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Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Metabolic Rate | 85 | measured during the day over temperature range -10 to 45 C | cm^3 O2/g BW/hr | Not Reported | Both Adults and Juveniles | 5 cormorants | Exposure Factor Datasets | |
Metabolic Rate | 74 | measured at night over temperature range -10 to 45 C | cm^3 O2/g BW/hr | Not Reported | Both Adults and Juveniles | 5 cormorants | Exposure Factor Datasets | |
Metabolic Rate | minimal metabolic rate measured over a range of incident radiation (0-700 watts/m^2) | 85-95 | cm^3 O2/g BW/hr | Not Reported | Both Adults and Juveniles | 5 cormorants | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Growth Rate | 0.120 | rate of growth from hatch to fledge | 0.017 SD | Not Reported | Juvenile | Iles de la Madeleine Archipelago, Gulf of St. Lawrence | 33 chicks | Exposure Factor Datasets | ||
Body Weight - Mean | 34.7 | 2.96 SD | g | Not Reported | Hatchling | Iles de la Madeleine Archipelago, Gulf of St. Lawrence | 33 chicks | Exposure Factor Datasets | ||
Body Weight - Mean | 1900.5 | mean asymptotic weight of fledglings | 189.8 SD | g | Not Reported | Fledgling | Iles de la Madeleine Archipelago, Gulf of St. Lawrence | 33 chicks | Exposure Factor Datasets | |
Food Ingestion Rate | 4.30 | mean frequency of daily feeding of first hatched chick of a brood | 1.90 SD | feedings/d | Not Reported | Juvenile | Iles de la Madeleine Archipelago, Gulf of St. Lawrence | 64 observations | Exposure Factor Datasets | |
Food Ingestion Rate | mean meal weight of chicks aged 5-37 days | 10-125 | g | Not Reported | Juvenile | Iles de la Madeleine Archipelago, Gulf of St. Lawrence | 2 chicks | Exposure Factor Datasets | ||
Survival/ Mortality | 12/46 | number died/number hatched | Not Reported | Juvenile | Iles de la Madeleine Archipelago, Gulf of St. Lawrence | 14 nests | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Foraging Distance | 15.7 | mean distance travelled from night roost to foraging site | 2.0 SE | 3.5-61.8 | km | Both Male and Female | Adult | Mississippi River Delta | 33 birds | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|
Longevity | 17-08 | from USFWS Bird Banding Laboratory data | yr-mo | Not Reported | Adult | 4174 band recoveries | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Time of Nesting | April-June | period during which nest initiations were observed | Both Male and Female | Adult | San Francisco Bay estuary | 296-424 nests/year | Exposure Factor Datasets |
Fledging or Weaning Rate | 0.98 +/- 0.07 to 1.78 +/- 0.06 | mean number of chicks fledged/nest (over 3 years) | Both Male and Female | Fledgling | San Francisco Bay estuary | 296-424 nests/year | Exposure Factor Datasets |
Clutch or Litter Size | 3.1+/- 0.1 to 3.2+/- 0.1 | mean number of eggs/nest (over 3 years) | Female | Adult | San Francisco Bay estuary | 263-312 nests/year | Exposure Factor Datasets |
Hatching Success | 76% | proportion of nests in which at least one egg hatched | Both Male and Female | Hatchling | San Francisco Bay estuary | 1056 nests | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | range in mean clutches in ground nests (across 4 years) | 2.82-3.62 | Female | Adult | Lake Ontario (43 deg 53'N, 76 deg 24'W) | 34-127 nests/colony | Exposure Factor Datasets | |
Fledging or Weaning Rate | 2.14 | mean number of young produced/active nest (across 10 yrs) | Both Male and Female | Fledgling | Lake Ontario (43 deg 53'N, 76 deg 24'W) | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Dietary Composition | herring (25%), sculpin (92%), flounder (8%), anemones (8%), snails (17%), mussels (33%), amphipods (25%), isopods (17%), benthic shrimp (25%), crabs (25%), bryozoans (58%), algae (50%) | frequency of occurrence of food items in stomach contents | Not Reported | Both Adults and Juveniles | Quoddy Region, New Brunswick | 12 stomachs | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Growth Rate | 0.208 | K; index of rate at which asymptotic weight is being gained | Not Reported | Nestling | Duck Island, Isle of Shoals | 1-52/sample day | Exposure Factor Datasets | |
Body Weight - Mean | 1900 | asymptotic weight of nestlings | g | Not Reported | Nestling | Duck Island, Isle of Shoals | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Dietary Composition | sculpin, rock gunnel, blueback herring, alewife, wrymouth, sand shrimp, cunner, American eel, rock crab, N. Caridean shrimp, sand shrimp, white perch, yellow perch, rainbow smelt, N. lobster, Atlantic tomcod | primary dietary items from nestling regurgitant samples | Not Reported | Nestling | Penobscot Bay | 673 samples | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Duration of Incubation or Gestation | 28 | average incubation | 26-30 | d | Not Reported | Hatchling | Utah Lake, Utah County | 16 eggs | Exposure Factor Datasets |
Clutches or Litters per year | 1-2 | clutches/yr | Female | Adult | Utah Lake, Utah County | 11 nests | Exposure Factor Datasets | ||
Clutch or Litter Size | 3.8 | 2-6 | eggs/nest | Female | Adult | Utah Lake, Utah County | Not Reported | Exposure Factor Datasets | |
Body Weight - Mean | 36 | g | Not Reported | Hatchling | Utah Lake, Utah County | 16 birds | Exposure Factor Datasets | ||
Body Weight - Mean | 1543 | g | Not Reported | Juvenile | Utah Lake, Utah County | 13 birds | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 2498.1 | body weight | 16.0 SE | 2000-3000 | g | Male | Adult | 160 | Exposure Factor Datasets |
Body Weight - Mean | 2162.2 | body weight | 29.8 SE | 1650-2600 | g | Female | Adult | 41 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | gunnels (5%), sculpins (1%), sand lance (44%), capelin (34%), flatfishes (11%), clupeids (4%), other (1%) | proportion of prey species in diet by percent volume | % | Not Reported | Both Adults and Juveniles | St. Lawrence Estuary and Gulf | 187 | Exposure Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), POLYCHLORINATED BIPHENYLS | 10.4 ppm DDE, 8 ppm est. PCBs, <0.1 ppm DDD, 0.2 ppm DDT | residues measured in live and dead eggs | Female | Adult | 11 colonies | <0.1-0.08 ppm DDE, <0.01-0.5 ppm est. PCBs, <0.01-0.04 ppm DDD, <0.01-0.01 ppm DDT in dietary fish | TOX-EXP IND - accumulation | parent diet | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), POLYCHLORINATED BIPHENYLS | negative correlation | correlation of egg concentration of DDE and est. PCB's and shell thickness and weight | Female | Adult | 35 eggs | <0.1-0.08 ppm DDE, <0.01-0.5 ppm est. PCBs, <0.01-0.04 ppm DDD, <0.01-0.01 ppm DDT in dietary fish | TOX-REPRO - physiology | parent diet | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), POLYCHLORINATED BIPHENYLS | decreased 8.3% compared with pre-1940 reference measurements | eggshell thickness | Female | Adult | 35 eggs | <0.1-0.08 ppm DDE, <0.01-0.5 ppm est. PCBs, <0.01-0.04 ppm DDD, <0.01-0.01 ppm DDT in dietary fish | TOX-REPRO - physiology | parent diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-), POLYCHLORINATED BIPHENYLS | no effect | shell thickness | Female | Adult | OR coast | 10 eggs from 10 nests | 1.6 ppm wet wt DDE, 1.3 ppm wet wt PCBs | TOX-REPRO - physiology | NR | dietary | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | increase | incidence of deformities in live embryos relative to 2,3,7,8-TCDD equivalents of PCBs, PCDFs, and PCDDs | Not Reported | Embryo | Lakes Michigan, Huron, Superior, North Channel | Not Reported | 3.6-7.3 ug/g wet wt | TOX-REPRO - development | 10-12 days and 21-24 days (embryo ages) | in ovo | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | decreased at 276, 672, 1606 ng/kg | Mean yolk weight of eggs | Female | Both Adults and Juveniles | Saskatchewan, British Columbia, Lake Ontario | 5-12 eggs/dose | 131, 250, 276, 672, 1606 ng/kg Toxic Equivalency Factors measured in eggs | TOX-REPRO - physiology | NR | in ovo | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS | increased at 1606 ng/kg | total hepatic cytochrome P450 content | Not Reported | Hatchling | Saskatchewan, British Columbia, Lake Ontario | 5-12 eggs/dose | 131, 250, 276, 672, 1606 ng/kg Toxic Equivalency Factors measured in eggs | TOX-EXP IND - biomarkers | NR | in ovo | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS | increased at 1606 ng/kg | hepatic EROD activity | Not Reported | Hatchling | Saskatchewan, British Columbia, Lake Ontario | 5-12 eggs/dose | 131, 250, 276, 672, 1606 ng/kg Toxic Equivalency Factors measured in eggs | TOX-EXP IND - biomarkers | NR | in ovo | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS | positive regression | linear regression of hepatic EROD activity or cyt P450 content on Toxic Equivalency Factors | Not Reported | Hatchling | Saskatchewan, British Columbia, Lake Ontario | 5-12 eggs/dose | 131, 250, 276, 672, 1606 ng/kg Toxic Equivalency Factors measured in eggs | TOX-EXP IND - biomarkers | NR | in ovo | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS | negative regression | linear regression of wing length on Toxic Equivalency Factors | Not Reported | Hatchling | Saskatchewan, British Columbia, Lake Ontario | 5-12 eggs/dose | 131, 250, 276, 672, 1606 ng/kg Toxic Equivalency Factors measured in eggs | TOX-REPRO - development | NR | in ovo | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | observed at 3, 10, 100 ug/kg | mortality | Not Reported | Hatchling | 6-10 eggs/dose | 0, 1, 3, 10, 100 ug/kg | TOX-REPRO - reproductive success | incubation day 22 to hatch | egg injection | Toxicity Factor Datasets |