Both Male and Female
Pacific Green Turtle (Chelonia mydas)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (2,4'-) | 0.005-0.32 ng/mL | Plasma concentration | Both Male and Female | Juvenile | 20 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
CHLORDANE | ?: not detected, ?: 0.313725 ng/mL | Plasma concentration | Both Male and Female | Juvenile | ?: 12, ?: 13 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO |
MERCURY (elemental) | 0.006 ± 0.002 µg/g ww | Egg concentration | Both Male and Female | Embryo | 29 | Pacific Coast | Toxicity Factor Datasets | PANAMA |
MERCURY (elemental) | 0.002 ± 0.001 µg/g ww | Eggshell concentration | Both Male and Female | Embryo | 48 eggs, 12 nests | Chabahar Beach | Toxicity Factor Datasets | IRAN |
CADMIUM (elemental) | < LOD µg/g ww | Blood concentration | Both Male and Female | Both Adults and Juveniles | 3 | Samanda? & Dörtyol | Toxicity Factor Datasets | TURKEY |
MERCURY (elemental) | 0.03 ± 0.02 µg/g ww | Kidney concentration | Both Male and Female | Both Adults and Juveniles | 3 | Samanda? & Dörtyol | Toxicity Factor Datasets | TURKEY |
SELENIUM (elemental) | 0.46 ± 0.34 µg/g ww | Liver concentration | Both Male and Female | Both Adults and Juveniles | 3 | Samanda? & Dörtyol | Toxicity Factor Datasets | TURKEY |
CADMIUM (elemental) | 0.06 µg/g ww | Blood concentration | Both Male and Female | Juvenile | 42 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
HEXACHLOROCYCLOHEXANE | ?: 0.16160, ?: 1.169761, ?: 0.773151, ?: 0.790514 ng/mL | Plasma concentration | Both Male and Female | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
DDT (4,4'-) | 0.001-0.26 ng/mL | Plasma concentration | Both Male and Female | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
HEPTACHLOR | 2.731588 ng/mL | Plasma concentration | Both Male and Female | Juvenile | 13 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO |
LEAD (elemental) | 0.003 ± 0.002 µg/g ww | Egg concentration | Both Male and Female | Embryo | 11 | Pacific Coast | Toxicity Factor Datasets | PANAMA |
LEAD (elemental) | 0.77 ± 0.20 µg/g ww | Blood concentration | Both Male and Female | Embryo | 48 eggs, 12 nests | Chabahar Beach | Toxicity Factor Datasets | IRAN |
CHROMIUM (elemental) | 0.04 ± 0.03 µg/g ww | Blood concentration | Both Male and Female | Both Adults and Juveniles | 3 | Samanda? & Dörtyol | Toxicity Factor Datasets | TURKEY |
MANGANESE COMPOUNDS | 0.31 ± 0.06 µg/g ww | Kidney concentration | Both Male and Female | Both Adults and Juveniles | 3 | Samanda? & Dörtyol | Toxicity Factor Datasets | TURKEY |
ZINC (elemental) | 4.04 ± 1.85 µg/g ww | Liver concentration | Both Male and Female | Both Adults and Juveniles | 3 | Samanda? & Dörtyol | Toxicity Factor Datasets | TURKEY |
STRONTIUM | 0.28 µg/g ww | Blood concentration | Both Male and Female | Juvenile | 14 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
ALDRIN | 0.957726 ng/mL | Plasma concentration | Both Male and Female | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
DDD (4,4'-) | Not detected | Plasma concentration | Both Male and Female | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
HEPTACHLOR EPOXIDE | 1.844882 ng/mL | Plasma concentration | Both Male and Female | Juvenile | 13 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO |
LEAD (elemental) | 3.31 ± 0.65 µg/g ww | Yolk concentration | Both Male and Female | Embryo | 48 eggs, 12 nests | Chabahar Beach | Toxicity Factor Datasets | IRAN |
ZINC (elemental) | 36.78 ± 3.20 µg/g ww | Blood concentration | Both Male and Female | Embryo | 48 eggs, 12 nests | Chabahar Beach | Toxicity Factor Datasets | IRAN |
COPPER (elemental) | 1.92 ± 1.69 µg/g ww | Blood concentration | Both Male and Female | Both Adults and Juveniles | 3 | Samanda? & Dörtyol | Toxicity Factor Datasets | TURKEY |
NICKEL (elemental) | 3.31 ± 1.69 µg/g ww | Kidney concentration | Both Male and Female | Both Adults and Juveniles | 3 | Samanda? & Dörtyol | Toxicity Factor Datasets | TURKEY |
IRON (elemental) | 343.57 µg/g ww | Blood concentration | Both Male and Female | Juvenile | 42 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
ENDRIN | 1.064513 ng/mL | Plasma concentration | Both Male and Female | Juvenile | 38 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
DDE (4,4'-) | Not detected | Plasma concentration | Both Male and Female | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
DDD (2,4'-) | Not detected | Plasma concentration | Both Male and Female | Juvenile | 1 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO |
ZINC (elemental) | 33.88 ± 2.65 µg/g ww | Yolk concentration | Both Male and Female | Embryo | 48 eggs, 12 nests | Chabahar Beach | Toxicity Factor Datasets | IRAN |
COPPER (elemental) | 2.01 ± 0.23 µg/g ww | Blood concentration | Both Male and Female | Embryo | 48 eggs, 12 nests | Chabahar Beach | Toxicity Factor Datasets | IRAN |
IRON (elemental) | 4.74 ± 1.12 µg/g ww | Blood concentration | Both Male and Female | Both Adults and Juveniles | 3 | Samanda? & Dörtyol | Toxicity Factor Datasets | TURKEY |
LEAD (elemental) | 0.03 ± 0.01 µg/g ww | Kidney concentration | Both Male and Female | Both Adults and Juveniles | 3 | Samanda? & Dörtyol | Toxicity Factor Datasets | TURKEY |
Snowy Egret (Egretta thula)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
MERCURY (elemental) | 0.81 ± 0.50 µg/g dw | Feather concentration | Both Male and Female | Nestling | 10 | Georgia & South Carolina | Toxicity Factor Datasets | USA |
Bullfrog (Lithobates catesbeianus formerly Rana catesbeiana)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | Both Male and Female | Adult | 5 animals/group | Toxicity Factor Datasets | Laboratory | ||
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | histopathological changes in liver, kidney, lung, heart and gonads | Both Male and Female | Adult | 5 animals/group | Toxicity Factor Datasets | Laboratory |
American Kestrel (Falco sparverius)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | decrease at 125, 625 mg/kg bw (71-79%) | kidney delta aminolevulinic acid dehydratase activity | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | decrease at 125, 625 mg/kg bw (20-25%) | liver delta aminolevulinic acid dehydratase activity | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
CARBOFURAN | 0.6 mg/kg bw (0.5-1.0 95% CI) | LD50 | Both Male and Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory | |
MONOCROTOPHOS | 1.5 mg/kg bw | LD50 | Both Male and Female | Adult | 5/group | Toxicity Factor Datasets | Laboratory | |
EPN | 68% (10.0 SD) | mean brain cholinesterase depression (relative to control) in birds that died in 8 hrs post-dose | Both Male and Female | Adult | 12 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
AROCLOR 1254, POLYCHLORINATED DIBENZO-P-DIOXINS | increased @ 0.5, 5 ppm | in vitro microsomal breakdown of oestradiol | Both Male and Female | Adult | 4/group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1262, POLYCHLORINATED DIBENZO-P-DIOXINS | increased @ 0.5, 5 ppm | in vitro microsomal breakdown of oestradiol | Both Male and Female | Adult | 4/group | Toxicity Factor Datasets | Laboratory | |
AROCLOR 1254, POLYCHLORINATED DIBENZO-P-DIOXINS | increased @ 5 ppm | amount of liver cytoplasmic RNA | Both Male and Female | Adult | 4/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | no effect | percent of pairs that laid eggs, number of fertile pairs and egg hatchability versus controls | Both Male and Female | Adult | 15 pairs/treatment group; 10 control pairs | Toxicity Factor Datasets | Laboratory | |
SELENOMETHIONINE | no effect | egg mass, width, length, and volume versus controls | Both Male and Female | Adult | 15 pairs/treatment group; 10 control pairs | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHYLPARATHION | increased at 2, 3 mg/kg bw | abnormal posture, ataxia, paresis | Both Male and Female | Adult | 5/dose | Toxicity Factor Datasets | Laboratory | |
METHYLPARATHION | increase at 3 mg/kg bw | mortality rate 2 hr post-dose | Both Male and Female | Adult | 5/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|
LEAD (elemental) | 40% at 625 mg/kg bw | Both Male and Female | Nestling | 10/group | Toxicity Factor Datasets | Laboratory |
Mourning Dove (Zenaida macroura)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
MEXACARBATE | 2.83 mg/kg | LD50 | Both Male and Female | Not Reported | 8 | Toxicity Factor Datasets | 3 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
LEAD (elemental) | increased at all doses | lead concentrations in blood | Both Male and Female | Adult | 10 birds/dose | Toxicity Factor Datasets | Laboratory | |
LEAD (elemental) | decreased at all doses | delta-aminolevulinic acid dehydratase (ALAD)activity in blood | Both Male and Female | Adult | 10 birds/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Condition | Lab |
---|---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | increased at 10, 40 ppm | length of courtship period | Both Male and Female | Adult | 8/group | Toxicity Factor Datasets | breeding | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
CESIUM COMPOUNDS | 0.24 (0.027 SE) Bq/g, wet weight (whole body) 0.30 (0.036 SE) Bq/g, wet weight (muscle) |
whole body and muscle concentrations of 137Cesium | Both Male and Female | Both Adults and Juveniles | 27 doves | Par Pond reservoir system, Savannah River Site | Toxicity Factor Datasets |
Deer Mouse (Peromyscus maniculatus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | no effect | population density (decreases) | Both Male and Female | Both Adults and Juveniles | Not Reported | 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 | Countries |
---|---|---|---|---|---|---|---|---|
CADMIUM COMPOUNDS, COPPER COMPOUNDS, ZINC COMPOUNDS | Diet:Soil; 128.0 (Cd), 1.31 (Cu), 1.87 (Zn). Liver:Soil; 35.3 (Cd), 0.17 (Cu), 1.25 (Zn). Liver:Diet; 0.27 (Cd), 0.12 (Cu), 0.66 (Zn). | Ratio of metal concentrations (ug/g dry weight) in diet:soil, liver:soil and liver:diet at an abandoned mine site. Diet concentrations measured from stomach contents. Soil based on acid extractable concentrations. Soil copper; liver cadmium, copper an | Both Male and Female | Adult | 6-9 soil or tissue samples/site | Blue Grouse Mountain Copper Mine, Honeymoon Bay, Vancouver Island, British Columbia | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
TERBUFOS | increase @ 1.69 and 2.48 mg/kg | Both Male and Female | Not Reported | 70 animals/dose | Toxicity Factor Datasets | Laboratory | ||
TERBUFOS | decrease at 1.69 and 2.48 mg/kg | brain cholinesterase activity | Both Male and Female | Not Reported | 70 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | no effect | population density, compared to control site | Both Male and Female | Both Adults and Juveniles | 13 trapping periods | Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
GLYPHOSATE | increase | % of trapped males and females in breeding condition, compared to control site | Both Male and Female | Adult | 24 - 62 animals | Maple Ridge, British Columbia | Toxicity Factor Datasets | CANADA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
GLYPHOSATE | decrease | number of hardwood trees in study area | Both Male and Female | Both Adults and Juveniles | 1 study area | Maple Ridge, BC | Toxicity Factor Datasets | CANADA |
Pallid Bat (Antrozous pallidus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | 5.8 ppm; range, 3.6-8.2 ppm (wet wt) | mean and range of concentration in carcass, wet wt | Both Male and Female | Adult | 4 bats | near cities | Toxicity Factor Datasets | MEXICO |
DDD (4,4'-) | 0.1 ppm; range, <0.1-0.3 ppm (wet wt) | mean and range of concentration in carcass, wet wt | Both Male and Female | Adult | 4 bats | near cities | Toxicity Factor Datasets | MEXICO |
DDT (4,4'-) | 1.8 ppm; range, 0.6-3.8 ppm (wet wt) | mean and range of concentration in carcass, wet wt | Both Male and Female | Adult | 4 bats | near cities | Toxicity Factor Datasets | MEXICO |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PARATHION | decrease | eggshell thickness, compared to controls | Both Male and Female | Adult | 5 trios (2F, 1M)/dose | Toxicity Factor Datasets | Laboratory | |
PARATHION | no effect | progeny growth (average body weights) at hatch to 6 wks of age | Both Male and Female | Juvenile | 5 trios (2F, 1M adults)/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEPTOPHOS | 5/5 @ 260 ppm | incidence of ataxia | Both Male and Female | Juvenile | 3-5/group | Toxicity Factor Datasets | 14 d | Laboratory | |
LEPTOPHOS | 4/5 @ 260 ppm | incidence of CNS lesions | Both Male and Female | Juvenile | 3-5/group | Toxicity Factor Datasets | 14 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | increase @ 0.025 - 5% | pathological release of ornithine carbamyltransferase from kidney | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 0-8 wks post-hatch | Laboratory | |
CRUDE OILS | increase @ 5% | incidence of degeneration of kidney tubules | Both Male and Female | Juvenile | 10/dose | Toxicity Factor Datasets | 0-8 wks post-hatch | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
ARSENATE, SODIUM | no effect | survival rate versus controls | Both Male and Female | Juvenile | 30 birds/group | Toxicity Factor Datasets | Laboratory | |
ARSENATE, SODIUM | no effect | incidence of histopathological lesions, and liver, brain, and spleen weights | Both Male and Female | Juvenile | 30 birds/group | Toxicity Factor Datasets | Laboratory | |
ARSENATE, SODIUM | increased @ 300 ppm | plasma biochemistry changes versus controls | 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 |
---|---|---|---|---|---|---|---|---|---|
NICKEL SULFATE | no effect | organ wt:body wt ratios | Both Male and Female | Juvenile | 36 birds/dose | Toxicity Factor Datasets | 14 d | Laboratory | |
NICKEL SULFATE | 1.0-22.7 (liver), 2.7-74.4 (kidney) ppm, wet wt | Ni concentrations (ranges) in liver and kidney in ducklings that died @ 1200 ppm | Both Male and Female | Juvenile | 36 birds/dose | Toxicity Factor Datasets | 14 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CARBOFURAN | 0.370 (0.283-0.484), 0.628 (0.530-0.744), 0.510 (0.410-0.635), 0.415 (0.333-0.516) | LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hr, 7 d, 30 d, or 6 mos | Laboratory | |
PARATHION | 1.65 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hours | Laboratory | |
DEMETON | 13.3 (11.0-16.2), 15.3 (12.9-18.1), 15.1 (12.0-19.0), 8.19 (6.58-10.2) | LD50's determined at ages 36 hr, 7 d, 30 d, and 6 mos, respectively (95% CI in parenth.) | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hr, 7 d, 30 d, or 6 mos | Laboratory | |
PARATHION | 1.44 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 |
---|---|---|---|---|---|---|---|---|---|
DDE (4,4'-) | no effect | nasal gland and kidney Na-K-ATPase activity, following exposure to 100% seawater | Both Male and Female | Juvenile | 4-5 | Toxicity Factor Datasets | 3-5 mo | Laboratory | |
DDE (4,4'-) | no effect | body weight or plasma electrolyte levels | Both Male and Female | Juvenile | 4 | Toxicity Factor Datasets | 3-5 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | decrease @ 1, 5, 10 ul | 18-d % survival, mean embryonic weight, crown-rump length (5ul) and bill length | Both Male and Female | Embryo | 50/dose | Toxicity Factor Datasets | 1d of development | Laboratory | |
CRUDE OILS | increase @ 1, 5 ul | % abnormal survivors, compared to controls | Both Male and Female | Embryo | 50/dose | Toxicity Factor Datasets | 1d of development | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PHOSPHORUS (YELLOW OR WHITE) | 91.1 ug/g | No Observable Effect Level, based on mortality, pathology, clinical signs | Both Male and Female | Adult | 5 males, 5 females/dose | Toxicity Factor Datasets | Laboratory | |
PHOSPHORUS (YELLOW OR WHITE) | 679.8 ug/g (194.3-442.6 95% CI ) | LC50 | Both Male and Female | Adult | 5 males, 5 females/dose | Toxicity Factor Datasets | 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 versus controls | Both Male and Female | Adult | 14 pairs/treatment | Toxicity Factor Datasets | 1 yr | Laboratory | |
BORIC ACID, SELENOMETHIONINE | no effect | onset of egg laying, eggshell thickness, frequency of embryo deformities versus controls | 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 | reduced for lead shot | body weight versus all other groups | Both Male and Female | Adult | 16/treatment | Toxicity Factor Datasets | 6 mo | Laboratory | |
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 | 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 | no effect | mortality versus controls | Both Male and Female | Adult | 20 males, 20 females per group | Toxicity Factor Datasets | 6-8 mo | Laboratory | |
BISMUTH COMPOUNDS, IRON COMPOUNDS | no effect | body weight, organ weights (liver, kidney, gonads, gizzard) or hematocrit versus controls | Both Male and Female | Adult | 20 males, 20 females per group | Toxicity Factor Datasets | 6-8 mo | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SELENOMETHIONINE | liver: 18.7 d muscle: 30.1 d |
half life of selenium in tissues | Both Male and Female | Adult | 3 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CRUDE OILS | decreased @ 5 uL/egg | embryonic weight (females) and crown rump length (both sexes) | Both Male and Female | Hatchling | 65 eggs/group | Toxicity Factor Datasets | 3 days | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
AROCLOR 1254 | significant effect | PCB treatment altered the shape of the body weight growth curve but not the asymptotic weight | Both Male and Female | Juvenile | 15/dose | Toxicity Factor Datasets | 1d at initiation | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DIISOPROPYL METHYLPHOSPHONATE | decrease | mean blood pressure, compared to baseline prior to exposure | Both Male and Female | Adult | 12 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
CADMIUM CHLORIDE | no effect | mortality versus controls | Both Male and Female | Adult | 20 pairs/group | Toxicity Factor Datasets | 1 yr | Laboratory |
Coyote (Canis latrans)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
DIPHACINONE | 0.6 [0.3 - 1.2 (95% CL)] mg/kg | LD50 | Both Male and Female | Adult | 2/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LITHIUM CHLORIDE | decrease @ 18g/1500 g/d | body weight gain in nursing pups of mothers fed LiCl contaminated diet | Both Male and Female | Both Adults and Juveniles | 4 pups/2 adults | Toxicity Factor Datasets | 10-19d | Laboratory |
Southern Sea Otter (Enhydra lutris ssp. nereis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
TIN, BUTYL | increase | otters that died of infectious disease contained butyltin liver concentrations greater than those that died of trauma | Both Male and Female | Adult | 8-14 animals | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
DDD (4,4'-), DDE (4,4'-), DDT (4,4'-) | increase | otters that died from infectious diseases contained higher liver DDTs concentrations that those that died of trauma | Both Male and Female | Adult | 4-8 | Toxicity Factor Datasets |
Loggerhead Shrike (Lanius ludovicianus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
AMMONIUM NITRATE | significantly increased (138.5% +/- 86.1 SD) | percent increase in breeding territory size post-spray vs. unsprayed controls | Both Male and Female | Both Adults and Juveniles | 4 control, 8 treatment territories | MacArthur Agroecology Research Center, Archbold Biological Station | Toxicity Factor Datasets |