Double-crested Cormorant (Phalacrocorax auritus)
Double-crested Cormorant (Phalacrocorax auritus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Striped mullet: 25.5, gulf menhaden: 17.6, hardhead catfish: 11.8, Sciaendiae: 15.7, unidentifiable fish: 5.9 | Frequency | % | Not Reported | 51 | Lavaca bay | Exposure Factor Datasets | USA |
Dietary Composition | Striped mullet: 28.5, hardhead catfish: 2.5, gulf toadfish: 46.4 Sciaendiae: 0, unidentifiable fish: 3.6 | Frequency | % | Not Reported | 28 | Laguna Madre | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Population Density | See citation Table 1 | Adults/sq km | Adults/sq km | NR | Adult | North Channel, Lake Huron | Exposure Factor Datasets | CANADA |
Population Density | See citation Table 1 | Adults/sq km | Adults/sq km | NR | Adult | Georgian Bay, Lake Huron | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|
Survival/ Mortality | See citation Figure 4 | Second-year birds | Adult | Great Lakes region | Exposure Factor Datasets | USA |
Survival/ Mortality | See citation Figure 5 | Hatch-year birds | Juvenile | Great Lakes region | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Survival/ Mortality | 0.696 | Survival, modeled average (Adult, at least 2 y) | Percent | Adult | Lake Michigan | Exposure Factor Datasets | USA |
Survival/ Mortality | 0.305 | Survival, modeled average (first year) | Percent | Juvenile | Lake Michigan | Exposure Factor Datasets | USA |
Survival/ Mortality | 0.774 | Survival, modeled average (Second/third year) | Percent | Juvenile | Lake Michigan | Exposure Factor Datasets | USA |
Survival/ Mortality | 0.633 | Survival, modeled average (Adult, at least 4 y) | Percent | Adult | Lake Michigan | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Pre-goby: 11.9, Transition 12.7, Post-goby: 16.7 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 923, Transition 1631, Post-goby: 2035 | McNair Island | Exposure Factor Datasets | CANADA |
Dietary Composition | Pre-goby: 13.2, Transition 12.8, Post-goby: 17.0 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 1187, Transition 518, Post-goby: 1404 | Strachan Island | Exposure Factor Datasets | CANADA |
Dietary Composition | See citation Table 4 | Percent species by number by different periods | % | NR | Not Reported | See citation | Three sites along St. Lawrence River | Exposure Factor Datasets | CANADA |
Dietary Composition | Pre-goby: 14.4, Transition 14.3, Post-goby: 20.1 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Adult | Pre-goby: 3100, Transition 2206, Post-goby: 1028 | Griswold Island | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Location | Type | Countries |
---|---|---|---|---|---|
Population Density | See citation | Breeding pairs/location | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | 2006: >93% alewife, 2007: 86.5%; balance made up of round goby, rainbow smelt, pumpkinseed | Chick diet | % by mass | B | Adult | Tommy Thompson Park, Lake Ontario | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 2008: 1.79 ± 0.03, 2009: 1.96 ± 0.02 | Brood size | Number of hatchlings | NR | Hatchling | 2008: 493 nests, 2009: 559 nests | Northeast SD | Exposure Factor Datasets | USA |
Time of Hatching or Parturition | 2008: June 4, 2009: May 29 | Earliest hatch date | Hatchling | 2008: 493 nests, 2009: 559 nests | Northeast SD | Exposure Factor Datasets | USA | ||
Hatching Success | 2008: 49.5% [45.9-52.9 (95% CI)], 2009: 59.4% [55.8-63.1 (95% CI)] | Fledge success | Hatchling | 2008: 28, 2009: 25 | Northeast SD | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Pre-goby: 10.15, Transition 10.25, Post-goby: 14.81 | Number of fish eaten per pellet by different periods | Numerb of fish | NR | Not Reported | Pre-goby: 17,681, Transition 1800, Post-goby: 4662 | Lilttle Galloo Island, Lake Ontario | Exposure Factor Datasets | CANADA |
Dietary Composition | See citation Table 4 | Percent species by number by different periods | % | NR | Not Reported | Pre-goby: 17,681, Transition 1800, Post-goby: 4662 | Lilttle Galloo Island, Lake Ontario | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|
Home Range | 17490 sq km | sq km | B | Adult | 37 | Mississipi Alluvial Valley (AR, MS, LA) & Upper Coastal Plain (AL, MS) | Exposure Factor Datasets | Over-wintering populations | USA | 1986 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Life Cycle Stage | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|
Population Density | See citation Figure 2 | Active nests/11,000 ha | Adult | Estero Bay Aquatic Preserve | Exposure Factor Datasets | Breeding | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Condition | Countries |
---|---|---|---|---|---|---|---|
Population Density | 1990: 3985, 1994: 9854, 1997: 8217, 2000: 12821, 2003: 11470 | Number of nests | Number of nests | Georgian Bay, Lake Huron | Exposure Factor Datasets | Breeding | CANADA |
Population Density | 1990: 4310, 1994: 7281, 1997: 8494, 2000: 12441, 2003: 11527 | Number of nests | Number of nests | North Channel, Lake Huron | Exposure Factor Datasets | Breeding | CANADA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Herring, shad: 0.6, Peamouth/Pikeminnow: 24.0, Sucker: 5.8, Smelt: 0.3, Salmonid: 45.5, Stickleback: 5.0, Sculpin: 8.0, Surfperch: 0.3, Flounder: 8.5, Other: 1.8 | Percent by mass from adult foregut and chick regurgitation samples | % | NR | Both Adults and Juveniles | 206 | Rice Island/Channel Markers | Exposure Factor Datasets | USA |
Dietary Composition | Herring, shad: 27.8, Peamouth/Pikeminnow: 0.7, Sucker: 4.7, Smelt: 7.6, Salmonid: 15.9, Stickleback: 2.1, Sculpin: 9.2, Surfperch: 7.3, Flounder: Pacific sand lance: 1.8, Flounder: 9.8 Other: 1.3 | Percent by mass from adult foregut and chick regurgitation samples | % | NR | Both Adults and Juveniles | 128 | East Sand Island | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | Cyprinid, Lepomis spp., rainbow smelt, rock bass, white perch, yellow perch | Percent by number before alewife eastablishment | % | Exposure Factor Datasets | USA | |
Dietary Composition | Alewife ,cyprinid, Lepomis spp., rainbow smelt, rock bass, white perch, yellow perch | Percent by number after alewife eastablishment | % | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Location | Type | Countries |
---|---|---|---|---|---|---|
Dietary Composition | See citation | Percent by number | % | Lake Oneida | Exposure Factor Datasets | USA |
Dietary Composition | See citation | Percent by number | % | Lake Oneida | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Type | Age-Specific | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation | Percent composition and biomass | B | Adult | Exposure Factor Datasets | Leech Lake | USA | |
Dietary Composition | See citation | Percent composition and biomass | B | Chick | Exposure Factor Datasets | Leech Lake | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | observed at 3, 10, 100 ug/kg | mortality | Not Reported | Hatchling | 6-10 eggs/dose | Toxicity Factor Datasets | Laboratory | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | body and organ weights | Not Reported | Hatchling | 6-10 eggs/dose | Toxicity Factor Datasets | Laboratory | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | observed at 3, 10, 100 ug/kg | edema | Not Reported | Hatchling | 6-10 eggs/dose | Toxicity Factor Datasets | Laboratory | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | increased at 10, 100 ug/kg | hepatic microsomal cytP450 content | Not Reported | Hatchling | 6-10 eggs/dose | Toxicity Factor Datasets | Laboratory | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | increased at 3, 10, 100 ug/kg | hepatic microsomal EROD activity | Not Reported | Hatchling | 6-10 eggs/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | increased at 400, 800 ug/kg egg | incidence of embryo mortality versus controls | Not Reported | Embryo | 15-60/group | Toxicity Factor Datasets | Laboratory | |
POLYCHLORINATED BIPHENYLS | increased @ 5 ug/kg | weight of heart, liver and spleen versus controls | Not Reported | Embryo | 15-60/group | Toxicity Factor Datasets | Laboratory | |
POLYCHLORINATED BIPHENYLS | increased at 5 ug/kg egg | weights of heart, liver and spleen versus controls | Not Reported | Hatchling | 8-29/group | Toxicity Factor Datasets | Laboratory | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | increased at 4.0 ug/kg egg | incidence of embryo mortality versus controls | Not Reported | Hatchling | 58-60/group | Toxicity Factor Datasets | Laboratory | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | weight of brain, heart, liver and spleen versus controls | Not Reported | Hatchling | Not Reported | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 2.4% | mean hatching success in contaminated colonies | Not Reported | Embryo | 331 eggs | Lake Huron | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 0.06-0.11 (1972); 0.3 (1973) | fledging success (young/nest) in contaminated colonies | Not Reported | Embryo | 42 (1973)-66 (1972) nests | Lake Huron | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 95% | percent of eggs lost or broken before hatching in contaminated colonies | Not Reported | Embryo | 235 eggs | Lake Huron | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, HEXACHLOROBENZENE, MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 23.9% thinner | eggshell thickness compared with pre-1947 eggshells in contaminated colonies | Not Reported | Embryo | 18 eggs | Lake Huron | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | review | incidence of embryonic deformities, depressed growth | Embryo, Juvenile | Not Reported | Toxicity Factor Datasets | |
POLYCHLORINATED BIPHENYLS, POLYCHLORINATED DIBENZO-P-DIOXINS | review | enzyme induction | Not Reported | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | decreased compared with reference | hatching success (# hatched/# eggs) | Both Male and Female | Hatchling | 466 and 953 nests (2 yrs) | Spider Is., Lake Michigan | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS | decreased compared with reference | clutch size | Female | Adult | 466 and 953 nests (2 yrs) | Spider Is., Lake Michigan | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS | increased compared with reference | proportion of nestlings with bill defects | Both Male and Female | Hatchling | 1,511 and 2,700 chicks (2 yrs) | Spider Is., Lake Michigan | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 250 | Ratio of carcass concentration (4.6 ppm wet wt) to dietary concentration of PCBs | Not Reported | Adult | 10 carcasses | Lake Pointsett, Dry Lake | Toxicity Factor Datasets | |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 5.7 ppm wet wt PCBs | concentration in eggs | Female | Adult | 5 eggs | Lake Pointsett, Dry Lake | Toxicity Factor Datasets | |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 0.24 ppm wet wt PCBs | concentration in carcass | Not Reported | Juvenile | 5 birds | Lake Pointsett, Dry Lake | Toxicity Factor Datasets | 2-4 wks old |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 14 | Ratio of concentration in carcass (0.64 ppm wet wt mercury) to dietary concentration (fish) | Not Reported | Adult | 10 carcasses | Lake Pointsett, Dry Lake | Toxicity Factor Datasets | |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 0.29 ppm wet wt mercury | mean concentration in eggs | Female | Adult | 5 eggs | Lake Pointsett, Dry Lake | Toxicity Factor Datasets | |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 0.28 ppm wet wt mercury | concentration in liver | Not Reported | Nestling | 5 birds | Lake Pointsett, Dry Lake | Toxicity Factor Datasets | 2-4 wks old |
MERCURY (elemental), POLYCHLORINATED BIPHENYLS | 7.98 ppm wet wt mercury | concentration in liver | Both Male and Female | Adult | 5 birds | Lake Pointsett, Dry Lake | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
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 | Toxicity Factor Datasets | CANADA | |
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 | Toxicity Factor Datasets | CANADA | |
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 | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | increased @ 5.4, 10.7, 11.7 ug/kg egg | mortality in treated embryos versus controls | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | increased @ 175, 349, 698 ug/kg egg | mortality in treated embryos versus controls | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 4.0 ug/kg egg (0.8-7.2) | LD50 (95% confidence limits) | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | 177 ug/kg egg (77-264) | LD50 (95% confidence limits) | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | no effect | incidence of developmental abnormalities, edema, body weight effects, spleen or gonad histopathologic anomalies, or sex ratio in treated embryos versus controls | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | incidence of developmental abnormalities, edema, body weight effects, spleen or gonad histopathologic anomalies, or sex ratio in treated embryos versus controls | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | increased @ all doses | hepatic EROD activity in treated embryos versus controls | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | increased @ all doses | hepatic EROD activity in treated embryos versus controls | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | decreased @ 349 ug/kg egg | spleen weights in treated embryos versus controls | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | decreased @ 5.4, 11.7 ug/kg egg | spleen weights in treated embryos versus controls | Not Reported | Embryo | 83-86 eggs/treatment | Lake Winnipegosis, Manitoba | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 31.3 | mean biomagnification factor for eggs from forage fish | Female | Adult | 12 eggs/site x 5 sites | Toxicity Factor Datasets | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 162.4 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained (from eggs to largest chicks) | Not Reported | Nestling | 20 chicks | Green Bay, Lake Michigan | Toxicity Factor Datasets |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 100.4 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained from egg to largest chick stage | Not Reported | Nestling | 20 chicks | Beaver Islands, Lake Michigan | Toxicity Factor Datasets |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 37.6 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained (from eggs to largest chicks) | Not Reported | Nestling | 20 chicks | Thunder Bay, Lake Huron | Toxicity Factor Datasets |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 28.3 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained (from eggs to largest chicks) | Not Reported | Nestling | 20 chicks | North Channel, Lake Huron | Toxicity Factor Datasets |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | 47.5 pg/g bw gained (wet wt) | pg TCDD equivalents accumulated per gram of body weight gained (from eggs to largest chicks) | Not Reported | Nestling | 20 chicks | St. Martin's Shoal, Lake Huron | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-), POLYCHLORINATED BIPHENYLS | no effect | shell thickness | Female | Adult | 10 eggs from 10 nests | OR coast | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | 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 | Not Reported | Lakes Michigan, Huron, Superior, North Channel | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | decreased at 276, 672, 1606 ng/kg | Mean yolk weight of eggs | Female | Both Adults and Juveniles | 5-12 eggs/dose | Saskatchewan, British Columbia, Lake Ontario | Toxicity Factor Datasets | CANADA |
POLYCHLORINATED BIPHENYLS | increased at 1606 ng/kg | total hepatic cytochrome P450 content | Not Reported | Hatchling | 5-12 eggs/dose | Saskatchewan, British Columbia, Lake Ontario | Toxicity Factor Datasets | CANADA |
POLYCHLORINATED BIPHENYLS | increased at 1606 ng/kg | hepatic EROD activity | Not Reported | Hatchling | 5-12 eggs/dose | Saskatchewan, British Columbia, Lake Ontario | Toxicity Factor Datasets | CANADA |
POLYCHLORINATED BIPHENYLS | positive regression | linear regression of hepatic EROD activity or cyt P450 content on Toxic Equivalency Factors | Not Reported | Hatchling | 5-12 eggs/dose | Saskatchewan, British Columbia, Lake Ontario | Toxicity Factor Datasets | CANADA |
POLYCHLORINATED BIPHENYLS | negative regression | linear regression of wing length on Toxic Equivalency Factors | Not Reported | Hatchling | 5-12 eggs/dose | Saskatchewan, British Columbia, Lake Ontario | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
CADMIUM (elemental), MERCURY (elemental) | no correlation | correlation of mean metallothionein concentration (13.2-24.4 ug/g tissue) and metal concentrations in kidneys | Not Reported | Both Adults and Juveniles | 24 birds | Heron Is., Manawagonish Is., Ile aux pommes | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | positive correlation | correlation of embryo mortality with TCDD equivalents in eggs | Not Reported | Embryo | 11 colonies @ 25-50 nests/colony | Great Lakes | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
POLYCHLORINATED DIBENZO-P-DIOXINS | increased | P-450-dependent arachidonic acid metabolism by liver microsomes | Not Reported | Embryo | 3 | Toxicity Factor Datasets | 1 day | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), POLYCHLORINATED BIPHENYLS | 28.8% decrease | mean thickness of eggshells collected in 1969 compared with pre-1946 museum specimens | Female | Adult | 17 eggs | Anacapa Island | Toxicity Factor Datasets |
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), POLYCHLORINATED BIPHENYLS | 38.3% decrease | mean thickness of eggshells collected in 1969 compared with pre-1946 museum specimens | Female | Adult | 23 eggs | Los Coronados Island | Toxicity Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Food Ingestion Rate | mean meal weight of chicks aged 5-37 days | g | Not Reported | Juvenile | 2 chicks | Iles de la Madeleine Archipelago, Gulf of St. Lawrence | Exposure Factor Datasets | CANADA | |
Survival/ Mortality | 12/46 | number died/number hatched | Not Reported | Juvenile | 14 nests | Iles de la Madeleine Archipelago, Gulf of St. Lawrence | Exposure Factor Datasets | CANADA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 3.8 | eggs/nest | Female | Adult | Not Reported | Utah Lake, Utah County | Exposure Factor Datasets | |
Body Weight - Mean | 36 | g | Not Reported | Hatchling | 16 birds | Utah Lake, Utah County | Exposure Factor Datasets | 1 d |
Body Weight - Mean | 1543 | g | Not Reported | Juvenile | 13 birds | Utah Lake, Utah County | Exposure Factor Datasets | 23 d |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | cunner (59.7%), winter flounder (15.5%), sculpin (2.4%), rock eel (0.3%), American eel (6.6%), pollack (9.8%), mummichog (5.8%) | frequency by weight of fish regurgitated by adult cormorants | Both Male and Female | Adult | 17 samples | Duck Island, Isles of Shoals (43 deg. N, 70 deg. 35' W) | Exposure Factor Datasets | |
Food Ingestion Rate | see figure | estimated average energy intake during the nestling period (to 50 days of age) | kcal/bird/day | Both Male and Female | Nestling | Not Reported | Duck Island, Isles of Shoals (43 deg. N, 70 deg. 35' W) | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
---|---|---|---|---|---|---|---|---|---|
Foraging Distance | 15.7 | mean distance travelled from night roost to foraging site | km | Both Male and Female | Adult | 33 birds | Mississippi River Delta | Exposure Factor Datasets | 2.0 SE |
Mallard duck (Anas platyrhynchos), Double-crested Cormorant (Phalacrocorax auritus)
Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | review | incidence of reproductive effects | Both Adults and Juveniles, Embryo | Not Reported | Toxicity Factor Datasets | |
POLYCHLORINATED BIPHENYLS | review | incidence of reproductive effects | Both Adults and Juveniles, Embryo | Not Reported | Toxicity Factor Datasets |