 1 2 UROPHYCIS SP. Il . 3h 10 1281 1671- 202 127 113 21 . 26 798 Al l 201; 232 1 2031 638 1 320' 7141 5821 795 523 578 3711 286l 5443 + t w _ _ _ . - _ . - _ _ - _ _ - - _ _ _ - - _ _ _ _ _ - _ _ - _ _ _ - - _ - _ . - - a ; RES801 DM801 3 4 r PCNT APPENDIX TABLE 2-1. (CONTINUED) MONTHLY CATCHES AND MONTHLY PERCENT COMPOSITION; (REPLICATES SUMMED); 0F FISH COLLECTED BY OTTER TRAWLS TRAWLS OFF IIAMPTON-SEABROOK. SEABROOK ENVIRONMENTAL STUDIES.1985. + 1 J l F ' M H A' l M i J l'J A. .S O N I D- l l l A E A I P l A ; U l U U E C 0 ' E l
- i i N . B R R H Y N I L G P T V. C l i I 2 , 2' 2 l 1 2 l 2 1 1 l 2 2 2 l 1 1 PERCENT COMPOSI T ION -4 l 5 1 1 8 3 l' 0- .8 5 1 5' 4 5 l 9 ALL-1 -.--.------......------...--........---------------.........--------......-------.-----..------.---.................--
5 lT1 IALOSA PSEUDOHARENCUS l l '1.61 I l l l l 0.2 i l lENCHELYOPUS CIMBRIUS I 0.61 1.7 0.2 1 :CADUS HORHUA 3.4 34.2 8.9 . 1,61 2.5 O.7 0.3 1 2.9 1.4 . 1.7 2.5 l lCLYPTOCEPHALUS CYNOCLOSSUS I 0.4 1.11 0.3 0.21 l IIEMITRIPTERUS AMERICANUS l l 0.6 . 0.8 0.11 l HIPPOCLOSSOIDES PLATESSotDES 1.0 : 1 1.1 . 0.28 l lLIMANDA FERRUGINEA 64.4 27.4: 58.4 : 45.11 53.4 38.9 33.7 25.7 30.4 3.8 45.7 24.7 34.7 p l lLOPHlUS AMERICANUS , l 0.3 0.6 . I 0.I' s-IMACROZOARCES AMERICANUS 5.5 : 2.0 1 1.6 : -1.7 1.1 1.0 1.4 0.6 . 1.3 ' '2.21 1.7' 1.5 ui I I MERLUCCIUS BILINEARIS I l 0.71 2.7 ~1.1 0.6 0.8 i 1.7 ~0.8 ; Myox0CEPilAlus OCIODECEMSPINOSUS 3.4 27.2l 24.4 18.9 l l- 4.1 5.0 : 15.4 , 9.4 6.8 41.4 20.31 24.1 i '19.0 I 'MYoXOCEPilALUS SCORPIUS 1.1 0.6l 0.1 l :0SMERUS MORDAX- 8.0 12.3 1.01 2.51 0.8 l PARALICHTHYS 00LONCUS I 0.4 3.4' 3.2 3.7 , ,2.58 ! 1.9 l -1.7 i 4 l ' PEPRit.Ils TRI ACANIHUS l 0.41 1.4 ' l' O.1J lPOLLACll10S VIRENS ' l I 4.5 0.4 1-4.6 0.8 H ,PRIONOIUS CAROLINUS I . L . 'l' O.8 0.1 PSEUDOPLEURONECIES AMERICANUS l 10.3 l 4.11 7.9 2.41 0.8 5.4 6.1 12.8 10.6 : 12.1 , 9.4 14.4 8.2 ; RJLJA SP. l ' 3.4 I 6.8H 11.9 .9.8 4.2 , 2.9 10.1 5.9 ' 17.4 15.9 8.0 10.3 8.6 i ,
- SCOPHIHALMUS AQU0 SUS l 5.7 l 5.5 3.0 5.7 ;
5.9 1.4 2.7 1 4.1 , 5.6 3.8 8.0 8.0 4.6 l lSPil0ERotDES MACULATUS I .I I I I l 0.7 . <0.1 1.3 1.4 a l lSTENOTOMUS CHRYSOPS 1. I l 1 1 0.2 l UROPHYCIS SP. I I , 1.01 l 3.41 27.9 l 29.6 27.7 l 21.7 14.6 1.4 '6.31 15.4 l ALL 1100.01100.0: 100. 01 100. 01100. 01 100. 01 100. 0 100. 0 1 100. 0 100. 0 100. 01 100. 0 l 100. 0 . 4 E 3 = i l g l RES8D1 DM801 PCNT APPENDIX TABLE 2-1 (CONTINUED) MONTHLY CATCHES AND MONTHLY PERCENT COMPOStil0N: (REPLICATES SUMMED): OF FISH COLLECTED BY OTTER TRAWLS' TRAWLS OFF HAMPTON-SEABROOK. SEABROOK ENVIRONMENTAL STUDIES,1985. J l t M ' A I M J J A S l O N D A l E A P A U U U E ' C 0 l E ll N I B R R Y -N L G I P l T V C I l l l 2 l 2 2 1 2 ' 2 1 1 1 2 . 2 ' 2 1 l PERCENT COMPOSITION l 4 1 5 1 8 3 0 8 5 I 5 1 4 l 5 9 ALL ...-----------l 112 ALOSA AESTIVAlls l l 0.7 i N i 0.1 ! l : ALOSA PSEUDOHARINGUS l ! 1.5 ' N 0.4 l lALOSA SAPIDISSIMA I 0.7 N O.9' O.1 l lAMMODYTES AMERICANUS 1.6 N 0.1 l lCLUPEA HARENGUS HARENGUS ' N l l[NCllELYOPUS CIMBRIUS ' l l 0.7 . 1.1 N 0.3 l l GADUS MORilUA I I 3.7 2.9 N 2.3 0.9 >, I lGLYPTOCEPHALUS CYNOGLOSSUS N l 4-1 HEMiiRIPi[RUS AMERICANUS 3.l u 4.3 5.9 2.9' 3.4 l . I lflPPOCLOSSOIDES PLATESSOIDES u L l : N N 8.3 0.9 2.4 $ l ;LIMANDA FERRUGINEA 12.5 34.51 61.7 , 35.3 17.1 1.1 . 13.8 3.7 N . 11.2 22.7 20.0 l .ItIPARIS ATLANilCUS 2.1 2.9 N 2.8 0.4 L ILOPillUS AMERICANUS N < MACROZOARCES AMERICANUS 1.1 14.0 ; 2.9 l 21.3 i N I 9.3 6.6 MELANOCRAMMUS AEGLEFINUS L H H I lMENIDIA MENIDIA 1.1 I H N 0.1 l lMERLUCCIUS BILINFARIS I . I 11.1 N 1.2 H 1MYOXOCEPilALUS OCTODECEMSPINOSUSR 9.4 2.1 15.4 20.0 1.1 2.5 N " 11.1l 20.6 20.5 9.7 "MYOXOCEPflALUS SCORPIUS l 7.8 , 2.9 1.1 . N 0.9 4.5 1.3 HOSMERUS MORDAX 1.6 ; 1.1 4.4 I 8.6 N 11.1 1.9 18.2 3.8 f I 'PARAllCHTHYS ODLONGUS I l N i l HPEPRILUS TRIACANillUS i l N I I POLLACillUS VIRENS l 3.4 N 2.8 14.0 2.5 I PRIONOTUS CAROLINUS I I I i N 0.9 0.1 1 PSEUDOPLEURONECTES AMERICANUS I 29.7 1 23.0 1 21.3 12.5 25.7" 33.7 10.3 60.5 N 38.9 ' 30.8 13.6 27.8 l L R AJ A SP. 1.6' 1.1 1 1 2.2 11.4 : 12.4 6.9 2.5 N 1.9 11.4 4.1 ISCOPil1HALMUS AQU0 SUS 32.8' 37.9 8.5 . 1.5 5.7 4.5 20.7 4.9 N 4.7 6.8 l 11.1 llSPfl0EROIDES MACULATUS I I l l N l l STEN 010MUS CilRYSOPS I N 11.1 0.51 h SYNGNAllius FUSCUS I I . N 2.8 0.1 i TAUTOCOLABRUS ADSPERSUS I 2.9 N 2.8 0.3 l H UROPHYCIS SP. 1.5 2.9' 20.2 l 44.8' 6.2 N 8.3' 1.9 5.8 I lALL 1100.01100.0 '100.0 100.0 100.0l100.01100.0:100.0 N 100.0(100.0 100.0l100.0 - . - - - - - - . - . . - - . . - _ . . . _ ~ . . _ _ . . - - . . _, . - - - . . . - . - - . - ~ . - - .. -- = . _ ~ . . RES801 DM801 l t PCNT APPENDIX TABLE 2-1. (CONTINUED) ' MONTHLY CATCHES AND MONTHLY PERCENT COMPOSITION; (REPLICATES SUMMED) OF FISH COLLECTED BY OTTER. TRAWLS TRAWLS OFF llAMPTON-SEABROOK. SEA 8 ROOK ENVIRONMENTAL STUDIES.1985. l l J ' F l M l A M I J l J ' A S 0 i N D. I I A ' E A l P A l U U U E C 0 E l l -! l N B R 1 R Y I N L C P T V C- 1 I i . I l L l l 2 1 2 1 2 1 1 1 2 2 1 1 2 2 2 1 l l PERCENT COMPOSITION I 4 1 5 l 1 1 8 l 3 0 8 5 5 1 4 1 5 ~ 9 ALL IT3 ______............__...__........ __.........__.___.........._____....................____l l l IALOSA PSEUDOHARENCUS l .I I l 2.71 I I l l 1- ' O.31 l "CLUPEA HARENCUS HARENGUS I I l l 0.41 H l l , <0.11 l i RGADUS MORHUA l l 1.41 3.51 1.6 6.4 11.O ! 3.1 l 1.5 l 0.71 2.4 4.4 .3.11 i 'HEMITRIPTERUS AMERICANUS 1 , I 5.51 1 O.31 0.31 0.8 ~0.31-l HIPPOCLOSSOIDES PLATESS01 DES 1 11 1.8 . I l I <0.1 i LIMANDA FERRUCINEA 38.01 48.6. 25.5 39.8 44.7 15.7 21.1 21.1 ' 14.61 7.9 l 20.6 22.1 21.4 ! i l (MACR 020ARCES AMERICANUS 2.0 l 15. 3 ll 1.8 10.9 6.4 4.1 0.4 0.7 O.31 'O.3 l i 2.9 y l NELANOCRAMMUS AECLEFINUS H I l l 0.9 ; I i 1 l 0.1 , 1 MINIDIA MENIDIA I I L i I 1 i : 1.51 <0.1 ui ! I IMERLUCCIUS BILINEARIS I l 2.2 - l 1.3l 0.8 ; 1 0.5 l l IMYOx0CEPHALUS OCTODECEMSPINOSUSl 16.0 4.2 30.91 34.8l 29.8 50.11 36.3 21.9 11.0 31.41 42.1 16.2 ' 29.6 i i 10SMERUS MORDAX l 12.01 6.9; 9.11 l i 0.8 1 5.9 1.0 l I lPARALICHIHYS OBLONGUS l l h l I 2.1 1.21 1.28 3.7 0.8: l l 1.0 ! l IPOLLACHlUS VIRENS I l l 1 0.4 I l 1 I.. <0.1 l l IPRIONOTUS CAROLINUS l H I I I l 0.31 3.2 i 0.2 l IPSEUOOPLEURONECTES AMERICANUS I 4.2 1.8 0.4 1 2.9 2.01 4.1 4.7 15.31 4.8 1.51 3.2 l l RAJA SP. l 16.0 15.3 12.7 5.1 ' 4.3 , 4.6 10.21 17.0 37.6 19.8l 2.41 22.11 15.5 : l lSCOPHTHALMUS AQU0 SUS l 16.0 2.8 5.5 3.51 4.3 0.31 1 0.4' 3.6 6.3 l 7.11 4.4' 3.2 l ISTENOTGH'JG CHRYSOPS l l l l l ' i 1.7l 2.4' O.4 1 ISYNCNATHUS FUSCUS l 1.41 1 I l l 0.81 l .1 0.2 I IUROPHYCIS SP. 1 I 0.41 2.11 9.31 25.8 27.41 25.41 24.81 13.5 22.11 16.9 l lALL 1100.0 100.01100.0 100.01100.0l100.01100.0:100.0l100.01100.01100.0 100.01100.01 ' _______. ___=====________. _____..__. __. __________.__..._________.. ____.....__...____ .........____...........___.__ l CES8D1 DM8DI l PCNT APPENDIX TABLE 2 1. ICONilNUED) MONTHLY CATCHES AND MONillLY PIRCENT COMPOSITION; IREPLICATES SUMMED) OF FISH COLLECTED BY OTTER TRAWLS 1RAWLS OFF HAMPTON.SEABROOK. SEABROOK ENVIRONMENTAL STUDIES.1985. I J l F l M A :l M i J ll J l A S ll 0 N D l l A I E I A P I A l U 1 U U E C D E I I N I B l R R Y l N L C P T V C ( n 1 1 1 I I , I I 2 l 2 1 2 1 1 1 2 1 2 1 1 1 1 2 l 2 l 2 l 1 1 PE RCE NT COMPOSI T ION 4 5 l 1 1 8 I 3 1 0 i 8 l 5 .........................................................................................l IALL lALOSA AESTIVALIS I l u l l l 0.21 l 5 l 4 l 5 l 9 l ALL H l l l l l l l <0.1l I lALOSA PSEUDOHARENCUS l l l l 2.0l I 1 l l 0.31 1 0.3 l l lALOSA SAPIDISSIMA l l l 0.21 l l l I l l 1 <0.1 ' l l lAMHODYTES AMERICANUS l 0.5! l I l i I I I i <0.1 I ICLUPEA HARENCUS HARENCUS I l O.21 l l l lENCHELYOPUS CIMBRIUS I l 0.1l l l l l <0.1 l 0.21 l O.2l h i l ICADUS HORHUA i 1 l 1.01 0.11 I 1.5 1 11.21 5.9: 2.01 3.1 1 5.6' 1.51 0.5 , i 1.61 1.3 2.41 2.5H l lCLYPIOCEPHALUS CYNOCLOSSUS I l l 0.3 0.21 l lilEMiiRIPIERUS AMERICANUS 0.4 1 H l l H 0.1 Y l 1.0' l 2.5 1.31 0.3 1 0.21 l 0.41 1.01 0.51 0.5 us l lillPPOGLOSSotDES PLATESSOIDES l 1 1 1.0 1 ; 0.4: l
- l l 1 l 0.1 I lLIMANDA EERRUCINEA I 41.3 36.61 50.21 40.91 48.1 23.0' 27.1 21.9: 19.51 5.71 27.21 23.8l 27.31 l lLIPARIS ATLANilCUS l l l 0.51 l 0.3 I I t 0.21 O.11 l
1 ILOPHlUS AMERICANUS I l l l l l 0.21 0.21 l lMACRol0ARCES AMERICANUS 8.O l L <0.11 I 0.51 6.91 1.51 l 2.51 5.01 0.71 1.0. 0.41 0.71 3.5 : 1.01 2.7l l lHELANOCRAMMOS ALGLEFINUS I l l l l U.4l l l l l 0.1l l lMENIDIA HENIOlA l l 0.41 l I I l l-l lMIRLUCCIUS Bil lNEARIS l L 1 0.3 <0.11 I I l l l l 0.31 1.4 2.51 0.211 1.01 0.3 1.0L 0.8 l l MYOX0CE PH ALUS OCTODECEMSP I NOSUS $ 8.51 2.61 11.31 27.7 24.7H 30.41 20.8 18.21 9.8! 34.31 27.8 l lMYOX0CEPHALUS SCORPlus 21.71 22.0 1 3.01 l 1 0.3 0.11 l t 0.3 ! 1.04 0.2 1 10SMERUS MORDAX l 7.08 6.51 3.01 0.911 . 1 0.91 1.3 0.71 0.5 4.2 1 1.3: l lPARAllCHIHYS OBLONCUS 1 l l l 0.21 2.88 1.8 : 2.41 2.61 1.1l L , 1.21 l lPEPRILUS 1RIACANiifUS L l I l l l 1 1 I H 0.2H 0.5: 0.11 l l POLI ACHlUS VIRENS l l l 1.91 0.61 l H 0.2h 4.0 2.8 0.7l l lPRIONOTUS CAROLlHUS i H l l l l l H 0.5 1.3 1 0.11 l lPSEUDOPLEURONECTES AMERICANUS I 13.9L 11.21 9.4l 3.81 3.4h 7.71 4.5 14.7 - 6.51 10.2 14.01 11.21 8.91 l l RAJA SP. I 6.0 7.3 9.4l 6.3 : 5.0 1 4.9l 10.0 9.3 31.41 17.01 4.31 13.31 10.81 l lSCOPHTilALMUS AQUOSUS l 16.9 ; 16.8 4.91 3.9 i 5.6 1 1.38 2.4 2.9 4.21 4.81 6.7 7.01 4.9ll l lSPHOERol0ES MACULATUS I I I ! H I 4 I I 0.3 i <0.1 h l ISTENOTOMUS CllRYSOPS l l l l l l l l 2.1. 1.3 1 0.3 l l lSYNGNAIHUS IUSCUS I l 0.41 l l l l l 0.6l 0.2 l l 0.1 l ITAUioGOLABRUS ADSPERSUS l l l 4 1 0.3 I I l < l 0.2 : l i <0.11 l lUROPHYCIS SP. 1 i 1 0.5l 0.51 3.1 17.91 28.71 25.4: 24.31 19.6: 5.71 9.11 14.71 l lALL 1100.08100.01100.0l100.01100.0 100.01100.0l100.0L100.01100.0,100.01100.01100.01 D4 DMD4 i APPE NDix TABLE 2-2. OVERAtt CATCil AND PERCENT COMPOSITION BY STATION FOR FISit COLLECTED IN OTTER 1RAWLS OFF HAMPION-SEABROOK. SEABROOK ENVIRONMENTAL STUDIES,1985. I T1 1 12 i T3 l ALL i 1 . . . . . . . . . . . . . . . . . . . . . . . . . . - - . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . l l SUM l PCNT l SUM I PCNT I SUM l PCNT I SUM I PCNT l ILIMANDA FERRUGINEA i 8601 34.71 1511 20.01 4741 21.41 14851 27.31 lMYOX0CEPHALUS OCTODECEMSPINOSUSl 471 ' 19.01 731 9.71 6551' 29.6L 1199L 22.0 IUROPHYCIS SP. I 381 1 15.4l 441 5.81 373l 16.9l 798 14,7 . l RAJA SP. I 213 l 8.6 1 318 4.11 343l 15.5: 587 10.8 l lPSEUDOPLEURONECTES AMERICANUS l 202 l 8.2 ; 2101 27.81 711 3.2' 483 1 8.9h ISCOPlilitALMUS AQUOSUS l 113ll 4.6L 841 11.11 101 3.2 267 l 4.9L lMACROZOARCES AMERICANUS l 361 1.5l 501 6.61 63l 2.91 149 2.7L lGADOS MORilHA l 62l 2.51 71 0.91 69 : 3.11 138 2.5 l 10SMERUS MORDAX l 211 0.81 29 l 3.81 23 l 1.01 73 1.3 l lPARALICtlTilYS OBtONCUS l 431 1.71 l 21'l 1.0 64 1.2 1 y, IMIRLUCCIUS BILINEARIS l 21 H 0.81 9 1.21 111 0.5 41: 0.8h I lrottACallUS VIRENS l Po l O.81 191 2.51 Il <0.1 h 40' O.71 U' lHEMiiRIPIERUS AMIRICANUS l 3 1 0.11 181 2.4H 61 0.3 21 , 0.51 lSTENOTOMUS Ci1RYSOPS l 5 1 0.2h 41 0.5 l 81 0.4 17 l 0.31 (ALOSA PSEUDOHARENGUS l 4 l 0.2L 31 0.4 71 0.31 14 l 0.3l lMVOX0CEPHALUS SCORPIUS I 2 l 0.1 h 10l 1.3 l l 12' O.2l l PRION 0TUS CAROLINUS l 2 l 0.1 l 11 0.11 51 0.21 8 0.11 lENCHELYOPUS CIMBRIUS l 4 1 0.2 . 2l 0.3l l l 61 0.11 lCLYPTOCEPilALUS CYNOCLOSSUS 5 l 0.2l l 1 1 I Sh 0.1 l lIllPPOCLOSSol0ES PLATESSOIDES 4 l 0.21 l l 11 <0.11 5 ; 0.1 ISYNCNATituS IUSCUS ' l l 11 0.11 4l 0.2 5 I O.1l ILIPARIS ATLANTICUS , I i 3L 0.41 h 3 0.11 lMELANOGRAMMUS AECLEFINUS i . ; I 3h 0.1h 3 0.11 lPE PRit us TRI ACANIHUS l 31 0.1 l l 31 0.l i ILOPillUS AMERICANUS l 21 0.11 h 21 <0.1 lMENIDIA MENIDIA l l l 11 0.1H l <0.1 21 <0.1. IIAUTOGOLABRUS ADSPERSUS l l l 2 0.3 I 21 <0.1 lALOSA AESTIVAllS I l l 1 0.1 l 11 <0.1 IALOSA SAPIDISSIMA I l i IN 0.11 H 1h <0.1 lAMMODYTES AMERICANUS l l l 1h 0.111 1: <0.1 1 lCLUPEA ifARENCUS ItARENCUS l l l l H I <0.1 1' <0 I ' ISPHOEROIDES MACULA 10S l 11 <0.11 I i 1 <0.1 lALL l 24781 100.01 7551 100.0 2210l 100.0 5443 100.0 l RES3D1 DM301 APPENDIX TABLE 2-3. NUMBER OF INDIVIDUALS AND SPECIES (REPLICATES SUMMED) COLLECTED PER MONTH BY OTIER TRAWLS Off HAMPION.SEABROOK. SEARROOK [NVIRONMENTAL STUDIES,1985. I 11 1 T2 l T3 l ALL l I SUM l N I NSPE I SUM l N l NSPE I SUM i N I NSPE I SUM l N l NSPE- I lJAN 241 871 41 81 641 41 91 50 : 41 61 2011 121 11h ifEB 251 731 41 81 871 41 71 72 48 9 . 2321 12L 10-l MAR 211 1011 4 ! 101 471 21 61 55 41 10 ' 203ll 10' 12 lAPR 181 2461 4 l 101 136ll 41 14 ; 256 4 l 11 : 638: 12 17 lMAY 231 2381 35l 21 12 47 4 8 320' 4l 101 l .10 14 lJUN 201 2801 41 131 89; 28 10 . 345 4 10 714 to 16 IJUL 181 2971 41 121 29 l 21 6 : 2561 4 8 582 10 13 -lAUG 151 4441 41 9h 81h 21 8 : 2701 4 101 795 10 11 ISEP 251 1611 41 13 N I l NI 3621 4h III 5231 8, 14 10CT 241 2391 41 13 361 2' 101 3031' 41 12 5781 10 18 (NOV 251 1381 41 11 107l 4 131 126 4 l 11 3711 12 - 18 Y IDEC 191 1741 41 121 441 4 l 81 68 . 4 l 9 2861 12 . 14 La lALL l 24781 481 23l 7551 32 l 241 2210h 48 " 21 54431 128 32, * . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . - ~ . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . , i I 'i i ~ CES803 DM8D3 1 l APPENDIX TABLE 2-4. OTTER TRAWL CATCit PER UNIT Eff0RT FOR SIX FINFISH SPECIES COLLECTED IN 1985. SEABROOK ENVIRONMENTAL STUDIES.1985. 1 5 l T1 i T2 l T3 l l CPUE l PCNT l CPUE l PCNT I CPUE I PCNT l 1 ~ g........................................................................ HLIMANDA FERRUGINEA 17.9 34.7 4. 7 l 20.01 9.91 21.4l ! UROPHYCIS SP. 7.9 15.4 1.4' 5.81 7.8 ; 16.9 PSEUDOPLEURONECTES AMERICANUS! 4.2 8.2 6.6 27.81 1.5 3.2 OSMERUS MORDAX l O.41 0.8 : 0.9 3.8 I O.5 1.0 ; GADUS MORHUA l 1.3 1 2.5 0.2 . 0.9 1.4 ' 3.1 1 MERLUCCIUS BILINEARIS I 0.4: 0.8 O.3 1.2 0.2 0.5 ll ALL OTHER T AXA i 19.4 37.6 : 9.5 40.4 24.8 53.8 1 ......................................................................... i s ut W l I i - M F i 1 h CES8D1 DM801 APPEN0lX TABLE 2-5. FISH SPECIES COLLECTED IN Gitt NETS (SUM OF TWO DAYS) FISHED MONTHLY AT SURFACE AND OFF-BOITOM DEPTHS OFF HAMPTON-SEABROOK. SEABROOK ENVIRONMENTAL STUDIES,1985. t l ...____...__..... ____.__..___.__..____....____..._____....______. I J ll F M l AI M J J l A SI O N I DI I l A E A P A U U U E l C 0 El l l N 8 R R Y N L G P T V Cl 1 l , -----------I 1 2 21 1 1 2 1 1 1 1 2 1 1l l l DEPTH l 5 i >1 1 1 1 6 6 0 6 1 4l 8 2 I; 4 l 7 l ALL l ,___........ _______....___..___...... __ __________....___________ ......__....____..__...._____..__....____..__..___ l lG1 lALOSA AESTIVALIS SURFACE I l l l 5l l 1l l 3l 3 121 l l I 0FF BOTIOM I I l l l I l l 2 2 l l IALOSA PSFUDOHARENGUS SURFACE I l l l l l 3 3 l lBREV00RTIA TYRANNUS l SUHFACE l l 1 1 l l lCLUPEA HARENGUS HARENGUS HSURfACE I I 21' 12 ' 33u l l HOFF BOTTOM I 1 . I 2 . 2 , 3 ' 9 l : CADUS MORHUA LOFF-Boi!OH ; , 1 : 1 1 l ! MERLUCCIUS BILINEARIS I OFF-BOTTOM : 1 1 1 3 l 4 l Y. l IMYOX0CEPHALUS OCTODECEMSPINOSUS l SURFACE L ; i 1 .1 1 m l IPEPRILUS TRIACANTHUS SURFACE I I 61 6 O l lPOLLACHlUS VIRENS OFF-BOTTOM I 27 l 11 l 4 L -11 43 l lPOMATOMUS SALTATRIX LSURFACE , 1 1 3 1h 4 ; I lPSEUDOPLEURONECTES #SERICANUS LOFF-BOTTOM l . 2 l 2 l lSCOMBER SCOMBRUS LSURFACE I i 1 . 2 : 3 l l :0FF-BOTTOM. l I 1 1 1 3 l lSCOPHTHALMUS AQUOSUS l SURFACE L l 1 I I I i l lSQUALUS ACANTHIAS l 0 F F-BO T T OM ll l h l L 8 8 i I lSYNCNATHUS FUSCUS ISURFACE I I I l 1 ! 1 l I UROPHYCIS SP. lOFF_ BOTTOM l l l 1 61 I . I 7 ; ALL l l SURFACE l 11 211 5 i 1 19 3 2 6l 7 65 l H l0FF-BOTTOMI l Il Il 3 l 28 191 13 l 3 1 1 7l 2 791 ____ - __.b CES8D1 DM801 APPENDIX TABLE 2-5. ICONTINU[D) FISH SPECIES COLLECTED IN CILL NETS ISUM OF TWO DAYS) FISil[D MONTHLY AT SURFACE AND OFF-BOTTOM DEPTHS OFF HAMPTON-SEABROOK. SEABROOK ENVIRONMENTAL STUDIES.1985. l J l F M I A l M ' J l J A S " O l' N Dl l' A l E A , P l A U U U E C , O E Nl B Rl R l Y N L G P T H V C ~ l l l l 'I 1 l 2 2 ' 1 1 2 1 1 'i 1 1 2 1 , 1 l DEPTH l 5l 1 1 6 6 0 6 4 ' 8l 2 4ll 7 ALLI ,.___ _......................___...... __l....... ................................ _.................................. lC2 lAtOSA AESTIVAllS ll SURFACE l h L L 11 l 3 i 31 1 7 l l Loff-BOTTOM l 2 5 l 2, 9 l lALOSA PSEUDOHARENCUS ! SURFACE l 21 l . 1 3 l l ,0FF-BOFTOMI 2 l , ! 9 11 l lBREV00RTIA TYRANNUS l SURFACE l , I I 2 l 2 4 l l 1 0FF.BOTTOMI l i I . 2 1 3 l lCLUPEA HARENCUS ItARENGUS I SURFACE 1 , 6 l 4 l l l 10 l 2 22 . l l '0FF-BOTTOMI 4 l 3 l 4 11 l lCADUS MonliUA 0FF-DOTTOMI l l l H l )* l l 1 l l IL en I lH[MITRIPTERUS AM[RICANUS .0FF.BOTTOMI , 1l l 1 21 F* l lMORONE SAXATILIS ISURFACE I l l l l 1 11 l l OFF-DOTTON! l 1 I Il l lMYOX0CEPilALUS OC10DECFMSPINOSUS OFF.BOTTOMI l l . 1 13 l l0NCORitYNCliUS KISUTCH l SURFACE I , 1 1 L l' l l0SMERUS MORDAX HSURFACE i , 2 1 I i l 2 l l l 10FF-BOTTOM" L 2 i l 3 l: 2 L 1 l 8 l lPEPRILUS TRIACANTHUS l SilR F ACE I l ' l 7 ; i 1 8 8 I II POLLAClllUS VIRENS !OFF-BOTTOME l 4. 8 : 6 3 3' 3 l 27 l 00MATOMUS SALTATRIX l SURFACE E , . I l , 7 . l l ' 7 l 'PSEUDOPLEURONECTES AMERICANUS ll0FF-BOTTOMI l l l l 11 1 l llSCOMBER SCOMBRUS SURFACE I H I I I l ' 10 , 1 12l l l OFF-BOTTOMI I I 1 4 l 1 1 6 l lSQUALUS ACANTHIAS OFF-DOTTOMI l , i ! 8 i . . 8 l lUROPHYCIS SP. OFF.BOTTOMI . l l . I 1 1 1 l lALL . SURFACE I l 8 4 3 31 4 27 9 11 8 ! 67 l l 10FF-BOTTOMI l l 51 7 10 91 20 7: 9 10l 12' 1l 93 . D ' t~ i ie t s .. s yam l . lilill . 1l 1l 11l1l8 _ L.340i0218121216316891174 L_1 1 1 4 13 1 ~ 07 1 _ A_ 11 l _ lI l _ 111' _ . 7 6 1 91 . 3 . _ DEC 2 17_.6 _ . IIII1l _ 11l l 1l1ll1l Illl1 . - . _ 33I1 1 1 5 05 . 1 . NOV 14_. _ . 1' 11 . lllllllll l8: Ill1l . - . . 1 1 - . . 0CT 22 . . , D . . N . _ A _ lIl1ll _ llll11 1li 1 6 . E5 _ SEP _ I 2232 113 1 02_ 11 - C8 _ 18_ _ A9 _ lI1l llil1l . F1 . llll1l . 1IIlll1l 50_. R , . . 1 1411 9 4 4 ~ - 21 US . AUC 14 1 SE . l . . l1l11i1Il1l _ T0 . l' .11 . 11Ill 6t5 I77 _ - AUT . . I0 1 1 . JUL - 16 . _ - YS _ L _ . 8 . HL _ l' 8l . 111llllllilil8l1ll 3 43 . - TA _ . 2 1 1 1 ' 1 NT _ JUN . ~ ION _ 20_ _ DME _ il l l1 _ E M _ lIl111 _ l1llIl ' l UDN _ _ I1 S 2 93 . NEO _ MAY - 16 . 1 1 IHR _ . TSI . . 1Illll1llIll1 . NIV . lllI1l _ llllllI1 3 . . OFN . _ 2 1 C E _ APR 16 . . () _ .S YOK . 1lIll1 . l 1I " IillllIlll . - _ 5AO . . _ - DR . MAR 21 . _ 2 B . _ _ OA . EWE LTS . lIlI1l . llllllIll IllllIlll . B ._ F E B 21 . . - AF _ .. _ TO'. - _.lllilllllIl1l1IlIllil1l K . lIIilI _ _ 2 2 . IXMO UO _ JAN . DSR NIB 15_ _ F A _IlllIl _ IIIIllIIlIlIllllIlIlIII . ~ PSE - . M M M HMMM M MMMM M-O ODOO PTS AE- . O O O 0OOO . T T T 1TII T TTTT O.- T - NN - . ETETETETTTTEETEEETITiET . O - . COCOCOCOOOOCCOCCCOOOoCO. . LT - . LP H.ABABAB.FABBBB.FFAABAAABBBBAB. - I F F - - - - FFF - - - F - IM CA P.FRFRFRFRFFFFRRFRRRFFffRF._ - E UFUFUFUFFFFUUFUUUFFffUF . N H - D S0S0S0SOOOOSS0SSS000oS0_. I1I1lllI ' lIl(11llI1 IF F - l l_ _ S . DO _ U . E _ S . - TS CH ET O N I P - LP LE _ S S S OD _ U M C _ C E U . M _ N sC S . SO _ S E lE S R . [T _ U S R RD U XS SE . lT . C U A AO H IU PP . . CO . N N H ET ISRN SOS . EB . S N NC NNIIS . P_ . I E R A S ID AEALU IASDYA . - SF F . L A R U . A H Y C L XCRTOR HR ISAAILRB THS . - HO V O T N ABUDIVAAM NCU S ._ I D E U LRR SCO A R _ I _ T U A R HSAOTS C CSB _ - F _ S E I A RUHM 0SSS AUA _ _ E S T H OIP S1UU ML _ - _ A P R MCESUHMTR SOO _ _ O A CCULCOOE UTC _ ._ _ A A O E SU0RIATMB LOO . _ S S V P ULXERLA0M ANT . _ O O E U DROMPLMlO UEuL _ - _ L L R L AEYSEOORC QTAL _ _ A A B C cMM0PPPPS SSTA . ,llliIlIlIlI1lllllilIlll . 1 _ 0 . 8 . M . 3 . D . C . .IIlIllllIlllllI1lIllIll . 1 0 8 S - E C T'mW 1 ._ _ l25625568326111214856'4'131715111893 _ l ;1 81l ! L_31111 L 92 201 31 2 34_ _ l A_ , _ 111li- ! 1' 1 .l1l 1 11llill8ll _ 22_ DEC _ 920 1 6 2 1 1 1 64_ 4 17_ _ l1' , _ I' I , 11llI 111 _ N0V _ 9520 33 41 1 81 144_ 22_ 14_ _ 1 l1 _ ,l 1ll111I 1hl' I1l _ 1 213 111 1 _ 0CT _ 11 1 1 4i_ t D N 2 2 . ._ ' _ .illli ,_ A , . ltli11 ill i lI ' 3'1 5'3 4432" 1 . . I 7 1 22_ 22_ SEP 18_. 1 E5 _ C8 _ A9 _ Hl' .1 _ F1 _ ll1lll11ll1l : R , US AUC _ i 301 31 2 23 2 5 1 4 10_ 72_ SE 14_ _ TD I Illl11 lI ' ,l 2o.. 'l AU T JUL 16 . . 4' 210 2 76 1 2 1 .1S. YS . L _ ' I lll111 . HL Il . . : Illl' ,ilIIlHH 2 1 2' 1 671 . TA . 2 3 1 3 4_ NT JUN 20 . _ ION DME . mIlH llIlIlll :1 M llll1l _ l1 .I1llI ' . 1 E UDN 3 71 _ lNEOHR MAY 16_76 _ 0 1 2 4 15_ _ iSI _' Hl l11l _ NIV lI I llll1l . . lIll1L' OFN C E APR _ 2 2 47 1 143_ 1 I) 1 6 ._ _ .SYOK i 1 _ l1llll1 Hl1lllIll l81 96 . 5AO _ 75 1 2 DR MAR 21 . 2 2 2 B . . OA _ EWE lliI , _ lllllll1' 1IIll1lIlIllll1llllll1 1 I1 _ LTS _ 1 B FEB 21 _ _ AF . _ TO . _ HHlllllllliliI1lIlIIlIlllIlll1l . K H' 1 _ XMO _ 2 2 . IUO JAN . _ DSR N(B 15_ _ , ,lllIIlllI . A lllIIl . llllIL lIlIl I lIl' I = PSE PTS MM O O O OODO O O Mu l'MMMM MM HH O O M M M MM MM O O OO OO M. . T T T TT IT T AE - NN _ T T T TTIT _ ETETETETTTTETETEETETEETETETTEIIEI T T T O ._ LI O P - l . - i l COCOCOCOOOOCOCoCCOCOCCOCOCOOCOOCO_ ABABABARBBBABABAABADAABADABBABBAB_ f - F F - F - F Ff - F FF F - F - - F - - I - t iM CA - PIRrRFRFRfFFfRFRFRRFRFRRFRFRfFRfFRF _ - E . UfUFUFUfFFfUFUFUUFUFUUFUFUfFUfFUF _ H -lD.SoSOSOSO0OOSOSOSSOSOSS0S0SOOSOOSO_ N ;lllI1l1[lllllll lIHUI IH' IF _ _ F _ S _ DO _ U _ E _ S S _ TS . O U _ CH . N N _ EI . I A _ LP . P CI LE . S S S _ OD . U U M R S _ C . G N E E U _ M _ N AS C M S _ SO _ S E CI E H S A S R _ ET _ U S R I R D C U XS U S E _ IT _ G U A RA O T l l IUS S P P _ CO . N N I I IE T U iSRNE OSOSS _ EB _ S E N MNS C S NNIIIS UASUD _ P - _ I R A S AII O I AEALCU Ql YCA _ SF _ L Al R U LL KX CRiOER AliRS _ S A IAIlRNB i iUS l F _ A l Y C SII . _ HO _ V O T N AUBT U SD VAAOM SNCFuP . S _ I D E UR A L UR R SCRO UA RS . I _ T U A R HESX A iO l TS UC MCSSB . F _ S E l AI RIUA H CM USSES LAUUAS . _ E S i I OPIS P N SlUUL A MiLIl _ A P R MIC E YS UaMTPRl HSOToC _ O A RCE C HU LC0OoE TUiAcY ._ _ A A O E STUN 0 RR I A1NDB iL0N0i t l _ S S V P UILO X OE RLAOuM PLMIEO PANG OuEHUOt 1P . _ . . O O E U DMRR O CM . L L R L AtEO Y NS EOORSC CQIYARt _ . A A B C CHMM M OO PPPPP$ SSSSIUA _ .l1llllllIllllllllIllIIIllIIIlIIll . 1 . _ 0 . _ 8 . L _ . L _ M D . A ,lllllllllllllIlIIIlllIIllIlIl11Ii _ 1 3 8 S _ E C l1ll Illl;j. !ll1ll;ll.(li ,tl ,l' i ; E s 3'oa. . e T5 _ l _ 1l1l1l1ll1 l1 . _ A8 . _ 1i211l2II16341 _ 9 _ _ I 2_. _ R _ L_ E 1, _ BS . L ._ OE TI A. _ - CD _ 1 _ . DU T 2_1I1llll8ll1l8l - 1 1 2 I . . 2 __ 1 . _ DS N . T. . _ AL C _ _ A _ ,T . O_ . _ EN . 1 _ iI1l1l1ill1l1l . NE . 2I1l2 6 UM . 0_ . 2_ I 49_1 JN _ O _ _ _ .R _ N_ _ YI U_ _ RV AN _ J_ . 1 _ I1IlliIIIll1ll . 1 UE . _ 1 I I . R . 18_ _ BK . . _ EO . . FO R . S. E. . F NB . . . IA . l . IIIllIIIIlIllI . E _ . M MMM M _ DS _ . O 0OO O M_ E . . T 1TT T O_ _ H _ - ET TTTEETE T_ T .S . _ _ CO OOOCCOC _ 6IK _H AABA O_ FO _ T _. A B. B_BB_FF - F B. _ . P.F ._ 2 O RFDDDFffRRFRDF _ )R . E UFIIIFffUUFUIF _ [SB . D . tYA 8AE ADS . l l. SOMMMOOOSSOSMO_ IlIIllllIIlllI T - _ _ . ON _ _ xWO _ - lTI _ ._ 0 P _ _ _ NFM EOA _ P H _ _ PM _ S _ _ AUF _ U . SF . N . IO . A C ._ _ SS ._ S I _ TH _ U R _ _ ET _ G E _ NP _ NS M . E _ EI A S LD _ SRR U . L IM CO UAA NHESS N NUN TSUU S S E OS T _ ASIRE CUQC - NT - RULUR ERAS . O - YCIAI NB U . . IB D. TNBTV E OMSFP ROU S _ EF ARSSS UCMS . TF IAUIu ESLUS . _ CO . THIPl L AHI _ E . R CSH PRHTC _ LD . OACAC OEIAY _ LN . OTUTA DBHNH . _. OA C , . VPLNL UMPCP _ EUROL EOONOL _ RLEDO SCCYRL _ SD . BCM0P PSSSuA ,llIllllllllllI EI I M _ =_ _ C _ _ E , _ __ PE . SC _ - _ A _ 1 . HF _C _ SR ,IlllllllllllIl _ I U FS 8 D 8 _- M D - 8 D 8 S E R CES8D8 DM6D8 APPENDIX TABLE 2 6. (COMilNUED) FISH SPECIES COLLECTED IN CILL NETS ISUM OF TWO DAYSt IISHED IN FEBRUARY. JUNE. AND OCTOBER AT SURIACE. MID, AND OFF. BOTTOM DEPTHS OFF HAMPION.SEABROOK. SEABROOK ENVIRONMENTAL STUDIES,1985. l ............................................ l lOEPTH I FEB 18l JUN 20l OCT 221 ALL l ........,.......................................l........................................... lC2 lALOSA PSEUDOHARENCUS ISURFACE I l 21 1 21 l l lBREVOORTIA TYRANNUS lMID l l l 91 91 l l (OFF-BOTTOMI l l 11 11 I lHFMITRIPIERUS AMERICANUS lOFF.BOliOMI l l Il 1l ) lMORONE SAXATIllS lOFF.BOTTOMl l l Il 1l t lMYOXOCE PHAL US OCTOOFCEMSPINOSUS lOFF. BOTTOM l 1 l Il il I lONCORitYNCilUS KISUICll ISURFACE I l Il l 1l l IOSMERUS MORDAx lOFF-BOTTOMI I I 21 21 l lPE PRIEUS TRI ACANTHUS ISURIACE l l l 11 IL j IPOll ACHlUS VIRENS lOFF-BOTTOMI l 81 31 111 l lPSEUDOPL EURONECTES AMERICANUS lOFF-BOTTOMI l l 11 11 l lSCOMB[R SCOMBRUS lOFF. BOTTOM l l Il I 11 p I l AI L ISURFACE I l 31 18 N1 , I I IMID l l l 91 91 at l l lOFF.BOTTOMI I 9l us 101 191 ..=_= _= =--- _.......................................................................... CES8D8 DM8D8 APPENDlX TABLE 2-6. (CONTINUID) FISH SPECRES COLLECTED IN CILL NETS (SUM OF TWO DAYS) FISHED IN FIBRUARY. JUNE, AND OCTOBER AT SURFACE. MID, AND OFF.BOTION DEPIHS OFF HAMPION-SEABROOK. SEABROOK ENVIRONMENTAL STUDIES,1985. IDEPTH I FEB 181 JUN 201 OCT 22l ALL lG3 lAlOSA AESilvALIS _...l...........................................l ISURFACE I l 21 1 21 l lALOSA PSEUDOHARENCUS l SURFACE I i 11 1 1l l lBRIVOORilA TYRANNUS IMID l l Il Il l I POLLACHlUS VIRTNS lOFF.BOTTOMI i 131 1 138 l IFRIONOTUS CAROLINUS l SURFACE I i 11 . Il i ISCOMBER SCOMBRUS l SURFACE 'l l l Il 1l l lALL l SURFACE l l 4l 1l $l l l lMID l l Il l 1l l l lOFF. BOTTOM l l 131 l 131 >e m I 1 CES8D8 DM6D8 I l l l APPENDIX TABLE 2-6. (CONTINUED) FISH SPECIES COLLECTED IN CILL NITS (SUM OF TWO DAYS) FISHED IN FEBRUARY, JUNE, AND OCTOBER AT SURFACE, MID, AND OFF-BOTTOM OEPTHS OFF HAMPTON-SEABROOK. SEABROOK [NVIRONMENTAL STUDIES.1985. IDEPTH l FEB 181 JUN 2Ol OCT 221 ALL l ,______ ,---=== - =.-....................- ...--l---.......................--.........--.... lALL lALOSA AESTIVALIS l SURFACE I l 21 21 l lALOSA PSEUDOHARENCUS " SURFACE I l 31 3ll l lBREVOORTIA TYRANNUS SURFACE l l 1 l l' I I MID I 11 9 1 10 l l lOFF-BOTTOM l ll l 11 1 l lCLUPEA HARENCUS HARENCUS lOFF-BOTTOMI il l 11 l lHFMITRIPTERUS AMERICANUS lOFF-BOTTOMI l 1l 1 l lMERLUCCIUS BILINEARIS IMID l i 2 : 1 2 l lMORONE SAXATILIS lOFF-BOTTOMI i 11 1 l l MYOx0CE PHAL US DCT DDECEMSP I NOSUS OFF-BOTTOM l 1l 1l MID l lODONTASPIS TAURUS 1 1 II l l ONCORHYNCHUS RISUTCil HSURFACE 11 l 11 3, l lOSMERUS MORDAX l OFF-BOTTOM i 2 2 a l l PE PRit US TRI ACANTHUS I SURFACE I l 1 1 as llMID " l lPOLLAClllUS VIRENS l i 11 l 1 i l l ll O F F -BO T T OM l l 32l 3l 351 l lPRIONOTUS CAROLINUS l SURFACE l l 18 l 1l l lPSEUDOPLEURONECIES AMERICANUS lOFF-BOTTOHf l 2l 11 3l l lSCOMBER SCOMBRUS ISURIACE I I i 11 11 l l lOFF-BOTTOM l l 11 Il 21 l lSCOPHTHALMUS AQUOSUS ISURFACE I 11 l l 11 I ISYNCNATHUS FUSCUS ISURFACE l l l 11 Il l lUROPHYCIS SP. IOF F-BO T T OM I l 6l l 61 l lALL l SURFACE I 11 71 41 121 I l lMID l i SI 91 14l l l IOFF-BOTTOMI 11 411 111 53l .. = - - - . . . _ _ _ = = = . . . . . . . . . . . . . . . . . . . . - - . . . . . . . . - - - - . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . . - - l CES807 DMSD7 AP PE NDI X TABLE 2 7. TOTAL CATCH AND PERCENT COMPOSlflON OVER ALL DEPTils. STATIONS. AND SAMPLING PERIOOS FOR FISH SPECIES COLLECTED IN CILL NETS OFE HAMPTON.SEABROOK. SEABROOK ENVIRONMENTAL STUDIES,1985. I C1 l C2 l C3 i ALL l l ...........-............................................................. l l SUM l PCNT I SUM I PCNT l SUM l PCNT l SUM l PCNT l ICLUPEA HARENCUS HARENGUS I 421 28.41 331 19.91 491 26.91 1241 25.0 ' IPott ACllluS VIR[NS l 44l 29.75 271 16.31 36 l 19.81 1071 21.6 ISCOM8ER SCOMBRUS l 61 4.11 181 10.81 24 . 13.21 481 9.7' lALOSA A[SilVAllS I 14l 9.5H 161 9.6l 17H 9.31 471 9.5 l IBREVOORTIA BYRANNUS l 11 0.7 161 9.61 131 7.11 301 6.O l IALOSA PSEUDOllARENGUS l 3l 2.0 141 8.41 111 6.08 281 5.6 l lPEPRit us IRI ACANIHUS l 61 4.1 : 81 4.81 til 6.01 25 5.0 1 lSQUALUS ACANTHIAS I 81 5.4 88 4.8l 91 4.9h 25 5.01 2.71 4.21 lPOMAIDMUS SALTAIRIX l 41 71 31 1.6 , 14 2.8 . IOSMERUS MORDAX l I i 10l 6.01 21 1.1ll 12h 2.4 l lMERIUCCIUS BILINEARIS I 61 4.11 l l 2 1.11 8h 1.6 : T ' luRornvCIS SP. I 71 4.71 11 0.61 . 8 1 1.6 1 as 0.71 11 0.61 1 1 0.5 3 0.61 # l ICADUS MORllUA 1 Il 1 l lMYOXOCEPHALUS OCIODECIMSPINOSUS l 11 0.71 18 0.61 1 0.51 3 0.61 IPSEUDOPLEURONECTES AMERICANUS l 2 l 1.411 11 0.61 1 3 0.61 tilf MiiRIPIERUS AMERICANUS I l 21 1.21 l 2 ; 0.48 lMORONE SAXATILIS l 2l 1.2 l l 2 0.41 10DONTASPts TAURUS I 1' O.7 I I l l 1 . O.21 IONCORHYNClfuS KISUICII l l l 11 0.61 l l 11 0.21 IPRIONO1US CAROLINUS 11 l l l l 11 0.51 Il 0.2l ISCOPfliHAtMuS AouOSuS 11 0.71 I l l l 11 0.2 ISTENOTOHuS CIIRYSOPS I I l i 11 0.51 11 0.2 ISYNCNATHUS FUSCUS I 11 0.7l l l l l 11 0.2 lieuTOCOLABRUS ADSPERSUS l l l l l 11 0.5l 11 0.2 ; l EMPTY SAMPLE l l l I I l l l H lALL i 1481 100.01 1661 100.0l 182l 100.01 4961 100.01 l l I 'l j s Yo* . 1 . l . 11111l1111l11 . . H5 E.12354l7890a642 P. I 1 C8 A9 . S. N. E1 . . l . L111 . , . . 2822282228222 . TS . L . 1111111111116 AE L.N. . . 1 SD HU I . A. . i . 111111u l TT PS E . . U. M.22578321'4 4'806. 31656942459 4 DL . . S. A . . . l l1 . . l . . 11l i1' LT LN . . 2355781546 . AE . IE.1 P. 1 RN EO M S. N. VR . . I . 11' 11111118 . OI . . . 4644464446444 . V . 3 . . 5 YN . . LE H . G.N.. TK . . l . 1l11l 1111 . .NO . . . 2 3284521502 . . . 148 8OO MR . . M.. 21232 1 2 B . U. S. . DA EEE . l . l . ll11111111111 . . . . 33445458617 . LTS BC AE E. P. 1 TL . LK S. N. . . I . 11111: .h1l . IXOO CO . . . 4644464446444 . D R . 2 . . 5 NSB ELA PAE . C.N.. PUS . . l . l111111l11111 . AD- . . . 31324480016 . IN . . . 111123122 6 . . M. U 1 IVO T . . S. . DP . . . . NM . l . l . I11 L11 A . . . 212354423537 . IH D E.. P 1 NF AF S. N. O . . I 1111111111111 . S . . 4644464446444 . EN . 1 . . 5 . C N.. IC CI . ET . . . . PA . . l . 1111111111 H . ST . . . 223334243398 . S . . . 2 3212 1 4 F . . M. U. 1 OT . . RN E . . .I S. . I . 1181l11111i ! E . 511660648247 . . BL . 122112111211 . ML . . UI . NBRRYNtcPTVCL. NC . AEAPAUuuECOEL. JFMAMJaASONDA.. .lIIIIIllIIIIl 7 D 3 H D - T - D _ 3 S E C - . _ - - - - - . . ~ . . RES803 DM803 APPENDIX TABLE 2 9. ' CATCH PER UNIT EFFORT (C/E=24 HR. SET) FOR FIVE FINFISH SPECIES COLLECTED BY CILL NLTS IN 1985. SEABROOK ENVIRONMENTAL STUDIES,1985. 1; 1~ T ~ l C1 l C2 i C3- l <se _, IDEPTH l CPUE l .PCNT l CPUE l PCNT l CPUE I PCNT l .........................u........................................................... ' ICLUPEA HARENCUS HARENCUSLSURFACE I 1.41 50.81 0.91 32.8)- 1.71 38.31' l OFF-BofTOMH 0.41 11.41 0.51 12.21 0.31 10.81 lALOSA AESTIVALIS SURFACE , 0.5 18.51 0.31 10.41 0.51 12.11 1 0FF-BOTTOM 0.1 2.51 0.41 10.01 0.21 5.4 IMERLUCCIUS BILINEARIS ISURFACE I l l l l l 10FF.BOTTOMI 0.2 5.11 I l 0.11 2.7' ~ lALOSA PSEUDOHARENGUS ISURFACE l 0.1 4.61 0.11 4.5H 0.41 9.3 l 10FF-DOTTOMI l 0.5 12.2h <0.1 1.4 ISCOMBFR SCOMBRUS ISURFACE I 0.1 4.61 0.5 17.9l 0.7 15.0 l . 10FF-BOTTOMI 0.1 3.81 -0.3 6.7 0.3 10.8 lALL OTHER TAXA ISURFACE l -0.61 21.51 1.0 34.3 .1.11- 25.2 l 10FF.00TTOMI 2.51 77.21 2.21 58.9 , 2.11 68.9 ..................................................................................... Y.a O, i l l i I l L . (' 1 ' ) l l I l4Y e e _l _ 1 _ lll11Il _ S . _ _ _ 0 00 H5 . . f T8 T _ 0 00 o.0 0.__ 000_ N9 O1 N_ 4 22 200_ 11 H . _ . C __ _ S _ . P_ _ NE _ 3 . _ , l1l . OI YU D _ c.l . 113 4 _ . _ 22 2 2 2... LT _ . _ 0 00 002 . NS _ E_ U . . O _ P_ , L _ . C, , . DA _ _ . - ET _ _ . . SN _l . l _ l 1: 1 AE _ . _ 0 3 0 0 7._ BM _ . _ N _ .T _ 0 50018 _ EO /R .N_ C_ 5 509_ 1 CI _ V .N _ 2_ .P_ _ 4 SE _ C_l _ lll ' . E _ _ _ 3 _ IK CO .E_ _ :0 2 0013 3 5 0._ _ + EO _ U PR _ ._ P _ , SB . _ . . A . _ C_ . . s HE . _ _ ,. a SS . l _ l _ lllilll1l . 8 0 . 0F .I s 0 800 8000 . 5.. N . _ _ T _ 1 1IR 2FE _ _ N_t _ . C_ 5 1059_ B _ _ P_ _ E.E _ _ . _ VTO t _ 1 _ _ ~ BIC _ . 1, AFO . c_I .. 2 3 T RD E.O ._P . lllI 0'l'!2 O003 5 3 2.__ _ IXON D FA _ U.. _ N) , ETE C. _ PEN hl _ l lI . l ._ l ._ l l ' PSU _ - A _M M . .J R , _O _ T O T M_ O_ T IIY . _ TE EETE T _ R . _ OC CCOC _ fsA _ A AABA O_ (n 2U ._TH _ B. F IF - F B. _ R _ P_FRDRRFRDF _ / =B _ [ _ fUIUUFUIF _ EF E _ _ D_OSHSS0SM0_ Iu.. S'l I i l / _ C: U _ (T . C _ E . N S . TS . E IS . R R RU . OE ._A AC . FR _ l EN . FE _ lSNES . , EW _ SlIRU _ _ UlLAR A _ TS _ CAIlD l X _ IT _ NVB0N A _ NE _ El DO T _ t:N _ RiSUC _ . ASUES R _ RD . ITIS . I E _ EI ACPR H _ PH . A C L T - _ EAUAB O _ HN ._ PSLSM _ F CE _ UOROO t + N n TH _ LLELC l _ t' AW _ CAMAS AI . C : Il . ;l ~ 6 0 8 M D 6 D 8 S E R t %' , 4 o A-72 APPENDIX TABLE 2-11. VOLUME (LITERS) 0F MACR 0 ALGAE COLLECTED IN OTTER TRAWLS DURING 1985. SEABROOK ENVIRONMENTAL
- STUDIES, 1985.
TRANSECT T1 TRANSECT T2 TRANSECT T3 TOW TOW TOW TOW TOW TOW TOW TOV TOW TOW TOW TOW 'A B C. D A B. C D A B C D , DATE i 1-24-85 - - - - 6 6 17 34 - - 2-25-85 - - - - 17 9 6 4 - - - - C8 - - - - 3-21-85, : - - - - 289 119 C 4-18-85 - - - - 34 128 85 30 - - 5-23-85 - - - - 468 187 C C - 6-20-85 - - - - 323 595 C C .- ,,' 7-29-85 - - - - 1700 255 C C - - - - ,5 8 - - ! 8-15-85 - - - - 26 - V V - - 9-25-85 - - - - V V- V V - - - 10-24-85 - - - - 340 119 C C - - 4 11-25-85 - - - - - -- - - - -~s_ ,- - 12-17-85 - - - - 34 51' 170 51 - C 2 = Tow void due to algae. V 8 = Unable to tow (lobster gear). - = No algae present. i 1 l 1 i 1 l APPENDIX 3.0 NYA ARENARIA (SOFT-SHELL CLAM) AND NYTILUS EBULIS (BLUE MUSSEL) LARVAE l l l l l \ RES2D1 DM2D1 APPEN0lX TABLE 3-1. DENSITIES (NO./CURIC METER) OF SOFT SHELL CLAM (MYA ARENARI A) AND BLUE HUSSEL (MYTILUS EDULIS) AT STATION P2. SEABROOK ENVIRONMENTAL S100lES,1985. l MYA ARENARIA l MYTILUS EDULIS l l MEAN l S.D. l MEAN 1 S.D. ! APR.18l 0.15l' O.22 ! APR 241 0.101 0.14 APR 29 l MAY 07 MAY 15 0.49 0.17 MAY 20 0.87 1.23 MAY 28 109.84 1.55 JUN 03 2010.11 164.21 JUN 101 1708.47 53.69 JUN 17 1.29 0.35 6644.64 1581.77 - p. JUN 24 5.30 2.79 10870.30 4210.07 I 'JUL 01 0.61 ~0.30 575.85 34.74 'd JUL 09 0.20 0.28 ; 1193.95 : . 526.88 JUL 15 8096.45 4167.24 JUL 22 3.09 0.60 3515.35 493.61 JUL 29 1.12 7788.42l 2893.53 0.79 AUG 05 1.06 0.75 : 1171.41 309.76L AUG 12 . 62.91' 8.00 719.91 . 104.39 AUG 21 45.72 7.52 1367.30 461.73 AUG 28 18.23 1.62 71.54 25.38 SEP 03 '4.66 2.67 66.11 38.15 SEP 09 ; 62.84 20.03 39.16 . 11.09 'SEP 18 4.96 ' O.22 16.04 8.12 SEP 23 . 3.08 0.91 11.61 2.87 SEP 30 26.84 1.99 19.141 . 0.66
- OCT 07 1,58 0.25 1 3.53 0.61 OCT 15 : 0.82 0.37 3.48 0.62 ALL 9.04! 18.83 1703.22 3123.12 d
t b w , - ___-______..__.--._m._ u e a _ h APPENDIX 4.0 EO&fRUS A#ERI m &S (LOBSTER) LARVAE O i - -,- -- - - = RES8D1 DM8D1 APPENDIX TABLE 4 1. TOTAL NUMBERS COLLECTED OF LOBSTER (HOMARUS AMERICANUS) LARVAE BY LIFESTAGE FOR EACH S1All0N AND DATE AND SUMMED OVER STATIONS. SEABROOK ENVIRONMENTAL STUDIES,1985. l ZOEA 1 l ZOEA 11 l ZOEA Ill l ZOEA IV l ALL I P2 MAY 20 MAY 28 JUN 03 JUN 10 .!JUN 17 1 1 Jt1N 24 'JtlL. 01 JUL 09 JUL 15 JUL 22 1 1 JUL 29 . I 1 AUG 05 2 2 20 24l AUG 12 8 8 Y AUG 21 11 11 %J AUG 28 I *. SEP 03 7 7
- SEP 09 10 101 SEP 19 SEP 23 . 5 5
'SEP 30 l OcT 07 OCT 15 ALL 1 .2 2 63' 68 H v-RES8DI DH8DI 1 APPFN0lX 'TARLE 4-1. (CONilNUED) TOTAL NUMBERS COLLECTED OF LOBSTER (ll0MARUS AMERICANUS) LARVAE BY LIFESTACE FOR EAcil STATION AND DATE AND SUMMED OVER STATIONS. SEAHROOK ENVIRONMENTAL STUDIES,1985. i l 20EA I l 20EA II l ZOEA t il. l 20EA IV l ALL l g.......i............................................................... l.P7 MAY 20 ' l MAY 28 1 1 -l JUN 03 JUN 10 JUN 17 1 1 JUN 24 JUL 01 JUL 09 i
- JUL 15 l i JUL 22 l 2 2
- JUL 29 8 '6 6 AUC 05 8 3 3 77 91 p-AUG IL I 4 4 s-AUG 21 7 7 4 AUG 28 .' 4 4 9 SEP 03 '
4 . 4 SEP 09 20 201 SEP 19 1, SEP 23 2 ' 2! SEP 30 1 1 . OCT 07 i OCT 15 I ALL 10 . 31 3:1 127 143 . f T b 4. e - - -m 1 ~. ____._-__- _ _ -_. _ .--- - . - . . . . .. .- 'RES8D1 DM8D1 ' APPENDlX TABLE 4-1. (CONTINUED) TOTAL NUMBERS COLLECTED of LOBSTER (HOMARUS AMERICANUS) LARVAE BY LIFESTAGE FOR EACH STATION AND DATE AND SUMMED OVER STATIONS. SEABROOK ENVIRONMENTAL STUDIES,1985. l 20EA i 1. 20EA 11 l ZOEA til l' ZOEA IV l ALL. 1 i......-g....................................---............--.......... ALL' MAY 20 l MAY 28 1 1 'I. 1 JUN 03 JUN 10 , e JUN 17 2 2
- JUN 24
'JUL 01 'JUL 09 JUL 15 l JUL 22' 3! 31 JUL 29 7: 71-lAUG 05 8 5 5 97 '115l AUG 12 12 12 Y AUG 21 18 18 4 AUG 28 84 fa #- SEP 03 1 11 11 SEP 09 30 30 SEP 19 1: SEP 23 7 l 7 SEP 30 1 1 S' OCT 07 -I OCT 15 l-ALL 11 l 5 5 190 2111 v , _ . _ _ _ _ _ _ ._ . . _ _ _ ~ _ _. _ . - _ _ _ .. RES8D4 DM8D4 APPENDIX TABLE 4-2. ABUNDANCE (NO./1000 SQUARE METERS) AND PERCENT COMPOSI T ION OF LOBSTER (HOMARUS AMERICANUSl LARVAE BY LIFESTAGE FOR EACH STATION AND DATE AND SUMMED OVER STATIONS. SEABROOK ENVIRONMENTAL STUDIES.1985. l ZOEA 1 l 20EA 18 I ZOEA til l ZOEA IV l ALL l i l ABUNO. l PCNT l ABUND. l PCNT l ABUNO. I PCNT l ABUNO. l- PCNT l ABUND. l PCNT l ,.......g............................................................................................................ .P2 lMAY 20 'I l l l l l l ,MAY 28 l l l l JUN 03 I l l
- JUN 10 l .
l- ' JUN 17 l 0.25L 100.0 1 0.25l 100.0 LJUN 24 l l lJUL 01 ( JUL 09 'JUL 15 "JUL 22 0.26 100.0 0.26 100.0 : p, JUL 29 0.26 100.0 0.26 100.0 AUG 05 0.61 8.3 0.61 8.3 6.06 83.3 7.27l 100.0 'J AUG 12 2.26 100.0 2.26' 100.0 AUG 21 2.65 100.0 2.65 100.0 AUG 28 SEP 03 1.84 , 100.0 1.84 100.0 ' SEP 09 2.43 l 100.0 2.43 .100.0 SEP 19 I SEP 23 i 1.42 100.0 1.42 100.0 I LSEP 30 1 1 OCT 07 OCT ' 15 l i ALL 0.25 1.31 0.61 - 3.3 0.61' 3.31 17.18 92.2 18.64 100.0l' I , -< v 3 Y00 e . l . l - - . . - 0 0 00000000 00 l10. . 0- . . . T - 0 0 00000000 00 5 . . N- 0 0 00000000 00 0-8 . . C- 1 1 11111111 11 1 - 9 . . P- . 1 - . - - S E L. . L.l - 9 5 0 2 2'99692 06 0 - ED AU I . A. . . D- .- 2 2 56708999 52 0. - VT . . N- 0 0 01811004 00 2. RS . - U- 2 4-A - - B- - LL . - A- - A . - - - )T . . - - SN . l . l - .- UE . . - 00600000 00 - NM . - - 2. - AN . . T - 00400000 00 8. CO . - N- 00800000 00 8-IR . . C- 11 11111 11 - RI . . P- - EV - . - - MN . IV. - - AE . - - . I . 1 A.l.-- l SK . E 02099692 06 4-UO . O. 56308999 52 - RO - Z.D- 0. - AR . - N- 01411004 00 7-MB . . U- 2 3 . OA . . B-HE . . A- - )(S . . - . D . . - .. ER . l . l - UE . . . - 3
- 3. -
NTS . .. - ISN . . T - 3 2 - TBO . . N-NOI . . C- - OLT . l . P-C A . l . - (FT . I . - .O S . . - - 2NR OE . A.l - E 0 .- - 5 9 5. 4IV . 2 D- 9. - TO . . N- 0 0-EI . . U- - , LSD . . B- .- BOE - . A- - APM - . - . TMM - . - . OU - l . I - lIl . XCS . . - 3 3 . I . . - . . DTD . . T - 3 2. NNN - . N- - EEA . . C- . PC . . P- - _ PRE . l . - - AET . f . - . PA . . - . D . . - A.I l D . E - 5 5 ND AN A 0.D-2.N-9 0 9. 0. ) . . U- - SN . . B- - RO . . A- . EI . . - - TT . . - . EA . l . l - l MT . . - 0 0 8 . S . - - 3. . . . T - 0 0 8 7 _._ El Rl . . N- 0 0 AC . . C- 1 1 . UA . . P- - QE . I . - - S . . .- . R . . - . 0O 0F . A.l . E - l 9 5 2 1 - 7 . 0 1E O. Z.D- .- 2 2 5
- 0. .
G . - N- 0 0 2 3- /. A . U- - _ oT . B-NS . . A- . (E . . - . F . . - . EI .l .l - ' l CL - . N - 0830741952952183993075 . AY - 2201120012201220012301 . _ DB - - N - YYNNNNLLLLLGGGGPPPPPTTL- - AAUUUUUUUUUUUUUEEEEECCL. U _ B A u. MMJJJJJJJJJAAAASSSSSOOA... H 4 . . _ D 8 . 7 M . P D . 4 _ 0 8 S E _ R _ I ,. j RES8Df4 DM8 Dis i APPENDIX TABLE 4-2. (CONTINUED) ABUNDANCE (NO./1000 SQUARE METERS) AND PLRCENT COMPOSITION-OF LOBSTER (HOMARUS AMERICANUS) LARVAE BY LIFESTAGE f0R EACH STATION AND DA1E AND SUMMED OVER STATIONS. SEABROOK ENVIRONMENTAL STUDIES,1985. a ....................................................._............................................... l- ALL l ZOEA B l 70EA II l ZOEA Ill -ZnEA IV l I l ABUND. l PCNT l ABUND. l PCNT l ABUND. l PCNT l. ABUND. I PCNT l ABUND. I PCN T I u.......u..............................__.................................................__.................._.._ .. ALL MAY 20 l l l 0.29 100.0 100.01 MAY 28 I 0.29 .JUN 03 JUN 10 ' JUN 17 0.50 100.0 0.50 100.0 l JUN 24 1 LJUL 01 l l JUL 09 'JUL 15 JUL 22 1 0.76 100.0 0.76 100.0 p, JUL 29 , 1.88 100.0 1.88 100.0 s 1.55 4.3 1.55 4.3 30.36 8fs.4 35.99 100.0 0) AUG 05 2.52 7.0 ! lAUG 12 3.35 100.0' 3.35 100.0 lAUG 21 84. 5f4 100.0 88.54 100.0 AUG 28 0.96 100.0 0.96' 100.0 SEP 03 1 2.83 100.0 2.83 100.0 - I SEP 09 l l 7.35 100.0 , 7.35' 100.01 i SEP 19 I l SEP 23 1.92 100.0 1.92 100.01-SEP 30 0.26 100.0 0.26l 100.01 Oct 07 l l OCT 15 l l l I "ALL 3.32 : 5.5 1.55 2.6. 1.55l 2.61 54.211 89.41 60.641 100.01 k i 1 i APPENDIX 5.0 MACR 0 ALGAE NSPE = number of taxa S.D. = standard deviation i -_ RES2D1 DH2D1 MEAN APPENDlX TABl.E 5-1. MEAN BIDMASS (GRAMS DRY WEIGili PER SQUARE METER) 0F MACROALCAL SPEClES AT SUBilDAL AND INTERTIDAL STATIONS DURING 1985. SEABROOK ENVIRONMENTAL STUDIES,1985. I MAY l AUG l NOV l ALL l 545.28 1272.69 17 Cil0NDRUS CRISPUS 498.031 772.001 PHYLLOPHORA SP, 103.47 30.35 193.12 108.98 JCORALLINA OFFICINAllS 27.04 79.84 51.36 52.75 CEllAHlUM RUBRUM 37.81 26.35 2.88 22.36 l PHYCODRYS RUBENS 15.79 6.67 7.73 10.06 l CYSTOCLONIUM PURPUREUM 16.64 2.29 0.69 : 6.541 l CALLOPHYLLIS CRISTATA l 33.65 4.11 0.85 12.87l PTILOTA SERRATA <0.01: 0.05 0.11 0.05 MEMBRAN0PTERA ALATA O.11 0.11 <0.01 0.07 GYMNOGONGRUS CRENULATUS 1.28 1.71 1.00 CilAE10MORPHA MELAGONIUM 0.05 , 0.051 0.16 0.09 POLYSIPHONIA UI<CE0 LATA <0.01 . 0.11 <0.01 0.04 > CHAETDMORPHA PICQUOTIANA <0.01 <0.01 0.05 0.02 g CHAETOHORPilA SP. <0.01 <0.01 w CALLilllAMNION TETRAGONUM <0.01 0.21 0.07 DESMARESilA ACULEAIA 0.11 0.05 0.05 ANTITIIAMN10NELLA FLOCCOSA <0.01 0.11 0.04 Ril0DOPHYLI.lS DICi!0TOMA . <0.01 <0.01 , POLYSIPHONIA NIGRESCENS 0.05 0.02 PORPHYRA MINIATA' <0.01 <0.01 i ALL 779.90L 1424.381 756.75 987.01 i 9 QES2D1 DH2D1 MEAN APPENDIX 1ABLE 5-1. (CONilNUED) HEAN BIONASS (CRAMS DRY WEIGiti PER SQUARE HETER) 0F HACROALGAL SPECIES AT SUBTIDAL AND INTERilDAL stall 0NS DURING 1985. SEABROOK ENVIRONMENTAL STUOlES,1985. l HAY l AUG l NOV l ALL l n.._........................................................................... 135 634.131 544.32 382.93 520.46l lCHONDRUS CRISPUS I lPHYLLOPHORA SP. 320.05 190.99 173.64 9.871 lCORALLINA OFFICINAllS 28.75' 26.45 16.21 23.80 lCFRAHlUM RUBRUM 21.12 172.64' 8.59 67.45 I lPilYCODRYS RUnENS I 10.72 14.35 2.99 9.354 H CYS10CIONIUM PURPUREUM 1.92 101.63 5.01 38.19 l CALLOPilYLLIS CRISTATA 4.161 T.47 1.65 4.43 l Pill.OTA SERRATA <0.01 <0.01 <0.01 <0.01 HEMBRANOPilRA AlATA , 0.05 0.11 <0. 01 : 0.05 CYHNOCONGRUS CRENULATUS L 4.31L 0.16 <0.01 1.51 H LCHAE10HORPilA HLLACONIUM i 0.91 1.71 0.321 0.98 POLYSIPil0NIA URCEOlATA 0.11 <0.01 : <0.01 0. 07: >e H CilAliOHORPilA PICQUOTIANA 0.16l 0.16 i 0.69 0.34 l lSCACELIA PYLAISAEl <0.01 <0.01 1 <0.01 <0.01 SE l HAllNFELilA PLICATA 0.59 <0.01 <0.01 0.20l 1 CilAETOHORPHA SP. U <0.01 <0.01 0.05 0.02 ,POLYSIPil0NIA FLEXICAULIS l <0.01 : 0.11 0.04 . .CALLliHANNION TETRAGONUM H <0. 01 ' O.05 0.02 l ANTlillAMN10NELLA FLOCCOSA <0.01 <0. 01 ' <0.01 <0.01 lSPilACELARIA RADICANS 0.11 1 <0.01 0.04L HPOLYlDES ROTUNDUS l 0.05 0.02L lRilODOPilYl.LIS DICHOTOMA , <0.01l <0.01' POLYSIPilONIA NICRESCENS <0.01 l <0.01 . 'PALMARIA PAlHATA I 0.05 0.02 ECTOCARPUS FASCICULATUS <0.01 <0.01 Ril000 HELA CONFERVOIDES <0.01 <0.01 HONOSIROMA FUSCUM <0.01 <0.01 , <0. 01 ' POLYSIPil0NI A IIARVEY1 <0.01 <0.01 ALL 716.97 1195.05 609.71 840.58 l RES201 DM201 ' 2 l 1 MEAN APPENDIX TABLE 5-1. (CONTINUED). MEAN BIOMASS (CRAMS DRY WElGHT PER SQUARE METER) 0F MACROALGAL SPECIES AT' SUBTIDAL AND INTERTIDAL STATIONS DURINC.1985. SEABROOK ENVIRONMENTAL STUDIES.1985. I MAY l AUG l NOV l ALL l. 40.27 202.031 68.75 103.68 l31 lCHONDRUS CRISPUS I i IPHYLLOPHORA SP. 354.67 152.43 106.51 204.53 lCORALLINA 0FFICINALIS 28.11 70.88 35.68 44.89 lCERAMlUM RUBRUM 0.05 1.39 0.05 0.50 I IPHYCODRYS RUBENS . 12.37 - 23.25 4.48 13.37 I ICYSTOCLONIUM PURPUREUM 1.92 0.80 0.05 . 0.92 - ! ICALLOPHYLLIS CRISTATA 1.71 5.81 0.69 2. 14 ;
- PTILOTA SERRATA 2.99 2.35 .
0.75 2.03 , MEMBRAN0PTERA ALATA 0.64 4.11 l 0.53 1.76 GYMNOGONGRUS CRENULA10S <0.01 0.11 h 0.431 0.18 CHAETOMORPHA MELAGONIUM <0.011 1 <0.01 , I 'POLYSIPHONIA URCEOLATA 0.05 0.11 0.21 0.12 y . I CHAETOMORPHA PICQUOTIANA <0.01 <0.01 s- 1; 1 1 SCACELI A PYL AISAEI , <0.01 <0.01 <0.01 <0.01 03 t l AllNFELil A PLICATA <0. 01 l <0.011 1 l CHAETDMORPHA SP. <0.01 <0.01 <0.01 ' i ANTITHAMN10NELLA FLOCCOSA <0.01 <0.01 <0.01 <0.01 l SPHACELARIA RADICANS <0.01 <0.01 : l ; ALL 442.78 463.26h 218.14 374.72 .4 4 6 1 . e i h h ., u- # , w g- , ,. - -' ii- l 1 3em* . L . l . ' l1l ;11 A . . 64747100121818111121111 D . . 48909705610104000000009. I . . . . . T5 B8 U9 L.033010822000000000O0004 L. 61 2 1 - < < <<<<' < < <2 2 _ S1 . A. 1 i TS . . . _ AE . . . . l . _ SDI . 9971720097 1 511 5 2 . EU . 5041432613 1 000 0 w- _ IT . . . 6. . CS . V 077010352O 0 000 0 8. E . . 2 1 << 5 PL . O. 2 2 SA . N. . _ ) T . . DLN . . _ EAE . UCM . l 1 1Il1 . lNLN . 4 0 3 1 1 8 3 4'3' 111 000 11 00 13 . AO 61002564 06. iOR . . . NRI . . 72011864 ' 000 00'01 . OCV . G. 32<4 1 <<( << <3 . CAN . U. 2 (HE . A.. 1 .F K . . 1 0O . . O I1 . i . l . _ 5)R . . 032143'753 13 9 11 00 1 0 8. RB . . 883045222 04 3 4. y EEA . . , LTE BES AM Y.062030251 A. 21 <1 1 11 00 1 00 0 4. 8 . 1 T E . . M. _ XR5 . . . lA8 . . . 0U9 . l . Illi' ,1 NQ1 . A . ES . A S . . P G . SM N O S' . PRN . M UUAA C AUSA . AEI . S UA TITl C MTER . PR . l ET ANAf AOSOADE . _ U . l HA ALOL0 TLNTLIF TD . A UT TUCOUI AIAOUOI - ... H GS IN . S N I SRI . U .CMNURAARERISPULDICER PS ANAEQE lELCCA . E. ACHCVL I ICIRO . _ EO PPIUEPCT CMUPISCLADSFP . WIT SSFRR AA A AER AN . . I FHUM.RRSAAALA . N SFOA . YA . RA0URU!REUHIHYHAOAI CH . _ RT . CR R ILETRPNPPPlIILS P . _ DS . OA SNLSPGROR RiNRLUA.R . . _ . SHNMYOY 0NOHOAOSMAYPtO- . . SL . UPIURLHANOMPMlMEALHREM MA . ROLODCPTACOIOlORHEPAMO . _ AD . DILMOOOOROTSTETAiC0COR . RI . NLAACTLLBNEYECEMlADODE . CT IR . OYRRYSLl HHOEHYAiEYHOHCHENPHCHNL. MMALAAASiHOTOTL. ST E CPCCPCCPMCCPCSCDASREREA. I 'I' I SN . AI . M . OD . . IN . . BA . 9 . 1 . _ N ' l' A E M 1 D 2 _ M D I D E N S A E E R M 1 4 4 !' ' ' .l ' jj' '
- 4' 1
3$ .I . l . . . 55599914207299521111111111111'110 . .17856506172100000000000000000008.. _ L . . A . . . . D I . . L L.92323173100000000000000000000006 463211 <<<<<<<<<<<0 . T5 . 6 B8 U9 . A.31 S1 . . . TS . l . 1l 8738172'0183218911113111 0 . 11 1 AE . SD I . 5469656666100100000000 00 0 .
- 8. .
. 79726111000O0000O0O000 0 . EU . . V.372 < < < 00 0 < 6 IT CS . O. N.21 .4 E - PL . . SA . . ) T . . , DLN .l . ,' 1 1 1' EAE . . 613920869941' 54153'3 1' 111 0 11 00 8. UGM . . 7180304713400000000 000 5. . NLN . . . . 00O 0 00 8 IAO TOR NRI U 40901864200000000O0 . G. 064522 < < < < < < < < 2 8. _ OCV CAN A.51 (ME . . . .F K . l . l .I .. 1 0O . . 2156'855619455451 H 1' 31 1' 11 13 . O . . 1707029550231010 0 00 0 00 . 5)R . . . . . . 0 0. . 000000 0 00 0 00 01 . , EEA RB . Y.5844352401 A.04211 1 < < < < << < 3 . 5 . LTE BES AH . M.31 T . . . E . . . . XR5 . l . I 1A8 . ,A' . 0U9 . A M SS . NQ1 . SM N U OI S S . ES . M UU AA N CL AN U SA . P G . s UA TI TI O CU ME T ER . PRN . l ET AN AT GAOAS OC A DEI . AEI . l RA ALO LO ATLCN TS L IFY . . PR . A UT TUGlOU RAFIA OE U OIE . . U . N PS ANAEEQATI XC HR SCMVLV . TD . S I SRI LfLACCTELAEI .CGAUIURORA . H . U , CMNURAARESRIATULLDPIITOCCIRAT . GS . PPIUtPCT CMIUPC CLFASDNANSSFPHA . IN . SSFRl l AA A INAE R MUAUN I . EO . I FDuMSRPSALAAL0 NA ASALTFFOAAN . WI . RA0URUIREUIYIiP1A0IAHIIAO I l CiII l T . CR R ILETRPPNP Nl1NIPLNPRSA PNM . YA . 0A SNLSPGR 0RAMiNORRLO UMARO . RT . SliNMYOV 0NOAliOIASMHAOYHASPOLOHA . DS . UPIURLiANOMlPMTHEAPLMiPIERREMPR l l . SL . ROLlDCPTAG0lIOL1RliIEOPIRDATMOI .. NLAACTtLBNEGYETLMlYAEDYMY0ODEYP DLLMOO0ORO1ESTElATSCTOSAlCSORSilY . MA . AD . OYRRYSlIMMAALANLSiLHAOLLLTN0TLRL 1 RI GT ..tCPCCPCC,lPMGCSPCACDAPSCRPPP,lEHREPPA. HliOEHYATEYlCOHHAINOPlHOAOCO1NOOL. l i (R ' ' E . L . ST . A . SN . D . AI . l M . i . . OD . B . IN . U . BA . S . N . L . A . L . E . A . M glll ii . l l1 . 5 D 2 M D 5 D 2 N S A _ E E R M ,4 " { >8 $ - -L . l . . . 8213945211164'414219111111 . l ! A . D I . . . 5074500000040100000000002... . 70380O0000000000O00000001 - T5 . B8 U9 L.9 L.9 1 < < < < <<<2 1 S1 A. 1 1 . , - TS . . . . AE . . . . I . l . i . - SD . . 95165 111 11 1 8 . EU . . 80930 000 10 1 . IT . . . . 4. . 8 . CS E . V.50830' O.1 2 000 00 0 < 4 - ) PL SA T N.7. 1 8 DLN . . . EAE . . UCM . l . ' 1' , 1' 5171' 1l NLN . . 7 1 2'83165 119111 1114 . LAO . . 40543110 003,000 0020 0 0 0 8.. iOR . . . . . 001000 O000 0002 . NRI OCV . G.30141000 . U.2 2 0<1 < < < < < < < <<<2 . A.1 CAN 4 (ME 1 .F K . . . - 10O . . _ - O . l . 5)R . . 9 9471 11 11 3 1 1 2. RB . 6430 00 00 4 0 0 . EEA . .3 3. . 2 . LTE . Y.3 0700 00 00 O 0 0 , BES . A.7 1 < < < < < < < 9 AM . M0 0 T . 1 1 ~ E . . . . - XR5 . . . IA8 . . . DU9 . I . lI . - NQ1 . A . . ES . A SM S . P G . M N IU OSS . - PRN . M M LN CUN . - AEI . S UA IUAA 1I U UO CTE . PR . l ET NAT S AG AOAC . U . l RA AOLO O CASTLLS . _ TD . AA UT TGOU' U RIAFUE . H . TN PS AAEQAT IXTME CN . GS . S AI SRI lLCCTR ,EERLAII ~ lN . U . LCMNURAAERIAOPLT0UICP . , EO . PPLIUEPCT MUPCTSF fCLSS . WIT . SSEFRR AA I NFAEA . - . I IFBUMSRRAAALMAAOI NFAA . YA . RAS 0URUIREHIlPUHIIDAO i HC . RT . CR R ILETPNP IPNN IISPU . DS . OAA SNLSPR0RANROMATNURT . . SHNNMYOY OO1OlOOHAISMPOC 1 _ SL . UPIIURLHANMPMiLMPlSEARMA l MA . ROTLlDCPTAOIOLC0IlERHAOL . AD . DIRLMOO0ORTSTI01SiHATCG RI . NLAAACTlLBEYEF2EYLTMI0NA . - . CT . OYCRRYSlIMALAN1ALLASTTOVL. (R . HilOEHYATFIOlHHHOAIENCPLL. l I l CPGCCPCCPMCPCARCPCLDAESUA... E . ST N lIll I SN .nl. AI . . M . . .W . IODN L . BA M . .I . -. N . I ll1" ;l ;1 i . A E M 1 0 2 M D 1 0 2 N S A E E C M m ,4 11!i!j' ,i ! * ! . 1 4 >ge L _ l _ 1 ,1 : 1 . D A . _ 763331711211111697119114212111114_ 6161213110002101 I T5 L 4009000000000000O0000000000000006_ 00100000000000004._ < < < < .< < < <<6 B8 17 U9 S1 _ L.7 A.9 1
- 1
. . ' 1. TS . _ . AE . _ -11l11 I I . l _ ll11 SD . . 7554651115 1351 1' 1 5 1 1 _ 5_ 1 EU . . 2088101010 0400 02 0 0 0 0 lT . . . . . 2. . CS . V.2025000000 00O0 00< 0 0 0 0 2. E . 35 < < < < < < PL . O ._ 5 4 0 ._ ) SA T N_9 _ 1 DLN . _ . EAE . _ _ UCM _ 1 8l111ll1 ' 1ll . l . 1 NLN LAO . . 81333711111 _ ~ . 82765202000 220420302001 111871211111 15111116_ _ iOR NRI G_0079O010000 <<< 000000O00000 00000003._ 00000002_ < < < < <<0 OCV 87 CAN (ME U_3 21 A_5 0_ 1 .fK _ _ _ 1OO _ . . - O _ l . L8lI l 1 l 5)R _ . 5112'111111 1151 1 1 1 5 3_ _ RB _ . 8239000120 0000 0 0 0 0 EEA . . . 7. _ 0000 0 0 0 0 , LTE BES AM _ Y_40O11000000 A . M_4 1 <<< < < < < < < < 4_ 5 4 T . _ 1 1 E . . . . XR5 . _ . IA8 . _ * . DU9 . l _ ' ' lI 4l I NQ1 . A . ES . A S M S . P G _ SM N I U O S S . . PRN _ M UUAA M L N C N US A . AtI _ S UA TITI U U O C EMTE I PR ET ANAT S A G AO CUADIR TD U . AA ll RA UT ALOLO TUGOU O C U AATL IARSAIA SSLIYAA EOUOETS . - H . TN PS ANAEQAT XETOE LSRTCVVNO . . S AI SRI LELCCTR .ECENLAOUCNIRRER . IGSN . U .LCMNURAARERIAOPLITAULCDIECEAMR . EO . PPLlU[ PCT CMUPCTSFR LCLINNMSIHOI . WIT _ SSEfRB AA I EN AECU OAN LC . _ I IfBUMSRRSAAALMAASOA NUTATEOA . YA _ RASOURUIREUlIlPUiI i i l IIA 0FOI CINA . RT . CR R ILETRPNP IPNANNI1 RNAS NOI - DS _ OAA SNLSPGRORANRORM0TNA OMUAOHR _ SHNNMYOY 0NOHOIOOHOA11SMTSHEPLHPA ._ SL _ UPIIURLHANOMPMTLMPliHPEASEPNREPIL _ MA . ROTLl0CPIACOIOLCOIPTIRilIDI0AMISE _ - AD DLRLM0OOOROTSIEOTSOISATHlSGCOSOC _ RI NLAAACTLLBNEYEFZEYDLYMICYYNODYTA _ GT . 0YGRRVSLIMMALANl (R . ilHIOEiYATEYiOll l l ll ALALLSTALLOT0LYHL__ HiOLAOENLOOPCHOCPL l ST E .CPGCCPCCPMGCPCARCPCCPDAEPPSER,lP S S. A _ gI :L' ll( L' ,lI i ' ' SN . _ AI . _ . M . . OD _W . IN _L . BA _H _5 N lllIilIlll . I , ll Ii . A E M - ) - 0 . 2 M D I D 2 N S A E E _ Q M _ t ; . _ _ _ _ _ . _. m___ .. , i _ . _ 1 i s a CES203 DM203 MEAN APPENDIX TABLE 5-1. (CONTINUED) ! MEAN BIOMASS (CRAMS DRY WElGHT PER SQUARE METERI 0F MACROALGAL SPECIES AT SUBTIDAL AND INTERTlDAL STATIONS DURING 1985. SEABROOK ENVIRONMENTAL STUDIES.1985. l' MAY I AUC I NOV I ALL. l
- ALL INTERTIDALI CHONDRUS CRISPUS 1257.12 867.17 .
834.08 986.121 .CICARTINA STELLATA 6.00 . 249.63 80.88 112.17 , , CORAL _tlNA 0FFICINALIS 9.68 92.05 29.60 43,T8
- CERAM10M RUBRUM 0.19' O.931 0.11 0.41 ',
POLYSIPHONIA URCEOLATA <0.01 0.80 0.21 0.34 , CVSIOCLONIUM PURPUREUM <0.01 0.59 0.05 0.21 ' 1 PHYLLOPHORA SP. 0.11 0.11 0.05 0.09 RH120CLONIUM TORIUOSUM l 0.24 0.088 i. 1 AHNFELTIA PLICATA l 0.21: <0.01 ; <0.01 0.071 'i <0.01 0.19h O.07l IPHYC00RYS RUBENS 0.03 ; l HCHAETOMORPHA PICQUOTIANA 0.03 0.111 0.088 0.07' I CALLOPHYLLIS CRISTATA 0.05 0.131 <U.01L 0.06 y , I CHAETOMORPHA SP. <0.01 0.131 0.05 0.06 : I l . PTILOTA SERRATA 0.11 <0.011 0.05' O.05
- CIADOPHORA SERICEA 1 0.16 0.05 0:
i :POLYSIPHONIA ILEXICAULIS 0.03 0.11 0.04 4 + j POLYSIPHONIA BANOSA <0.01 0.11 0.03 0.04 LEATHESIA DIFFORMIS 0.13 0.04 -) i ELACHISTA FUCICOLA 0.05 0.02 "MEMBRAN0PTERA ALATA <0.01 <0.01 0.03 ; 0.01 . SPONG0 NEMA TOMENTOSUM 0.03 0.011 POLYlDES ROIUNDUS 0.03 . 0.01 . I CHAETOMORPHA MELACONIUM <0.011. <0.01 ~<0.01 <0.01 ! L ECT0 CARPUS FASCICULATUS -<0.01 <0.01 <0.01i I L ANTITHAMN10NELLA FLOCCOSA <0.01 <0.011 <0.011 <0.01 LCALLITHAMMION TETRAGONUM <0.011 <0.01 DESMARESTIA ACULEATA <0.01H <0.01 l POLYSlPHONIA NICRESCENS , <0. 01 ' <0.01 <0.01 CYMNOCONCRUS CRENULATUS I <0.01 ; <0.01 -i <0.01 '<0.01
- POLYSIPHONIA HARVEYI RHODOMELA CONFERVotDES <0.01 <0.01 i SCYTOSIPHON LOMENTARIA <0.01 <0.01 ,
i SPHACELARIA CIRROSA <0.01 . , <0.01 t , I SPONCOMORPHA SPINESCENS <0.01 i <0.01 ; I ULVA LACTUCA i <0. 01 ' <0.01 1 ,ALL 1273.521 1212.60l 945.36 1143.83 i 4 ' . ' * ,',t* l 9 ( m 3sW"' _ . S . [5 _ l8 C9 . I . 1' ' 11111 . ,1ll E1 . . 611620012621516'811513 . P , . . 347197411711001010009 . SS . . . . . . . . LI E . L.289202500100000000003 L.2852112 < < <9 AD GU LT . A.4 3 AS . . O . . . _ RL . l . 1I11 l 1 ll1 CA . . 39194218 . 8'6 91 9 1 5 AT . . 35908801 61 00 0 0 1 MN . . .-
- 9. .
. V.19 20 00 0 0 547' 12010 E FM . O 1 < < 1 ON . 1 )R O . N. - RI . . EV . . TN . l . I EE . . 7237764999981 498 9' .0 _ M EO K . . 1268891006010 . 62566140O1000 000 0 0 201 0 4 G.6372 RO . < 9 AR UR U. A.3 3 QA . . _ .SE . . _ 2 S . . R . l . , ' l _ 5E . . 7903148 8 9 1 1 1 12 . P . . . 3447827 1 0 0 0 0 06 E 5 . . . LT8 . Y 5896309 0 O 0 0 0 02 BH9 AG1 TI A.0811123 M.1 <5 1 . EG . . _ XWN . . l I . . _ 0YR . l . l 1 lillIlil I __ MRU . A fDD . A M S ._ P . SM N U O S PSS . M UUAA N CAN AMN AO RI S l l UA ET RA ALOLO TITI ANAT CAOOC O CME AILTS . CT . A UT TUGOU RAIOE _ (A . N PS ANAEQ II . ELACGA HR m T . S I SRI L[LCC SS . U . CMNURAARERIPTULIIT _ S . PPlUEPCT CMUPS CLDNA AL . SSfRB I AA NAE MA . I fI . RAOURUIREUHIlHIAOI UMSRRSAAA'AO f NSANI II IODl . CR R ILETRPNPPNIILNM _ Bi . OA SNLSPGR0RRMTML0 _ R . SHNMYOY ONOiOOASMYiA l l FE . UPIURLHANOMPMMHEAHPR OT . ROLlDCPTACOIOOTRHPIY N . DLLMOOOOROTSTIIAIOSH NI . NLAACTLLBNEYEELMIDYP O . OYRRYSLIMMALAALSTOLRL ID . iHOEHYAT[YHOHHAfNHOOL l TN . CPCCPCCPMCCPCCCDARPPA _ AA I' I l ul I . . VL . EA . DD . l . ., Di . 7 RB . 1 AU ,lllIllilllli' i' , DS N _ AT TA _ S 1 0 2 M D 1 0 2 . S E D. R S i ; a4 < { s ' ' ' <i < ,li ;i1a 4 ii, $1 1 4 .s - _ _. RES2D1 DH2D1 4 S.D. APPENDIX TABLE 5-2. (CONTINUED) STANDARD DEVI ATION OF BIDMASS (CRAMS DRY WElGHT PER SQUARE METER) Of MACROALCAL SPECIES AT SUBTIDAL AND INTERTIDAL STATIONS DURING 1985. SEABROOK ENVIRONMENTAL STUDIES,1985. l MAY l AUC l NOV i ALL l l35 ICHONDRUS CRISPUS i 120.95l 428.361 127.86 l 256.45 ' l PHYLt0Pil0RA SP. 3.45l 192.18 170.04 l 186.21 l CORALLINA 0FFICINALIS 11.911 32.53 8.91 : 18.80 CERAM1UM RUliRUM 16.80 16.74 l 7.84 80.06l l lPHYCODRYS RUBENS 15.20 2.13 2.66' 9.27 l CYSTOCLONIUM PURPUREUM . 1.28 73.12 3.51' 63.67 i CALLOPilYLLIS CRISTATA i 3.72 8.10 1.30 5.16 PTILOTA SERRATA i <0.01 l <0.01 <0.01 MEMBRAN0PTERA ALATA l 0.09 0.09 <0.01 1 0.08 GYMNOGONGRUS CRENULATUS 7.44 0.28 <0.01 4.30 CilAE TOMORPflA MEl. AGONIUM 0.81 2.68 0.42 1.54 . i l POLYSIPHONIA URC[0 LATA I 0.18 : 0.11 p i CHAETOMORPHA PICQUOTIANA l 0.16 0.79 , 0.48 s l SCAGELIA PYLAISAEl <0.01 <0. 01 : <0.01 <0.01 W k' l AHNi[LTIA PLICATA 1.02 <0.01 <0.01 0.59 CHAE10MORPHA SP. <0.01 0.09 ; 0.05 IPOLYSIPHONIA FLEXICAULIS 0.09 0.01 CALLITHAMNION TETRAGONUM i 0.09 0.05 ANTITilAMN10NELLA FLOCCOSA ; <0.01 <0.01 <0.01 'SrilACELARIA RADICANS , 0.18 <0.01 0.11 : I ,POLYlDES ROTUNDUS I l 0.09' O.051 h RHOD 0PHYLLIS DICHOTOMA i <0.01 <0.01 POLYSIPHONIA HlCRESCENS L <0.01 <0.01 ; PALMARIA PALMATA l 0.09: 0.05' <0.01 IECTOCARPUS FASCICULATUS I l (Ril0DOMELA CONFERV0lDES <0.011 I i <0.01 l MONOSTROMA FUSCUM <0.01 l <0.01l <0.01 ' lPOLYSIPHONIA HARVEYI <0.018 l. <0.011 l lALL I 118.37 347.44l 224.031 345.061 i .-- ~ . - - . .. . . _ . - _ _ . _ - - - - i CES201 DM201 S.D. APPEN0ix TABLE 5-2. ICONTINUED) STANDARD DEVI AT ION Of BlDMASS (CRAMS DRY WEIGHT PER SQUARE METER) 0F MACROALCAL SPECIES AT SUBTIDAL AND INTERTIDAL STATIONS DURING 1985. SEABROOK [NVIRONMENTAL STUDIES 1985. I MAY l AUG l NOV I ALL l t ........,...................................................................... ! l31 LCHONDRUS CRISPUS I 50.801 81.12 44.52 91.531 l PHYLLOPHORA SP. l 133.80L 99.77 '70.88' 145.92 l CORALLINA OfflCINAllS i 3.70' 7.84l 29.521 25.05 l HCERAMlUM RUBRUM I 0.09 : 1.998 0.091 1.20 l 1PHYC00RYS RUBENS 6.71' 14.231 3.20 11.451 I I CYSTOCLONIUM PURPUREUM 2.51 1.11 0.09 1.60l 1.431 1.52 O.56 2.591 l I CALLOPHYLLIS CRISTAT A l PTILOTA SERRATA I 4.35 0.88l 0.37' 2.441 l MEMBRAN0PTLRA ALATA l 0.28 : 1.911 0.33 ; 2.01 l CYMNOGONGRUS CRENULATUS l <0.01 1 0.181' O.61 0.37 . I iCHAE TOMORPilA MELAGONIUM l l <0.011 m <0.01 l lPOLYSIPHONIA URCEOLATA l 0.09 , 0.09 : 0.241 0.16' ' l lCilAETOMORPilA PICQUOTI ANA l <0.01 l <0.01 Y lSCACELIA PYLAISAEl I. <0.01 <0. 01 ' <0.011 <0.01 u) l W I lAltNFEL11A PLICATA l <0.01 i I <0.0t h l lCilAETOMORPHA SP. I <0.011 <0.01 <0. 01 ; <0.011 <0.01 l lANTITHAMN10NELLA FLOCCOSAl <0.01 ' <0.01 l lSP11ACELARIA RADICANS l , I <0.01 <0.011 - l lALL l 102.251 27.231 110.371 140.411 t 4 1 l pe[j S , E5 I8 C9 . l . : 81l1l11 . .. 381130917'71614111151113 1 E1 P , SS 96112036230309000000008.. LI AD E . L_O76071592000000000000065 . L . A_ 61 1 < < < <<< < < < CU . . tT . . . AS . . . O . . . RL . l . II ii l l hI11 . CA . . 2668322505 9 911 9 8 . AT . . 0051946106 0. 000 0 MN _ . . 0. . 0 3 FM ON E _ V.116070322O . O. 4 0 O00 < < 3 ))R O . N. DRI . . EEV . . UIN . l _ ' : . lilllil1l11 . NEE . _ 83197855' 1 11 12 lM i K 65006267 0 00 00 009. 2. . NEO . G 27041372 0 ORO . 62<1 < < < < 5 . CAR (UB U. A. . QA . . .S E . . S . . .
- 2. R . I . '
l1 . l ilI1l1 5E . . 97715'9974 11 9 11 00 1 0 9 P . . . 313034409 06 2 E 5 . . 9. . LT8 BH9 AG1 Y.108000540 A. 6 < 1 1 00 1 00 0 3 6 Tl . M. EG _ . XWN . . . I I . . . DYR . l . l' I .I L il NRU . AH EDD . A S . P . SM N O S . PSS . M 0UAA C AUSA . AMN _ s UA 1ITI C MTER . AO _ i ET ANAT AOSOADE . RI . l RA ALOLO TLNILIF . CT . A UT TUCOUI AI AOUOI . (A . N PS ANAEQE E ClCVL l T . S I SRI LELCCA .LAICIRO . SS . U .CMNURAARERISPULDICER . S . PPlUEPCT CMUPISCLADSFP . AL . SSfRB AA A ALR AN . MA . I fDUMSRRSAAALA N SFOA OD . RAOURUIRIUiIiYiAOAI l l t CH Il . CR R ILETRPNPPPlIILS P . Bi . OA SNLSPGROR RiNRlUAR . R . SlNMYOY i 0NOHOAOSMAYPLO . FE .UPIURLHANOMPMlMEALHREM . OT . ROLlDCPTAGOIOlORHEPAMO . N . DLLMOOOOROTSTETAlCOCOR . NI . NLAACTLtBNEYECEMlAD0DE . O . OYRRYSLtMMALAAASiH010TL f ID . HHOEHYAiEYiOiClENPfiCiNL l l i TN AA lCPCCPCCPMGCPCSCDASREREA... H llllll lllL - H IVL . EA DD . . l . . Di . 9 RB . 1 AU ,llllllH Hllilllllllli . DS N AT TA S _ 1 0 _ 2 _ M D _ 1 3 2 . S E D. _ C S - - _ _ . . - - . .. - - - - . - . . - - . . . - _ . _ _ , ._ ~_- ~ - - . - . , ~ . - - - . . - QES2D5 DM205 S.D. APPENDIX TABLE 5 2. (CONTINUED) STANDARD DEVI AT ION OF BIOMASS (CRAMS DRY WEIGHT PER SOUARE METER) OF MACROALCAL SPECIES AT SUBTIDAL AND INTERTIDAL STATIONS DURING 1985. SEABROOK ENVIRONMENTAL STUDIES,1985. l MAY l AUG l. NOV l ALL I a............,...................................................................... lALL SUBilDAllCHONORUS CRISPUS I 307.88h 560.961 226.20: 397.50'
- l l PHYLE0ril0RA SP. 151.18' 145.441 95.30; 129.81 l lCORALLINA OTTICINAllS 12.64, 45.89 -
40.02 1 36.73 l lCERAMlUM RUBRUM 19.42; 75.92 . 5.111 48.49 16.15 '7.49 13.061 I lPifYCODRYS RUHENS ll 10.39l lCYSTOCLONIUM PURPUREUM i 11.111 57.27 i 2.62 34.82l CAILOPHYLLIS CRISTATA 21.65 4.53H 2.01' 13.31l ' 1 l PTILOIA SERRATA 9.09 7.94L 2.60 7.0T I HMEMBRANOPIFRA ALAT A 0.65 2.60; 1.27l 1.83 I l lCYMNOGONGRUS CRENULATUS I 3.74 0.91l 1.38 2.31 l lCHAETOMORPHA MELAGONIUM l 0.53 l 1.38 ; 0.24 0.85 I 'ISCACELIA PYLAISAEl 1 0.83 <0. 01 1 0.051 0.50 l p. I IPOLYSIPHONIA URCIOLATA O.32 0.10 0.14 . 0.21 1 i l CilAETDMORPHA PICQUOTIANA l 0.07 0.10 0.46 0.27 y( l lAHNTELTIA PLICATA 0.51 . <0.01 L <0.01 0.29 l CALLliHAMNION IETRAGONUM <0.01 , 0.141 0.05 0.09 ; 0.061 0.04 l lDESMARESTIA ACULEATA . 1 0.05 l : ANT I THAMNIONELL A It 0CCOSA l <0.011 0.09: <0.011 0.05 ) i POLYSIPHONIA ILEXICAULIS 1. <0. 01 ' O.06l 0.04 l SPHACEEARIA RADICANS . 0.09 . <0.011 0.05 l l CilAETDMORPHA SP. <0.01 <0.01 0.051 'O.03 l l RHODOPHYLLIS DIC160TOMA <0.01 0.05 1 0.03 POLYSIPHONIA NICRESCINS . <0.01l 0.05 0.03 PALMARIA PALMATA l l 0.05 0.03 i l IPOLYlDES f4TUNDUS l 1 0.05 0.03 , .ECTOCARPUS FASCICULATUS . <0.01 <0.01 1 MONOSIROMA FUSCUM L <0. 01 ' <0.01 <0.01 4 L RilODOMELA CONFERVOIDES <0.011 <0.01 ENTEROMORPilA PROLIFIRA <0.01 <0.01 POLYSIPHONIA HARVEYI <0.01 <0.01 lPORPHYRA MINIATA <0.01 1 <0.01 l l lALL 265.75; 563.43 266.951 412.921 Y a ,i i .k t , . h ps*0' S . E5 I8 l1 l' . C9 . l . E1 . . 157381'1511177311518111115. P , SS . . . . 1058811000020401001000009. . LI AD E . L.008300000001000000O000002 L.4 91 1 <<< < < <<<<<4 3 GU LT . A.3 _. AS . . O . . RL . l . ' 1" ih . 91 8 t . CA . . 59899 111 AT . . 70650 000 00 1
- 6. .
_ MN . . . 0 . . 00 0 FM E . V.50640 O.8 0 000 <<< < 9 3 ))R 0N O . N.4 1 DRI . . . EEV . . . UTN .l . : 4 . I 4' 1 NEF . . 01831869 1131 1 9 1115 . IM . . 90312110 0010 0 0 20 0 0 0 3.. T K . . . . . . 0020 0 0 00 0000< . NEO ORO . G.90561000 U.7<3 < < < < <<<5 2 CAR (UB QA . A.1 3 .S E . . . 2 S . . - L . R . I . 1I .I 1 1' _ 5E . . 2 4'711 11 11 4 1 0 1 . P . . . 3 9850 00 00 7 0 9. . 7 E 5 . . . 6 LT8 BH9 . Y.6 . A.5 02O0 00 00 0 0 2 < << < < < 0 < 7 . _ AG1 TI . M. . EG . . . XWN . . . l I . . . oYR . I . ' ' , il1 iH ll . NRU . A . EDD . A SM S . P . M N IU OSS _. PSS . M UAA M LN CUN AMN . S UA TI U UO CTE . _ AO . l ET INAT S AC A0LS AC . RI . l RA AOLO O CAST t CT . AA UT TGOU U I RiAFUE (A . TN PS AAEQAT XTME CN T . S AI SRI LLCCTR .EERLAII . SS . U . LCMNURAAERIAOPLTOULCP . S . PPLIUEPCT MUPCTSF FCLSS . AL . SSEFRB AA I NFAEA . NFAA . _ MA DD . I IIBUMSRRAAALMAAOI . RASOURUIREiIiPUiIIDA0 l l l I1SPU HC . II . CR R ILETPNP IPNN BT . OAA SNLSPR0RANROMATNURT . R . SHNNMYOY 0O1OIOOaAISMPOC 1 l FE . UPIIURLiANMPMTLMPHSEARMA l OT . ROTLlDCPTAOIOLCOITERiAOL l N . DLRLMOOOORTSTE0TSIIATCG I NI . NLAAACTLLBEYEF2EYLTMIONA . O ID .. OYGRRYSLIMALANlALLASTTOVL. HHlOEHYATEiOllil l llllOAEENCPLL ,.CPCCCPCCPMCPCARCPCIDAESUA. . TN _ AA ll I . . VL . . EA . . DD .W . I . L . 0T . M RB . 1 AU g1 i' ' DS N AT TA S 1 D 2 M D 1 0 2 . S E D. C S i ; ,( l I , 3 3:$ + S .- E5 I8 C9 . l . ' : 1L 1 E1 . . 560474261511511961212111515111115 . 818,221711000210212301001000000001 P . . . SS . . . . . . . . . . LI E . L.304900000000000000O00000000000006 L.6 83 << < < < < < < < < < <9 2 AD CU LT A.4. 11 AS . . . O . . . RL . l . H ,: CA . . 0957 99199 1391 7' 91 1 1 4 AT . . 3084 00000 0300 3 0 0 0 0 MN . . 3. . .0 0 0 0 2 . FM ON E O.4025 . V. N.7 29 00000 0O00 0 < < < 5 1 O . . . ))R . . . w DRI . . . EEV . . . UTN 1 . l . NEE . . 841449781 1 ,l9'9128 519118 1911111'3. IM . . 628620010 0 00031 500001 00000007. T K . . . . NEO . . 0 00000 000000 00000008 < .< ORO CAR G.7904800100< . U . A4 50 - 22 < < < < < < < < <6 3 (UB . QA . . . .S E . . . S . . .
- 2. R . l .
L1' 5E . . 6976 11891 1191 1 1 9 2 . P . . . 2011 00100 0000 0 0 0 0 E 5 . . . . . 8. . LT8 BH9 AG1 Y.3050 A.5 1 00000 0000 0 0 0 0 8. 5 Tl . M. . EG . . . ixWN I . . DYR .l . Illl . - NRU . A . EDD . A S M S . P . SM N I U O S S . PSS . M UUAA M L N C N US A . AMN . S UA TITI U U O C EMTE I . AO . l ET ANAT S A G-AO CUADIR . RI . l RA ALOLO O C AATL SSLIYAA . GT . AA UT TUGOU U IARSAIA EOUOETS . (A . TN PS ANAEQAT XETOF LSRTCVVNO . T . S AI SRI LELCCTR .ECENLAOUGNIRRER . SS . U . LCMNURAARERIAOPLITAULCOlECFAMR . S . PPLIUEPCT CMUPCTSFR LCLINHMSFlOI . AL MA . I SSEFRB TFBUMSRRSAAALMAASOA AA I EN AECU NUTATFOA OANfLC . DD . RAS 0URUIREUiIHPUlI l i IIAOFOI . CINA . II . CR R ILETRPNP IPNANNII RNAS N0I . BT . 0AA SNLSPGR0RANR0RMOTNA OMUAUiR l R . l Y ONOiOIOOi0AiSMTSiEPLiPA l l l l l FE OT SiNNMYO.HANOMPMTLMP1lHPEASEPNREPIL . UPIIURI . ROTLO0CPTAGOIOLCOIPTIRHlDIOAMISE N . DLRLM0OO0ROTSTEOTSOISATilSCC0 SOC l NI . NLAAACTLtBNEYEFZEYDLYMICYYNO0YTA . O ID 0YGRRYSLiMMALANIALALLSTALLOT0LYliL. . iHIOEHYATEYliOillilOLAOENLOOPCl l l l l 1OCPL. TN AA , CPGCCPCCPMGCPCARCPCCPDAEPPSERPSSA. . l ' i H I . . VL . . IA . . DD .W . I . L . DT . M . RB . 5 . AU ,1lI IlI . DS N AT TA S 1 D 2 M D 1 D 2 . S E D. R S s RES2D3 DM203 .s S.D. APPENDIX TABLE 5 2 (CONTINUED) ,'r ' STANDARD DEVI ATION OF BIOMASS (CRAMS DRY WElGHT PER SQUARE METER)'Of MACROALGAL SPECIES AT SUBilDAL AND INTERTIDAL STATIONS DURING 1985. 'SEABROOK ENVIRONMENTAL STUDIES,1985. y, -.~ l MAY l AUG l NOV l ALL l , ALL INTERTIDAL lCIIONDRUS CRISPUS 207.15L 490.61 336.67: 394.75! lCICARTINA SIELLATA 11.231 269.64 86.17' 186.09' CORALLINA OfflCINAlls 16.78 163.19 66.94 102.65 CERAMlUM RUBRUM 0.38 0.90 0.08 0.65 POLYSIPil0NIA URCEOLATA <0.01 1.49 0.31 0.90 CYS10CLONIUM PURPUREUM <0.01 0.83 0.08: 0.53 -- PilYLLOPHORA SP. 0.13 0.19 0.08 0.14 RillZOCLONIUM TORTUOSUM 0.33 0.21 ,- AllNFELT I A PLICATA 0.52 <0.01 <0.01 0.30 - PHYCODRYS RUBENS <0.01 0.16 0.07 0.13
- CHAE10MORPHA PICQUOTIANA 0.07 0.13 0.09 0.10 ~
CALLOPilYLLIS CRISTATA 0.13 0.16' <0.01 0.121 3, . CllAETOMORPHA SP.. I <0.01 0.19 0.13 0.14 s PTILOTA SERRATA 0.13 <0.01 0.08 0.09 W CLADOP110RA SERICEA 0.39 0.23 ^ POLYSIPil0NIA (LEXICAULIS 0.06 0.26 0.15 l POLYSIPHONIA LANOSA <0.01 0.13 0.07 0.09 - R LEATilESI A DI F FORM 1S 0.21 ' O.13 ' IELACillSTA FUCICOLA 0.13 0.08 . MEMBRAN0PIERA ALATA <0.01' <0.01 0.07 0.04 l - SPONGONEMA TOMENTOSUM 0.07: 0.04 , ; POLYlDES ROTUNDUS 0.07 0.04 . CilAETOMORPHA MELAGONIUM ~ <0.01 <0.01 <0.01 <0.011 ECTOCARPUS FASCICULATUS <0.01 <0.01 <0.01 ANTITHAMNIONELLA FLOCCOSA <0.01 <0.01 , <0.01 <0.01 CALLITilAMN10N TETRAGONUM <0.011 <0.01 DESMAREST1A ACULEATA <0.01 <0.01
- POLYSIPilONIA NICRESCENS ,
~<0.01 i <0.01 <0.01 ; ..GYMNOCONGRUS CRENULA10S <0.01 <0.01 I POLYSI PilONI A ilARVEYI <0.01 <0.01 I RH0DOMELA CONFERVolDES <0.01l <0.01 . SCYTOSIPliOH LOMENTARIA <0.01 <0.01 SPHACELARIA CIRROSA <0.01 <0.01 ' SPONG0MORPilA SPINr.SCENS J <0.01 <0.01 ; ULVA LACTUCA <0.01 . <0.01 IALL 207.73: 364.00 285.61 311.71 % i 7 . _ _ _ _ . _ _ _ _ _ _ _ _ . _ _ - . _ _ _ _ _ - _ _ . - _ _ _ _ _ . , - . . - - . . . ~ _ . ., + ,. g RES?D1 DM2D1 . , -f , ~ m; /x-e es w ~ PCNT' APPENDIX TABLE 5-3. PERCENT COMPOSITION OF BIOMASS (CRAMS DRY WEICilf PER SQUARE HETER) 0F MACROALCAL SPEclES AT SUnilDAL AND INTERTlDAL STATIONS DURINC.1985. SEABROOK ENVIRONMENTAL STUDIES,1985. l MAY l AUG l NO[ l ALL l ....... ..a.................................................................... ( 17 Cil0NDRUS CRISPUS l 69.921 89.351 65.81 78.22 ,ih. . - PHYLLOPII0ftA SP. I 13.271 2.13! 25.52 11. 08a m. -^^y CORALLINA OFFICINAllS I 3.47l 5.61 6.79 5 . 38: ~? l CERAMlUM RUDRUM 4.86 1.85 0.38 2.27 .s l PilYCODRYS RUBCNS 2.02 0.47 1.02 1.02 '. -- CYSTOCLONIUM PURPUREUM 2.13' O.16 : G.09 ~ 0.66 ', s CALLOPHYLLIS CRISTATA 4.32 0.29 - 0.11 1.30 d IPilLOTA SERRATA <0.01 <0.01 0.01 0.01 ~~ MEMBRANOPTLRA ALATA 0.01 0.011 <0.01 0.01 GYMNOGONGRUS CRENULATUS , 0.09 0.23 0.10 - CllAETOMORPilA MELACONIUM 0.01 <0.01 0.02 0.01l , POLYSIPilONIA URCEOLATA <0.01 -0.01 <0.01 <0.01: y 1 CHAETOMORPHA PICQU0ilANA <0.01 <0.01 0.01 <0.01 e CHAETOMORPflA SP. F <0. 01 ' <0.01 W' <0.01 0.02 0.01 CALLliHAMNION TETRAGONUM DESMARESTIA ACULEATA O.01 0.01: 0.01 ANTITHAMN10NELLA FLOCCOSA <0. 01 ' O.01 1 <0.01 Ril0DOPilYLLIS DICHOTOMA <0.01! <0.011 <0.01l <0.01 POLYStPHoulA NICRESCENS PORPilYRA MINIATA <0.01 l <0.01 1 ALL ' 100.00 100.001 100.00 100.00 i ' i [ *~*,3 Fj. p y p 'O %, [ "v s g F n _ . _ _ _ _ _ _ _ _ - . . _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ _ IC - - . , . ,, M ; L 1 i' ' [1. e ? ~ ~ y8HO 5 S . E5 l8 . c9 I i E1 26321431182141211111111111110. P , . 000000000000. SS LI E L L.62 96801550011000000 10281400000000000000000000000 < < < <<<<<<<<<<<<0 . 1 AD A . CU . LT . . AS . . O . ; l1l1 . RL l ' _ CA . 126192711151111121111' 1' 1 0 . AT . s . 0 0 MN . 8 3 6 4.i.8 2 0 0 0 0 0 1 0 0 0 0 0 0 0 0.-. 0. . . 212100000000000000000 0 .00. - FM 0N E V.63 O. <<< < < < << < 0 . 1 N. .. O . ))R .. . DRI . . EEV . 1 UTN l 1 10 - EE 5815012111411111111 1 1 lM . 5724206000100000000 0 0 i K . . 0 0. . . 5624190000000000000 0' 0 00. NEO ORO CAR C.42 U A. 1 < < < <<<<< < < <0 . 1 HUB . . QA . .SE . 4 S l1 L . R 1 - l . 1l .1' 1 5E . 5815078111312181 11 1 0 - P . 4309525006100000 0 00 '0. E 5 . 0 0. - , Li8 Y.8142100000O00000 0O 0 > 00 0. Bi9 l A.8 < < < < < << 0 1 AG1 M . TI EG . IXWN . . DYRI 1 . A i . NRU . EDD . A SMS ' 4 P . - SM N IUO S - . 4 , PSS . M UUAA' LNC' AN -- TE S-US . C AMN . S UA TIII UOC ME *- " AO . l ET' ANAT AGOS OC AD I . RI . l RA ALOLO CALN TS- Ll Y . GT . A . UT TUCOUl IRFA OL U0 E . i CSHR CVMV . (A . N PS ANALQEA XI _ T . S I SRI LELCCAT . EEAlUCCAIRUR SS . U .CMNURAARERISAPLTLbDIITCECA . S . PPIUEPCT CMUPICSF LANDNASFSH . _. AL . SSFRB AA AI NERU MANU . e MA . I FBUMSRRSAAALLAAON TSALFOFA . , OD II . CR R R'A0URUIREUHIHYPlIIOAOIIA ILETRPNPP i PNNIIRLNPS C AN I BT . OA SNLSPGR0R AROMNR LO UAMO . R . SHNMYOY ONOiOAIOHAMASYHAPLOH l FE . UPIURLHANOMPMlTMPHALEHPIRERP ' . . OT . ROLlDCPTAGOIOlLOITHEDPIRAMTI N . DLLMOOOOROTSTEETSITCl0SACOSS AYDYMODOY NI O ID .. NLAACTLLBNEYEGFEYLIlLOLLT0NLL. OYRRYSLIMMALAANALLTi . HHOEliYATEYHOHCHllOANPOHOACHOOL TN IA. . CPCCPCCPHGCPCSACPCASPRPPERHPAI .. .IlI I .I ll' S . OL . . PA . . MD . . OI . . CT . 5 . B . 3 . TU iI Il l . NS E CT RA E P 1 0 2 H D _ 1 A _ 0 2 T S N E C R P -
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3:Hf S . E5 8 IC9 . ) . .111l8 l l E 7883753475131111110. P 1, . SS . . 6591527540000000000. LI AD E . L.7410300000000000000 L.251 < <<<<<<0 1 CU LT A.. . AS . . . O . . . RL . l . 1 . CA . . 2362522440 0 1 1110 AT . MN . 5830003322.: 1 . 0 0 0 0 0.. FM ON E . V.1860200000 O.341 0 0 0000 . < <<<0 1 ))R O . N. . DRI . . . EEV . . . UTN . l . L' . NEE . . 10002751921 211111 0' . IM . . 69330125800000000 . T K . . . 0. . NEO . . 32505010000O00000 0 . ORO CAR G.431 U. < ' < < <<< 0 (UB QA A.. 1 .SE . . . 3 S . . . - R . l . 11 l _ 5E . . 9051939741 1 1 1 0 . P . . . 0130743610 0 E 5 . . . . 0. ^ 0 0. . 7 LT8 BH9 AC1 Y.9060200000 A. 8 0 0 0 0 < 0 1 . . TI . M.. . EG . - XWN . . . I . . . loYR . l . . A-NRU [DD . A S . P . SM N O . PSS . M UUAA C . AMN . S UA TITI C . AO . l ET ANAT OS . RI . l RA ALOLO LN . CT . A UT TUCOUl FA . (A . N PS ANAEQEA C . T . S I SRI LELCCAT . AI . . SS . U .CMNURAARLRISAPLD . S . PPIUEPCT CMUPICSLA . AL . SSFRB AA AI ER . MA . I FBUMSRRSAAALLAN . OD . RA0URUIRLUHIHYPH0A . If . CR R ILETRPNPP P1I . - BT . OA SNLSPCROR ARNR . . R . SHNMYOY ONOHOAIOMA . FE . UPIURLHANOMPMITMAL . OT . ROLIDCPTACOIOLLOHE . N . OLLMOOOOROISTEETTC . _ NI . NLAACTLLBNEYEGILIA . O . OYRRYSLI . ID . HHOEHYATEYHOHCHHNPL MMALAANATHL. TN IA CPCCPCCPMGCPCSACASA;L l I S . . OL . . PA . . _ MD . Ol Ci . 1 . B . 3 . TU e11' illl . NS E . CT RA E P 1 - D _ 2 _ M D _ 1 D _ 2 S E T N C K P ) 4 ,
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- i
) ! J.4 : I RES?DI DM201 PCNT APPENDIX 1ABLF 5-3. (CONTINUED) PERCENT COMPOSITION of BIOMASS (CRAMS DRY WEIGHT PER SQUARE METER) of MACROALCAL SPECIES AT SUBilDAL AND INTERTIDAL STATIONS DURING 1985. SEABROOK ENVIRONMENTAL STUDIES,1985. l MAY l AUG l NOV l ALL l i.......i......................_ ...._.............................._.......... .119 l Cif0NDRUS CRISPUS ll 0.43 0.23 0.21' I PHYLLOPHORA SP. 68.75 59.40 87.81 72.85 l LCORALLINA OfflCINAlls 6.68 9.56 2.89;' 6.21 1 CERAMIUM RUBRUM <0.01 <0.01 0.04 O 02
- PHYCODRYS RilBENS 7.29 17.71 4.43' 9.77l l CVSTOCLONIUM PURPUREUM 0.29 0.55 0.12 0.321 CALLOPHYLLIS CRISTATA 6.65 3.68 1.24 3.56 i PTILOTA SERRATA 8.27 7.18 2.17 5.56 l 1MEMBRAN0PILHA ALATA 0.66 1.91 0.85 1.16 -
ll ; GYMNOCONGRUS CRENULATUS 0.14 0.06 . CHAETOMORPHA MELAGONIUM <0.01 . <0.01 .POLYSIPil0NIA URCEOLATA 0.23 <0.01 : 0.04 0.08 l 'CilAETOMORPilA PICQUOT I ANA <0.01 <0.01 >I lSCAGELIA PYLAISAEI CilAETOMORPilA SP. 0.75 <0.01 0.02 <0.01 0.21' <0.01 y w. DESMARESilA ACUlfATA <0.01 <0.01; ANilillAMN10NELLA FLOCCOSA <0.01 <0.01 .SPilACELARIA RADICANS <0.01 <0.01
- Ril0DOPilYLLIS DICll0TOMA <0.01 L 0.02 0.01
- ECTOCARPUS FASCICULAIUS <0.01 '
<0.01 RilODOMELA CONFERVotDES <0.01 <0.01 ENTEROMORPilA PROLIFERA <0.01 <0.01 l o ALL 100.00 100.00 . 100.00 100.00 : RES2D5 DM2D5 PCNT APPEN0lX TABLE 5-3. (CONTINUED) l PERCENT COMPOSITION OF BIOMASS (GRAMS DRY WElGili PER SQUARE METER) Of MACROALCAL SPECIES AT SUBilDAL ANO INTERTIDAL STATIONS DURING 1985. SEABROOK ENVIRONMENTAL STUDIES,1985. l MAY l AUG l NOV l ALL l .._..........a ...__.....__...___..__. ...............___...... ........... ......... lALL SUBTlDAL' CHONDRUS CRISPUS 57.46 60.92 51.56 57.54 19.32 38.94 PHYLLOPl10RA SP. 28.00 26.82 l l CORALLINA OFFICINAllS 4.53 6.01 6.01 5.58 l CERAMOUM RUBRUM 2.78 6.05 0.63 3.72 l l PHYCODRYS RUDENS ' 2.46 2.57 1.45 2.26 ' l H CYSTOCLONIUM PURPUREUM i 0.99 : 3.38 ; O.33' 1.91 CAtt0PHYLLIS CRISTATA 2.44: 0.78 ; 0.35, 1.16 PTILOTA SERRATA 0.86 0.57 l 0.35 0.60 h HIMBRANOPTE RA ALATA 0.10 0.26 0.15 0.19 I LGYMNOGONGRUS CRENULATUS l 0.21 0.05 0.14 0.12 i lCllALTOMORPilA MELAGONIUM l 0.05. 0.05 0.03 0.04 : 1 iSCAGEllA PYLAISAEl ' O.07 : <0. 01 l <0.01 0.02 1 3, I lPOLYSIPHONIA URCEOLATA 0.03 0.01 0.02 0.02 I e l lCHAETOMORPilA PICQUOTIANA 0.01 <0.01 0.04 0.01 H lAHNFELTIA PLICATA 0.03 <0.01 <0.01 l 0.01 8 lCALLITHAMNION TETRAGONUM <0.01 0.01 <0.01 <0.01 ; lDESMARESTIA ACULEATA <0.01 <0.01 <0.01 L ANTITHAMNIONEttA FLOCCOSA <0.01 <0.011 <0.01 <0.01 POLYSIPil0NIA FLEXICAULIS <0.01 1 0.01 <0.01 SPHACELARIA RADICANS 0.01 1 <0.01 <0.01 l CilAETOMORPHA SP. <0.01 <0.01 <0.01 <0.01 l Rl10DOPilYLLIS DICl10TOMA 1 <0.01 <0.01 <0.01 , POLYSIPilONIA NIGRESCENS <0.01 <0.01' <0.01 PAtHARIA PALMATA <0.01 <0.01 . JPOLY1 DES ROTUNDUS < 0. 01. <0.01 ECTOCARPUS FASCICULATUS L <0.01 <0.01 MONOSTROMA IUSCUM I <0.01 <0.01 <0.01
- l R110DOMELA CONIERV0lDES <0.011 <0.01 ENTEROMORPIIA PROLIFERA I
<0.01 <0.01 . POLYSIPilONIA HARVEYI . <0.01 <0.01 : 'PORPilYRA MINIATA I <0.01' . <0.01 h I ALL 100.00 100.00 100.001 100.00 ______........_....___..__ ..................... I ..._.........'..... .__.._____...... 1 - 2 !. , l , s , , s p P2 S . . E5 I8 C9 . l . .I11 . E 1, . . 7145511111141111111111110 . P SS . . 9017000000000000000000000... ._ LI AD E . . L.8000000000000000000000000 . L.8<1 < < < < << < <<<< < <<<<0 1 CU LT . A. AS . . . O . .. . RL . 1 . l . 11 I CA . . 71901 111 11 1 0 . AT . . 30180 4 000 00 0 _ MN . . 0. . 0 . _ FM ON E . V.40500 O.8 1 000 00 0 < 0 1 ))R O . N. . DRI . . .. EEV . . . UTN . l . 1; . . 1111 . _ NEE . . 81719111 110111 1121 1110 . _ IM T K ... .. 50830000 001000 . 000000 0000 0000 . . 0000 0 0 0 0.. . G.40400000 NEO . ORO < << < << << < < . U.8<1 <<0 CAR . A. _ 1 (UB . QA . . . _ . SE . . . 3 S . . . _. 5E - R . l . . . 7 l 6031 1 11 11 - 4 L!1il 1' I 1 0' . P . . . 2 0600 00 00 0 0 0 . _., E 5 . . 0. . LT8 BH9 AG1 Y.8 . A M9 . 0100 00 00 0 0 0 0 0 1 . _. TI . . _ EG . . . XWN . . . I . . . DYRI . l . I . l i .Ill . _ NRU . - A EDD . A SM S . _ P . M N I U OSS . PSS . M UAA M LN CUN . AMN . S UA TI U UO CTE . _ AO . I ET INAT S AG AOAC . RI . L RA AOLO 0 CASTLLS _ CT . AA UT TGOU U I RIAIUE . . (A . TN PS AAEQAT XTME CN . T . S AI SRI LLCCTR .EERLAII . SS S . U .LCMNURAAERIAOPLTOULCP . PPLlUEPCT MUPCTSF FCLSS AL . SSEfRB AA I NFAEA . MA . I TfBUMSRRAAALMAAOI NFAA . OD . RASOURUIREHIHPUHIIDAO R ILETPNP IPNN IISPU HC . I . CR _._ BTI . OAA SNLSPRORANROMATNURT . R . SHNNMYOY OOHOIOOHAISMPOC FE . UPIIURLHANMPMTLMPHSEARMA . OT . ROTLl0CPIAOIOLCOITERHAOL . N . DLRLM0OOORTSIE0TSIHATCG . . _ NI . NLAAACTLLBEYEF2EYLTMIONA . O . ID . OYCRRYSLlMALAN1ALLASTTOVL. . HHI OEHVAiEHOHHHHOA[ENCPLL. ., CPC,CCPCCPMCPCARCPClDAESUA. _ TN ' IA l uH _. S OL . . PA . _. MD .W . Ol . L . Ci . M . B . 1 . TU .1lH lI li l .l . l l . NS E CT RA E P 1 D 2 M D 1 _ D 2 T S N _ E C _ R P ,! i j ;1j!.tj.jii. 1l' ; j.) i ,1Iil- i. i, ; ! l; RES2D1 DM2D1 PCNI APPENDIX IABLE 5-3. (CONTINUED) PERCENT COMPOSITION OF BIOMASS (CRAMS DRY WEIGili PER SQUARE METER) 0F MACROALCAL SPECIES AT SUOTIDAL AND INTERilDAL STATIONS DURING 1985. SEABROOK ENVIRONMENTAL STUDIES,1985. l MAY l AUG l NOV l ALL l 15MLW Cil0NDRUS CRISPUS 99.05' $2.96 91.37 . 83.56 l PHYLt0Pil0RA SP. 0.01 0.02 0.01 : 0.01 l : CICARTINA STELLATA l 0.78i 28.71' 3.15 ; 9.f 4 8 . 17.92: l l CORAL. LINA 0FFICINALIS 0.13 5.36; 6.78 l lCERAMlUM RUBRUM l <0.01 0.05 0.02l 0.02 l l PHYCODRYS RUBENS l <0.01 0.03 0.011 0.01 l CYS10CLONIUM PURPUREUM l <0.01 0.10 0.01 0.03 l LCALLOPflVLLIS CRISTATA 0.01L 0.02 <0.01 0.01 l PitLOTA SERRATA 0.01 <0.011 0.01 0.01 l MEMBRAN0PIERA AtATA <0.01 <0.011 0.01 <0.01 1 l lGYMNOGONGRUS CRENULAIUS <0.01L <0.01 l l lCilAETOMORPilA MELAGONIUM <0.01 1 <0.01 : <0.01 3, I lPotYSIPil0NIA URCIOLAIA <0.01 1 0.02 0.084 ' O.h2 l 'CilAETOMORPilA PICQUOT I ANA <0.01 0.02 . 0.01 0.01t H AIINFEl.ilA PLICATA <0.01 i <0.011 <0.01 1 <0.01 O Rill 20CLONIUM TORTUOSUM , 0.05 0.01 l ! CIIAETOMORPilA SP. <0.01 0.03 : <0.01 0.01 (POLYSIPil0NIA FLEXICAULIS l <0.01 0.02 0.01 l l CLAD 0Pil0RA SERICEA , 0.03 0.011 l lCALLilflAMN10N 1EIRAGONUM l <0.01 . <0.01 l lPOLYSIPil0NIA LANOSA l <0.01 l 0.02 0.01 0.01 : 1 1.DESMARESilA ACULEATA . <0.01 <0.01 l l ANT lillAMNIONELLA FLOCCOSA I <0.01 <0.01 <0.01 <0.01 , I EtACHISTA FUCICOLA 0.01 <0.01 l l hPOLYlDES ROTUNDUS <0.01 1 <0.01 1 <0.01 <0.01 <0.011 h IPOLYSIP110NIA NICRESCENS l
- l lSPONG0 NEMA TOMENTOSUM 0.01 ; <0.01l
'l IECTOCARPUS FASCICULATUS i <0.01 <0.01 <0.019 l lRIIOOOMELA CONFERVotDES l <0. 01 1 <0.01 1 l POLYSI PilONI A IIARVEY1 l <0.01 <0.01 l :SCYTOSIPl10N LOMENTARIA l <0.01 <0.01 : - l lSPIIACELARI A CIRROSA l . <0.01 . <0.01 l lALL l 100.00 i 100.00 : 100.001 100.00 RES203 DM203 PCNT APPENDIX IABLE 5 3. (CONilNUEO) PERCENT COMPOSITION OF B10HASS (CRAMS DRY WElGili PER SQUARE METER) 0F MACROALCAL SPECIES AT SunilDAL AND INTERilDAL stall 0NS DURING 1985. SEABROOK ENVIRONMENTAL STUDIES.1985. l MAY l AUG l NOV l ALL l g.....__.. .... ...... .....__..............__............................. .......... l ALL INTERTIDALI Cll0NDRUS CRISPUS 98.71 l 71.51 88.23l 86.21. GlCARTINA SIELLATA 0.874 20.59 8.56 9.81 CORALLINA 0FFICINALIS 0.76 7.59 3.13: 3.83 CERAMlUM RUBRUM i 0.01 0.08 : 0.01; 0.04 POLYSIPil0NIA URCEOLATA <0. 01 ' O.07: 0.02 0.03 lCYSIOCLONIUM PURPUREUM <0.01 0.05 0.01 0.02 .PilVLLOPil0RA SP. l 0.01 0.01 0.01' O.01 l Rill 20CLONIUM TORTUOSUM 0.02 l 0.01 l AllNFELTIA PLICATA 0.02 <0. 01. <0.01 . 0.01 l PilYC00RYS RUBENS , <0.01 0.02 <0.01 0.01 I ICllAEIOMORPflA PICQUOTIANA I <0.01 . 0.01 0.01 0.01 CALLOPilYLLIS CRISTATA <0.01 1 0.01 <0.01 0.01 p Cll AE T OMOR Pila SP. <0.01 0.01 : 0.01 0.01 e l PTILOTA SERRATA 0.01 <0.01 0.01 <0.01 H CLADOPilORA SERICEA 0.01 <0.01 0.01 <0.01 <0.01 1 POLYSIPil0NIA FLEXICAULIS ll l POLYSIPil0NIA LANOSA <0. 01 ' O.01 <0.01 <0.01 lLEATilESI A OlF FORMIS 0.01 <0.01 l ELACillST A IUCICOLA <0.01 <0.01 MEMBRAN0PTERA ALATA .<0.01 <0.01 <0.01 <0.01 , S PONGONE MA TOMENTOSUM <0.01 <0.01 IPOLYlDES ROTUNDUS <0.01 <0.01 CllAETOM0ftPilA MELACONIUM <0.01 <0.01 <0.01 <0.01 ECTOCARPUS FASCICULATUS <0.01 <0.01 <0.01 ANTilllAMN10NELLA FLOCCOSA . <0.01 <0. 01 ' <0.01 <0.01 CALLITilAMNION TETRAGONUM <U.01 <0.01 'DESMARESTIA ACUL[ATA 1 <0. 01 ' <0.01 L <0.01 <0.01 <0.01 lPOLYSIPilONIA NICRESCENS . GYMNOGONGRUS CRENULATUS <0.01 1 <0.01 POLYSi rtl0NI A ilARVEYI <0. 01 ' <0.01 , RilODOMELA CONIERV010ES <0.01 <0.01 l SCYTOSIPilON LOMENTARIA <0. 01 : <0.01 l SPilACILARIA CIRROSA <0.01 <0.01 l .SPONG0MORPilA SPINESCENS <0. 01 : I <0.01 l : ULVA LACTUCA <0.01 l <0.01 . [ :ALL 100.00 . 100.00 , 100.00l 100.00 . , _. _.m_. ._ ~_ - - - RES3D3 DM303 APPENDIX TABLE 5-4. STAT IST ICS ( SUM, MEAN, STANDARD DEVIATION, NUMBER OF SPECIES) 0F MACROALCAL SPECIES BIOMASS (GRAMS DRY WEIGHT PER SQUARE METER) AT A. SUBilDAL AND B. INTERTfDAL STATIONS DURING 1985. SEABROOK ENVIRONMENTAL STUDIES,1985. A. SUBTIDAL ...........i....................................................... l17 I SUM N 2339.69L 4273.13' 2270.251 8883.07' l MEAN 779.90 l 1424.38 756.75 : 987.01 ; S.D. 152.62 390.40 : 119.15 393.93' I NSPE 15.00 17.001 16.00 20.00 l h19 SUM . 553.45 694.89 775.85 2024.19' MEAN I 184.48 231.63 258.62 224.91 ' S.D. 63.99 59.22 . 33.08 56.83 15.00 14.00 NSPE 15.00 . 22.00 31 SUM 1328.33 1389.77 654.41 . 3372.51 . , . MEAN . 442.78 463.26 218.14 374.72 i S.D. l 102.25 27.23 , 110.37 , 140.41 .NSPE I 13.001 17.00 15.00 18.00 Y" 35 l SUM i 2150.901 3585.14 1829.14 7565.18 H' MEAN 716.97 1 1195.05 609.71 840.58 -$ S.D. 118.37 347.44 224.03 345.06! .NSPE . 21.00 : 22.00 23.00 28.00 ALL : SUM . 6372.37 i 9942.93l 5529.65 21844.95' MEAN l 531.03 828.581 460.80 : 606.80 IS.D. 265.75 . 563.43l 266.95 1 412.92 lNSPE 23.00 25.001 25.00h '31.00 B. INTERTIDAL . 4 l MAY l AUG l NOV l ALL l u----------l------------------------------------------------------- l 1MLW SUM l 3276.97 4268.51 2545.45L 10090.92' 1092.32 1422.84 848.48 1121.21 .MEAN I l lS.D. I 76.91 250.35 390.61 342.95 l lNSPE h 12.00 21.001 11.00 24.00 . '5MLW ISUM '4364.18 3007.07 3126.74 10497.98 i IMEAN 1454.73h 1002.36 1042.25 l 1166.44 l LS.D. I 58.821 368.73 152.34 296.15 l ' NSPE 18.00 ; 30.00 20.00 32.00
- ALL sum 7641.15 !
7275.57 5672.18 20588.90 ; IMEAN ' 1273.52 1212.60 . 945.36 1143.83 : IS.D. 207.73 364.00 285.61 . 311.71 18.00 34.00 20.00ll 35.00 . . . . . . . . INSPE I; yIyo o , E V I T C U R T S E
- D L S x x x x x x L WM A L D H I 5 T L W x x x x x R O I E OM T P N
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[ J 4 3 % 9 et % % % 4 b % D % % % % % et t e % u 3 % % M e 4e % 4 0 0 .1C g ** *e Q 9 w w w at eg og og as e 4 g 4 ( ( ( ( > < u e A w % % w w 4 ** % % 4 % % % % % 4 C 9 9 9 4 M D D h 4 A 4 C % et et 85 % 0 % % % C k h t t L 6 e t O X g W3 % 88 C 4 9 L L 9 9 4 4 4 4 M 9 C C% C 9 b o e % A M 4 O 4 u u u9 9 C th *e et at A % %% *e et et C A L L g 0 u4 w4w0*, as u 4o 3 3 3 y a g og 4. % % % x ( c c c 0 E O at t t % 9 et 9 4 0 4-4 4 4 w w On % M D D 4 % 3 3 3 84 et M M Q Q ka 44 % % % w w % 4 4m % % % % % % % % % g gM < = _ - - - _ - - - - - . . _ . - - _ - - - - - - - - _ - _ _ _ . - _ - _ _ . . _ _ - . _ _ . . _ _ _ _. . - - - _ _ _ - ____-_.-.-_.-_.a I l I APPENDIX TABLE 5-5. (Continued) INTERTIDAL SUBTIDAL CENERAL TIDE POOL l 1MLW SHLW IHLW 5MLW 17 35 31 19 HLW MSL MLW MSL HLW MSL MLW MSL RHOD 0PilYTA Ahnfelgia plicata x x x x x x x x x x x x x x x x x Antichamnionella floccosa AudouineiIa purpurea x Callithamnion tetragonum x x x x x x x Callophyllis cristata x x x x x x Ceranium rubrum x x x x x x x x x x x Ceratocolat hartzil x x Chondrus crispus x x x x x x x x x x x x Clathromorphum circumscriptum x x u x x x & H x x 'x x x x x x x o Corallina officinalis x Cystoctonium purpureum v. x x x x x x x x cirrhosum Dermatolithon pustulatum x x x x x x Devalersea ramentaces x x x x . Dumontla contorta x x x x x x x Cigartina stellata x x x x x Cyanogongrus crenulatus leptophytum laeva K K Lithothamniun glaciale x x x x Melobesia lejollsli x x x x x x x x x l Membranopters stata Palmaria palmata x x x x x x x x x x x Petrocelis cruenta 1 teyssonnelis rosenvingii x l l t l + , . L l yayH L x x S x x WM L M S t WL x x x x x x . o - o M P E D L x x x x x f S x TWM t M L I ~ A W x x x x x D L l M i - R . E L x T N S x ~ I WM L - M S . L L W x x x x x x x x x x x A M R E N E C S L x x x x x WM ._ t M I w t x x x x x x x x x .. M 9 x x x M x x 1 x x x L 1 3 K x x x x x x x x _ A D # . I T B U 5 x x x x u x x x x x x u x x - S 3 - 7 1 x x x x u x x x x u x ) d s e e ._ u - i n d i l t o n i s n u d m i s n a n u l n at s s c o r t a a s u e e n _ . ( ) e i a g m o a i c y s s c al s t i s d o s l t n . d c i t i r l o o a l e o l a c evn o g u i e s e o c s x v o r e i 1 a v h g e - 5 . u n s du il n n e u s u e r n g cl t a ci a e i r c e as l n . e a u i t r n d a a i r s t 5 - I t e p s r r n n n g ua n f h l n u oc si i Ia nt f d e i a - n b s p t t r o s a l - E o u o o o e o i i i i i e ni bm r c i m y t a a a a a u C r a a a a h h h l e r no n m u es a l es p o on on on L B ( r r r r t t t l l A s o o o o i i i l l a s h h h h h a a a l y y n ~. A y h h h h f T T r p p p p o t o o i er dpi pi ipi pi ypy ry r r s e h h mip t p l X Y d o ot o lo l i t t am ma ma na yiy sy sy s y ys ps phprh r hr o o dod od g e I H o l D P c l l l l i o oh oh ah c - O I O y y y y y y y y u D h h h h h h h h ! l o o l o l o l o l o l o o o t P P OH P P P P t P P P ! P P P P P P P F P P R R R S A R . _ _ _ _ _ . . . - . . . _ . _ . - . _ . . _ . _ - _ _ _ _ _ . _ . _ . . . - . _ . ._ _. -. - . - _ _. _ y _ _m_ _ - _ . . _ _ _ . . , _ _ _ . ~ e APPENDlX TABLE 5-6. A. THE IOUMBER OF UNIQUE TAXA RECORDED FROM ALL DESTRUCTIVE SU8 TIDAL AIID INTERTIDAL SAMPLES AND GENERAL- - COLLECT 1000S SY STATIOtt, 8. THE NUMBER OF TAMA IN DESTRUCTIVE Coll _ECTICIIS A800 C. INE 80UNSER OF TAXA PRESEsti tM CENERAL COLLECT IONS IN MAY, AUGUST A800 910VEMBER. SEABROOK EltVIR000 MENTAL STU0lES, 1985. A. 300MBER OF 0918000 TAXA STAil000S PRESENI IN 1985 a fDEPTH) SUSIIDAL INTERYIDAL ULutMAL TIDEPOOL TOTAL 17 35 31 19 IMLW SMLW IMLW 500LW # PHYttM (4.6) (6.1) (9.4) (12.2) MLW MSL MLW MSL MLW MSL- MLW MSL- TAXA $ ; Chlorophyta 4 5' 5 4 11 5 7 2 4 to 5 6 15 18 Phaeophyta 7 8 5 6 11 10 12 4 8 9 4 8 24 28 Rtedophyta 26 29 22 25 21 11 26 8 16 11- 15 13 46 54
- 8. 90 UMBER OF TAXA IN DESTRUCTIVE COLLECTIOttS TOTAL 4 w
I te PtfYLUM MAY AUC NOV TAXA % Seebtida l . Chlorophyta 4 4 4 5 16 Phaeophyta 1 2 2 3 , 10 R":f:fc;ta 18 19 19 23 74 Intertidal - Chlorophyta 3 7 3 7 20 Phaeophyta 0 7 1 7 20 Rt:f:,N-ta a 15 20 16 21 60 t, TOTALS Stehtidal 23 25 .25 31 100 Intertidal 18 34 20 35 100 l , - . = , ~ _ _ >,W j[ s n % 9 1 0 3 2 2 4 9 8 0 0 0 0 io. t) 1 2 6 1 1 cd ee ld l u ol L ccx AFA 4 S 0 2 2 l e TOX 8 9 5 o O A 2 1 I 3 4 6 T T oe pr e ew d ie ta g V 7 6 2 0 9 3 5 2 dl O 2 1 2 3 4 na a S N N e O Ls I , So T s Mt C r s E e nu ir L C 6 8 3 9 4 6 7 9 3 4 t e c L U 2 1 2 ) O A m t( d C n e n es u L i sn n A eo i R e ri t E r pt n N Y 5 5 1 2 2 4 1 8 a a A 2 2 3 4 al o E 1 1 s xu C C M t ac ( N n tl I e a m dc 0-A e r an n X u 5 A a a s s i T t a a t a a l E y t t y t t a a dd L F h y y h y y l d e ie B O p h h p h h a i m cd A p p o p p d t cu T R o. o o l r o o i r h ul E o e d a o e d t e t fc X B l l a o d l a o b t p n I M a h h h i h h h u n e s ,i D U M d C P R t C P R S S I d pe N N U i r L L t e A l l r I P Y b t T l ee P . I I u n O A Kw A C P S I T a b _ . _ _ . . _ . . . -_ . . m.._ ._.. _ _ _ _ _ . ._ ____ . _ . . _ . , _ _ _ _ . _ , ..__._o_. _ . . . . . _ _ _ _ . . _ _ _ . . _ _ . _ . . . . . . _ _ . _ . . ._ . . - APPENDIX TABLE 5-7. MEAN MEDIAN AND RANCE OF PERCENT COVER OF MELP SPECIES FROM TRANSECT SluolES AT SU8 TIDAL STATIONS' OVER THREE SAMPLING PER1005. S[ABROOK ENVIRONMENTAL STUDIES, 1985. , . ~> PERCENT COVER APRIL JULY OCTOBER , STATION MEAN MEDIAN (RANCE) MEAN ME01AN (RANCE) MEAN MEDIAN (RANCE) , Ataria escutenga 17 0 0 (0) 0 0 -(0) 0 0 (0) 19 0 0 (0) 0 0 (0) 0 0 (0) 31 2.9 0 (0-50) 3.7 0 (0-25) 0.4 0 (0-5) 35 0 0 (0) 0 0 (0) 0 0 (0) Agarum cribrosum 17 0 0 (0) <0.1 0 (0-2) 0 0 (0) 19 33.8 20 (10-75) 29.6 20 (0-70) 28.3 25 (0-60) > 31 20.0 20 (0-50) 14.6 10 (0-50) 9.2 5 (0-25) f; 35 0 0 (0) 0 0 (0) 0 0 (0) Laminaria digigata 17 11.1 0 (0-80) 12.3 0 (0-80) 7.2 0 (0-80) 19 6.0 1 (0-25) 9.6 0 (0-60) 6.1 5 (0-25) 31 48.2 50 -(0-100) 60.8 60 (0-100) 49.3 40 (10-100) ' 35 10.1 0 (0-75) 14.3 5 (0-100) 10.5 0 (0-60) 4 i Laminaria saccharina 17 15.8 5 (0-90) 16.4 10 (0-75) 19.2 0 (0-100) 19 0.4 0 (0-15) 2.4 0 (0-15) 1.4 0 (0-15) - 31 5.4 0 (0-40) 11.1 10 (0-50) 9.1 0 (0-100) 35' 5.4 0 (0-50) 19.3 0 (0-100) 6.4 0 (0-40) - - -. 4 A-ll5 M E C .= n em. sm. am .m. asm an ,= a== a= aun m ,= .a= ( .s. a=. .m= asm w C C N C C X C a e @ C m m o >= o O w e w w - e w e e e a N e
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9 9 A M ( at t u % % L A 9 4 9 9 C I % 3 C l t, t. 9 9 4 4 == tm 9 9 M M M W l l r A-116 APPENDIX TABLE 5-9. A. MEAN PERCENT FREQUENCY OF DOMINANT "UNDERSTORY" ALGAE, B. TOTAL NUMBER OF STRONCYEOCENTROTUS DROEBACFIENSIS AND NUMBER PER SQUARE METER AND C. MEAN PERCENT COVER OF SUBSTRATE TYPE FROM TRANSECT SWDIES AT SUBTIDAL STATIONS DURING 1985. SEABROOK ENVIRONMENTAL STUDIES, 1985. A. MEAN PERCEhT FREQUENCY OF DOMINANT "UNDERSTORY" ALGAE APRIL JULY OCTOBER STATION
- FREQUENCY . FREQUENCY . FREQUENCY Chondrus crispus 17 81 95 67 19 0 7 18 31 39 35 19 35 73 76 63 Phyllophors sp. 17 6 4 30 19 31 22 15 31 27 25 . 34 35 5 3 0 Ptilots serrsts 17 5 1 2 19 51 52 35 31 10 19 16 35 2 3 0 a
B. TOTAL NUMBER OF S. DROEBACEIENSIS AND NUMBER PER SQUARE METER APRIL JULY OCTOBER 8 8 STATION TOTAL # #/m TOTAL # #/m TOTAL # #/m* Strongylocentrotus 17 167 4 1 <1 0 0 droebschiensis 19 0 0 2 <1 0 0 31 0 0 4 <1 26 <1 35 0 0 0 0 0 0 I i A-117 APPENDIX TABLE 5-9. (Continued) C. MEAN PERCENT COVER OF SUBSTRATE TYPE APRIL JULY OCTOBER STATION % COVER % COVER % COVER 17 100 99+ 99 Rock 19 95 99 93 31 67 73 97 35 89 81 89 Cobble 17 0 <1 1 19 0 1 7 31 19 24 3 35 11 10 11 Mixture 17 0 0 0 19 5 0 0 31 14 3 0 35 0 9 0 a n = 42 I l A-118 . 8 APPENDIX TABLE 5-10. PERCENT FREQUENCY AND PERCEhT COVER PER 0.25 m 0F A. PERENNIAL AND B. " EPHEMERAL" MACROALGAL SPECIES AND C. PRESENCE OF EPIPHYTES ON FUCOID ALGAE AT FIXED IhTERTIDAL NON-DESTRUCTIVE SITES. SEAR 00K ENVIRONMENTAL STUDIES,1985. "FUCOID" LEDGE " BARE" LEDGE A. DOMINANT (SITE B) (SITE C) PERENNIAL ALGAE APR JUL DEC APR JUL DEC STATION IMSL Ascophyllun nodosua %C* Fucus distichus ssp. edentatus %C - - 20 25 60 50 8 10 <1 Fucus vesiculosus' %C b 81 38 63 94 6 Fucus vesiculosus' %F 75 Chondrus crispus %F - S 1 Gigartina stellata %F 3 8 21 STATION SMSL Ascophyllun nodosua %C - 10 95 89 94 <1 <1 15 Fucus vesiculosus' %C 94 88 94 69 94 100 Fucus vesiculosus* %F - 1 Chondrus crispus %F - Gigartina stellata %F 8 4 8 I i r i: A-119 i i APPENDIX TABLE 5-10. (Continued) " EPHEMERAL" b (SITE B) (SITE C) B. MACROALGAE (All *.F) APR JUL DEC APR JUL DEC STATION 1MSL - - 1 1 9 B11 dingle minima 1 Elachista fucicola 1 Honostrona grevi))el 2 - - - 1 Palmaria palmata 1 - - Pflayella littoralis 1 1 Porphyra spp.d 9 17 - 2 1 Spongomorpha spinescens 5 l Ulva lactuca - 3 } 2 - -
- \ Urospora penicilliformis t .
j STATION SMSL Audoulnella purpurea - - 1 24 - Bangle atropurpurea Eccocarpus sillculosus 13 - 91 - Urospora penicilliformis l i s 1 1 ] l i i i A-120 APPENDIX TABLE 5-10. (Continued) C. EPIP}nTES PRESENT (SITE B) ON FUCOID ALGAE APR JUL DEC STATION 1MSL Elachista fucicola x x x Pilayella littoralis x Total % Frequency 16 24 2 STATION SMSL Elachista fucicola x x Polysiphonia lanosa x Total % Frequency 98 42 a%C = % Cover (estimated) b %F = % Frequency (counted); see Methods c%C of whole plants; %F of holdfast only d p, u,5,,,,,,,,,p, y,,,,,,,,,, I l l l l l l l A-121 - 9 APPENDIX TABLE 5-11. PERCENT FREQUENCY OF SELECTED I EERTIDAL FAUNA IN , THE FIXED 0.25 m 2 NON-DESTRUCTIVE SITES AT STATIONS IMSL AND 5MSL. SEAR 00K ENVIRONMEhTAL i STUDIES, 1985, 1 i PERCENT FREQUENCY "FUCOID" LEDGE " BARE" LEDGE (SITE B) (SITE C) APR JUL DEC APR JUL DEC STATION 1MSL j - 6 6 Acases testudinsils l - 64 59 2 Bs/snus sp. 19 1 ! - 13 Littorins sp. 6 l LittorJns littores - - 6 6 Littorins obtusses - 19 88 63 Littorins saxatills 59 35 47 20 40 - l Mytilidae Nucells lapillus 13 100 13 h l ! STATION SMSL ! 6 6 6 Acases testudinalis 29 19 7 97 71 65 Bs/snus sp. 19 - 13 100 Littorina littores 25 50 - 19 \ Littorina obtusses 50 75 100 } 1 Littorins saxatills - - - 9 $ Mytilidae 5 -
- Nucella lapillus - 63 -
} l 1 } I 4 l r l A-122 APPENDIX TABLE 5-12. FREQUENCY OF FUCOID ALGAE AT WO U FI. D TRANSECT SITES IN THE MEAN SEA LEVEL ZONE. SEAR 00K ENVIRONMENTAL STUDIES, 1985. X PERCENT FREQUENCY" APR JUL DEC ALL E S.D. 5 S.D. E S.D. I S.D. STATION IMSL 33 35 0 37 24 Ascophyllun nodosue 42 t3 23 Tucus vesiculosus 47 23 62 28 65 29 58 210 Tucus distichus ssp. 3 2 12 23 6 25 edentstus 23 23 t 2 - - - - 0.6 22 Tucus sp. 23 STATION 3MSL Ascophyllua nodosue 32 23 48 23 37 't6 39 28 Tucus vesiculosus 38 23 35 25 37 t3 37 th 'n = 60 APPENDIX 6.0 MARINE MACROFAUNA NSPE = number of taxa CVSD = coefficient of variation S.D. = standard deviation P = present e i CES201 DH2D1 APPENDIX TABLE 6-1. MEAN DENSITY IPER METER SQUAREDI AND STANDARD DEVIATION OF SELECTED MACROFAUNAL SPECIES BY SAMPLING PERIOD AND STATION. SEABROOK ENVIRONMENTAL STUDIES, 1985. I 1MLW I SMLW l 17 1 35 l 19 I 31 l ALL l lMAY lACllEllA SPINOSA lMEAN ' l 1 5.3I 5.3 570.7H 64.01 107.6 l l l IS.D. I I I 9.21 9.2 : 413.OH 42.3l 257.4 l lAMPlTit0E RUPRICATA lHEAN H 10.7l l 10.71 16.0 1 48.0 1 10.78 16.0' I I 15.D. I 18.51 l 18.51 16.0 l 27.7 9.21 21.3 . l lANOM1A SP. IMEAN H 341.3l 1637.31 96.0l 501.3' 2352.0 1376.0: 1050.7l l l 1:S.D. H 64.71 903.01 84.7l 729.9' 1499.9 115.4l 1052.31 I lASTERilDAE I HEAN 58.7h 58.71 602.71 357.3 146.71 21.3 200.9H I l S.D. 40.3 101.61 201.3:1 157.0 117.91 9.2. 240.7 I I ICANCER BOREALIS lMEAN I 16.0 I l 5.3 l 3.6,}}