Laboratory
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Lab |
---|---|---|---|---|---|---|---|---|---|---|
HDBP (halogenated dimethyl bipyrroles) | 15.4 ± 0.1 g | Egg mass | Embryo | 8 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HDBP (halogenated dimethyl bipyrroles) | 0.51 | % eggs laid that resulted in banded juvenile kestrels | Embryo | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory | ||
MERCURY (elemental) | 0.17 ppm ± 0.09 | Egg concentration | Embryo | 20 | Pamlico Sound, Island MN | Toxicity Factor Datasets | USA | Laboratory | ||
PERFLUOROOCTANE SULFONATE | 36.65 ng/g ww (4.02-55.73) | Liver concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | ||
PBDE MIXTURE | 25.8 ng/g ww (10.6-66.6) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | |||
PBDE MIXTURE | 61.5 ng/g ww (11.7-262) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | |||
DDE (4,4'-) | 0.62 µg/g (0.20-3.40) | Egg concentration | Embryo | 7 | Salton Sea | Toxicity Factor Datasets | Imperial | USA | Laboratory | |
MERCURY (elemental) | 0.57 µg/g [0.15-2.70 (95% CI)] | Egg concentration | NR | Embryo | 13 | San Francisco Bay marshes | Toxicity Factor Datasets | Alameda | USA | Laboratory |
AROCLOR 1268 | 222 ppm ± 213 | Hatchling concentration | Hatchling | 16 | LCP Superfund site, Brunswick | Toxicity Factor Datasets | USA | Laboratory | ||
OXYCHLORDANE | 0.0039 µg/g ww ± 0.0009 | Liver concentration | NR | Hatchling | 4 | Hamilton Harbour, Western Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory | |
DIELDRIN | 0.03 µg/g ww ± 0.02 | Liver concentration | NR | Hatchling | 4 | Snake and Pigeon Islands, Eastern Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory | |
6 | Mean days to death | B | Not Reported | 10 | USDA National Wildlife Research Center, Fort Collins, CO | Toxicity Factor Datasets | Lab | USA | Laboratory | |
GLYPHOSATE | 0.458 | % mortality | NR | Tadpole | 24 | San Francisco State University | Toxicity Factor Datasets | Lab | USA | Laboratory |
GLYPHOSATE | 0.958 | % mortality | NR | Tadpole | 24 | San Francisco State University | Toxicity Factor Datasets | Lab | USA | Laboratory |
ENDOSULFAN | 5.0 [2.9-7.6 (84% CI)] | LC10 | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | Laboratory |
TRICAINE METHANESULFONATE | 2 min | Time to no response to tow pinch | NR | Not Reported | 1 | Toxicity Factor Datasets | Lab | USA | Laboratory | |
DIELDRIN | 13 ± 22 ng/g | Accumulation in eggs from spiked nest material | NR | Embryo | 10 | Texas Tech University, Lubbock | Toxicity Factor Datasets | Lab | USA | Laboratory |
CADMIUM (elemental) | 27.2 ± 8.2 ppb | Muscle concentration, dead-captured | 20 | Pine Barrens | Toxicity Factor Datasets | USA | Laboratory | |||
0.167 mg/kg | Plasma vitellogenin induction ED50 | M | Not Reported | 64 | Oaklahoma State University | Toxicity Factor Datasets | Lab | USA | Laboratory | |
2-AMINO-4,6-DINITROTOLUENE | Decreased | Days of survival | M | Adult | 42 | Toxicity Factor Datasets | Lab | USA | Laboratory | |
METHYLMERCURY | No effect | Body mass | B | Nestling | 154 | Patuxent Wildlife Research Center, Laurel |
Toxicity Factor Datasets | Lab | USA | Laboratory |
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 |
PBDE MIXTURE | 86.09 ± 8.40 | Nestling concentration, whole body | NR | Nestling | 12 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HEXABROMOCYCLODODECANE (HBCDD) | Increased | Egg concentrations | NR | Embryo | 28 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
COPPER (elemental) | No effect | Blood concentration | Adult | 26 | Toxicity Factor Datasets | Lab | USA | Laboratory | ||
BUPRENORPHINE HYDROCHLORIDE | See citation | Plasma concentration | B | Adult | 13 | Toxicity Factor Datasets | Lab | USA | Laboratory | |
2,2',3,3',4,4',5,5',6,6'-DECABROMODIPHENYL ETHER (BDE-209) | 384 ng/g ww | Liver concentration | B | Adult | 34 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HEXABROMOCYCLODODECANE (HBCDD) | Unpaired exposed: increased mass | Testes weight | M | Adult | 22 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HEXABROMOCYCLODODECANE (HBCDD) | Increased | Solicitation of food from males | F | Adult | 30 | McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
1,2-DIBROMO-4-(1,2-DIBROMOETHYL)CYCLOHEXANE (DBE-DBCH - FORMERLY TBECH) | Decreased | Plasma TT4 concentration | M | Adult | 32 | McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | Decreased | T4/mg thyroid | Embryo | 60 | Toxicity Factor Datasets | Lab | Laboratory | |||
PBDE TECHNICAL MIXTURE, DE-71 | 0.969 | Survival to 90% incubation | Embryo | 70 | Patuxent Wildlife Research Center |
Toxicity Factor Datasets | Lab | Laboratory | ||
PCB | Decreased | Heterophil/lymphocyte | M | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PBDE TECHNICAL MIXTURE, DE-71 | See citation Table 1 | Retinol | F | Adult | 64 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HDBP (halogenated dimethyl bipyrroles) | 43 ± 6 ng/g | Carcass concentration | M | Adult | 12 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
HDBP (halogenated dimethyl bipyrroles) | 11.8 ± 0.4 d | Laying lag of first egg | Embryo | 8 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HDBP (halogenated dimethyl bipyrroles) | 15 ± 1 d | Laying lag of first egg | Embryo | 8 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
MERCURY (elemental) | 0.34 ppm ± 0.21 | Egg concentration | Embryo | 7 | Palmico Sound, DOT | Toxicity Factor Datasets | USA | Laboratory | ||
PERFLUOROOCTANE SULFONATE | 0.8 ng/g ww (0.7-2.7) | Muscle concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | ||
PCB | 565 ng/g ww (262-1800) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | |||
PCB | 135 ng/g ww (28.6-945) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | |||
SELENIUM COMPOUNDS | 0.365 µg/g (0.319-0.476) | Egg concentration | Embryo | 7 | Salton Sea | Toxicity Factor Datasets | Imperial | USA | Laboratory | |
MERCURY (elemental) | 5.9 µg/g dw (3.1) | Muscle concentration | B | Adult | 46 | LCP Superfund Site, Tutle River | Toxicity Factor Datasets | USA | Laboratory | |
MERCURY (elemental) | See citation Table 2 | Bone properties | Hatchling | 15 | Blythe Island | Toxicity Factor Datasets | USA | Laboratory | ||
MIREX | 0.03 µg/g ww ± 0.02 | Liver concentration | NR | Hatchling | 4 | Hamilton Harbour, Western Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory | |
HEPTACHLOR EPOXIDE | 0.008 µg/g ww ± 0.006 | Liver concentration | NR | Hatchling | 4 | Snake and Pigeon Islands, Eastern Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory | |
6.5 | Mean days to death | B | Not Reported | 10 | USDA National Wildlife Research Center, Fort Collins, CO | Toxicity Factor Datasets | Lab | USA | Laboratory | |
GLYPHOSATE | 0.292 | % mortality | NR | Tadpole | 24 | San Francisco State University | Toxicity Factor Datasets | Lab | USA | Laboratory |
GLYPHOSATE | 0.792 | % mortality | NR | Tadpole | 24 | San Francisco State University | Toxicity Factor Datasets | Lab | USA | Laboratory |
ENDOSULFAN | 76.1 [56.3-109 (84% CI)] | LC50 | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | Laboratory |
MEDETOMIDINE | See citation Figure 1 | Mean heart rate | NR | 10 | Tortoise Colony at Colorado State University | Toxicity Factor Datasets | Lab | USA | Laboratory | |
ENDRIN | 106 ± 71 ng/g | Accumulation in eggs from spiked nest material | NR | Embryo | 10 | Texas Tech University, Lubbock | Toxicity Factor Datasets | Lab | USA | Laboratory |
CHROMIUM (elemental) | 150 ± 21.8 ppb | Muscle concentration, dead-captured | 20 | Pine Barrens | Toxicity Factor Datasets | USA | Laboratory | |||
0.095 mg/kg | Plasma alkaline-labile phosphate induction ED50 | M | Not Reported | 64 | Oaklahoma State University | Toxicity Factor Datasets | Lab | USA | Laboratory | |
2-AMINO-4,6-DINITROTOLUENE | Decreased | Cricket consumption | M | Adult | 42 | Toxicity Factor Datasets | Lab | USA | Laboratory | |
METHYLMERCURY | See citation Table 4 | Immune responses | B | Nestling | 154 | Patuxent Wildlife Research Center, Laurel |
Toxicity Factor Datasets | Lab | USA | Laboratory |
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 |
PBDE MIXTURE | Increased | Body mass, 21 d | F | Nestling | 7 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HEXABROMOCYCLODODECANE (HBCDD) | Decreased | Second clutch | B | Adult | 29 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
COPPER (elemental) | Increased | Metallotionein | M | Adult | 26 | Toxicity Factor Datasets | Lab | USA | Laboratory | |
BUPRENORPHINE HYDROCHLORIDE | 0.948 | Bioavailability | B | Adult | 13 | Toxicity Factor Datasets | Lab | USA | Laboratory | |
2,2',3,3',4,4',5,5',6,6'-DECABROMODIPHENYL ETHER (BDE-209) | 1583 ng/g ww | Plasma concentration | B | Adult | 34 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HEXABROMOCYCLODODECANE (HBCDD) | Unpaired exposed: increased | Seminiferous tubules, elongated spermatids | M | Adult | 22 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
1,2-DIBROMO-4-(1,2-DIBROMOETHYL)CYCLOHEXANE (DBE-DBCH - FORMERLY TBECH) | Below detection limit | Plasma, liver, kidney, fat, egg concentrations | B | Adult | 46 pairs | McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
1,2-DIBROMO-4-(1,2-DIBROMOETHYL)CYCLOHEXANE (DBE-DBCH - FORMERLY TBECH) | Increased | Plasma FT4 concentration | M | Adult | 32 | McGill University | Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | No effect | Body weight | Embryo | 60 | Toxicity Factor Datasets | Lab | Laboratory | |||
PBDE TECHNICAL MIXTURE, DE-71 | 0.938 | Pipped egg | Embryo | 70 | Patuxent Wildlife Research Center |
Toxicity Factor Datasets | Lab | Laboratory | ||
PCB | Increased | Heterophil/lymphocyte | F | Adult | 152 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PBDE TECHNICAL MIXTURE, DE-71 | Increased | ƩPBDE | M | Adult | 64 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HDBP (halogenated dimethyl bipyrroles) | 310 ± 20 ng/g | Egg concentration | Embryo | 16 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HDBP (halogenated dimethyl bipyrroles) | 8.3 ± 0.1 d | Time to complete clutch | Embryo | 8 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HDBP (halogenated dimethyl bipyrroles) | 10.1 ± 0.2 d | Time to complete clutch | Embryo | 8 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
MERCURY (elemental) | 0.16 ppm ± 0.14 | Egg concentration | Embryo | 21 | Palmico Sound, Beacon | Toxicity Factor Datasets | USA | Laboratory | ||
PERFLUOROOCTANE SULFONATE | 59.8 ng/g ww (6.2-131.5) | Spleen concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | ||
DIELDRIN | 16.7 ng/g ww (9.26-56.8) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | |||
DIELDRIN | 5.42 ng/g ww (3.15-9.96) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | |||
DDE (4,4'-) | 0.10 µg/g (0.09-0.30) | Egg concentration | Embryo | 4 | Carrizo Plain | Toxicity Factor Datasets | San Luis Obispo | USA | Laboratory | |
MERCURY (elemental) | 20.9 µg/g dw (11.3) | Liver concentration | B | Adult | 22 | LCP Superfund Site, Tutle River | Toxicity Factor Datasets | USA | Laboratory | |
AROCLOR 1268 | See citation Table 2 | Bone properties | Hatchling | 16 | LCP Superfund site, Brunswick | Toxicity Factor Datasets | USA | Laboratory | ||
PCB | 0.43 µg/g ww ± 0.089 | Liver concentration | NR | Hatchling | 4 | Hamilton Harbour, Western Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory | |
HEXACHLOROBENZENE | 0.008 µg/g ww ± 0.009 | Liver concentration | NR | Hatchling | 4 | Snake and Pigeon Islands, Eastern Lake Ontario | Toxicity Factor Datasets | CANADA | Laboratory | |
4.5 | Mean days to death | B | Not Reported | 5 | USDA National Wildlife Research Center, Fort Collins, CO | Toxicity Factor Datasets | Lab | USA | Laboratory | |
GLYPHOSATE | 0.417 | % mortality | NR | Tadpole | 24 | San Francisco State University | Toxicity Factor Datasets | Lab | USA | Laboratory |
GLYPHOSATE | 0.583 | % mortality | NR | Tadpole | 24 | San Francisco State University | Toxicity Factor Datasets | Lab | USA | Laboratory |
ENDOSULFAN | 4.9 [3.1-7.0 (84% CI)] | LC10 | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | Laboratory |
MEDETOMIDINE | See citation Figure 2 | Mean respiratory rate | NR | 10 | Tortoise Colony at Colorado State University | Toxicity Factor Datasets | Lab | USA | Laboratory | |
DDT (4,4'-) | Not detected | Accumulation in eggs from spiked nest material | NR | Embryo | 10 | Texas Tech University, Lubbock | Toxicity Factor Datasets | Lab | USA | Laboratory |
MERCURY (elemental) | 75.8 ± 11.9 ppb | Muscle concentration, dead-captured | 20 | Pine Barrens | Toxicity Factor Datasets | USA | Laboratory | |||
MALATHION | See citation Figure 1 | Mean max sprint velocity, m/s | NR | Juvenile | 10 | Savannah River Ecology Laboratory | Toxicity Factor Datasets | Lab | USA | Laboratory |
2-AMINO-4,6-DINITROTOLUENE | Decreased >5 mg/kg/d | Body weight change | M | Adult | 42 | Toxicity Factor Datasets | Lab | USA | Laboratory | |
METHYLMERCURY | No effect | Spleen weight | B | Nestling | 154 | Patuxent Wildlife Research Center, Laurel |
Toxicity Factor Datasets | Lab | USA | Laboratory |
PCB | 0.29 | Exothalmic eyes | NR | Embryo | NR | 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 | M | Nestling | 33 pairs | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
PBDE MIXTURE | Increased | Body mass, 27 d | F | Nestling | 7 | Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
HEXABROMOCYCLODODECANE (HBCDD) | Decreased | Timing of laying | B | Adult | 29 | Toxicity Factor Datasets | Lab | CANADA | Laboratory |