PCB
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Lab |
---|---|---|---|---|---|---|---|---|---|---|
PCB | 0.64 | Any embryonic abnormality | NR | Embryo | NR | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Longer | Tarsus: asymptotic size | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Antebrachrium: growth rate | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | No effect | Flight | F | Adult | 50 pairs | Avian Science and Conservation Centre of McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Heterophil/lymphocyte | F | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 1.3 | Egg concentration | Embryo | 22 | South San Francisco Bay marshes | Toxicity Factor Datasets | USA | Laboratory | ||
PCB | 1982-1986: 0.64, 1990-1998: 0.11, 2004-2006: 0.32 mg/kg | Plasma concentration | NR | Adult | 1982-1986: 70, 1990-1998: 97, 2004-2006: 25 | Rankin Inlet, Nunavut | Toxicity Factor Datasets | CANADA | ||
PCB | Alaska: 390, California: 645 ng/g lw | Blood concentration | F | Adult | Alaska: 38, California: 18 | Alaksa: 3 sites in eastern AK, California: 3 sites between Santa Cruz and Monterey | Toxicity Factor Datasets | USA | ||
PCB | See citation Figure 2 | Egg concentration; congener pattern | B | Embryo | 4 | Lower Laguna Madre | Toxicity Factor Datasets | USA | ||
PCB | 0.29 | Shortened mandible | NR | Embryo | NR | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Tarsus: growth rate | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Earlier | Antebrachrium: maximal growth | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | No effect | Copulation frequency | B | Adult | 50 pairs | Avian Science and Conservation Centre of McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Plasma T3 | M | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 5120 ng/g lw ± 1910 | Egg concentration | Embryo | 4 | Marshes around San Francisco Bay | Toxicity Factor Datasets | USA | Laboratory | ||
PCB | non-ortho-PCBs: Reference site: 147.39 ± 22.22, study site: 519.47 ± 194.89 pg/g ww | Egg concentration | Embryo | 7 | Toxicity Factor Datasets | SPAIN | ||||
PCB | Alaska: 705, California: 650 ng/g lw | Blood concentration | M | Adult | Alaska: 16, California: 11 | Alaksa: 3 sites in eastern AK, California: 3 sites between Santa Cruz and Monterey | Toxicity Factor Datasets | USA | ||
PCB | 0.29 | Shortened limbs | NR | Embryo | NR | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Earlier | Tarsus: maximal growth | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Tarsus: asymptotic size | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | No effect | Sex hormones | M | Adult | 50 pairs | Avian Science and Conservation Centre of McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Plasma T4 | M | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 0.43 µg/g ww ± 0.089 | Liver concentration | NR | Hatchling | 4 | Hamilton Harbour, Western Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory | |
PCB | ortho-PCBs: Reference site: 242.07 ± 43.32, study site: 1492.51 ± 1090.08 ng/g ww | Egg concentration | Embryo | 7 | Toxicity Factor Datasets | SPAIN | ||||
PCB | See citation; captive vs. free ranging | Monocyte phagocytosis | B | Both Adults and Juveniles | See citation | California coast | Toxicity Factor Datasets | Monterey | USA | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | Decreased | Survival to day 24 | Embryo | 60 | Toxicity Factor Datasets | Lab | Laboratory |
Snowy Egret (Egretta thula)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
PCB | 2.49 µg/g ww | Egg concentration | Not Reported | Embryo | 5 | Mallard Slough | Toxicity Factor Datasets | USA |
PCB | 1982: 3.32, 1989: 1.23, 1990: 5.38 µg/g ww | Egg concentration | Not Reported | Embryo | 1982: 10, 1989: 5, 1990: 5 | Bair Island | Toxicity Factor Datasets | USA |
PCB | 1989: 2.19, 1990: 0.792, 1991: 1.55 | Egg concentration | Not Reported | Embryo | 5 | W. Marin Island | Toxicity Factor Datasets | USA |
Pacific Green Turtle (Chelonia mydas)
Chemical | Endpoint Value | Endpoint Description | Sex | Sample Size | Location | Type |
---|---|---|---|---|---|---|
PCB | 2.71 ng/g ww | Fat concentration | Not Reported | 6 | Pelagic Pacific | Toxicity Factor Datasets |
PCB | Review | Fat concentration | Not Reported | Toxicity Factor Datasets |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1242 | 8.9% decrease @ 150 ppm | eggshell thickness, compared to control | Female | Adult | 12 pairs/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1242 | 105.0 (7.7 SE) mg Aroclor 1260/kg egg @ 150 ppm | PCB concentration in eggs (PCB resembled Aroclor 1260 profile most closely) | Female | Adult | 12 pairs/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1242 | no effect @ 150 ppm | weight and survival of offspring (exposed in ovo) fed control diet after hatching for 3 wks | Female | Adult | 12 pairs/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | no effect | food consumption rate (184 g/d) compared to control (173 g/d) | Female | Adult | 10/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, DDE (4,4'-) | no effect | food consumption rate (181 g/d) compared to control (173 g/d) | Female | Adult | 10/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | no effect | eggshell thickness | Female | Adult | 10 hens/dose; 8-9 eggs/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, DDE (4,4'-) | 19% decrease | eggshell thickness, compared to control | Female | Adult | 10 hens/dose; 8 eggs/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, DDE (4,4'-) | see citation | figure of # eggs/female/wk over time | Female | Adult | 10/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, DDE (4,4'-) | 344 (95% CL; 156-686) ppm DDE lipid basis and 346 (95%CL; 133-686) ppm PCB lipid basis @ 40 ppm DDE + 40 ppm PCB diet | mean DDE and PCB residue levels in eggs | Female | Adult | 13 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | decreased @ 20, 100, 250, 500 mg/kg bw | plasma triiodothyronine concentrations versus controls | Male | Adult | 6-12/dose | Toxicity Factor Datasets | 1-2 yr | Laboratory | |
AROCLOR 1254 | no effect | leukocyte counts, plasma biochemistry, corticosterone concentration versus controls | Male | Adult | 6-12/dose | Toxicity Factor Datasets | 1-2 yr | Laboratory | |
AROCLOR 1254 | increased @ 250, 500 mg/kg bw | lymphocyte proliferation to PHA versus controls | Male | Adult | 6-12/dose | Toxicity Factor Datasets | 1-2 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | no effect | reproductive success or nest attentiveness versus controls | Both Male and Female | Adult | 22 pairs | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | no effect | body and liver weights of parents and offspring versus controls | Both Male and Female | Both Adults and Juveniles | 22 pairs | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | 55-65 ppm | range of wet wt concentrations of Aroclor 1254 in adult carcasses | Both Male and Female | Adult | 22 pairs | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | 29.5(1.4) ppm | mean(SE) wet wt concentrations of Aroclor 1254 in carcasses of 3 week old ducklings | Not Reported | Juvenile | 10 | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | 23.3(1.0) ppm | mean(SE) wet wt concentrations of Aroclor 1254 in eggs | Not Reported | Embryo | 19 eggs | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | decreased @ 1000 mg/kg bw | post-dose eggshell thickness versus pre-dose thickness | Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory |
Mourning Dove (Zenaida macroura)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Lab |
---|---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | decreased at 40 ppm | courtship behavior score (intensity) | Both Male and Female | Adult | 8/group | Toxicity Factor Datasets | breeding | Laboratory | |
AROCLOR 1254 | decreased at 10, 40 ppm | number of pairs nesting | Both Male and Female | Adult | 8/group | Toxicity Factor Datasets | breeding | Laboratory | |
AROCLOR 1254 | delayed at 10 ppm | onset of nest initiation | Both Male and Female | Adult | 8/group | Toxicity Factor Datasets | breeding | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | no effect | metabolic rate at a range of ambient temperatures | Male | Adult | 4/group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | no effect | body weight | Male | Adult | 10/group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | decreased at 40 ppm | body temperature at a range of ambient temperatures | Male | Adult | 4/group | Toxicity Factor Datasets | Laboratory |
American Kestrel (Falco sparverius)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | decreased @ 250, 1000 ng/g bw | body and organ growth versus controls | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | increased @ 50,250,1000 ng/g bw | incidence and severity of lesions in liver, spleen, bursa, thyroid versus controls | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | increased | plasma enzyme activities indicative of hepatotoxicity versus controls | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | no effect | hematocrit and hemoglobin values versus controls | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | increased @ 50,250,1000 ng/g bw | hepatic monooxygenase activities versus controls | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | in ng/g, wet wt: 156 (@ 50 ng/g), 380 (@ 250 ng/g), 1098 (@1000 ng/g) | concentration in liver | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory | |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | positive correlation | relationship between hepatic PCB 126 concentrations and ratio of oxidized to reduced glutathione | Not Reported | Nestling | 9-11/group | Toxicity Factor Datasets | Day 1-Day 10 | Laboratory |
Chemical | Endpoint Value | Location | Type |
---|---|---|---|
POLYCHLORINATED BIPHENYLS | review | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1248 | 18.5 ug/g (5.1SD), PCBs; 0.10 ug/g (0.03 SD), dieldrin;1.02 ug/g (0.39 SD), DDE @ 3.0 ug/g | mean carcass concentrations, wet wt | Both Male and Female | Adult | 8 pairs/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | 21.5-22.6% decrease @ 33 ppm | sperm concentration | Male | Adult | 10/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254, PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL), PCB 77 (3,3',4,4'-TETRACHLOROBIPHENYL) | increased with PCB 77 | liver weight (as percent of body weight) versus controls | Female | Adult | 4/treatment group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
PCB 77 (3,3',4,4'-TETRACHLOROBIPHENYL) | reduced @ 100, 1000 ng/g | percent hatching success, percent pipped versus controls | Not Reported | Hatchling | 24-26/treatment group | Toxicity Factor Datasets | hatchling | Laboratory |
Double-crested Cormorant (Phalacrocorax auritus)
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 | Lab |
---|---|---|---|---|---|---|---|---|
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 |
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 |
---|---|---|---|---|---|---|---|
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 |
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 |
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 |
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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
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 |
California Sea Lion (Zalophus californianus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
DDT (Technical Grade Mixture), POLYCHLORINATED BIPHENYLS | increase | incidence of premature parturtion associated with elevated DDT and PCB residues, compared to full term parturient group | Female | Adult | 4-6/group | San Miguel Island | Toxicity Factor Datasets | 6 - 15 yrs |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-), POLYCHLORINATED BIPHENYLS | increase | incidence of premature parturition associated with elevated DDT and PCB levels, compared to full term parturient group | Female | Adult | 10/group | San Miguel Island | Toxicity Factor Datasets | 6 - 14 yrs |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
CADMIUM COMPOUNDS, DDT (Technical Grade Mixture), MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | increase | incidence of kidney histopathological lesions in "sick" or dead animals compared to "healthy" animals, consistent with diagnosis of leptospirosis | Male | Adult | 2-8/group | Toxicity Factor Datasets | 5 - 9 yr |
Peregrine Falcon (Falco peregrinus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-), POLYCHLORINATED BIPHENYLS | 11.4% | percent eggshell thinning compared to pre-DDT reference eggs | Female | Adult | 8 nests | Kola Peninsula | Toxicity Factor Datasets | RUSSIA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | review | concentrations in brain associated with mortality (various raptor species) | Not Reported | Not Reported | Not Reported | Toxicity Factor Datasets | Laboratory | |
POLYCHLORINATED BIPHENYLS | review | concentrations in eggs associated with reduced reproduction (various raptor species) | Not Reported | Adult | 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'-), HEPTACHLOR EPOXIDE, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | 12.1% | percent eggshell thinning (as indicated by Ratcliffe Index) compared to pre-1947 eggs | Not Reported | Embryo | 39 eggs | Mid-Atlantic coastal and urban breeding sites | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-), POLYCHLORINATED BIPHENYLS | 11% decrease | eggshell thickness compared to pre-1947 reference eggs | Female | Adult | 112 eggs | eastern U.S. coast | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-), MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | 2.4-25.0 (DDE); 0.5-10.6 (PCBs); 0.2-4.2 (Hg) | residues in eggs (ppm, wet wt) | Female | Adult | 5 eggs (from 5 nests) | Gulf of California | Toxicity Factor Datasets | MEXICO |
Western Grebe (Aechmophorus occidentalis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), POLYCHLORINATED BIPHENYLS | no effect | eggshell thickness compared with pre-1947 measurements | Not Reported | Embryo | 29 eggs | Tule Lake National Wildlife Refuge | Toxicity Factor Datasets |
Brown Pelican (Pelecanus occidentalis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
AROCLOR 1254, DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN | 0.896 ppm DDE, 0.256 ppm DDD, 0.166 ppm DDT, 0.208 dieldrin, 2.241 ppm PCB 1254 | mean residues in eggs | Female | Adult | 29 eggs | east coast | Toxicity Factor Datasets |
California Clapper Rail (Rallus longirostris ssp. obsoletus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
CHLORDANE, DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR, MERCURY (elemental), POLYCHLORINATED BIPHENYLS, SELENIUM (elemental) | no effect | eggshell thickness compared to those of museum eggs from 1907 and 1936 | Female | Adult | 29 eggs | North and South San Francisco Bay | Toxicity Factor Datasets |
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 |
Great Horned Owl (Bubo virginianus)
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, MIREX, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | increased | mortality due to pesticide exposure based on history, ante-mortem signs, and gross pathology | Not Reported | Not Reported | 8 owls | Toxicity Factor Datasets |