Female
American Kestrel (Falco sparverius)
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) | 2.4 (control), 119.0 (PCB 153), 182.0 (PCB 105), 3.3 (PCB 126) mg/kg, wet weight | PCB concentrations in pooled adipose tissue | 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 |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | decreased after 4 weeks | liver ethoxyresorufin-O-deethylase activity versus controls | Female | Adult | 4/treatment group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | no effect | calcium concentration in blood | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 0.71 (0.05 SE) ppm at 0 ppm, 32.4 (2.78 SE) ppm at 10 ppm |
mean residues in eggs | Female | Embryo | 9-10 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1248 | 5% decrease @ 3.0 ug/g | mean eggshell thickness | 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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | decrease at all doses (15.1-29.2%) | eggshell thickness | Female | Adult | 2-5 pairs/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | decrease at 3 ppm | mean eggshell thickness | Female | Adult | 18 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | no effect | eggshell thickness | Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | no effect | lead concentration in eggshell | Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | 62.0 ppm tibia, 13.5 ppm humeri at 50 ppm | lead concentrations in bones | Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-) | 10% decrease | eggshell thickness change relative to control | Female | Adult | 34 eggs | Cayuga Lake Basin | Toxicity Factor Datasets |
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 | |
DICOFOL | 82.36 (fat), 4.93 (liver), 1.15 (brain), 0.84 (oviduct) ug/g @ 3.0 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 |
---|---|---|---|---|---|---|---|
DDT (Technical Grade Mixture) | 10.4% decrease | change in mean eggshell thickness (relative to control) 0-0.8 miles from sprayed area | Female | Adult | 21 eggs | La Grande-Enterprise (OR), Potlatch (ID) | Toxicity Factor Datasets |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DIELDRIN | no effect | fertility, hatchability and duckling weight | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory | |
DDT (Technical Grade Mixture) | no effect | hepatic microsomal enzyme activity (aniline hydroxylase and aminopyrine N-demethylase) | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory | |
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 | |
DDT (Technical Grade Mixture) | DDT <0.1, DDE 0.2 - 1.2 ug/g dry wt @ 0 ppm; DDT 0.3 - 4.2, DDE 1.0 - 12.7 @ 2 ppm; DDT 1.3 - 25.0, DDE 5.0 - 110.1 @ 20 ppm; DDT 25.5 - 254, DDE 58.0 - 1234 @ 200 ppm | DDT and DDE concentrations in egg dry matter ranging from 0-14 d to 330 - 343 d sampling periods at 4 dietary doses | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory | |
DDT (4,4'-) | DDT <0.1, DDE 0.2 - 1.2 ug/g dry wt @ 0 ppm; DDT 0.6 - 2.4, DDE 1.2 - 10.1 @ 2 ppm; DDT 2.2 - 29.2, DDE 15.7 - 153.5 @ 20 ppm; DDT 14.9 - 102.0, DDE 45.0 - 187.0 @ 200 ppm | DDT and DDE concentrations in egg dry matter ranging from 0-14 d to 330 - 343 d sampling periods at 4 dietary doses | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
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 | |
DICOFOL | ST = 1.020 - 0.056C | regression equation relating shell thickness (mm) to log10 yolk concentration (C, ug/g); r2=0.39 | Female | Adult | 100 | Toxicity Factor Datasets | Laboratory | |
DDE (4,4'-) | no effect | egg production during study period | Female | Adult | 5-10/dose | Toxicity Factor Datasets | Laboratory | |
DDE (4,4'-) | no effect | body weight at end of study | Female | Adult | 5-10/dose | Toxicity Factor Datasets | Laboratory | |
DDE (4,4'-) | 2 - 17% decrease @ 3-100 ug/g | eggshell thickness, compared to controls | Female | Adult | 5-10/dose | Toxicity Factor Datasets | Laboratory | |
DDE (4,4'-) | 10.3 (0.9 SE) ug/g wet wt. @ 3 ug/g diet; 91.5 (1.5 SE) @ 30 ug/g diet; 332.0 (26.0 SE) @ 100 ug/g diet | mean egg yolk concentrations after 37-42 d on DDE diet | Female | Adult | 5-10/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDT (Technical Grade Mixture) | increase @ 200 ppm | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory | ||
DDT (4,4'-) | decrease @ 20 - 200 ppm | eggshell thickness, weight and calcium concentration | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory | |
DIELDRIN | 6% decrease @ 10 ppm | eggshell thickness | Female | Adult | 18/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
EPN | increased @ all doses | incidence of hyperactivity, ataxia, and/or paralysis compared with controls | Female | Juvenile | 6/group | Toxicity Factor Datasets | 20 wks | Laboratory | |
EPN | increased @ 30, 90, 270 ppm | incidence of CNS lesions (demyelination, axonal degeneration in spinal cord) compared with controls | Female | Juvenile | 6/group | Toxicity Factor Datasets | 20 wks | Laboratory | |
EPN | decreased @ all doses | activity of brain and plasma cholinesterase, and brain neurotoxic esterase compared with controls | Female | Juvenile | 6/group | Toxicity Factor Datasets | 20 wks | Laboratory | |
EPN | decreased @ 90, 270 pmm | plasma alkaline phosphatase activity compared with controls | Female | Juvenile | 6/group | Toxicity Factor Datasets | 20 wks | Laboratory | |
LEPTOPHOS | decreased @ 270, 540 ppm | body weight compared with controls | Female | Juvenile | 6/group | Toxicity Factor Datasets | 20 wks | Laboratory | |
LEPTOPHOS | increased @ all doses | incidence of CNS lesions (demyelination, axonal degeneration in spinal cord) compared with controls | Female | Juvenile | 6/group | Toxicity Factor Datasets | 20 wks | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | no effect | food consumption rate (174 g/d) compared to control (173 g/d) | Female | Adult | 10/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | no effect | food consumption rate (184 g/d) compared to control (173 g/d) | Female | Adult | 10/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, DDE (4,4'-) | no effect | food consumption rate (181 g/d) compared to control (173 g/d) | Female | Adult | 10/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | no effect | eggshell thickness | Female | Adult | 10 hens/dose; 8-9 eggs/dose | Toxicity Factor Datasets | Laboratory | |
DDE (4,4'-) | 17% decrease | eggshell thickness, compared to control | Female | Adult | 10 hens /dose; 8 eggs/dose | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, DDE (4,4'-) | 19% decrease | eggshell thickness, compared to control | Female | Adult | 10 hens/dose; 8 eggs/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
IRON (elemental), LEAD (elemental) | increased @ 8 #four iron shot | serum glutamic pyruvic transaminase activity vs controls | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory | |
IRON (elemental), LEAD (elemental) | increased with all treatments | incidence of hemosiderosis in liver vs controls | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory | |
IRON (elemental), LEAD (elemental) | increased @ 8 #four iron shot | incidence of inclusion bodies in kidney vs controls | Female | Adult | 8/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | decreased @ 1000 mg/kg bw | post-dose eggshell thickness versus pre-dose thickness | Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory | |
CHLOROETHYLMERCURY | decreased @ 500 mg/kg bw | post-dose eggshell thickness versus pre-dose thickness | Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory | |
DICHLOROPHENOXY-ACETIC ACID (2,4-) | decreased @ 1500 mg/kg bw | post-dose eggshell thickness versus pre-dose thickness | Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory | |
HEPTACHLOR | decreased @ 1000 mg/kg bw | post-dose eggshell thickness versus pre-dose thickness | Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory | |
ARSENITE, SODIUM | decreased @ 100 mg/kg bw | post-dose eggshell thickness versus pre-dose thickness | Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-), METHYLMERCURY CHLORIDE | 1.0 +/- 0.06 (@ 1 ppm Hg, no DDE), 5.3 +/- 0.56 (@ 5 ppm Hg, no DDE) ppm Hg, wet wt | Hg concentration in breast muscle (mean +/- SE) | Female | Adult | 10/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
BORIC ACID | no effect | eggshell thickness and Ratcliffe index of eggshell quality | Female | Adult | 15/dose | Toxicity Factor Datasets | 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 | Lab |
---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | 13-20 ppm, wet wt | mean Se concentration in eggs | Female | Adult | 5 birds | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CRUDE OILS | no effect | onset of laying, egg production, egg fertility, compared to controls | Female | Adult | 20 hens/dose | Toxicity Factor Datasets | Laboratory | |
CRUDE OILS | decrease | egg hatchability (# eggs hatching/# fertile eggs), compared to controls | Female | Adult | 20 hens/dose | Toxicity Factor Datasets | Laboratory | |
DDE (4,4'-) | no effect | onset of laying, egg production, egg fertility and egg hatchability, 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) | 6.96 mg/kg bw (2.66-8.96 95% CI) | 24 hour median lethal dose | Female | Adult | 6 birds/dose | Toxicity Factor Datasets | Laboratory | |
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 | 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 |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | California Counties |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | ppm wet wt: 1.21 (0.78), blood; 2.32 (1.10), liver; 131.13 (90.94), femur @ 2 #four shot | mean (2SE) lead concentrations in liver, femur and blood | Female | Adult | 24 birds | Sacramento National Wildlife Refuge | Toxicity Factor Datasets | 1 yr | Sacramento |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | increase @ 10-20 ug/g | estradiol metabolism and cytochrome P450 concentration | Female | Adult | 4/dose/sampling time | Toxicity Factor Datasets | 90 d at initiation | Laboratory | |
DIELDRIN | no effect | body or liver weight at end of experiment | Female | Adult | 4/dose/sampling time | Toxicity Factor Datasets | 90 d at initiation | Laboratory | |
DDT (4,4'-) | no effect | body weight at end of experiment | Female | Adult | 4/dose/sampling time | Toxicity Factor Datasets | 80 d at initiation | 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 | |
CYANIDE | no effect | ATP levels in heart versus controls | Female | Adult | 5/treatment | Toxicity Factor Datasets | Laboratory | |
CYANIDE | increased | rhodanese and 3-mercaptopyruvate sulfurtransferase activities in brain versus controls | Female | Adult | 5/treatment | Toxicity Factor Datasets | 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 | |
METHYLMERCURY DICYANDIAMIDE | decreased in 3rd generation | eggshell thickness versus controls | Female | Adult | 14 pairs/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-), DIELDRIN, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | positive correlation | relationships between EROD activity and dieldrin concentrations | Female | Adult | 5 birds/timepoint (timepoints = 0,10,20,32,42,52,59,70,80,90,100 days) | Bloomington | Toxicity Factor Datasets |
DDE (4,4'-), DIELDRIN, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | positive correlation | relationship between BROD, PROD, and EROD activities and total PCB, oxychlordane, and TEQs concentrations | Female | Adult | 5 birds/timepoint (timepoints = 0,10,20,32,42,52,59,70,80,90,100 days) | Bloomington | Toxicity Factor Datasets |
Peregrine Falcon (Falco peregrinus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-), DIELDRIN, POLYCHLORINATED BIPHENYLS | 15% | percent eggshell thinning compared with pre-DDT reference eggs | Female | Adult | 20 eggs | Rankin Inlet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 16% | percent eggshell thinning compared to pre-1947 reference eggs | Female | Adult | 13 eggs | South Australia | Toxicity Factor Datasets | AUSTRALIA |
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 |
DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, POLYCHLORINATED BIPHENYLS | log DDE in eggs = 0.9723 + 0.8506(log DDE in plasma); r = 0.66 | log-log relationship between DDE in plasma of female birds and DDE in eggs | Female | Adult | 10 females | Rankin Inlet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | eggshell thickness index = 1.888 - 0.281(log DDE) | linear regression of eggshell thickness index and DDE content of eggs | Female | Adult | 137 eggs | Tasmania, Victoria, South Australia | Toxicity Factor Datasets | AUSTRALIA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | review | data correlating eggshell thinning and DDE concentrations in eggs | Female | Adult | Not Reported | Toxicity Factor Datasets | GLOBAL |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-) | 1.89 (1.27-2.43) -6.96 (3.28-13.37) ppm, wet wt | annual mean (range) concentrations in eggs | Female | Adult | 3-6 eggs/year | Amchitka Island | Toxicity Factor Datasets |
DDE (4,4'-) | 7.5% decrease | eggshell thickness compared to "pre-pesticide" reference eggs | Female | Adult | 3-6 eggs/year | Amchitka Island | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | no relation | linear regression of eggshell thickness and DDE concentration in eggs | Female | Adult | 35 eggs | Victoria | Toxicity Factor Datasets | AUSTRALIA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 12.7 +/- 8.7 ppm (wet wt), 253 +/- 160 ppm (lipid wt) | mean (+/-SE) DDE concentration in eggs | Female | Adult | 10 eggs | Ungava region, Quebec; islands of Northwest Territories | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | no effect | eggshell thickness compared to pre-1947 reference eggs | Female | Adult | 2 eggs, 1 nest | Toxicity Factor Datasets | ECUADOR |
Clapper Rail (Rallus longirostris)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DDT (4,4'-) | 1896 ppm | 5 day dietary LC50 | Female | Juvenile | 4 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'-) | 44.6 ppm | mean residue concentration in brains of birds that died | Female | Juvenile | 4 birds | Toxicity Factor Datasets | Laboratory |
Mourning Dove (Zenaida macroura)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | 47.2-190.7 ug/g, dry wt | mean lead concentrations in kidney (greater accumulation with mixed seed vs. pelleted diet) | Female | Adult | 12/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | no effect | female fertility or productivity, egg weight and size | Female | Adult | 25 birds/dose | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | no effect | mortality | Female | Adult | 25 birds/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | increased at 10 ppm | interval from nest occupation to egg-laying | Female | Adult | 10-13/group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254 | decreased at 10 ppm | percent of birds that laid eggs | Female | Adult | 10-13/group | Toxicity Factor Datasets | Laboratory |
Deer Mouse (Peromyscus maniculatus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CHLOROCHOLINE CHLORIDE | increase @ 1, 20, 80 mg/kg bw/d | liver weight to bw ratio | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
CHLOROCHOLINE CHLORIDE | increase @ 1-80 mg/kg | thymus weight to bw ratios | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory | |
CHLOROCHOLINE CHLORIDE | increase @ 80 mg/kg bw/d | white blood cell counts | Female | Adult | 12/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|
ALDICARB | no effect | food intake | Female | 8 animals/dose | Toxicity Factor Datasets | 29 - 32 d | Laboratory |
Double-crested Cormorant (Phalacrocorax auritus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-), POLYCHLORINATED BIPHENYLS | no effect | shell thickness | Female | Adult | 10 eggs from 10 nests | OR coast | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | decreased at 276, 672, 1606 ng/kg | Mean yolk weight of eggs | Female | Both Adults and Juveniles | 5-12 eggs/dose | Saskatchewan, British Columbia, Lake Ontario | Toxicity Factor Datasets | CANADA |
California Clapper Rail (Rallus longirostris ssp. obsoletus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
CHLORDANE, DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR, MERCURY (elemental), POLYCHLORINATED BIPHENYLS, SELENIUM (elemental) | no effect | eggshell thickness compared to those of museum eggs from 1907 and 1936 | Female | Adult | 29 eggs | North and South San Francisco Bay | Toxicity Factor Datasets |