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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 |
---|---|---|---|---|---|---|---|---|---|---|
LEAD COMPOUNDS | increased @ 642 and 1284 ug/g | occurrence of renal tubular nuclear inclusion bodies versus controls | Male | Adult | 10/ Pb treatment; 5/control treatment | 0, 8.7 (sediment control), 642, 1284 ug/g diet, added as contaminated sediment | TOX-Non-Repro-Sublethal - organ/system effects | 10 wks | diet | Toxicity Factor Datasets |
LEAD COMPOUNDS | 3.0(0.30) ppm @ 642 ug/g Pb; 6.8(0.84) ppm @ 1284 ug/g Pb | mean (SE) wet wt Pb concentrations in blood | Male | Adult | 10/ Pb treatment; 5/control treatment | 0, 8.7 (sediment control), 642, 1284 ug/g diet, added as contaminated sediment | TOX-EXP IND - accumulation | 10 wks | diet | Toxicity Factor Datasets |
LEAD COMPOUNDS | 9.1(0.61) ppm @ 642 ug/g Pb; 16(1.5) ppm @ 1284 ug/g Pb | mean (SE) wet wt Pb concentrations in liver | Male | Adult | 10/ Pb treatment; 5/control treatment | 0, 8.7 (sediment control), 642, 1284 ug/g diet, added as contaminated sediment | TOX-EXP IND - accumulation | 10 wks | diet | Toxicity Factor Datasets |
LEAD COMPOUNDS | reduced @ 869 ug/g, corn diet | body weight compared to corn diet controls | Male | Adult | 5/ Pb treatment;3/control treatments | 0, 3.0 (sediment control, complete diet), 3.7 (sediment control, corn diet), 954 (complete diet), 869 (corn diet) ug/g diet, added as contaminated sediment | TOX-Non-Repro-Sublethal - whole animal | 15 wks | diet | Toxicity Factor Datasets |
LEAD COMPOUNDS | reduced @ 869 ug/g, corn diet | hemoglobin concentration versus corn diet controls | Male | Adult | 5/ Pb treatment;3/control treatments | 0, 3.0 (sediment control, complete diet), 3.7 (sediment control, corn diet), 954 (complete diet), 869 (corn diet) ug/g diet, added as contaminated sediment | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 15 wks | diet | Toxicity Factor Datasets |
LEAD COMPOUNDS | increased @ 869 and 954 ug/g | protoporphyrin versus corn or complete diet controls | Male | Adult | 5/ Pb treatment;3/control treatments | 0, 3.0 (sediment control, complete diet), 3.7 (sediment control, corn diet), 954 (complete diet), 869 (corn diet) ug/g diet, added as contaminated sediment | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 15 wks | diet | Toxicity Factor Datasets |
LEAD COMPOUNDS | reduced @ 869 and 954 ug/g | delta aminolevulinic acid dehydratase activity versus corn or complete diet controls | Male | Adult | 5/ Pb treatment;3/control treatments | 0, 3.0 (sediment control, complete diet), 3.7 (sediment control, corn diet), 954 (complete diet), 869 (corn diet) ug/g diet, added as contaminated sediment | TOX-Non-Repro-Sublethal - cellular/biochemical effects | 15 wks | diet | Toxicity Factor Datasets |
LEAD COMPOUNDS | increased @ 869 ug/g, corn diet | mortality versus corn diet controls | Male | Adult | 5/ Pb treatment;3/control treatments | 0, 3.0 (sediment control, complete diet), 3.7 (sediment control, corn diet), 954 (complete diet), 869 (corn diet) ug/g diet, added as contaminated sediment | TOX-MORT - dose-response data | 15 wks | diet | Toxicity Factor Datasets |
LEAD COMPOUNDS | increased @ 869 and 954 ug/g | incidence of renal tubular intranuclear inclusion bodies versus corn or complete diet controls | Male | Adult | 5/ Pb treatment;3/control treatments | 0, 3.0 (sediment control, complete diet), 3.7 (sediment control, corn diet), 954 (complete diet), 869 (corn diet) ug/g diet, added as contaminated sediment | TOX-Non-Repro-Sublethal - organ/system effects | 15 wks | diet | Toxicity Factor Datasets |
LEAD COMPOUNDS | 4.1(1.03) ppm in blood, 13(1.2) ppm in liver @ 954 ug/g, complete diet; 4.0(0.58) ppm in blood, 38(6.5) ppm in liver @ 869 ug/g, corn diet | mean (SE) wet wt Pb concentrations in blood and liver | Male | Adult | 5/ Pb treatment;3/control treatments | 0, 3.0 (sediment control, complete diet), 3.7 (sediment control, corn diet), 954 (complete diet), 869 (corn diet) ug/g diet, added as contaminated sediment | TOX-EXP IND - accumulation | 15 wks | 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 |
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LEAD (elemental) | higher in P8 than in T19 and TF, and in T19 than in TF | maximum likelihood estimate of 2-week Pb exposure rate | Both Male and Female | Both Adults and Juveniles | Sacramento National Wildlife Refuge; Willows, CA (39deg29'N, 122deg20'W) | 50 birds/treatment | 15750 (TF enclosure) , 173200 (T19 enclosure), or 2299700 (P8 enclosure) lead pellets/ha | TOX-EXP IND - accumulation | 4 mos | habitat contamination | Toxicity Factor Datasets |
LEAD (elemental) | higher in P8 than in T19 and TF, and in T19 than in TF | mortality rate (over 4 years) | Both Male and Female | Both Adults and Juveniles | Sacramento National Wildlife Refuge; Willows, CA (39deg29'N, 122deg20'W) | 50 birds/treatment | 15750 (TF enclosure) , 173200 (T19 enclosure), or 2299700 (P8 enclosure) lead pellets/ha | TOX-MORT - mortality in the field | 4 mos | habitat 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 |
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LEAD COMPOUNDS | Equation: fecal Pb conc./fecal acid insoluble ash content = 61 + (1.06 x sediment Pb conc.) | relation between waterfowl fecal lead concentration (dry wt) and sediment lead concentration (dry wt) | Not Reported | Not Reported | Coeur d'Alene and St. Joe River Basins | 521 fecal analyses at 11 wetlands (at least 20 per wetland) | 0-5,000 mg/kg in sediments | TOX-EXP IND - accumulation | NR | contaminated sediment ingestion | 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 |
---|---|---|---|---|---|---|---|---|---|---|
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | increased for lead shot | mortality rate versus all other groups | Both Male and Female | Adult | 16/treatment | control, steel (eight #4 pellets), lead (eight #4 pellets), tungsten-iron (eight BB size pellets), tungsten-polymer (eight BB size pellets); See paper for data on shot recovery and erosion in dosed ducks. | TOX-MORT - dose-response data | single exposure; 30 d observation | oral | Toxicity Factor Datasets |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | increased for lead shot | incidence of clinical signs versus other groups | Both Male and Female | Adult | 16/treatment | control, steel (eight #4 pellets), lead (eight #4 pellets), tungsten-iron (eight BB size pellets), tungsten-polymer (eight BB size pellets); See paper for data on shot recovery and erosion in dosed ducks. | TOX-Non-Repro-Sublethal - whole animal | single exposure; 30 d observation | oral | Toxicity Factor Datasets |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | reduced for lead shot | body weight versus all other groups | Both Male and Female | Adult | 16/treatment | control, steel (eight #4 pellets), lead (eight #4 pellets), tungsten-iron (eight BB size pellets), tungsten-polymer (eight BB size pellets); See paper for data on shot recovery and erosion in dosed ducks. | TOX-Non-Repro-Sublethal - whole animal | single exposure; 30 d observation | oral | Toxicity Factor Datasets |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | reduced for lead shot | hematocrit and hemoglobin concentrations versus all other groups | Both Male and Female | Adult | 16/treatment | control, steel (eight #4 pellets), lead (eight #4 pellets), tungsten-iron (eight BB size pellets), tungsten-polymer (eight BB size pellets); See paper for data on shot recovery and erosion in dosed ducks. | TOX-Non-Repro-Sublethal - cellular/biochemical effects | single exposure; 30 d observation | oral | Toxicity Factor Datasets |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | increased for lead shot | plasma activities of alanine aminotransferase, creatine phosphokinase, aspartate aminotransferase, lactate dehydrogenase versus control group | Both Male and Female | Adult | 16/treatment | control, steel (eight #4 pellets), lead (eight #4 pellets), tungsten-iron (eight BB size pellets), tungsten-polymer (eight BB size pellets); See paper for data on shot recovery and erosion in dosed ducks. | TOX-Non-Repro-Sublethal - cellular/biochemical effects | single exposure; 30 d observation | oral | Toxicity Factor Datasets |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | increased for lead shot | relative kidney weights versus controls | Both Male and Female | Adult | 16/treatment | control, steel (eight #4 pellets), lead (eight #4 pellets), tungsten-iron (eight BB size pellets), tungsten-polymer (eight BB size pellets); See paper for data on shot recovery and erosion in dosed ducks. | TOX-Non-Repro-Sublethal - organ/system effects | single exposure; 30 d observation | oral | Toxicity Factor Datasets |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | increased for lead shot, steel and tungsten-iron groups | iron concentrations in femur and liver versus controls | Both Male and Female | Adult | 16/treatment | control, steel (eight #4 pellets), lead (eight #4 pellets), tungsten-iron (eight BB size pellets), tungsten-polymer (eight BB size pellets); See paper for data on shot recovery and erosion in dosed ducks. | TOX-Non-Repro-Sublethal - organ/system effects | single exposure; 30 d observation | oral | Toxicity Factor Datasets |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | increased for lead, steel shot | renal concentrations of iron versus controls | Both Male and Female | Adult | 16/treatment | control, steel (eight #4 pellets), lead (eight #4 pellets), tungsten-iron (eight BB size pellets), tungsten-polymer (eight BB size pellets); See paper for data on shot recovery and erosion in dosed ducks. | TOX-Non-Repro-Sublethal - organ/system effects | single exposure; 30 d observation | oral | Toxicity Factor Datasets |
LEAD (elemental), STEEL COMPOUNDS, TUNGSTEN COMPOUNDS | 250.6(39.0) ppm in femur, 78.3(9.7) ppm in liver, 256.3(22.2) in kidneys | mean(SE) dry wt lead concentrations in tissues of lead-dosed birds | Both Male and Female | Adult | 16/treatment | control, steel (eight #4 pellets), lead (eight #4 pellets), tungsten-iron (eight BB size pellets), tungsten-polymer (eight BB size pellets); See paper for data on shot recovery and erosion in dosed ducks. | TOX-EXP IND - accumulation | single exposure; 30 d observation | 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 |
---|---|---|---|---|---|---|---|---|---|---|
SELENIUM COMPOUNDS, SELENOMETHIONINE | reduced with selenized yeast | body weight of 6 day old ducklings versus controls | Both Male and Female | Both Adults and Juveniles | 15 pairs/treatment group, 10 pairs/control group | 0, 10.3 ppm Se as seleno-L-methionine, 9.3 ppm Se as seleno-D,L-methionine, and 10.9 ppm Se as selenized yeast | TOX-REPRO - development | through reproduction until 6 days of age in ducklings | diet | Toxicity Factor Datasets |
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 | 0, 10.3 ppm Se as seleno-L-methionine, 9.3 ppm Se as seleno-D,L-methionine, and 10.9 ppm Se as selenized yeast | TOX-REPRO - development | through reproduction until 6 days of age in ducklings | diet | Toxicity Factor Datasets |
SELENIUM COMPOUNDS, SELENOMETHIONINE | 9.2(0.52) ppm with seleno-D,L-methionine; 8.9(0.35) ppm with seleno-L-methionine; 6.6(0.37) ppm with selenized yeast | mean(SE) wet wt concentrations of selenium in 8th egg laid | Female | Adult | 15 pairs/treatment group, 10 pairs/control group | 0, 10.3 ppm Se as seleno-L-methionine, 9.3 ppm Se as seleno-D,L-methionine, and 10.9 ppm Se as selenized yeast | TOX-EXP IND - accumulation | through reproduction until 6 days of age in ducklings | 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 |
---|---|---|---|---|---|---|---|---|---|---|
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | no effect | body weight versus controls | Both Male and Female | Adult | 12/group | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-Non-Repro-Sublethal - whole animal | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | increased @ 10 ppm Hg | incidence of leg weakness versus controls | Male | Adult | 12/group | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-Non-Repro-Sublethal - whole animal | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | decreased @ 10 ppm Hg, 10 ppm Hg + 10 ppm Se | hatchability versus controls | Both Male and Female | Both Adults and Juveniles | 12/group | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-REPRO - reproductive success | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | no effect | egg laying interval, egg weight, egg shell thickness, fertility, duckling survival, hatchling body weights versus controls | Both Male and Female | Both Adults and Juveniles | 12/group | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-REPRO - reproductive success | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | reduced @ 10 ppm Se, 10 ppm Hg + 10 ppm Se | weight of 7 day old ducklings versus controls | Both Male and Female | Both Adults and Juveniles | 12/group | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-REPRO - development | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | increased @ 10 ppm Se, 10 ppm Hg, 10 ppm Hg + 10 ppm Se | incidence of deformities in embryos that died (1 wk or older) versus controls | Both Male and Female | Both Adults and Juveniles | 12/group | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-REPRO - development | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | 7.6(0.26) ppm, egg, 6.0(0.31) ppm, fem. liver, 9.6(0.95) ppm, male liver @ 10 ppm Se; 9.3(0.85) ppm, egg, 9.2(1.61) ppm, female liver, 114(25.3) ppm, male liver @ 10 ppm Se + 10 ppm Hg | mean(SE) wet wt concentration of Se in egg and liver of treated birds | Both Male and Female | Adult | 12/group | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-EXP IND - accumulation | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | 16(0.8) ppm, egg, 22(1.5) ppm, fem. liver, 71(8.9) ppm, male liver @ 10 ppm Hg; 17(0.6) ppm, egg, 21(4.3) ppm, female liver, 65(4.1) ppm, male liver @ 10 ppm Se + 10 ppm Hg | mean(SE) wet wt concentration of Hg in egg and liver of treated birds | Both Male and Female | Adult | 12/group | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-EXP IND - accumulation | April 1-June 16 | 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 |
---|---|---|---|---|---|---|---|---|---|---|
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | reduced @ 10 ppm Se, 10 ppm Se + 10 ppm Hg | hematocrit and hemoglobin values versus controls | Male | Adult | 12/treatment | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-Non-Repro-Sublethal - cellular/biochemical effects | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | increased @ 10 ppm Hg + 10 ppm Se | plasma glucose concentrations versus controls | Male | Adult | 12/treatment | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-Non-Repro-Sublethal - cellular/biochemical effects | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | decreased @ 10 ppm Se, 10 ppm Hg, 10 ppm Hg + 10 ppm Se | plasma phosphorus concentrations versus controls | Male | Adult | 12/treatment | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-Non-Repro-Sublethal - cellular/biochemical effects | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | decreased @ 10 ppm Hg | glutathione peroxidase activity (plasma and liver) and glucose-6-phosphate dehydrogenase (liver and brain) versus controls | Male | Adult | 12/treatment | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-Non-Repro-Sublethal - cellular/biochemical effects | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | increased @ 10 ppm Se | hepatic GSSG reductase activity versus controls | Male | Adult | 12/treatment | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-Non-Repro-Sublethal - cellular/biochemical effects | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | increased @ 10 ppm Hg | oxidized glutathione (GSSG) level versus controls | Male | Adult | 12/treatment | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-Non-Repro-Sublethal - cellular/biochemical effects | April 1-June 16 | diet | Toxicity Factor Datasets |
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | reduced @ 10 ppm Hg, 10 ppm Hg + 10 ppm Se | protein-bound sulfhydryl in liver versus controls | Male | Adult | 12/treatment | 0, 10 ppm Hg, 10 ppm Se, 10 ppm Hg plus 10 ppm Se in diet | TOX-Non-Repro-Sublethal - cellular/biochemical effects | April 1-June 16 | diet | Toxicity Factor Datasets |