PCB
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Lab |
---|---|---|---|---|---|---|---|---|---|---|
PCB | Review | Fat concentration | NR | Toxicity Factor Datasets | ||||||
AROCLOR 1242 | Decreased | Plasma thyroxine concentration | F | Adult | 36 | Toxicity Factor Datasets | Lab | Laboratory | ||
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | No effect | Body weight | Embryo | 60 | Toxicity Factor Datasets | Lab | Laboratory | |||
PCB | 0.6 | Cracked eggs, multiple | B | Adult | F0: 50 pairs | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 0.36 | Shortened limbs | NR | Hatchling | NR | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | No effect | Antebrachrium: growth rate | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Earlier | Body mass: maximal growth | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Antibody response | F | Adult | 37 | Avian Science and Conservation Centre, McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Plasma T3 | F | Nestling | 46 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 0.013 µg/g ww | Body concentration | NR | Hatchling | 20 | Piyas Lake, SD & Marsh Lake, MN | Toxicity Factor Datasets | USA | ||
PCB | Review | Eggshell thickness | Embryo | See citation | Toxicity Factor Datasets | GERMANY | ||||
PCB | Range: <1.6 ng/g | Liver concentration | M | 6 | Sao Paulo | Toxicity Factor Datasets | BRAZIL | |||
AROCLOR 1242 | Decreased | Plasma estradiol concentration | B | Adult | 36 | Toxicity Factor Datasets | Lab | Laboratory | ||
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | No effect | Liver:body weight | Embryo | 60 | Toxicity Factor Datasets | Lab | Laboratory | |||
PCB | 0.64 | Embryo abnormalities | B | Adult | F0: 50 pairs | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 0.29 | Underdevelopment | NR | Hatchling | NR | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Later | Antebrachrium: maximal growth | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | No effect | Antebrachrium: asymptotic size | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Anti-DNP-KLH titer concentration | Embryo | Avian Science and Conservation Centre, McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory | ||
PCB | Decreased | Plasma T4 | F | Nestling | 46 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 1.64 µg/g ww | Body concentration | NR | Hatchling | 10 | Spider Island | Toxicity Factor Datasets | USA | ||
PCB | Review | Egg concentration | Embryo | See citation | North Rhine-Westphalia / Rhineland Palatinate | Toxicity Factor Datasets | GERMANY | |||
PCB | 4.47 ± 0.56 ng/g ww | Egg yolk concentration | NR | Embryo | 11 nests, 20 eggs | Guadeloupe, French West Indies | Toxicity Factor Datasets | |||
AROCLOR 1242 | No effect | Time of molting | B | Adult | 36 | Toxicity Factor Datasets | Lab | Laboratory | ||
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | See citation | Liver histology | Embryo | 60 | Toxicity Factor Datasets | Lab | Laboratory | |||
PCB | 0.29 | Hatchling abnormalities | B | Adult | F0: 50 pairs | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 0.21 | Hematomas, red bodies | NR | Hatchling | NR | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | No effect | 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 | Increased | Total WBC count | M | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Plasma T3 | M | Nestling | 46 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 1.89 µg/g ww | Body concentration | NR | Hatchling | 10 | Hat Island | Toxicity Factor Datasets | USA | ||
PCB | Review | Eggshell thickness | Embryo | See citation | North Rhine-Westphalia / Rhineland Palatinate | Toxicity Factor Datasets | GERMANY | |||
PCB | 0.08 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA | |||
AROCLOR 1242 | No effect | Plumage color | B | Adult | 36 | Toxicity Factor Datasets | Lab | Laboratory | ||
PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL) | Beach: 1631, reference: 12.4 ng/g | Body concentration | Beach: 20, reference: 7 | Saglek, Labrador | Toxicity Factor Datasets | CANADA | ||||
PCB | No effect | Aggressive courtship | B | Adult | F0: 50 pairs | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Body mass: asymptotic size | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
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 | Total WBC count | F | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Plasma T4 | M | Nestling | 46 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | See citation | Egg concentration | NR | Embryo | Varied by site | Multiple sites in Straight of Georgia | Toxicity Factor Datasets | CANADA | ||
PCB | 2.96 µg/g lw | Blubber concentration | B | Not Reported | 18 | Todos Santos Bay, Ensenada, Baja California | Toxicity Factor Datasets | MEXICO | ||
PCB | 0.19 ppm ww | Egg concentration | Embryo | 3 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA | |||
PCB | No effect | Abandoned incubation | B | Adult | F0: 50 pairs | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Body mass: growth rate | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Later | Tarsus: maximal growth | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | No effect | Tarsus: asymptotic size | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Lynphocytes | M | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Plasma T3 | F | Nestling | 46 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 0.789 µg/g fw | Egg concentration | Embryo | 4 | Naval Air Base Coronado | Toxicity Factor Datasets | San Diego | USA | ||
PCB | 2757 ng/g ww | Maternal blubber concentration | F | Adult | 20 | Coastal sites | Toxicity Factor Datasets | USA | ||
PCB | 2.49 µg/g ww | Egg concentration | NR | Embryo | 5 | Mallard Slough | Toxicity Factor Datasets | USA | ||
PCB | No effect | Cracked eggs, multiple | B | Adult | F0: 50 pairs | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Earlier | Body mass: maximal growth | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Body mass: asymptotic size | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Tarsus: growth rate | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | No effect | Lynphocytes | F | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Plasma T4 | F | Nestling | 46 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 0.232 µg/g fw | Egg concentration | Embryo | 5 | Tijuana Slough | Toxicity Factor Datasets | San Diego | USA | ||
PCB | 7096 ng/g lw | Maternal blubber concentration | F | Adult | 20 | Coastal sites | Toxicity Factor Datasets | USA | ||
PCB | 1982: 3.32, 1989: 1.23, 1990: 5.38 µg/g ww | Egg concentration | NR | Embryo | 1982: 10, 1989: 5, 1990: 5 | Bair Island | Toxicity Factor Datasets | USA | ||
PCB | 0.78 | Embryo abnormalities | B | Adult | F0: 50 pairs | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Longer | Antebrachrium: asymptotic size | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Body mass: growth rate | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Tarsus: maximal growth | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Heterophils | M | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 565 ng/g ww (262-1800) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | |||
PCB | 34800 ng/g lw | Egg concentration | Embryo | 5 | San Francisco bay sites | Toxicity Factor Datasets | USA | |||
PCB | 757 ng/g ww | Premature fetus concentration | B | Embryo | 9 | Coastal sites | Toxicity Factor Datasets | USA | ||
PCB | 1989: 2.19, 1990: 0.792, 1991: 1.55 | Egg concentration | NR | Embryo | 5 | W. Marin Island | Toxicity Factor Datasets | USA | ||
PCB | 0.11 | Hatchling abnormalities | B | Adult | F0: 50 pairs | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Antebrachrium: growth rate | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Earlier | Body mass: maximal growth | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Flight | M | Adult | 50 pairs | Avian Science and Conservation Centre of McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Heterophils | F | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 512 ng/g ww (162-1490) | Egg concentration | 10 | Marsh Island | Toxicity Factor Datasets | USA | Laboratory | |||
PCB | 7.62 mg/kg | Egg concentration | Embryo | 60 | NJ, PA, DE, MD, VA | Toxicity Factor Datasets | USA | |||
PCB | 5449 ng/g lw | Premature fetus concentration | B | Embryo | 9 | Coastal sites | Toxicity Factor Datasets | USA | ||
PCB | 0.185 µg/g ww | Egg concentration | NR | Embryo | 5 | S. Wilbur Flood Area | Toxicity Factor Datasets | USA | ||
PCB | 34.1 µg/g | Egg concentrations | NR | Embryo | NR | University of Saskatchewan | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Earlier | Antebrachrium: maximal growth | F | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Antebrachrium: asymptotic size | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Increased | Sexual behaviors | M | Adult | 50 pairs | Avian Science and Conservation Centre of McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | Decreased | Heterophil/lymphocyte | M | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB | 135 ng/g ww (28.6-945) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | |||
PCB | 35.16 ng/g ww | Plasma concentration, geometric mean | NR | Nestling | 34 nests | Great Lake Basin | Toxicity Factor Datasets | CANADA | ||
PCB | Beach: 5769, reference: 79.8 ng/g | Body concentration | Beach: 20, reference: 7 | Saglek, Labrador | Toxicity Factor Datasets | CANADA | ||||
PCB | 0.078 µg/g ww | Egg concentration | B | Embryo | 4 | Lower Laguna Madre | Toxicity Factor Datasets | USA |
Pacific Green Turtle (Chelonia mydas)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
PCB | Range: <1.6 ng/g | Liver concentration | Male | 6 | Sao Paulo | Toxicity Factor Datasets | BRAZIL | |
PCB | Range: <1.6 ng/g | Kidney concentration | Female | 21 | Sao Paulo | Toxicity Factor Datasets | BRAZIL | |
PCB | Range: <1.6-17.4 ng/g | Liver concentration | Male | 6 | Sao Paulo | Toxicity Factor Datasets | BRAZIL | |
PCB | Range: <1.6-37.7 ng/g | Kidney concentration | Female | 21 | Sao Paulo | Toxicity Factor Datasets | BRAZIL | |
PCB | 4.47 ± 0.56 ng/g ww | Egg yolk concentration | Not Reported | Embryo | 11 nests, 20 eggs | Guadeloupe, French West Indies | Toxicity Factor Datasets | |
PCB | 4.57 ± 0.47 ng/g ww | Egg concentration | Not Reported | Embryo | 11 nests, 20 eggs | Guadeloupe, French West Indies | Toxicity Factor Datasets | |
PCB | Review | Egg concentration | Not Reported | Embryo | 11 nests, 20 eggs | Guadeloupe, French West Indies | Toxicity Factor Datasets | |
PCB | 291.94 ± 116.54 ng/g ww | Egg concentration | Not Reported | Embryo | 10 | Guadeloupe, French West Indies | Toxicity Factor Datasets |
Snowy Egret (Egretta thula)
Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
PCB | 0.08 ppm ww | Egg concentration | Embryo | 1 | Blackfoot Reservoir | Toxicity Factor Datasets | USA |
PCB | 0.19 ppm ww | Egg concentration | Embryo | 3 | Minidoka National Wildlife Refuge | Toxicity Factor Datasets | USA |