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Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | no effect | sperm motility | Male | Adult | 10/group | 0 and 33 ppm, wet weight (=9-10 mg/kg bw/d) | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | diet | Toxicity Factor Datasets |
MIREX | 40.3% decrease @ 8 ppm | sperm concentration | Male | Adult | 5-10/group | 0 and 8 ppm, wet weight (=2.3-2.5 mg/kg bw/d) | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | diet | Toxicity Factor Datasets |
MIREX | no effect | sperm motility | Male | Adult | 5-10/group | 0 and 8 ppm, wet weight (=2.3-2.5 mg/kg bw/d) | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | diet | Toxicity Factor Datasets |
AROCLOR 1254, MIREX | 73.3% increase @ 8ppm mirex + 33 ppm Aroclor | semen volume | Male | Adult | 5-10/group | 0 and 8 ppm mirex + 33 ppm Aroclor, wet weight | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | diet | Toxicity Factor Datasets |
AROCLOR 1254, MIREX | 20.3% decrease @ 8 ppm mirex + 33 ppm Aroclor | sperm concentration | Male | Adult | 5-10/group | 0 and 8 ppm mirex + 33 ppm Aroclor, wet weight | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | diet | Toxicity Factor Datasets |
AROCLOR 1254, MIREX | no effect | sperm motility | Male | Adult | 5-10/group | 0 and 8 ppm mirex + 33 ppm Aroclor, wet weight | TOX-REPRO - physiology | 62 and 69 d (2 study periods) | 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 |
---|---|---|---|---|---|---|---|---|---|---|
AROCLOR 1254, POLYCHLORINATED DIBENZO-P-DIOXINS | increased @ 0.5, 5 ppm | in vitro microsomal breakdown of oestradiol | Both Male and Female | Adult | 4/group | 0, 0.5, 5 ppm, wet wt | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 5 mo | diet | Toxicity Factor Datasets |
AROCLOR 1262, POLYCHLORINATED DIBENZO-P-DIOXINS | increased @ 0.5, 5 ppm | in vitro microsomal breakdown of oestradiol | Both Male and Female | Adult | 4/group | 0, 0.5, 5 ppm, wet wt | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 5 mo | diet | Toxicity Factor Datasets |
AROCLOR 1254, POLYCHLORINATED DIBENZO-P-DIOXINS | increased @ 5 ppm | amount of liver cytoplasmic RNA | Both Male and Female | Adult | 4/group | 0, 5 ppm, wet wt | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 14 d | diet | Toxicity Factor Datasets |
Chemical | Endpoint Value | Toxicity Endpoint Type | Type |
---|---|---|---|
POLYCHLORINATED BIPHENYLS | review | TOX-EXP IND - accumulation | 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 |
---|---|---|---|---|---|---|---|---|---|---|
CYANIDE, SODIUM | 4.0 mg/kg bw | LD50 | Both Male and Female | Adult | 5/dose | NR | TOX-MORT - dose-response data | single dose | oral | 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 |
---|---|---|---|---|---|---|---|---|---|---|
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 | 0, 3.0 ug/g, wet wt | TOX-EXP IND - accumulation | 6 mo | diet | Toxicity Factor Datasets |
AROCLOR 1248 | 5% decrease @ 3.0 ug/g | mean eggshell thickness | Female | Adult | 8 pairs/group | 0, 3.0 ug/g, wet wt | TOX-REPRO - physiology | 6 mo | diet | Toxicity Factor Datasets |
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 | 0, 3.0 ug/g, wet wt | TOX-EXP IND - accumulation | 6 mo | 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 |
---|---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | decreased @ 3.0% | body weight | Both Male and Female | Juvenile | 16/group | 0, 0.3, 3.0% diet | TOX-Non-Repro-Sublethal - whole animal | 4 wks | diet | Toxicity Factor Datasets |
CRUDE OILS | increased @ 3.0% | food consumption | Both Male and Female | Juvenile | 16/group | 0, 0.3, 3.0% diet | TOX-Non-Repro-Sublethal - behavioral effects | 4 wks | diet | Toxicity Factor Datasets |
CRUDE OILS | decreased @ 3.0% | hemoglobin | Both Male and Female | Juvenile | 16/group | 0, 0.3, 3.0% diet | TOX-Non-Repro-Sublethal - organ/system effects | 4 wks | diet | Toxicity Factor Datasets |
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 | 0, 0.3, 3.0% diet | TOX-Non-Repro-Sublethal - organ/system effects | 4 wks | 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 |
---|---|---|---|---|---|---|---|---|---|---|
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 | 0, 0.3, 3.0 mg/kg bw/d | TOX-EXP IND - accumulation | 39 d | oral | Toxicity Factor Datasets |
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 | 0, 0.3, 3.0 mg/kg bw/d | TOX-EXP IND - accumulation | 39 d | oral | 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 |
---|---|---|---|---|---|---|---|---|---|---|
PHOSPHORUS (YELLOW OR WHITE) | increased | accumulation in skin | Not Reported | Adult | 4/group | 6.4 ug/g diet, wet wt (1.1 SE) | TOX-EXP IND - accumulation | 7 d | diet | Toxicity Factor Datasets |
PHOSPHORUS (YELLOW OR WHITE) | no effect | occurence of phosphorus intoxication symptoms | Not Reported | Adult | 4/group | 6.4 ug/g diet, wet wt (1.1 SE) | TOX-Non-Repro-Sublethal - whole animal | 7 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 |
---|---|---|---|---|---|---|---|---|---|---|
PARAQUAT | 22% @ 10 mg/kg, 18% @ 25 mg/kg, 44% @ 60 mg/kg | percent mortality | Not Reported | Juvenile | 11/group | 0,10,25,60 mg/kg bw/d | TOX-MORT - dose-response data | 10 d | oral | Toxicity Factor Datasets |
PARAQUAT | 86% of control @ 25 mg/kg, 74% of control @ 60 mg/kg | body weight by 10 days of dosing | Not Reported | Juvenile | 11/group | 0,10,25,60 mg/kg bw/d | TOX-REPRO - development | 10 d | oral | Toxicity Factor Datasets |
PARAQUAT | 11% @ 25 mg/kg, 25% @ 60 mg/kg | percent increase over controls in brain to body weight ratio | Not Reported | Juvenile | 11/group | 0,10,25,60 mg/kg bw/d | TOX-REPRO - development | 10 d | oral | Toxicity Factor Datasets |
PARAQUAT | 14% @ 25 mg/kg, 18% @ 60 mg/kg | percent increase over controls in liver to body weight ratio | Not Reported | Juvenile | 11/group | 0,10,25,60 mg/kg bw/d | TOX-REPRO - development | 10 d | oral | Toxicity Factor Datasets |
PARAQUAT | 51% @ 60 mg/kg | percent increase over controls in kidney to body weight ratio | Not Reported | Juvenile | 11/group | 0,10,25,60 mg/kg bw/d | TOX-REPRO - development | 10 d | oral | Toxicity Factor Datasets |
PARAQUAT | no effect | percent increase over controls in lung to body weight ratio | Not Reported | Juvenile | 11/group | 0,10,25,60 mg/kg bw/d | TOX-REPRO - development | 10 d | oral | Toxicity Factor Datasets |
PARAQUAT | decreased @ 25, 60 mg/kg | skeletal growth (humerus, femur, radius-ulna, tibia-fibula) | Not Reported | Juvenile | 11/group | 0,10,25,60 mg/kg bw/d | TOX-REPRO - development | 10 d | oral | 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 | 5 kestrels | 0.17-12.0 (DDE), 0.61-6.55 (PCBs), 0.08-5.17 (heptachlor epoxide), 1.97-5.15 (oxychlordane), 0.38-3.26 (trans-nonachlor), 0.75-3.70 (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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DDT (Technical Grade Mixture) | no effect | eggshell thickness | Female | Adult | NE Oregon, SE Washington, Idaho | 8 eggs (reference), 12 eggs (treatment) | 0.24 (reference), 0.58 (treatment) ppm DDT and metabolites, wet wt, in eggs | TOX-REPRO - physiology | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
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 |