Birds
Mourning Dove (Zenaida macroura)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | 169.2 ug/g, dry wt. | lead concentration in bone | Not Reported | Adult | 10 birds | Toxicity Factor Datasets | 33.9 SE | Laboratory | |
LEAD (elemental) | 198.2 ug/g, dry wt | lead concentration in bone | Not Reported | Adult | 10 birds | Toxicity Factor Datasets | 39.9 SE | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | decreased at 10 ppm | percent of birds that laid eggs | Female | Adult | 10-13/group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | no effect | progesterone concentration in blood | Female | Adult | 10-13/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
PICLORAM, TRICLOPYR | no effect | nesting success in treated plots | Both Male and Female | Adult | Not Reported | Rob and Bessie Welder Wildlife Refuge | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | California Counties |
---|---|---|---|---|---|---|---|
TRICHLOROPHENOXYACETIC ACID (2,4,5-) | increased post-application from 1 to 4.1 birds per 40 ha | population density | Adult | 9 censuses pre- and post-spray | Truckee area | Toxicity Factor Datasets | Nevada |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
DDT (4,4'-) | no effect | Not Reported | Embryo | 2 eggs | Patuxent Research Refuge | Toxicity Factor Datasets |
Burrowing Owl (Athene cunicularia formerly Speotyto cunicularia)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
HEPTACHLOR | no effect | mean clutch size | Female | Adult | 6 nests | Columbia Basin | Toxicity Factor Datasets |
HEPTACHLOR | no effect | eggshell thickness | Female | Adult | 6 nests | Columbia Basin | Toxicity Factor Datasets |
Great Horned Owl (Bubo virginianus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
TERBUFOS | decreased (>2 standard deviations of control mean) in 3 samples | plasma cholinesterase activity after pesticide applications | Not Reported | Not Reported | 6 samples | Toxicity Factor Datasets | |
TERBUFOS | no effect | occurence of pesticide metabolites in fecal-urate samples | Not Reported | Not Reported | 29 owls | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DIELDRIN | 0.07 +/- 0.03 ppm (uncontaminated site); 0.34 +/- 0.21 ppm (contaminated site) | mean (+/- SE) concentrations in plasma | Not Reported | Adult | 2 birds on contaminated sites; 5 birds on uncontaminated sites | Rocky Mountain Arsenal National Wildlife Refuge | Toxicity Factor Datasets |
DIELDRIN | 0.01 +/- 0.003 ppm (uncontaminated site); 0.22 +/- 0.03 ppm (contaminated site) | mean (+/- SE) concentrations in plasma | Not Reported | Juvenile | 6 birds on contaminated sites; 10 birds on uncontaminated sites | Rocky Mountain Arsenal National Wildlife Refuge | Toxicity Factor Datasets |
Loggerhead Shrike (Lanius ludovicianus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | increased at 1 mg/kg | latency to formation of natural prey killing behaviors | Not Reported | Juvenile | 10-11/dose | collected in San Diego County, CA | Toxicity Factor Datasets | 1 day post-hatch (begin) | Laboratory |
DIELDRIN | increased at 1, 2, 4, 8 mg/kg/d | rate of mortality compared with controls | Not Reported | Juvenile | 10-11/dose | collected in San Diego County, CA | Toxicity Factor Datasets | 1 day post-hatch (begin) | Laboratory |
Double-crested Cormorant (Phalacrocorax auritus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | observed at 3, 10, 100 ug/kg | mortality | Not Reported | Hatchling | 6-10 eggs/dose | Toxicity Factor Datasets | Laboratory | |
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | body and organ weights | Not Reported | Hatchling | 6-10 eggs/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | increased at 400, 800 ug/kg egg | incidence of embryo mortality versus controls | Not Reported | Embryo | 15-60/group | Toxicity Factor Datasets | Laboratory | |
POLYCHLORINATED BIPHENYLS | increased @ 5 ug/kg | weight of heart, liver and spleen versus controls | Not Reported | Embryo | 15-60/group | Toxicity Factor Datasets | Laboratory | |
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 |
---|---|---|---|---|---|---|---|
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 |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CADMIUM CHLORIDE | no effect | brain, liver, kidney, testes weights versus controls | Male | Adult | 8 | Toxicity Factor Datasets | 32 weeks | Laboratory | |
CADMIUM CHLORIDE | no effect | liver glycogen concentration versus controls | Male | Adult | 8 | Toxicity Factor Datasets | 32 weeks | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENITE, SODIUM, SELENOMETHIONINE | increased @ 40, 80 ppm selenite or selenomethionine | duckling mortality versus controls | Not Reported | Juvenile | 40 birds/group | Toxicity Factor Datasets | Laboratory | |
SELENITE, SODIUM, SELENOMETHIONINE | decreased | food consumption versus controls | Not Reported | Juvenile | 40 birds/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDT (4,4'-) | no effect | hepatic microsomal enzyme activity (aniline hydroxylase and aminopyrine N-demethylase) | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory | |
DIELDRIN | no effect | hepatic microsomal enzyme activity (aniline hydroxylase and aminopyrine N-demethylase) | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | 4.3(0.7) ppm in femur, non-detect. in liver, 2.4(0.2) in kidneys | mean(SE) dry wt tungsten concentrations in tissues of tungsten-polymer-dosed birds | Both Male and Female | Adult | 16/treatment | Toxicity Factor Datasets | 6 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
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 |
---|---|---|---|---|---|---|---|---|
DICOFOL | 2-12% decrease @ 10-100 ug/g | eggshell thickness, compared to controls | Female | Adult | 4-8/dose | Toxicity Factor Datasets | Laboratory | |
DICOFOL | 5.4 (0.3 SE) ug/g wet wt. @ 3 ug/g diet; 18.1 (1.2 SE) @ 10 ug/g diet; 37.1 (1.6 SE) @ 30 ug/g diet; 150.7 (9.9SE) @ 100 ug/g diet, | mean egg yolk concentrations of p,p'-dicofol after 37-42 d on dicofol diet | Female | Adult | 4-8/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDT (Technical Grade Mixture) | decrease @ 20 - 200 ppm | eggshell thickness, weight and calcium concentration | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory | |
DDT (Technical Grade Mixture) | increase @ 200 ppm | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LINDANE | 62 lbs AI/acre (slope = 8.13) for exposure of 3d embryo; 52 lbs AI/acre (slope = 9.19) for exposure of 8d embryo | LC50 | Not Reported | Embryo | 30/dose | Toxicity Factor Datasets | 3 or 8d of development | Laboratory | |
PARAQUAT | 1.5 lbs AI/acre (slope = 1.66) for exposure of 3d embryo; 2.5 lbs AI/acre (slope = 1.40) for exposure of 8d embryo | LC50 | Not Reported | Embryo | 30/dose | Toxicity Factor Datasets | 3 or 8d of development | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CHLORPYRIFOS | no effect | fertility and hatchability of eggs, and duckling survival to 14 days | Not Reported | Juvenile | 24 pairs/dose | Toxicity Factor Datasets | 7 and 11 months old | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DICROTOPHOS, FENTHION | 68-78% | maximal brain acetylcholinesterase activity inhibition compared to control (after 3 days treatmentt) | Not Reported | Juvenile | 4/group | Toxicity Factor Datasets | 1 day old | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
CARBOFURAN | decreased @ 132 g/ha (150, 300 m exposure distances), 264 g/ha (all exposure distances) | brain cholinesterase activities compared with controls | Not Reported | Juvenile | 8/group | Toxicity Factor Datasets | CANADA | |
CARBOFURAN | no effect | growth rate to four weeks of age compared with controls | Not Reported | Juvenile | 8/group | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
MALATHION | 49.5 lb/acre | LC50, exposed on day 3 or 8 of incubation | Not Reported | Embryo | 30/group | Toxicity Factor Datasets | Day 3 or 8 of incubation | Laboratory | |
DIAZINON | 9.7 (day 3), 11.1 (day 8) lb/acre | LC50, exposed on day 3 or 8 of incubation | Not Reported | Embryo | 30/group | Toxicity Factor Datasets | Day 3 or 8 of incubation | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEPTOPHOS | 5/5 @ 260 ppm | incidence of ataxia | Both Male and Female | Juvenile | 3-5/group | Toxicity Factor Datasets | 14 d | Laboratory | |
LEPTOPHOS | 4/5 @ 260 ppm | incidence of CNS lesions | Both Male and Female | Juvenile | 3-5/group | Toxicity Factor Datasets | 14 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CRUDE OILS | 53% increase | plasma triiodothryonine concentration | Not Reported | Adult | 5/dose | Toxicity Factor Datasets | Laboratory | |
CRUDE OILS | 56% increase | hepatic cytochrome P450 content | Not Reported | Adult | 5/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254, DDE (4,4'-) | see citation | figure of # eggs/female/wk over time | Female | Adult | 10/dose | Toxicity Factor Datasets | Laboratory | |
DDE (4,4'-) | 373 (95% CL; 152-574) ppm lipid basis @ 40 ppm diet | DDE residue concentrations in eggs | Female | Adult | 12 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | decrease @ 2.5 - 5% | hematocrit, compared to control | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 0-8 wks post-hatch | Laboratory | |
CRUDE OILS | increase @ 0.25 - 5.0% | plasma alanine aminotransferase activity, from liver | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 0-8 wks post-hatch | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
IRON (elemental), LEAD (elemental) | no effect | serum enzyme levels versus controls (at 30 or 60 d post dose) | Male | Adult | 2/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CYANIDE | decreased @ all doses | ATP levels in liver and brain tissues versus controls | Female | Adult | 5/treatment | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | decreased with increasing lead in bone | number of eggs laid | Female | Adult | control=2 F, 4 M; treatment=6 M-F pairs/group | Toxicity Factor Datasets | 6 mos | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | increased in all groups dosed with lead shot | incidence of clinical signs, weight loss, breast muscle atrophy | Both Male and Female | Adult | treatment = 10/group control = 5 |
Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
LEAD COMPOUNDS | 1.367 (<0.05-29.80) | geometric mean concentration in kidneys (range) | Not Reported | Not Reported | 39 birds | Ebro Delta Natural Park | Toxicity Factor Datasets | ITALY |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
ARSENATE, SODIUM, SELENOMETHIONINE | increased @ 60 ppm Se | glutathione peroxidase activity versus controls | Not Reported | Juvenile | 15 birds/group | Toxicity Factor Datasets | 1 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
ALUMINUM SULFATE | decreased with LL and LH diets | femur breaking strength (LL,LH vs. NN diets) after 10 wks of treatment | Not Reported | Juvenile | 12-14/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
NICKEL SULFATE | 1.0-22.7 (liver), 2.7-74.4 (kidney) ppm, wet wt | Ni concentrations (ranges) in liver and kidney in ducklings that died @ 1200 ppm | Both Male and Female | Juvenile | 36 birds/dose | Toxicity Factor Datasets | 14 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHYLMERCURY DICYANDIAMIDE | 1 (@ 0.5 ppm), 6.46-9.19 (@ 3 ppm) ppm in eggs | mercury concentrations in eggs (at plateau) | Female | Adult | 10 females, 3 males/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
SELENIUM COMPOUNDS, SELENOMETHIONINE | decreased @ 30 ppm as Se-L-met | survival rate compared to controls | Not Reported | Juvenile | 25 birds/group | Toxicity Factor Datasets | 1 day | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENITE, SODIUM, SELENOMETHIONINE | decreased @ 25 ppm (selenite), 10 ppm (selenomethionine) | hatchability compared to controls | Not Reported | Juvenile | 5-11 pairs/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | increased @ 32 ppm | incidence of liver histopathological lesions, liver:body wt ratios versus controls | Male | Adult | 10 birds/group | Toxicity Factor Datasets | 2 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BORIC ACID, SELENOMETHIONINE | 22.5 (@ 15 ppm Se w/out B), 41.9 (@ 15 ppm Se w/B) ppm Se, wet wt 13.0 (@ 1000 ppm B) ppm B, wet wt |
geometric mean Se and B concentrations in liver | Not Reported | Juvenile | 15 birds/group | Toxicity Factor Datasets | day old | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHYLMERCURY DICYANDIAMIDE | ppm, wet wt: 0.79-0.86 (egg); 0.89-1.62 (liver); 1.52-1.82 (kidney); 9.03-11.17 (primary feathers); 0.67-0.83 (breast muscle); 0.44-0.59 (brain); 0.51-0.65 (ovary) | mean concentration of Hg in tissues (ranges are for 3 generations) | Female | Adult | 3-14 birds/tissue x generation group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CRUDE OILS | increased with light, moderate and heavy oiling | thermal conductance of feathers and body heat loss versus controls | Both Male and Female | Adult | 3 birds/treatment | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | no effect | plasma calcium concentration | Female | Adult | Not Reported | Toxicity Factor Datasets | 1 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BORIC ACID | decrease @ 1600 ppm | growth rate measured as changes in body weight, compared to control | Both Male and Female | Juvenile | 10 animals/pen; 3 pens/dose | Toxicity Factor Datasets | 1 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
FUEL OILS | decrease @ 4.0, 7.0, 12.0 ml/kg/d | mean spleen index (spleen wt./body wt.) | Male | Adult | 4-5/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CRUDE OILS | decrease | egg hatchability (# eggs hatching/# fertile eggs), compared to controls | Female | Adult | 20 hens/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PHOSPHORUS (YELLOW OR WHITE) | 3.90 mg/kg bw (3.24-4.69 95% CI) | 24 hour median lethal dose | Female | Adult | 4-5 birds/dose | 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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
EMAMECTIN BENZOATE | < 25 mg/kg bw | no-observed-effect level, based on body weight loss | Both Male and Female | Adult | 10/dose | Toxicity Factor Datasets | 19 weeks | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BORIC ACID, SELENOMETHIONINE | reduced @ 900 ppm B | hemoglobin concentrations versus controls | Male | Adult | 14 pairs/treatment | Toxicity Factor Datasets | 1 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD COMPOUNDS | reduced @ all doses | delta aminolevulinic acid dehydratase activity versus controls | Male | Adult | 10/ Pb treatment; 20/control treatment | Toxicity Factor Datasets | approx. 5 mo | Laboratory | |
LEAD COMPOUNDS | increased @ 869 ug/g, corn diet | mortality versus corn diet controls | Male | Adult | 5/ Pb treatment;3/control treatments | Toxicity Factor Datasets | approx. 7 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENIUM COMPOUNDS, SELENOMETHIONINE | increased with seleno-D,L-methionine, seleno-L-methionine, or selenized yeast | incidence of embryo deformities versus controls | Both Male and Female | Both Adults and Juveniles | 15 pairs/treatment group, 10 pairs/control group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | reduced @ 10 ppm Hg, 10 ppm Hg + 10 ppm Se | protein-bound sulfhydryl in liver versus controls | Male | Adult | 12/treatment | Toxicity Factor Datasets | 18 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | decreased with Bi | weight of hatchlings versus controls | Both Male and Female | Juvenile | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
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 | 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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
PARATHION | 1.65 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hours | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDT (4,4'-) | no effect | calcium concentration in eggshell versus controls | Female | Adult | 5 hens; 19 eggs | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no differences | mean survival times compared among lead, iron and bismuth dosed birds | Both Male and Female | Adult | 5 males, 5 females per group | Toxicity Factor Datasets | 6-8 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | no effect | body weight at end of experiment | Not Reported | Juvenile | 12/dose | Toxicity Factor Datasets | 1 d at initiation | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
PARATHION | 100% @ 5mg/L | percent mortality | Not Reported | Juvenile | 4-5/dose | Toxicity Factor Datasets | 2 weeks old | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CHLORPYRIFOS | 357 ppm | 11 day dietary LC50 | Not Reported | Juvenile | 10/group | Toxicity Factor Datasets | 14 d | Laboratory |
Peregrine Falcon (Falco peregrinus)
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'-), DIELDRIN, HEPTACHLOR EPOXIDE, POLYCHLORINATED BIPHENYLS | 15.8% | mean eggshell thinning compared to "pre-pesticide" reference eggs | Female | Adult | 78 eggs | Rankin Inlet | Toxicity Factor Datasets |
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 |
American Kestrel (Falco sparverius)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PARATHION | 56% decrease at 4.6 ppm | mean plasma cholinesterase activity relative to control | Not Reported | Adult | 4/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | no effect | mean organ and carcass weights | Both Male and Female | Adult | 16 pairs/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHYLPARATHION | decrease at 2, 3 mg/kg bw | cloacal temperature | Both Male and Female | Adult | 5/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
CARBOFURAN | 1.7-7.4 ppm (wet wt) | carcass residues of kestrels found dead | Not Reported | Not Reported | 3 birds | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 88.1 ppm (dry wt) | mean liver residues in birds that survived | Male | Adult | 11 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
FLUORIDE, SODIUM | 247.0 +/- 103.1 ppm @ 0 ppm; 6137.9 +/- 823.8 ppm @ 1120 ppm; 10,272.6 +/- 865.8 ppm @ 2240 ppm | mean fluoride content in the diaphyses of femurae | Both Male and Female | Juvenile | 9-10/group | Toxicity Factor Datasets | 7 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254, MIREX | no effect | sperm motility | Male | Adult | 5-10/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PHOSPHORUS (YELLOW OR WHITE) | no effect | occurence of phosphorus intoxication symptoms | Not Reported | Adult | 4/group | 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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
PCB 126 (3,3',4,4',5-PENTACHLOROBIPHENYL) | reduced @ 233 ng/g | percent hatching success, percent pipped versus controls | Not Reported | Hatchling | 24-26/treatment group | Toxicity Factor Datasets | hatchling | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | no effect | percent of pairs that laid eggs, number of fertile pairs and egg hatchability versus controls | Both Male and Female | Adult | 15 pairs/treatment group; 10 control pairs | Toxicity Factor Datasets | Laboratory |