Birds
Mallard duck (Anas platyrhynchos)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| CYANOFENPHOS | decreased @ 2.0, 4.0 mg/kg/d | bw versus controls | Both Male and Female | Juvenile | 10 | laboratory | Toxicity Factor Datasets | 1 week | Laboratory |
| CYANOFENPHOS | increased @ 2.0, or 4.0 mg cyanofen/kg/d, 10 mg leptophos/kg/d. | incidence of histological lesions in axons and myelin sheaths | Both Male and Female | Juvenile | 10 | laboratory | Toxicity Factor Datasets | 1 week | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| SELENOMETHIONINE | decreased | incidence of delayed hypersensitivity reactions to antigen versus controls | Male | Adult | Controls = 24 Treated = 8 |
Laboratory | Toxicity Factor Datasets | Laboratory |
| SELENITE, SODIUM, SELENOMETHIONINE | decreased | blood monocyte counts after 78 days exposure versus controls | Male | Adult | Controls = 24 Treated = 8 |
Laboratory | Toxicity Factor Datasets | Laboratory |
| SELENITE, SODIUM, SELENOMETHIONINE | increased @ 3.5 mg/L (selenite) or 2.2 mg/L (selenomethionine) | serum ALT enzyme activity versus controls n high selenite and selenomethionine groups. | Male | Adult | Controls = 24 Treated = 8 |
laboratory | Toxicity Factor Datasets | Laboratory |
| SELENOMETHIONINE | increased (12-fold) | selenium concentrations in pectoral muscle | Male | Adult | Controls = 24 Treated = 8 |
Laboratory | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| LEAD (elemental) | decreased | hemoglobin and hematocrit versus controls | Male | Juvenile | 8 | Laboratory | Toxicity Factor Datasets | 6 months | Laboratory |
| LEAD (elemental) | decreased (60%) | blood ALAD activity versus controls | Male | Juvenile | 8 | Laboratory | Toxicity Factor Datasets | 6 months | Laboratory |
| LEAD (elemental) | increased | blood protoporphyrin levels versus controls | Male | Juvenile | 8 | Laboratory | Toxicity Factor Datasets | 6 months | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| LEAD (elemental) | increased @ 5 shot (33%) and repeated 5 shot (40%) | percent mortality versus controls | Both Male and Female | Not Reported | 5-6/group | Toxicity Factor Datasets | Laboratory | |
| LEAD (elemental) | decreased | bw versus controls | Both Male and Female | Not Reported | 5-6/group | Toxicity Factor Datasets | Laboratory | |
| LEAD (elemental) | increased @ all doses | Pb concentrations in wing bone and liver | Both Male and Female | Not Reported | 5-6/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| SELENOMETHIONINE | liver: C = 7.4(1-e^-0.382t) muscle: C = 8.0(1-e^-0.037t) |
selenium accumulation equations | Both Male and Female | Adult | 3 | Toxicity Factor Datasets | Laboratory | |
| SELENOMETHIONINE | liver: C = 7.4e^-0.037t muscle: C = 5.6e^-0.023t liver at peak body burden: C = 22.6e^-0.246t + 2.5 e^-0.008t muscle at peak body burden: C = 6.4e^-0.029t Loss phase for blood at peak body burden: C = 12.0e^-0.071t |
selenium depuration equations | Both Male and Female | Adult | 3 | Toxicity Factor Datasets | Laboratory | |
| SELENOMETHIONINE | liver: 18.7 d muscle: 30.1 d |
half life of selenium in tissues | Both Male and Female | Adult | 3 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| CRUDE OILS | decreased @ 5 uL/egg | embryonic weight (females) and crown rump length (both sexes) | Both Male and Female | Hatchling | 65 eggs/group | Toxicity Factor Datasets | 3 days | Laboratory | |
| CRUDE OILS | decreased to 65% @ 1 uL/egg); 9% @ 5 uL/egg | embryo survival to 18 days | Both Male and Female | Embryo | 65 eggs/group | Toxicity Factor Datasets | 3 days | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| SELENOMETHIONINE | increased @ 15 ppm, 60 ppm (adequate protein, no methionine added) | incidence of histopathological changes in livers versus controls | Not Reported | Juvenile | 15/group | Toxicity Factor Datasets | 1-day old | Laboratory | |
| SELENOMETHIONINE | decreased @ 60 ppm (regardless of methionine suppl. or protein levels) | body, liver and spleen weights, and tarsus length versus controls | Not Reported | Juvenile | 15/group | Toxicity Factor Datasets | 1-day old | Laboratory | |
| SELENOMETHIONINE | increased @ 15 (GSH-peroxidase only), 60 ppm Se, adequate protein | plasma GSH-peroxidase and alkaline phosphatase activities versus controls | Not Reported | Juvenile | 15/group | Toxicity Factor Datasets | 1-day old | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| SELENOMETHIONINE | no effect | distance run in 2 seconds from a fright stimulus vs controls | Not Reported | Chick | 32, 14, 14, 14, 11 in the 0, 1, 2, 4, and 8 ppm groups | Toxicity Factor Datasets | 6 days | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | decreased | % normal hatchlings versus controls | Not Reported | Embryo | 492-518, 232-384, and 128-276 for the 0, 10, and 40 ppm DDE groups | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | decreased | number of 14-day old ducklings per hen versus controls | Both Male and Female | Hatchling | 274-327, 69-167, and 26-113 for the 0, 10, and 40 ppm DDE groups | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | increased | % cracked eggs versus controls | Female | Hatchling | 666-696, 620-664, and 317-602 for the 0, 10, and 40 ppm DDE groups | Toxicity Factor Datasets | Laboratory | |
| DDE (4,4'-) | decreased | eggshell thickness versus controls | Female | Adult | 20-28, 21-25, and 10-23 for the 0, 10, and 40 ppm DDE groups | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| CHLORPYRIFOS | 145 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hours | Laboratory | |
| CHLORPYRIFOS | 29.4 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 7 days | Laboratory | |
| CHLORPYRIFOS | 50.4 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 30 days | Laboratory | |
| CHLORPYRIFOS | 83.3 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 6 mos | Laboratory | |
| ENDOSULFAN | 27.8 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hours | Laboratory | |
| ENDOSULFAN | 6.47 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 7 days | Laboratory | |
| ENDOSULFAN | 7.89 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 30 days | Laboratory | |
| ENDOSULFAN | 34.4 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 6 mos | Laboratory | |
| ALDICARB | 1.92 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hours | Laboratory | |
| ALDICARB | 3.60 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 7 days | Laboratory | |
| ALDICARB | 6.73 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 30 days | Laboratory | |
| ALDICARB | 4.44 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 6 mos | Laboratory | |
| PARATHION | 1.65 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hours | Laboratory | |
| PARATHION | 1.44 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 7 days | Laboratory | |
| PARATHION | 1.65 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 30 days | Laboratory | |
| PARATHION | 2.34 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 6 mos | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| AROCLOR 1254, DDE (4,4'-) | decreased with all treatments | numbers of mammillary cores and basal caps on eggshell membranes versus controls | Female | Adult | 6-8 eggs/group from 10 hens | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| DIELDRIN | decreased @ 10 ppm (serotonin only) and 30 ppm | Serotonin, norepinephrine, and dopamine levels versus controls | Both Male and Female | Juvenile | 3-6 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
| DIELDRIN | increased with all doses | brain, liver, and adipose dieldrin concentrations | Both Male and Female | Juvenile | 4-6 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
| DIELDRIN | no effect | bw versus controls | Both Male and Female | Juvenile | 9-25 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
| DIELDRIN | increased @ 10 ppm (liver only), 30 ppm (brain only) | brain and liver weight to body weight ratios versus controls | Both Male and Female | Juvenile | 9-25 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
| DIELDRIN | increased@ 4, 10, 30 ppm | hepatic microsomal enzyme activity versus controls | Both Male and Female | Juvenile | 5-15 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
| DIELDRIN | increased @ 30 ppm | liver protein concentration versus controls | Both Male and Female | Juvenile | 5-15 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
| DIELDRIN | increased @ 10, 30 ppm | liver DNA content versus controls | Male | Both Adults and Juveniles | 5-15 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
| DIELDRIN | decreased @ all doses | % drake encounter scores | Male | Both Adults and Juveniles | 30 per group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DDT (4,4'-) | decreased | eggshell thickness versus controls | Female | Adult | 5 hens; 19 eggs | Toxicity Factor Datasets | Laboratory | |
| DDT (4,4'-) | decreased | eggshell weight versus controls | Female | Adult | 5 hens; 19 eggs | Toxicity Factor Datasets | Laboratory | |
| DDT (4,4'-) | decreased | eggshell quality (R-value) versus controls | Female | Adult | 5 hens; 19 eggs | Toxicity Factor Datasets | Laboratory | |
| DDT (4,4'-) | no effect | calcium concentration in eggshell versus controls | Female | Adult | 5 hens; 19 eggs | Toxicity Factor Datasets | Laboratory | |
| DDT (4,4'-) | no effect | total Ca/eggshell | Female | Adult | 5 hens; 19 eggs | Toxicity Factor Datasets | Laboratory | |
| DDT (4,4'-) | no effect | Ca - ATPase activity in eggshell glands versus controls | Female | Adult | 5 hens; 19 eggs | Toxicity Factor Datasets | Laboratory |
American Kestrel (Falco sparverius)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| AROCLOR 1254, MIREX | 20.3% decrease @ 8 ppm mirex + 33 ppm Aroclor | sperm concentration | Male | Adult | 5-10/group | Toxicity Factor Datasets | Laboratory | |
| AROCLOR 1254, MIREX | 73.3% increase @ 8ppm mirex + 33 ppm Aroclor | semen volume | Male | Adult | 5-10/group | Toxicity Factor Datasets | Laboratory | |
| AROCLOR 1254 | no effect | sperm motility | Male | Adult | 10/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Location | Type |
|---|---|---|---|
| POLYCHLORINATED BIPHENYLS | review | Toxicity Factor Datasets | |
| POLYCHLORINATED BIPHENYLS | review | Toxicity Factor Datasets | |
| 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 | |
| AROCLOR 1248 | 5.60 ug/g (1.15 SD), PCBs; 0.15 ug/g (0.05 SD), dieldrin; 0.15 ug/g (0.07 SD), DDE @ 3.0 ug/g | mean egg concentrations, wet wt | Female | Adult | 8 pairs/group | Toxicity Factor Datasets | Laboratory | |
| AROCLOR 1248 | 5% decrease @ 3.0 ug/g | mean eggshell thickness | 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, POLYCHLORINATED DIBENZO-P-DIOXINS | increased @ 5 ppm | amount of liver cytoplasmic RNA | Both Male and Female | Adult | 4/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| PCB 105 (2,3,3',4,4'-PENTACHLOROBIPHENYL), PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL), PCB 153 (2,2',4,4',5,5'-HEXACHLOROBIPHENYL) | increased with PCB 126 | 7-ethoxyresorufin O-deethylase and aldrin epoxidase activities in liver | Female | Adult | 5-6/group | Toxicity Factor Datasets | 1 yr | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| FENTHION | 96% | range of plasma cholinesterase inhibition (relative to control) in birds that died | Male | Adult | 14 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| METHYLPARATHION | decrease at 1, 2, 3 mg/kg bw | brain acetylcholinesterase activity 10 hr post-dose | Both Male and Female | Adult | 5/dose | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| PHOSPHORUS (YELLOW OR WHITE) | increased | accumulation in skin | Not Reported | Adult | 4/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DICOFOL | 8.11 (fat), 0.28 (liver) ug/g @ 0.3 mg/kg bw/d | sum of geometric mean tissue concentrations (wet wt) of dicofol and metabolites (dichlorobenzophenone, mono-dechlorinated dicofol, dichlorobenzhydrol, DDE) | Female | Adult | 2-4/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| PARAQUAT | no effect | percent increase over controls in lung to body weight ratio | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory | |
| PARAQUAT | 51% @ 60 mg/kg | percent increase over controls in kidney to body weight ratio | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory | |
| PARAQUAT | 14% @ 25 mg/kg, 18% @ 60 mg/kg | percent increase over controls in liver to body weight ratio | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory | |
| PARAQUAT | decreased @ 25, 60 mg/kg | skeletal growth (humerus, femur, radius-ulna, tibia-fibula) | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory | |
| PARAQUAT | 11% @ 25 mg/kg, 25% @ 60 mg/kg | percent increase over controls in brain to body weight ratio | Not Reported | Juvenile | 11/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | increased | occurence of wild birds dying diagnosed with organochlorine poisoning | Both Male and Female | Both Adults and Juveniles | 5 kestrels | Toxicity Factor Datasets |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| CRUDE OILS | no effect | various hematological measurements (packed cell volume, erythrocyte counts, plasma uric acid, plasma alanine aminotransferase) | Both Male and Female | Juvenile | 16/group | Toxicity Factor Datasets | Laboratory | |
| CRUDE OILS | decreased @ 3.0% | hemoglobin | Both Male and Female | Juvenile | 16/group | Toxicity Factor Datasets | Laboratory | |
| CRUDE OILS | increased @ 3.0% | food consumption | Both Male and Female | Juvenile | 16/group | Toxicity Factor Datasets | Laboratory | |
| CRUDE OILS | decreased @ 3.0% | body weight | Both Male and Female | Juvenile | 16/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| CARBOFURAN | increased at 63.4, 126.8, 253.6 ppm | mortality versus controls | Both Male and Female | Adult | 8 | Toxicity Factor Datasets | Laboratory | |
| FENTHION | increased @ all doses | mortality versus controls | Both Male and Female | Adult | 8 | Toxicity Factor Datasets | Laboratory | |
| CARBOFURAN | decreased to 35% of controls | brain cholinesterase activity in birds that died | Both Male and Female | Adult | 8 | Toxicity Factor Datasets | Laboratory | |
| FENTHION | decreased to 10% of control levels | brain cholinesterase activity of birds that died | Both Male and Female | Adult | 8 | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| SELENIUM COMPOUNDS | 7.5 ppm Se, dry wt | maximum observed Se concentration in blood | Both Male and Female | Adult | 10 pairs/group | Toxicity Factor Datasets | Laboratory | |
| SELENOMETHIONINE | Y=1.132 + 0.801X (R^2 = 0.932) | relationship between Se concentrations in diet and blood | Both Male and Female | Adult | 9-10 pairs/group | Toxicity Factor Datasets | Laboratory | |
| SELENOMETHIONINE | no effect | incidence of mortality or signs of toxicity | Both Male and Female | Adult | 9-10 pairs/group | Toxicity Factor Datasets | Laboratory |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DICOFOL | decreased 5.45% (@ 5 mg/kg), 10.98% (@ 20 mg/kg) | eggshell thickness compared to controls | Female | Adult | 10/group | Toxicity Factor Datasets | Laboratory |
Clapper Rail (Rallus longirostris)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| DDT (4,4'-) | 1612 ppm | 5 day dietary LC50 | Male | Juvenile | 7 birds | Toxicity Factor Datasets | Laboratory | |
| DDT (4,4'-) | 1896 ppm | 5 day dietary LC50 | Female | Juvenile | 4 birds | Toxicity Factor Datasets | Laboratory | |
| DDD (4,4'-), DDT (4,4'-) | 13.3 ppm | mean residue concentration in brains of birds that survived | Male | Juvenile | 7 birds | Toxicity Factor Datasets | Laboratory | |
| DDD (4,4'-), DDT (4,4'-) | 19.0 ppm | mean residue concentration in brains of birds that survived | Female | Juvenile | 4 birds | Toxicity Factor Datasets | Laboratory | |
| DDD (4,4'-), DDT (4,4'-) | 42.9 ppm | mean residue concentration in brains of birds that died | Male | Juvenile | 7 birds | Toxicity Factor Datasets | Laboratory | |
| DDD (4,4'-), DDT (4,4'-) | 44.6 ppm | mean residue concentration in brains of birds that died | Female | Juvenile | 4 birds | Toxicity Factor Datasets | Laboratory |
Peregrine Falcon (Falco peregrinus)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Countries |
|---|---|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | eggshell thickness index = 1.799 - 0.243(log DDE) | linear regression of eggshell thickness index vs. log DDE concentration in eggs | Female | Adult | 295 eggs | Toxicity Factor Datasets | eggs were addled and/or deserted | UNITED KINGDOM |
Killdeer (Charadrius vociferus)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| CARBARYL | increased at 0.56 kg/ha (2, 8-9 d. post-spray) | whole carcass concentration of carbaryl | Not Reported | Not Reported | 8-9 birds/group | Toxicity Factor Datasets | |
| CARBARYL | no effect | whole carcass lipid content | Not Reported | Not Reported | 6-13 birds/group | Toxicity Factor Datasets | |
| CARBARYL | no effect | brain acetylcholinesterase activity | Not Reported | Not Reported | 6-13 birds/group | Toxicity Factor Datasets |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| DDE (4,4'-) | no correlation with DDE residues in eggs | eggshell thickness | Female | Adult | 12 eggs | McHenry and Billings Counties | Toxicity Factor Datasets |