Both Male and Female
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
VANADYL SULFATE | increased @ 100 ppm | plasma cholesterol levels in drakes and laying hens | Both Male and Female | Adult | 5 pairs/group | Toxicity Factor Datasets | 1 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | decreased @ > 60 ug/dl blood | delta-aminolevulinic acid dehydratase activity | Both Male and Female | Not Reported | 21 birds | World Wildlife Fund Refuge, Tuscany | Toxicity Factor Datasets | ITALY |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
STEEL COMPOUNDS, TRIBUTYLTIN | increased in both groups (no treatment diffs) | white blood cell counts, monocyte counts, total protein concentrations over study period | Both Male and Female | Juvenile | 20/group | Toxicity Factor Datasets | 7 wks | Laboratory | |
STEEL COMPOUNDS, TRIBUTYLTIN | increased with steel shot, wk 8 | overall response score (inflammation, muscle damage changes) | Both Male and Female | Juvenile | 20/group | Toxicity Factor Datasets | 7 wks | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CADMIUM CHLORIDE | increased to 0.010 (@ 20 ppm), 0.040 (@ 200 ppm) ppm, wet wt | Cd concentrations in eggs versus controls | Both Male and Female | Adult | 15 eggs (20 ppm), 3 eggs (200 ppm) | Toxicity Factor Datasets | 1 yr | Laboratory | |
CADMIUM CHLORIDE | increased @ 200 ppm/60 or 90 d of treatment, 30 d post-treatment | mean kidney weight versus controls | Both Male and Female | Adult | 10 kidneys/group | Toxicity Factor Datasets | 1 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
ARSENATE, SODIUM | increased @ 100 ppm ( 0.4 ppm, dry wt), 300 ppm (0.8 ppm, dry wt) | accumulation of arsenic in brain tissue (geometric means in parentheses) | Both Male and Female | Juvenile | 30 birds/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BORIC ACID | increase @ 1600 ppm | plasma calcium concentration (6-10% greater than controls) and brain acetylcholinestrase activity (umol/min/g) | Both Male and Female | Juvenile | 10 animals/pen; 3 pens/dose | Toxicity Factor Datasets | 1 d | Laboratory | |
BORIC ACID | 2 ug/g @ control; 4 ug/g @ 100 ppm; 5 ug/g @ 400 ppm; 51 ug/g @ 1600 ppm | boron accumulation in brain (geometric mean; ug/g dry weight) | Both Male and Female | Juvenile | 10 animals/pen; 3 pens/dose | Toxicity Factor Datasets | 1 d | Laboratory | |
BORIC ACID | decrease @ 400 and 1600 ppm | brain ATP (nmol/g) and protein (mg/g) concentrations | Both Male and Female | Juvenile | 10 animals/pen; 3 pens/dose | Toxicity Factor Datasets | 1 d | Laboratory | |
BORIC ACID | 1 ug/g @ controls; 3 ug/g @ 100 ppm; 3 ug/g @ 400 ppm; 29 ug/g @ 1600 ppm | liver boron concentration (geometric mean; ug/g dry weight) | Both Male and Female | Juvenile | 10 animals/pen; 3 pens/dose | Toxicity Factor Datasets | 1 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
EMAMECTIN BENZOATE | no effect | mortality versus controls | Both Male and Female | Adult | 16 pairs/group | Toxicity Factor Datasets | 22 weeks | Laboratory | |
EMAMECTIN BENZOATE | no effect | incidence of signs of toxicity and body weight versus controls | Both Male and Female | Adult | 16 pairs/group | Toxicity Factor Datasets | 22 weeks | Laboratory | |
EMAMECTIN BENZOATE | no effect | feed consumption versus controls | Both Male and Female | Adult | 16 pairs/group | Toxicity Factor Datasets | 22 weeks | Laboratory | |
EMAMECTIN BENZOATE | no effect | microscopic changes to brain, spinal cord, or peripheral nerves versus controls | Both Male and Female | Adult | 16 pairs/group | Toxicity Factor Datasets | 22 weeks | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BORIC ACID, SELENOMETHIONINE | reduced @ 900 ppm B | body weight and growth at 0, 7,and 14 days post-hatch versus controls | Both Male and Female | Juvenile | 14 pairs/treatment | Toxicity Factor Datasets | 1 yr | Laboratory | |
BORIC ACID, SELENOMETHIONINE | reduced @ 7 ppm Se | body weight and weight gain at 7 and 14 days post-hatch versus 3.5 ppm Se group | Both Male and Female | Juvenile | 14 pairs/treatment | Toxicity Factor Datasets | 1 yr | Laboratory | |
BORIC ACID, SELENOMETHIONINE | increased @ 3.5 ppm Se | survival between 7 and 14 days post-hatch versus controls | Both Male and Female | Juvenile | 14 pairs/treatment | Toxicity Factor Datasets | 1 yr | Laboratory | |
BORIC ACID, SELENOMETHIONINE | reduced @ 7 ppm | duckling production versus 3.5 ppm Se group | Both Male and Female | Both Adults and Juveniles | 14 pairs/treatment | Toxicity Factor Datasets | 1 yr | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
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 | Toxicity Factor Datasets | 6 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | decreased with Pb; no effect with Fe or Bi | body weight, gonad weight, hematocrit versus controls | Both Male and Female | Adult | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | increased with Pb; no effect with Fe or Bi | gizzard and kidney weight versus controls | Both Male and Female | Adult | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | decreased with Bi | weight of hatchlings versus controls | Both Male and Female | Juvenile | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no effect with Fe or Bi | survival to 7 d, organ histopathology, hematocrit, sex ratios, kidney or liver weights of ducklings versus controls | Both Male and Female | Juvenile | 18 pairs/group (control, Fe, Bi); 6 pairs/Pb group | Toxicity Factor Datasets | 6-8 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | increased | blood Pb concentrations versus pre-dose controls | Both Male and Female | Adult | 20 per sex | laboratory | Toxicity Factor Datasets | 8 months | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CHLORPYRIFOS | 50.4 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 30 days | Laboratory | |
CHLORPYRIFOS | 83.3 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 6 mos | Laboratory | |
ENDOSULFAN | 27.8 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hours | Laboratory | |
ENDOSULFAN | 6.47 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 7 days | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | no effect | bw versus controls | Both Male and Female | Juvenile | 9-25 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
DIELDRIN | increased @ 10 ppm (liver only), 30 ppm (brain only) | brain and liver weight to body weight ratios versus controls | Both Male and Female | Juvenile | 9-25 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
DIELDRIN | increased@ 4, 10, 30 ppm | hepatic microsomal enzyme activity versus controls | Both Male and Female | Juvenile | 5-15 per group | Toxicity Factor Datasets | 75 days | Laboratory | |
DIELDRIN | increased @ 30 ppm | liver protein concentration versus controls | Both Male and Female | Juvenile | 5-15 per group | Toxicity Factor Datasets | 75 days | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no differences | mean survival times compared among lead, iron and bismuth dosed birds | Both Male and Female | Adult | 5 males, 5 females per group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no differences | mean body weight and organ weights compared among lead, iron and bismuth dosed birds | Both Male and Female | Adult | 5 males, 5 females per group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS, LEAD (elemental) | no differences | mean hematocrit values compared among lead, iron and bismuth dosed birds | Both Male and Female | Adult | 5 males, 5 females per group | Toxicity Factor Datasets | 6-8 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CHLORPYRIFOS | decreased | number of eggs produced, egg weight, eggshell thickness compared to controls | Both Male and Female | Adult | 24 pairs/dose | Toxicity Factor Datasets | 7 and 11 months old | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD (elemental) | no effect | body weight and food consumption versus controls | Both Male and Female | Adult | control=2 F, 4 M; treatment=6 M-F pairs/group | Toxicity Factor Datasets | 6 mos | Laboratory | |
LEAD (elemental) | no effect | incidence of lead poisoning tissue lesions versus controls | Both Male and Female | Adult | control=2 F, 4 M; treatment=6 M-F pairs/group | Toxicity Factor Datasets | 6 mos | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHYLMERCURY DICYANDIAMIDE | no effect | body weight versus controls | Both Male and Female | Adult | 14 pairs/group | Toxicity Factor Datasets | Laboratory | |
METHYLMERCURY DICYANDIAMIDE | increased in 2nd generation | food consumption versus controls | Both Male and Female | Adult | 14 pairs/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
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 | Toxicity Factor Datasets | Laboratory | |
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 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CYANOFENPHOS | increased | incidence of delayed neurotoxicity signs | Both Male and Female | Juvenile | 10 | laboratory | Toxicity Factor Datasets | 1 week | Laboratory |
CYANOFENPHOS | increased (30% @ 10 mg leptophos/kg/d; 10% @ 0.5 mg cyanofenphos/kg/d; 0% @ 1.0 mg cyanofenphos/kg/d; 20% @ 2.0 mg cyanofenphos/kg/d ;60% @ 4.0 mg cyanofenphos/kg/d; 100% @ 8.0 mg cyanofenphos/kg/d | mortality versus controls) | Both Male and Female | Juvenile | 10 | laboratory | Toxicity Factor Datasets | 1 week | Laboratory |
CYANOFENPHOS | decreased @ 2.0, 4.0 mg/kg/d | bw versus controls | Both Male and Female | Juvenile | 10 | laboratory | Toxicity Factor Datasets | 1 week | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
ASULAM | 10% @ 4000 mg/kg | percent mortality after 21 days | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 7 d | Laboratory | |
ASULAM | decreased @ all doses | food consumption compared with controls | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 7 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | increase @ 2-15 ul/egg | percent mortality versus controls | Both Male and Female | Embryo | 100 eggs/dose | Toxicity Factor Datasets | days 2-18 of incubation | Laboratory | |
CRUDE OILS | increase @ 2-15 ul/egg | incidence of survivors with abnormalities versus controls | Both Male and Female | Embryo | 100 eggs/dose | Toxicity Factor Datasets | days 2-18 of incubation | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
NICKEL SULFATE | increased @ 200, 800 ppm | food consumption compared to controls | Both Male and Female | Adult | 6 pairs/group | Toxicity Factor Datasets | Laboratory | |
NICKEL SULFATE | no effects | body wt, liver wt:brain wt, kidney wt:brain wt, duodenal wt compared to controls | Both Male and Female | Adult | 6 pairs/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
METHYLMERCURY CHLORIDE | increased @ 1,3,9,27,90 ug Hg | % abnormal survivors by day 18 of incubation versus controls | Both Male and Female | Embryo | 80 eggs/group | Toxicity Factor Datasets | incubation day 3 | Laboratory | |
METHYLMERCURY CHLORIDE | decreased @ 27, 90 ug Hg | embryo crown to rump length by day 18 of incubation versus controls | Both Male and Female | Embryo | 80 eggs/group | Toxicity Factor Datasets | incubation day 3 | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | increased in all groups dosed with lead shot | incidence of clinical signs, weight loss, breast muscle atrophy | Both Male and Female | Adult | treatment = 10/group control = 5 |
Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | no effect | body weight compared to controls | Both Male and Female | Adult | 20 females, 10 males/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
METHYLMERCURY CHLORIDE, SELENOMETHIONINE | no effect | body weight versus controls | Both Male and Female | Adult | 12/group | Toxicity Factor Datasets | 18 mo | Laboratory |
Peregrine Falcon (Falco peregrinus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
MERCURY (elemental) | 6.90-29.50 ppm, dry wt (females) 12.10 ppm, dry wt (males) |
concentrations measured in primary and rectrix feathers | Both Male and Female | Adult | 20 females, 1 male | Northern Sweden | Toxicity Factor Datasets | SWEDEN |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | productivity = 1.79 - 0.04(DDE) | linear regression of productivity (number of young fledged per site) and DDE concentrations in eggs | Both Male and Female | Adult | 9 eggs | Tasmania | Toxicity Factor Datasets | AUSTRALIA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-), HEPTACHLOR EPOXIDE | 15 ppm DDE, 0.7 ppm heptachlor epoxide | concentrations in eggs associated with population recovery | Both Male and Female | Both Adults and Juveniles | 550 eggs from 469 clutches | Toxicity Factor Datasets | UNITED KINGDOM |
American Kestrel (Falco sparverius)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | Y=1.132 + 0.801X (R^2 = 0.932) | relationship between Se concentrations in diet and blood | Both Male and Female | Adult | 9-10 pairs/group | Toxicity Factor Datasets | Laboratory | |
SELENIUM COMPOUNDS | 7.5 ppm Se, dry wt | maximum observed Se concentration in blood | Both Male and Female | Adult | 10 pairs/group | Toxicity Factor Datasets | Laboratory | |
SELENOMETHIONINE | no effect | incidence of mortality or signs of toxicity | Both Male and Female | Adult | 9-10 pairs/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | decrease at 10, 50 ppm | mean blood delta aminolevulinic acid dehydratase | Both Male and Female | Adult | 16 pairs/dose | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | no effect | mean packed cell volume and red blood cell hemoglobin | Both Male and Female | Adult | 16 pairs/dose | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | increase at 50 ppm 1.3 ppm (1.00 SD) males; 2.4 ppm (1.40 SD) females |
mean lead concentration in liver | Both Male and Female | Adult | 16 pairs/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | no effect | mean organ and carcass weights | Both Male and Female | Adult | 16 pairs/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
LEAD COMPOUNDS | 0.46 ug/g at study area 0.25 ug/g at reference area |
mean lead concentration in blood (wet wt) | Both Male and Female | Adult | 3 (study area) 6 (reference) |
Coeur D'Alene River | Toxicity Factor Datasets |
LEAD COMPOUNDS | decreased | red blood cell delta aminolevulinic acid dehydratase activity (relative to control) | Both Male and Female | Both Adults and Juveniles | 33 | Coeur D'Alene River | Toxicity Factor Datasets |
LEAD COMPOUNDS | decreased | hematocrit | Both Male and Female | Juvenile | 30 | Coeur D'Alene River | Toxicity Factor Datasets |
LEAD COMPOUNDS | decreased | hemoglobin (relative to control) | Both Male and Female | Both Adults and Juveniles | 33 | Coeur D'Alene River | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CRUDE OILS | decreased @ 3.0% | hemoglobin | Both Male and Female | Juvenile | 16/group | Toxicity Factor Datasets | Laboratory | |
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 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DICOFOL | increased @ 5 and 20 mg/kg | incidence of abnormal embyronic gonads | Both Male and Female | Embryo | 10/group | Toxicity Factor Datasets | Laboratory |
Deer Mouse (Peromyscus maniculatus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | decrease | percent vegetation cover (vs control) in study area | Both Male and Female | Both Adults and Juveniles | 285 | Vancouver Island | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | adult sex ratios | Both Male and Female | Both Adults and Juveniles | 285 | Vancouver Island | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | age structure as indicated by number of juveniles trapped | Both Male and Female | Both Adults and Juveniles | 285 | Vancouver Island | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | increase | mean number of foeti in trapped females | Both Male and Female | Both Adults and Juveniles | 285 | Vancouver Island | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|
DIPHACINONE | increase at 0.0025% | Both Male and Female | Not Reported | 10 animals/dose | Toxicity Factor Datasets | Laboratory | |
CHLOROPHACINONE | increase at 0.00125% | Both Male and Female | Not Reported | 10 animals/dose | Toxicity Factor Datasets | Laboratory | |
DIPHACINONE | increase @ 0.00125- 0.02% | Both Male and Female | Not Reported | 10 animals/dose | Toxicity Factor Datasets | Laboratory | |
CHLOROPHACINONE | increase @ 0.00125-0.02% | Both Male and Female | Not Reported | 10 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | no effect | body weight | Both Male and Female | Both Adults and Juveniles | 67 - 138 animals | University of British Columbia Research Forest, Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | no effect | growth rate, estimated by changes in body weight | Both Male and Female | Juvenile | 23 - 55 | University of British Columbia Research Forest, Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
LEAD COMPOUNDS | Bone; 52.10 +/- 33.81SD, Kidney; 8.46 +/- 3.03SE, Liver; 3.29 +/- 1.77SD, Brain; 0.84 +/- 0.25SE, Feces; 153.6+/- 103.5SD ppm (dry weight) | Mean concentrations in deer mice from roadside site (ppm, dry weight). Feces collected from nest box after 1 yr accumulation. Roadside tissue concentrations significantly different from control site. | Both Male and Female | Adult | 9 - 10 animals | Interstate 25, Denver (elev. 1884-2018 m) | Toxicity Factor Datasets |
LEAD COMPOUNDS | significant increase | mortality during winter, estimated by number of mice recaptured the following breeding season at a control and roadside site | Both Male and Female | Adult | 98 - 180 tagged animals | Interstate 25, Denver (elev. 1884-2018 m) | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
CARBOFURAN | no effect | maximum number of young observed per nest (vs. untreated controls) | Both Male and Female | Juvenile | 30 pairs | Saskatchewan | Toxicity Factor Datasets | CANADA |
CARBARYL, CARBOFURAN | no effect | maximum number of young observed per nest (vs. untreated controls) | Both Male and Female | Juvenile | 18 pairs | Saskatchewan | Toxicity Factor Datasets | CANADA |
CARBARYL, CARBOFURAN | no effect | proportion of pairs that raised at least 1 young (vs. untreated controls) | Both Male and Female | Adult | 18 pairs | Saskatchewan | Toxicity Factor Datasets | CANADA |
Double-crested Cormorant (Phalacrocorax auritus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
POLYCHLORINATED BIPHENYLS | decreased compared with reference | hatching success (# hatched/# eggs) | Both Male and Female | Hatchling | 466 and 953 nests (2 yrs) | Spider Is., Lake Michigan | Toxicity Factor Datasets |
POLYCHLORINATED BIPHENYLS | increased compared with reference | proportion of nestlings with bill defects | Both Male and Female | Hatchling | 1,511 and 2,700 chicks (2 yrs) | Spider Is., Lake Michigan | Toxicity Factor Datasets |
Brown Pelican (Pelecanus occidentalis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-) | 8 ug/g | critical threshold of DDE concentration in egg (wet wt basis) associated with 20% eggshell thinning | Both Male and Female | Embryo | 813 eggs | Toxicity Factor Datasets | |
DDE (4,4'-) | 3 ug/g | lowest level of DDE that would result in severely lowered reproductive success | Both Male and Female | Embryo | 156 eggs | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDE (4,4'-) | 3 ug/g | level in eggs associated with impaired reproductive success (successful nests fledged at least one chick) | Both Male and Female | Juvenile | 156 eggs | Toxicity Factor Datasets |
California Sea Lion (Zalophus californianus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | 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 | Toxicity Factor Datasets |
Merriam's Kangaroo Rat (Dipodomys merriami)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHYLPARATHION | no effect | discrimination between seeds and beads | Both Male and Female | Adult | 22 animals | Toxicity Factor Datasets | Laboratory | |
METHYLPARATHION | 18-19 % decrease | brain cholinesterase activity, compared to control | Both Male and Female | Adult | 2 animals | Toxicity Factor Datasets | Laboratory |
Great Horned Owl (Bubo virginianus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | 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 | Toxicity Factor Datasets |
Alameda Song Sparrow (Melospiza melodia ssp. pusillula)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | California Counties | Condition | Lab |
---|---|---|---|---|---|---|---|---|---|---|---|
DIBENZ[A]ANTHRACENE (1,2,5,6-) | 5 | description | Both Male and Female | Adult | sample size | location | Toxicity Factor Datasets | age | Alameda | condition | Laboratory |
Burrowing Owl (Athene cunicularia formerly Speotyto cunicularia)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
STRYCHNINE | no effect | proportion of pairs that raised at least 1 young | Both Male and Female | Adult | 27 pr | Saskatchewan | Toxicity Factor Datasets | CANADA |