Species
Filter by Species
Filter by Toxicity Endpoint Type
Filter by Exposure Endpoint Type
Filter by Chemical
Filter by Location
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Clutch or Litter Size | 1-4 | brood size at the time of banding | young/nest | Not Reported | Juvenile | near Cincinnati | 906 nests | Exposure Factor Datasets |
Hatching Success | 47.3% | percent of nests with at least one young surviving to banding age (of all pairs observed) | Not Reported | Juvenile | near Cincinnati | 1777 territories | Exposure Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE | no effect | eggshell thickness compared to pre-1946 museum speciments | Female | Adult | south-central Montana | 3 eggs | 0.74 (DDE), 0.07 (DDD + DDT), 0.16 (dieldrin), 0.11 (heptachlor epoxide) ppm, wet wt., in viable eggs | TOX-REPRO - physiology | NR | parent | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
AROCLOR 1254, DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, OXYCHLORDANE | 5% decrease | eggshell thickness index compared with reference eggs | Female | Adult | Butler, Delaware, Hamilton Counties | 18 eggs, 15 clutches | 3.0 (DDE), 1.7 (dieldrin), 0.1 (heptachlor epoxide), 3.1 (Arochlor 1254/60), 0.2 (oxychlordane) ppm (wet wt) in 4 eggs | TOX-REPRO - physiology | NR | site contamination | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, MIREX, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | increased | mortality due to pesticide exposure based on history, ante-mortem signs, and gross pathology | Not Reported | Not Reported | 8 owls | 13-96 (DDE), 0.01-0.65 (DDD), 0.03-0.17 (DDT, 2.83-71.0 (PCBs), 0.50-9.89 (dieldrin), 0.012-0.27 (HCB), 0.02-1.99 (Mirex), 0.12-7.74 (heptachlor epoxide), 0.98-8.68 (oxychlordane), 0.50-2.29 (trans-nonachlor), ppm wet wt, in brain | TOX-MORT - mortality in the field | NR | NR | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-), POLYCHLORINATED BIPHENYLS | increased | mortality due to PCB intoxication, based on brain residues | Female | Adult | Greene County | 1 owl | 44.7 (DDE), 357 (PCB) ppm wet wt in brain | TOX-MORT - mortality in the field | NR | NR | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | 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 | 13 owls | 3.96-75.7 (DDE), <0.01-49.6 (PCBs), 0.44-14.6 (heptachlor epoxide), 1.16-5.87 (oxychlordane), 0.02-1.36 (trans-nonachlor), <0.01-10.3 (dieldrin) wet wt in brain | TOX-MORT - mortality in the field | NR | NR | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-), DIELDRIN, HEPTACHLOR EPOXIDE, OXYCHLORDANE, POLYCHLORINATED BIPHENYLS | increased | occurence of mortality as a result of organochlorine poisoning | Female | Adult | 6 km s. of Corvallis | 1 owl | 28.0 (DDE), 0.8 (dieldrin), 5.1 (hexachlorobenzene), 5.8 (heptachlor epoxide), 3.7 (oxychlordane), 0.1 (cis-chlordane), 0.1 (trans-onachlor), 8.2 (PCBs) ppm wet wt in brain | TOX-MORT - mortality in the field | NR | NR | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
TERBUFOS | decreased (>2 standard deviations of control mean) in 3 samples | plasma cholinesterase activity after pesticide applications | Not Reported | Not Reported | 6 samples | 1.45 kg terbufos/ha | TOX-EXP IND - biomarkers | NR | pesticide application | Toxicity Factor Datasets |
TERBUFOS | no effect | occurence of pesticide metabolites in fecal-urate samples | Not Reported | Not Reported | 29 owls | 1.45 kg terbufos/ha | TOX-EXP IND - biomarkers | NR | pesticide application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
FAMPHUR | 85% decrease | post-mortem brain cholinesterase activity compared to control | Not Reported | Not Reported | Malheur County | 1 owl | 15 ppm in post-mortem stomach contents | TOX-EXP IND - biomarkers | NR | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
CHLOROPHACINONE | 99 ug | total carcass residues 28 d after removal from treatment | Not Reported | Adult | 1 owl | 3.2 ppm in voles maintained on treated food | TOX-EXP IND - accumulation | 6 d | diet | Toxicity Factor Datasets |
CHLOROPHACINONE | no effect | occurence of external bleeding or internal abnormalities after removal from treated diet | Not Reported | Adult | 1 owl | 3.2 ppm in voles maintained on treated food | TOX-Non-Repro-Sublethal - whole animal | 6 d | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
DIPHACINONE | 4.1-5.5 mg | doses resulting in symptoms and death in 2/3 birds within 14 days | Not Reported | Adult | 3 owls | 4.1-5.5 mg total consumed in mice fed a 0.01% bait | TOX-MORT - toxicity benchmarks | 5 days | diet | Toxicity Factor Datasets |
DIPHACINONE | increased | time to coagulation in blood sampled 3 days after treatment ended | Not Reported | Adult | 3 owls | 4.1-5.5 mg total consumed in mice fed a 0.01% bait | TOX-Non-Repro-Sublethal - organ/system effects | 5 days | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
STRYCHNINE | increased | occurence (compared with pre-dose values) of uncoordinated movement, tremors, loss of perching ability and ability to stand on the ground | Not Reported | Adult | 1 bird | 1.8 mg injected into mouse | TOX-Non-Repro-Sublethal - behavioral effects | single exposure | diet | Toxicity Factor Datasets |
STRYCHNINE | increased | occurence (compared with pre-dose values) of uncoordinated movement, tremors, loss of perching ability and ability to stand on the ground | Not Reported | Adult | 1 bird | 1.0 mg injected into mouse | TOX-Non-Repro-Sublethal - behavioral effects | single exposure | diet | Toxicity Factor Datasets |
STRYCHNINE | increased | occurence of errors (compared with pre-test values) in a reversal learning test | Not Reported | Adult | 1 bird | 0.4 mg injected into mouse | TOX-Non-Repro-Sublethal - behavioral effects | single exposure | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
ENDRIN | breast muscle=0.02 ppm, wet wt | tissue endrin residues | Not Reported | Not Reported | Wenatchee | 1 animal | 1.3-1.7 kg/ha | TOX-EXP IND - accumulation | NR | pesticide application (late fall) | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Toxicity Endpoint Type | Type |
---|---|---|---|---|---|---|
ALDRIN, BRODIFACOUM, CARBOFURAN, CHLORDANE, DIELDRIN, ENDRIN, FAMPHUR, FENTHION, PHORATE, STRYCHNINE | review | summaries of mortality due to organochlorine, anticholinesterase, anticoagulant, strychnine pesticides | Not Reported | Not Reported | TOX-MORT - mortality in the field | Toxicity Factor Datasets |
STRYCHNINE, ZINC PHOSPHIDE | review | summaries of sublethal effects due to organochlorine, anticholinesterase, anticoagulant, strychnine pesticides | Not Reported | Not Reported | TOX-Non-Repro-Sublethal - whole animal | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
DIELDRIN | no effect | productivity in contaminated versus uncontaminated sites | Both Male and Female | Adult | Rocky Mountain Arsenal National Wildlife Refuge | 3-4 nests on contaminated sites; 5-9 nests on uncontaminated sites | 0.18 ppm (uncontaminated), 1.15 ppm (contaminated) in soil within adult home ranges | TOX-REPRO - reproductive success | NR | habitat contamination | Toxicity Factor Datasets |
DIELDRIN | negative correlation | relationship between residue in plasma and survival | Not Reported | Juvenile | Rocky Mountain Arsenal National Wildlife Refuge | 6 birds (contaminated sites), 10 birds (uncontaminated sites) | 0.01 ppm (uncontaminated), 0.22 ppm (contaminated) in plasma | TOX-MORT - mortality in the field | NR | habitat contamination | Toxicity Factor Datasets |
DIELDRIN | no effect | daily and interval survival estimates on uncontaminated versus contaminated sites | Not Reported | Juvenile | Rocky Mountain Arsenal National Wildlife Refuge | 14 birds on contaminated sites; 41 birds on uncontaminated sites | 0.18 ppm (uncontaminated), 1.15 ppm (contaminated) in soil within adult home ranges | TOX-MORT - mortality in the field | NR | habitat contamination | Toxicity Factor Datasets |
DIELDRIN | no effect | daily survival rates on uncontaminated versus contaminated sites | Not Reported | Adult | Rocky Mountain Arsenal National Wildlife Refuge | 9 birds on contaminated sites; 11 birds on uncontaminated sites | 0.18 ppm (uncontaminated), 1.15 ppm (contaminated) in soil within adult home ranges | TOX-MORT - mortality in the field | NR | habitat contamination | Toxicity Factor Datasets |
DIELDRIN | 0.07 +/- 0.03 ppm (uncontaminated site); 0.34 +/- 0.21 ppm (contaminated site) | mean (+/- SE) concentrations in plasma | Not Reported | Adult | Rocky Mountain Arsenal National Wildlife Refuge | 2 birds on contaminated sites; 5 birds on uncontaminated sites | 0.18 ppm (uncontaminated), 1.15 ppm (contaminated) in soil within adult home ranges | TOX-EXP IND - accumulation | NR | habitat contamination | 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 | Rocky Mountain Arsenal National Wildlife Refuge | 6 birds on contaminated sites; 10 birds on uncontaminated sites | 0.18 ppm (uncontaminated), 1.15 ppm (contaminated) in soil within adult home ranges | TOX-EXP IND - accumulation | NR | habitat contamination | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
ALDRIN, DIELDRIN | 6.1 ppm (brain), 10.7 ppm (body remainder) dieldrin, wet wt | post-mortem concentrations | Not Reported | Not Reported | 1 bird | 4 oz aldrin/100 lbs seeds | TOX-EXP IND - accumulation | NR | pesticide application | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|
ENDRIN | brain=greater than or equal to 0.8 ppm, wet wt | tissue endrin residues | Not Reported | Not Reported | Wenatchee | 1-3 animals | 1.3-1.7 kg/ha | TOX-EXP IND - accumulation | NR | pesticide application (late fall) | Toxicity Factor Datasets |
Chemical | Endpoint Value | Toxicity Endpoint Type | Type |
---|---|---|---|
CARBARYL, CARBOFURAN, DDE (4,4'-) | review | TOX-REPRO - reproductive success | Toxicity Factor Datasets |