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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 |
---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-), DDT (4,4'-) | see citation | figure of eggshell thickness over 30 d period (significant differences noted at various times) | Female | Adult | 20/dose | 0, 10, 50 ppm DDT, DDE, DDT-SO4 or DDE-SO4 | TOX-REPRO - physiology | 30 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 |
---|---|---|---|---|---|---|---|---|---|---|
DDT (4,4'-) | 13.8% decrease | eggshell thickness, compared to controls | Female | Adult | 3/dose | 0, 75 ppm | TOX-REPRO - physiology | 7 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 |
---|---|---|---|---|---|---|---|---|---|---|
DDT (4,4'-) | decreased | eggshell weight and thickness, total eggshell calcium and shell gland epithelial microsomal Ca-ATPase activity, compared to controls | Female | Adult | 5 hens/dose; 19 eggs/dose | 0, 50 ppm | TOX-REPRO - physiology | 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 |
---|---|---|---|---|---|---|---|---|---|---|
LINDANE | serum (0.13); fat (0.20); muscle (0.70); kidney (0.02); liver (0.02); brain (0.01) ppm @ 20 mg/kg 2x/wk | mean lindane residue levels | Female | Adult | 5/dose | 20 mg/kg given 7x, 3x or 2x per wk | TOX-EXP IND - accumulation | 8 wks | gavage | Toxicity Factor Datasets |
LINDANE | serum (0.20); fat (0.68); muscle (0.30); kidney (0.23); liver (0.14); brain (0.11) ppm @ 20 mg/kg 3x/wk | mean lindane residue levels | Female | Adult | 5/dose | 20 mg/kg given 7x, 3x or 2x per wk | TOX-EXP IND - accumulation | 8 wks | gavage | Toxicity Factor Datasets |
LINDANE | serum (0.50); fat (1.14); muscle (0.82); kidney (0.28); liver (0.21); brain (0.13) ppm @ 20 mg/kg 7x/wk | mean lindane residue levels | Female | Adult | 5/dose | 20 mg/kg given 7x, 3x or 2x per wk | TOX-EXP IND - accumulation | 8 wks | gavage | 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'-) | no effect | food consumption rate (174 g/d) compared to control (173 g/d) | Female | Adult | 10/dose | 0, 40 ppm | TOX-Non-Repro-Sublethal - behavioral effects | 50 - 52 d | diet | Toxicity Factor Datasets |
AROCLOR 1254 | no effect | food consumption rate (184 g/d) compared to control (173 g/d) | Female | Adult | 10/dose | 0, 40 ppm | TOX-Non-Repro-Sublethal - behavioral effects | 50 - 52 d | diet | Toxicity Factor Datasets |
AROCLOR 1254, DDE (4,4'-) | no effect | food consumption rate (181 g/d) compared to control (173 g/d) | Female | Adult | 10/dose | 0, 40 ppm DDE + 40 ppm PCB | TOX-Non-Repro-Sublethal - behavioral effects | 50 - 52 d | diet | Toxicity Factor Datasets |
AROCLOR 1254 | no effect | eggshell thickness | Female | Adult | 10 hens/dose; 8-9 eggs/dose | 0, 40 ppm | TOX-REPRO - physiology | 50 - 52 d | diet | Toxicity Factor Datasets |
DDE (4,4'-) | 17% decrease | eggshell thickness, compared to control | Female | Adult | 10 hens /dose; 8 eggs/dose | 0, 40 ppm | TOX-REPRO - physiology | 50 - 52 d | diet | Toxicity Factor Datasets |
AROCLOR 1254, DDE (4,4'-) | 19% decrease | eggshell thickness, compared to control | Female | Adult | 10 hens/dose; 8 eggs/dose | 0, 40 ppm DDE + 40 ppm PCB | TOX-REPRO - physiology | 50 - 52 d | diet | Toxicity Factor Datasets |
AROCLOR 1254, DDE (4,4'-) | see citation | figure of # eggs/female/wk over time | Female | Adult | 10/dose | 0, 40 ppm DDE + 40 ppm PCB | TOX-REPRO - reproductive success | 50 - 52 d | diet | Toxicity Factor Datasets |
DDE (4,4'-) | 373 (95% CL; 152-574) ppm lipid basis @ 40 ppm diet | DDE residue concentrations in eggs | Female | Adult | 12 | 0, 40 ppm DDE | TOX-EXP IND - accumulation | 8-94 d | diet | Toxicity Factor Datasets |
AROCLOR 1254, DDE (4,4'-) | 344 (95% CL; 156-686) ppm DDE lipid basis and 346 (95%CL; 133-686) ppm PCB lipid basis @ 40 ppm DDE + 40 ppm PCB diet | mean DDE and PCB residue levels in eggs | Female | Adult | 13 | 0, 40 ppm DDE + 40 ppm PCB | TOX-EXP IND - accumulation | 7-128 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 |
---|---|---|---|---|---|---|---|---|---|---|
VANADYL SULFATE | no effect | body weight and food consumption compared among groups | Both Male and Female | Adult | 5 pairs/group | 0, 1, 10, 100 ppm diet | TOX-Non-Repro-Sublethal - whole animal | 12 wks | diet | Toxicity Factor Datasets |
VANADYL SULFATE | increased @ 100 ppm (maximum = 106 +/- 19 ppb, wet wt) | vanadium concentration in blood (sampled at 3 wk intervals) | Both Male and Female | Adult | 5 pairs/group | 0, 1, 10, 100 ppm diet | TOX-EXP IND - accumulation | 12 wks | diet | Toxicity Factor Datasets |
VANADYL SULFATE | brain, 9(1); fat, 20(11); kidney, 273(49); liver, 657(113), male femur 274(47); female femur 3327(2208) ppm, wet wt | mean (SE) vanadium concentrations @ 100 ppm dose in brain, fat, kidney, liver, and femur | Both Male and Female | Adult | 5 pairs/group | 0, 1, 10, 100 ppm diet | TOX-EXP IND - accumulation | 12 wks | diet | Toxicity Factor Datasets |
VANADYL SULFATE | <0.02 ppb, wet wt @ 1, 10 ppm; 63 ppb, wet wt @ 100 ppm | vanadium concentration in eggs | Female | Adult | 5 pairs/group | 0, 1, 10, 100 ppm diet | TOX-EXP IND - accumulation | 12 wks | diet | Toxicity Factor Datasets |
VANADYL SULFATE | increased @ 100 ppm | plasma cholesterol levels in drakes and laying hens | Both Male and Female | Adult | 5 pairs/group | 0, 1, 10, 100 ppm diet | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 12 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 |
---|---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | increase @ 2-15 ul/egg | percent mortality versus controls | Both Male and Female | Embryo | 100 eggs/dose | 0, 2, 5, 15 ul waste crankcase oil/egg | TOX-REPRO - reproductive success | single | application to egg surface | Toxicity Factor Datasets |
CRUDE OILS | increase @ 2-15 ul/egg | incidence of survivors with abnormalities versus controls | Both Male and Female | Embryo | 100 eggs/dose | 0, 2, 5, 15 ul waste crankcase oil/egg | TOX-REPRO - development | single | application to egg surface | Toxicity Factor Datasets |
CRUDE OILS | decrease @ 15 ul/egg | red blood cell and liver ALAD activity and hemoglobin concentration, compared to controls | Both Male and Female | Embryo | 100 eggs/dose | 0, 2, 5, 15 ul waste crankcase oil/egg | TOX-REPRO - physiology | single | application to egg surface | 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 | decrease | egg weight, length and breadth, compared to control | Female | Adult | 25/dose | control, 2% south Louisiana crude oil (w/w) | TOX-REPRO - physiology | NR | diet | Toxicity Factor Datasets |
DDE (4,4'-) | no effect | egg weight, length or breadth, compared to control | Female | Adult | 21-25/dose | control, 10 ppm DDE | TOX-REPRO - physiology | 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 |
---|---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | decrease @ 5% | growth rate, estimated as change in body weight, compared to control | Both Male and Female | Juvenile | 50/dose | 0, 0.025, 0.25, 2.5, 5% south Louisiana crude oil | TOX-Non-Repro-Sublethal - whole animal | 8 wks | diet | Toxicity Factor Datasets |
CRUDE OILS | decrease @ 0.25 - 5% | distance retreated from a frightening stimulus; impaired avoidance behavior | Both Male and Female | Juvenile | 10/dose | 0, 0.025, 0.25, 2.5, 5% south Louisiana crude oil | TOX-Non-Repro-Sublethal - behavioral effects | 6 d | diet | Toxicity Factor Datasets |
CRUDE OILS | increase @ 2.5 - 5% | incidence of liver hypertrophy and splenic atropy | Both Male and Female | Juvenile | 10/dose | 0, 0.025, 0.25, 2.5, 5% south Louisiana crude oil | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 8 wks | diet | Toxicity Factor Datasets |
CRUDE OILS | decrease @ 2.5 - 5% | hematocrit, compared to control | Both Male and Female | Juvenile | 10/dose | 0, 0.025, 0.25, 2.5, 5% south Louisiana crude oil | TOX-Non-Repro-Sublethal - organ/system effects | 8 wks | diet | Toxicity Factor Datasets |
CRUDE OILS | increase @ 0.25 - 5.0% | plasma alanine aminotransferase activity, from liver | Both Male and Female | Juvenile | 10/dose | 0, 0.025, 0.25, 2.5, 5% south Louisiana crude oil | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 8 wks | diet | Toxicity Factor Datasets |
CRUDE OILS | increase @ 0.025 - 5% | pathological release of ornithine carbamyltransferase from kidney | Both Male and Female | Juvenile | 10/dose | 0, 0.025, 0.25, 2.5, 5% south Louisiana crude oil | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 8 wks | diet | Toxicity Factor Datasets |
CRUDE OILS | increase @ 5% | incidence of degeneration of kidney tubules | Both Male and Female | Juvenile | 10/dose | 0, 0.025, 0.25, 2.5, 5% south Louisiana crude oil | TOX-Non-Repro-Sublethal - organ/system effects | 8 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 |
---|---|---|---|---|---|---|---|---|---|---|
CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, LEAD COMPOUNDS, SELENIUM COMPOUNDS, ZINC COMPOUNDS | increase | incidence of epileptiform seizures and subsequent death associated with "unusual" Se levels | Female | Adult | 1 | range of metal residue levels in brain, liver, heart, muscle and fat (ppm dry wt); Cd, 0.18 - 3.03; Cr, 1.24-2.39; Cu 1.86 - 87.74; Pb, 77.21-110.90; Se 222-255; Zn 4.89-240.28 | TOX-Non-Repro-Sublethal - whole animal | NR | site contamination | 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), POLYCHLORINATED BIPHENYLS | increase | incidence of premature parturtion associated with elevated DDT and PCB residues, compared to full term parturient group | Female | Adult | San Miguel Island | 4-6/group | Premature parturient group (ppm wet wt): DDT 824.4 (blubber), PCBs 112.4 (blubber), DDT 25.24 (liver), PCBs 5.74 (liver): Full term parturient group (ppm wt wt): DDT 103.2 (blubber), PCBs 17.1 (blubber), DDT 6.67 (liver), PCBs 1.32 (liver) | 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 |
---|---|---|---|---|---|---|---|---|---|---|
SELENIUM COMPOUNDS | 36.11 - 88.4 ug/g wet wt (liver); 7.12 - 32.8 ug/g wet wt (kidney) | selenium concentration range in liver and kidney of dead animals | Not Reported | Not Reported | 3 | fish diet Se concn. range; 0.70 - 1.06 ug/g wet wt | TOX-EXP IND - accumulation | NR | 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 |
---|---|---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-), POLYCHLORINATED BIPHENYLS | increase | incidence of premature parturition associated with elevated DDT and PCB levels, compared to full term parturient group | Female | Adult | San Miguel Island | 10/group | Premature parturient group (ppm wet wt): p,p'-DDE 350-939 (blubber), PCBs 33.0-92.4 (blubber); p,p'-DDE 8.54-30.4 (liver), PCBs 0.63-6.08 (liver): Full term parturient group (ppm wt wt): p,p'-DDE 16.3-342 (blubber), PCBs 4.73-39.5 (blubber); p,p'-DDE 0.93 | 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 |
---|---|---|---|---|---|---|---|---|---|---|
CADMIUM COMPOUNDS, DDT (Technical Grade Mixture), MERCURY COMPOUNDS, POLYCHLORINATED BIPHENYLS | increase | incidence of kidney histopathological lesions in "sick" or dead animals compared to "healthy" animals, consistent with diagnosis of leptospirosis | Male | Adult | 2-8/group | residues significantly different between groups (ppm, wet wt): "Sick"; Hg 127.5 - 170.1(liver), Cd 0.17 (cerebellum), DDE 23.9 (liver), PCBs 2.79 (liver): "Healthy"; Hg 74.1 - 95.7 (liver), Cd 0.042 (cerebellum), DDE 11.1 (liver), PCBs 4.87(liver) | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 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 |
---|---|---|---|---|---|---|---|---|---|---|
BROMINE COMPOUNDS, CADMIUM COMPOUNDS, COPPER COMPOUNDS, IRON COMPOUNDS, MANGANESE COMPOUNDS, MERCURY COMPOUNDS, SELENIUM COMPOUNDS, SILVER COMPOUNDS, ZINC COMPOUNDS | increase | incidence of premature parturition correlated with different metal concentrations and ratios | Both Male and Female | Both Adults and Juveniles | 10/group | see citation for table of residue data for 13 metals in pre-term vs full-term mothers and pups | 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 |
---|---|---|---|---|---|---|---|---|---|---|
DIURON | 15.2 mg/l | 14-d LC50 value; mean of 2 tests | Not Reported | Tadpole | 8/replicate; 3 replicates/dose | 0, 0.5, 1.0, 3.8, 7.6, 14.5, 21.1, 29.1 mg/l | TOX-MORT - toxicity benchmarks | 14 d | waterborne | Toxicity Factor Datasets |
DIURON | 14.5 mg/l | lowest NOAEL based on body length/weight endpoints | Not Reported | Tadpole | 8/replicate; 3 replicates/dose | 0, 0.5, 1.0, 3.8, 7.6, 14.5, 21.1, 29.1 mg/l | TOX-Non-Repro-Sublethal - whole animal | 14 d | waterborne | Toxicity Factor Datasets |