Falco sparverius (American Kestrel)
| Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Lab |
|---|---|---|---|---|---|---|---|---|---|
| HDBP (halogenated dimethyl bipyrroles) | 15.00 ± 0.08 g | Egg mass | Embryo | 8 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
| HDBP (halogenated dimethyl bipyrroles) | 14,040 ± 20 mm3 | Egg volume | Embryo | 43 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
| HDBP (halogenated dimethyl bipyrroles) | 0.173 ± 0.002 mm | Egg shell thickness | Embryo | 9 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
| HDBP (halogenated dimethyl bipyrroles) | 5.50 ± 0.09 eggs | Clutch size | Embryo | 8 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
| HDBP (halogenated dimethyl bipyrroles) | 79 ± 3 % | % fertile eggs in clutch | Embryo | 8 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
| HDBP (halogenated dimethyl bipyrroles) | 0.56 | % eggs laid that resulted in banded juvenile kestrels | Embryo | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory | |
| HDBP (halogenated dimethyl bipyrroles) | 14.9 ± 0.7 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) | 10.0 ± 0.4 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) | 15.2 ± 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) | 14,370 ± 20 mm3 | Egg volume | Embryo | 42 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
| HDBP (halogenated dimethyl bipyrroles) | 0.189 ± 0.001 mm | Egg shell thickness | Embryo | 14 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
| HDBP (halogenated dimethyl bipyrroles) | 5.38 ± 0.06 eggs | Clutch size | Embryo | 8 | Avian Science and Conservation Centre of McGill University |
Toxicity Factor Datasets | Lab | CANADA | Laboratory |
| HDBP (halogenated dimethyl bipyrroles) | 60 ± 5 % | % fertile eggs in clutch | 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 | |
| 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 |
| 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 |
| See citation Figure 4 | Copro-, uro-, and proto-porphyrin content of excreta | 3 | South Coast of Chile | Toxicity Factor Datasets | CHILE | Laboratory | |||
| CADMIUM (elemental) | 0.09 µg/g ww ± 0.20 | Egg concentration | Embryo | 63 | Sinaloa Coast | Toxicity Factor Datasets | MEXICO | Laboratory | |
| MERCURY (elemental) | 0.42 µg/g ww ± 0.63 | Egg concentration | Embryo | 63 | Sinaloa Coast | Toxicity Factor Datasets | MEXICO | Laboratory | |
| CADMIUM (elemental) | See citation figures | Egg concentration | Embryo | 4 different colonies along Sinaloa Coast | Toxicity Factor Datasets | MEXICO | Laboratory | ||
| MERCURY (elemental) | See citation figures | Egg concentration | Embryo | 4 different colonies along Sinaloa Coast | Toxicity Factor Datasets | MEXICO | Laboratory | ||
| LEAD (elemental) | See citation | Liver concentration | Not Reported | 12 | Toxicity Factor Datasets | USA | Laboratory | ||
| LEAD (elemental) | See citation | Blood concentration | Not Reported | 12 | Toxicity Factor Datasets | USA | Laboratory | ||
| LEAD (elemental) | No effect | Liver concentration | Not Reported | 1 | Toxicity Factor Datasets | USA | Laboratory | ||
| METHYLMERCURY | 0.89 µg/g [0.56-1.52 (95% CI)] | Embryonic LD50 | Embryo | 98 | Patuxent Wildlife Research Center | Toxicity Factor Datasets | USA | Laboratory | |
| METHYLMERCURY | 0.12 µg/g [0.08-0.19 (95% CI)] | Embryonic LD50 | Embryo | 81 | Patuxent Wildlife Research Center | Toxicity Factor Datasets | USA | Laboratory | |
| METHYLMERCURY | 0.33 µg/g [0.15-0.73 (95% CI)] | Embryonic LD50 | Embryo | 88 | Patuxent Wildlife Research Center | Toxicity Factor Datasets | USA | Laboratory | |
| METHYLMERCURY | 0.15 µg/g [0.05-0.31 (95% CI)] | Embryonic LD50 | Embryo | 63 | Patuxent Wildlife Research Center | Toxicity Factor Datasets | USA | Laboratory | |
| PERFLUOROOCTANE SULFONATE | 254, 533, 118 ng/g | Liver concentration | Not Reported | 3 | Various USA locations | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 0.17 ppm ± 0.09 | Egg concentration | Embryo | 20 | Pamlico Sound, Island MN | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 0.34 ppm ± 0.21 | Egg concentration | Embryo | 7 | Palmico Sound, DOT | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 0.16 ppm ± 0.14 | Egg concentration | Embryo | 21 | Palmico Sound, Beacon | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 0..27 ppm ± 0.08 | Egg concentration | Embryo | 4 | Palmico Sound, New Dump | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 0.18 ppm ± 0.13 | Egg concentration | Embryo | 8 | Cape Fear River, North Pelican | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 0.14 ppm ± 0.17 | Egg concentration | Embryo | 24 | Cape Fear River, Ferry Slip | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 0.27 ppm ± 0.11 | Egg concentration | Embryo | 19 | Cape Fear River, South Pelican | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 0.98 ppm ± 0.23 | Chick feathers | Chick | 21 | Pamlico Sound, Island MN | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 1.19 ppm ± 0.42 | Chick feathers | Chick | 22 | Palmico Sound, Beacon | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 0.97 ppm ± 0.19 | Chick feathers | Chick | 19 | Palmico Sound, New Dump | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 1.82 ppm ± 1.66 | Chick feathers | Chick | 20 | Cape Fear River, North Pelican | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 1.03 ppm ± 0.11 | Chick feathers | Chick | 20 | Cape Fear River, Ferry Slip | Toxicity Factor Datasets | USA | Laboratory | |
| MERCURY (elemental) | 0.86 ppm ± 0.18 | Chick feathers | Chick | 25 | Cape Fear River, South Pelican | Toxicity Factor Datasets | USA | Laboratory | |
| PERFLUOROOCTANE SULFONATE | 3.5 ng/g ww (1.3-11.4) | Brain concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANE SULFONATE | 2.1 ng/g ww (1.7-6.9) | Heart concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANE SULFONATE | 7.5 ng/g ww (2.9-11.3) | Lung concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANE SULFONATE | 36.65 ng/g ww (4.02-55.73) | Liver concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANE SULFONATE | 0.8 ng/g ww (0.7-2.7) | Muscle concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANE SULFONATE | 59.8 ng/g ww (6.2-131.5) | Spleen concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANE SULFONATE | 4.3 ng/g ww (1.2-17.3) | Kidney concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANOIC ACID | 1.3 ng/g ww (1.0-1.8) | Brain concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANOIC ACID | <1 ng/g ww | Heart concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANOIC ACID | 1.1 ng/g ww (<1-1.5) | Lung concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANOIC ACID | <1 ng/g ww | Liver concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANOIC ACID | 1.1 ng/g ww (<1-2.2) | Muscle concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANOIC ACID | <1 ng/g ww (<1-1) | Spleen concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| PERFLUOROOCTANOIC ACID | 1.6 ng/g ww (<1-2.7) | Kidney concentration | Not Reported | 5 | Cartagena Bay | Toxicity Factor Datasets | COLUMBIA | Laboratory | |
| MERCURY COMPOUNDS | See citation Figure 2 | Muscle concentration, total mercury | Not Reported | 5 | Southeast Gulf of California | Toxicity Factor Datasets | MEXICO | Laboratory | |
| MERCURY COMPOUNDS | See citation Figure 2 | Muscle concentration, organic mercury | Not Reported | 5 | Southeast Gulf of California | Toxicity Factor Datasets | MEXICO | Laboratory | |
| CHLORDANE | 43.2 ng/g ww (22.8-148) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | ||
| DDT (4,4'-) | 132 ng/g ww (53.8-466) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | ||
| HEXACHLOROCYCLOHEXANE | 1.05 ng/g ww (0.542-3.42) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | ||
| PBDE MIXTURE | 25.8 ng/g ww (10.6-66.6) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | ||
| PCB | 565 ng/g ww (262-1800) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | ||
| DIELDRIN | 16.7 ng/g ww (9.26-56.8) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | ||
| HEXACHLOROBENZENE | 1.54 ng/g ww (0.819-3.66) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | ||
| MIREX | 5.53 ng/g ww (2.56-14.2) | Egg concentration | 18 | Crab Bank | Toxicity Factor Datasets | USA | Laboratory | ||
| CHLORDANE | 35.8 ng/g ww (11.0-118) | Egg concentration | 10 | Marsh Island | Toxicity Factor Datasets | USA | Laboratory | ||
| DDT (4,4'-) | 119 ng/g ww (38.8-541) | Egg concentration | 10 | Marsh Island | Toxicity Factor Datasets | USA | Laboratory | ||
| HEXACHLOROCYCLOHEXANE | 0.830 ng/g ww (0.486-1.30) | Egg concentration | 10 | Marsh Island | Toxicity Factor Datasets | USA | Laboratory | ||
| PBDE MIXTURE | 25.3 ng/g ww (10.2-69.8) | Egg concentration | 10 | Marsh Island | Toxicity Factor Datasets | USA | Laboratory | ||
| PCB | 512 ng/g ww (162-1490) | Egg concentration | 10 | Marsh Island | Toxicity Factor Datasets | USA | Laboratory | ||
| HEXACHLOROBENZENE | 1.45 ng/g ww (0.563-3.60) | Egg concentration | 10 | Marsh Island | Toxicity Factor Datasets | USA | Laboratory | ||
| MIREX | 4.80 ng/g ww (1.92-18.6) | Egg concentration | 10 | Marsh Island | Toxicity Factor Datasets | USA | Laboratory | ||
| CHLORDANE | 13.6 ng/g ww (6.20-25.1) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | ||
| DDT (4,4'-) | 486 ng/g ww (223-1210) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | ||
| HEXACHLOROCYCLOHEXANE | 13.6 ng/g ww (6.46-36.7) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | ||
| PBDE MIXTURE | 61.5 ng/g ww (11.7-262) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | ||
| PCB | 135 ng/g ww (28.6-945) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | ||
| DIELDRIN | 5.42 ng/g ww (3.15-9.96) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | ||
| HEXACHLOROBENZENE | 2.73 ng/g ww (1.06-5.16) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | ||
| MIREX | 0.287 (0.146-0.629) | Egg concentration | 33 | Marsh Island | Toxicity Factor Datasets | MEXICO | Laboratory | ||
| DDE (4,4'-) | 22.33 ng/g ww ± 12.2 | Egg concentration | Embryo | 8 | Colorado River Delta | Toxicity Factor Datasets | MEXICO | Laboratory | |
| DDD (4,4'-) | 9.25 ng/g ww ± 9.3 | Egg concentration | Embryo | 8 | Colorado River Delta | Toxicity Factor Datasets | MEXICO | Laboratory | |
| DDT (4,4'-) | 16.51 ng/g ww ± 13.5 | Egg concentration | Embryo | 8 | Colorado River Delta | Toxicity Factor Datasets | MEXICO | Laboratory | |
| LINDANE | 14.16 ng/g ww ± 8.8 | Egg concentration | Embryo | 8 | Colorado River Delta | Toxicity Factor Datasets | MEXICO | Laboratory | |
| HEPTACHLOR | 8.26 ng/g ww ± 15.2 | Egg concentration | Embryo | 8 | Colorado River Delta | Toxicity Factor Datasets | MEXICO | Laboratory | |
| DIELDRIN | 0.50 ng/g ww ± 0.4 | Egg concentration | Embryo | 8 | Colorado River Delta | Toxicity Factor Datasets | MEXICO | Laboratory | |
| DIMETHOATE | 2.00 ng/g ww ± 1.6 | Egg concentration | Embryo | 8 | Colorado River Delta | Toxicity Factor Datasets | MEXICO | Laboratory | |
| MALATHION | 3.96 ng/g ww ± 3.9 | Egg concentration | Embryo | 8 | Colorado River Delta | Toxicity Factor Datasets | MEXICO | Laboratory | |
| DDE (4,4'-) | 7.52 µg/g (1.50-33.00) | Egg concentration | Embryo | 9 | Lemoore | Toxicity Factor Datasets | Fresno | USA | Laboratory |
| SELENIUM COMPOUNDS | 0.404 µg/g (0.335-0.840) | Egg concentration | Embryo | 9 | Lemoore | Toxicity Factor Datasets | Fresno | USA | Laboratory |
| DDE (4,4'-) | 0.62 µg/g (0.20-3.40) | Egg concentration | Embryo | 7 | Salton Sea | Toxicity Factor Datasets | Imperial | USA | Laboratory |
| SELENIUM COMPOUNDS | 0.365 µg/g (0.319-0.476) | Egg concentration | Embryo | 7 | Salton Sea | Toxicity Factor Datasets | Imperial | USA | 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 |
| SELENIUM COMPOUNDS | 0.423 µg/g (0.383-0.487) | Egg concentration | Embryo | 4 | Carrizo Plain | Toxicity Factor Datasets | San Luis Obispo | USA | Laboratory |
| DDE (4,4'-) | 1.19 µg/g (0.70-2.82) | Egg concentration | Embryo | 5 | Pixley | Toxicity Factor Datasets | Tulare | USA | Laboratory |
| DDE (4,4'), SELENIUM COMPOUNDS | 0.169 mm (0.150-0.183) | Eggshell thickness | Embryo | 10 | Lemoore | Toxicity Factor Datasets | Fresno | USA | Laboratory |
| DDE (4,4'), SELENIUM COMPOUNDS | 0.183 mm (0.170-0.194) | Eggshell thickness | Embryo | 9 | Salton Sea | Toxicity Factor Datasets | Imperial | USA | Laboratory |
| DDE (4,4'), SELENIUM COMPOUNDS | 0.183 mm (0.175-0.187) | Eggshell thickness | Embryo | 4 | Carrizo Plain | Toxicity Factor Datasets | San Luis Obispo | USA | Laboratory |
| DDE (4,4'-) | 2.60 µg/g (0.90-10.11) | Egg concentration | Embryo | 21 | Lemoore | Toxicity Factor Datasets | Fresno | USA | Laboratory |
