Amphibians
Western Toad (Anaxyrus boreas)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 41.4 (1.9) - 59.3 (2.4) | Nonhibernated females, age range 2-5 y | g (± SEM) | F | Adult | 32 | Center for Conservation and Research of Endangered Wildlife, Cincinnati Zoo & Botanical Garden |
Exposure Factor Datasets | Lab | Nonhibernated | USA |
Ensatina (Ensatina eschscholtzii)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|---|
Population Density | See citation Table 1 | 21-150 ha | Individuals captured | NR | Not Reported | 2420 | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Population Density | 33 | >30 ha area | Individuals captured | NR | Not Reported | Pierce County, Washington | Exposure Factor Datasets | USA |
Population Density | 12 | >30 ha area | Individuals captured | NR | Not Reported | Pierce County, Washington | Exposure Factor Datasets | USA |
Population Density | 34 | >30 ha area | Individuals captured | NR | Not Reported | Pierce County, Washington | Exposure Factor Datasets | USA |
Population Density | 137 | >30 ha area | Individuals captured | NR | Not Reported | Pierce County, Washington | Exposure Factor Datasets | USA |
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | See citation | F | Adult | 19 | Exposure Factor Datasets | Lab | Gravid | USA |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Population Density | See citation | 46 ha | Individuals captured | NR | Not Reported | Green Peak forest, Benton County, N 44.3667, W 123.4583 |
Exposure Factor Datasets | USA |
California Giant Salamander (Dicamptodon ensatus)
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|
Population Density | 28 | Removed drainage culvert; 2.1 m wide x 1.4 m high x 12.2 m long | Individuals captured | B | Adult | Estero Road, Point Reyes National Seashore | Exposure Factor Datasets | Marin | USA |
Population Density | 45 | Removed drainage culvert; 1.2 m diameter x 12.2 m long | Individuals captured | B | Adult | Glenbrook Creek, Point Reyes National Seashore | Exposure Factor Datasets | Marin | USA |
Bullfrog (Lithobates catesbeianus)
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Frequencies of occurrence: Terrestrial prey (86.96 %) Aquatic prey (28.26 %) Amphibious prey (30.43 %) Arthropod remains (21.74 %), Undetermined remains (15.22 %) | Frequency of occurrence | M | Adult | 46 | 20⁰45'S, 42⁰07'W | Exposure Factor Datasets | NR | NR | BRAZIL |
Dietary Composition | Frequencies of occurrence: Terrestrial prey (63.64 %) Aquatic prey (39.39 %) Amphibious prey (33.33 %) Arthropod remains (21.21 %), Undetermined remains (9.09 %) | Frequency of occurrence | F | Adult | 33 | 20⁰45'S, 42⁰07'W | Exposure Factor Datasets | NR | NR | BRAZIL |
Dietary Composition | Frequencies of occurrence: Terrestrial prey (79.41 %) Aquatic prey (26.47 %) Amphibious prey (3.26 %) Arthropod remains (20.59 %), Undetermined remains (11.76 %) | Frequency of occurrence | NR | Juvenile | 34 | 20⁰45'S, 42⁰07'W | Exposure Factor Datasets | NR | NR | BRAZIL |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Table 1 | Frequency of occurrence | NR | Juvenile | 21 | Caohai: 27°42' N 100°51' E | Exposure Factor Datasets | CHINA |
Dietary Composition | See citation Table 1 | Frequency of occurrence | M | Adult | 40 | Shiping: 23°42' N 102°28' E | Exposure Factor Datasets | CHINA |
Dietary Composition | See citation Table 1 | Frequency of occurrence | F | Adult | 37 | Shiping: 23°42' N 102°28' E | Exposure Factor Datasets | CHINA |
Dietary Composition | See citation Table 1 | Frequency of occurrence | NR | Juvenile | 24 | Shiping: 23°42' N 102°28' E | Exposure Factor Datasets | CHINA |
Dietary Composition | See citation Table 1 | Frequency of occurrence | M | Adult | 47 | Caohai: 27°42' N 100°51' E | Exposure Factor Datasets | CHINA |
Dietary Composition | See citation Table 1 | Frequency of occurrence | F | Adult | 45 | Caohai: 27°42' N 100°51' E | Exposure Factor Datasets | CHINA |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Condition | Countries |
---|---|---|---|---|---|---|---|---|---|---|
Dietary Composition | See Table 1 in citation | Frequency of occurrence | B | Both Adults and Juveniles | 21 males, 14 females, 159 juveniles | Kyoto | Exposure Factor Datasets | NR | NR | JAPAN |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Countries |
---|---|---|---|---|---|---|---|---|---|
Dietary Composition | Annelida (4.60), Arachnida (18.80), Crustacea (3.80), Insecta 54.80), Mollusca (0.40), Myriapoda (3.80), Anura (11.30), Osteichthyes (2.50) | Precentage of occurrence | B | Both Adults and Juveniles | 181 | 25°18’47"S, 48°58’07"W; 25°17’09"S, 49°00’05"W; 25°14’21"S, 49°02’10"W | Exposure Factor Datasets | 173 adults, 8 young females | BRAZIL |
Location | Type | Countries |
---|---|---|
25⁰14'21''S, 49⁰02'10''W, 25⁰17'09''S, 49⁰00'05''W, 25⁰18'47''S, 48⁰58'07''W |
Exposure Factor Datasets | BRAZIL |
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Table 1 for percentage of occurrence frequency of 15 prey items | B | Both Adults and Juveniles | 64 | Between 31⁰47'47.23"N, 116°30'04.02"W and between 31°47'55.46"N, 116°29'17.39"W | Exposure Factor Datasets | NR | MEXICO |
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Countries |
---|---|---|---|---|---|---|---|---|
Dietary Composition | See citation Table 2 for number of prey | B | Adult | 82 | 31.2515°S, 69.4417°W | Exposure Factor Datasets | NR | ARGENTINA |
Dietary Composition | See citation Table 2 for number of prey | B | Juvenile | 87 | 31.2515°S, 69.4417°W | Exposure Factor Datasets | NR | ARGENTINA |
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
Age at Sexual Maturity | See citation Table II | B | Both Adults and Juveniles | 50 | Vancouver Island | Exposure Factor Datasets | CANADA |
Age at Sexual Maturity | See citation Table II | B | Both Adults and Juveniles | 241 | 3 populations in France: Gironde Gabauds, Loir et Cher, Perigord Limousin |
Exposure Factor Datasets | FRANCE |
Bullfrog (Lithobates catesbeianus formerly Rana catesbeiana)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Lab |
---|---|---|---|---|---|---|---|---|---|
METHYLPARATHION | 79.5 | in loco heart rate | Not Reported | Tadpole | 36 | NR | Toxicity Factor Datasets | BRAZIL | Laboratory |
PENOXSULAM | 7.52 mg/L | LC50 | Not Reported | Tadpole | 6 | Experimental Frog Farm, São Paulo | Toxicity Factor Datasets | BRAZIL | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | Not Reported | Tadpole | 15 animals/group | Toxicity Factor Datasets | Taylor-Kollros stages I-VII | Laboratory | ||
TETRACHLORODIBENZO-P-DIOXIN (2,3,7,8-) | no effect | incidence of morphological abnormalities | Not Reported | Tadpole | 15 animals/group | Toxicity Factor Datasets | Taylor-Kollros stages I-VII | Laboratory | |
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 |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|
SULFURIC ACID | significant increase at pH 3.5 and 4.0 | Not Reported | Tadpole | 120 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 34.4 ug/l (95% CL: 31.1 - 38.1 ug/l) | LC50 | Not Reported | Embryo | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | embryo-larvae, 11d | Laboratory | |
DIELDRIN | 0.5 ug/g at 12.3 ug/l | whole body dieldrin concentration (ug/g, wet wt.) at the NOAEL | Not Reported | Tadpole | Not Reported | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 25.1 ug/l | LOAEL, based on mortality but gross spinal deformities also observed | Not Reported | Embryo | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | embryo-larvae, 11d | Laboratory | |
DIELDRIN | 360 - 900 | range of bioconcentration factors; calculated by dividing the whole body tissue dieldrin concentration by water dieldrin concentration | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 11.0 ug/l | NOAEL | Not Reported | Embryo | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | embryo-larvae, 11d | Laboratory | |
DIELDRIN | 36,000 - 90,000 | range of lipid bioconcentration factors; calculated by dividing the whole body bioconcentration values x 100 by percent lipid | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 8.7 ug/l (95% CL: 7.8-9.7 ug/l) | LC50 | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 50 d | Laboratory | |
DIELDRIN | 11.2 ug/l | LOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 50 d | Laboratory | |
DIELDRIN | 4.0 ug/l | NOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 50 d | Laboratory | |
DIELDRIN | 5.1 ug/g at 8.7 ug/l | whole body dieldrin concentration (ug/g, wet wt.) at the LC50 | Not Reported | Tadpole | Not Reported | Toxicity Factor Datasets | 50 d | Laboratory | |
DIELDRIN | 6.0 ug/g at 11.2 ug/l | whole body dieldrin concentration (ug/g, wet wt.) | Not Reported | Tadpole | Not Reported | Toxicity Factor Datasets | 50 d | Laboratory | |
DIELDRIN | 2.0 ug/g at 4.0 ug/l | whole body dieldrin concentration (ug/g, wet wt.) | Not Reported | Tadpole | Not Reported | Toxicity Factor Datasets | 50 d | Laboratory | |
DIELDRIN | 360 - 540 | range of bioconcentration factors; calculated by dividing the whole body tissue dieldrin concentration by water dieldrin concentration | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 50 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIURON | 12.7 mg/l (95% CI; 9.8 - 16.4) | 21 d LC50 | Not Reported | Tadpole | 5/replicate; 3 replicates/dose | Toxicity Factor Datasets | 15 mo | Laboratory | |
DIURON | 7.6 mg/l | lowest NOAEL based on body weight endpoint | Not Reported | Tadpole | 5/replicate; 3 replicates/dose | Toxicity Factor Datasets | 15 mo | Laboratory |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|
PARATHION | no effect | Not Reported | Tadpole | 30 animals/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
TOXAPHENE (POLYCHLORINATED CAMPHENES) | 99 ug/l (95% CL: 71-116 ug/l) | LC50 | Not Reported | Tadpole | 220 animals | Toxicity Factor Datasets | Laboratory | |
ENDRIN | 2 ug/l (95% CL: 1-5 ug/l) | LC50 | Not Reported | Tadpole | 220 animals | Toxicity Factor Datasets | Laboratory | |
TOXAPHENE (POLYCHLORINATED CAMPHENES) | 312 ug/l (95% CL: 225-435 ug/l) | EC50; Loss of equilibrium | Not Reported | Tadpole | 220 animals | Toxicity Factor Datasets | Laboratory | |
ENDRIN | > 40 ug/l | EC50; Loss of equilibrium | Not Reported | Tadpole | 220 animals | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|---|
MERCURIC CHLORIDE | 63.36 | 96 hour LC50 (95% Confidence Interval); based on measured concentrations | ug Hg/L | Not Reported | Not Reported | 10/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
LEAD NITRATE | no effect | preference/avoidance behavior and spontaneous locomotor activity | Not Reported | Tadpole | 8 animals/dose | Toxicity Factor Datasets | premetamorphic | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|---|
ARSENIC COMPOUNDS, CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, SELENIUM COMPOUNDS | increase at contaminated, relative to reference site | resting oxygen consumption at 25C, measured in the lab | ml O2/hr/tadpole | Not Reported | Tadpole | 8-11 | Savannah River | Toxicity Factor Datasets | 80 d |
ARSENIC COMPOUNDS, CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, SELENIUM COMPOUNDS | decrease at contaminated, compared to reference site | % survival to 80 d posthatching | % | Not Reported | Tadpole | Not Reported | Savannah River | Toxicity Factor Datasets | 80 d |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
FENITROTHION | no effect | hatching success | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | embryo; midneurulation stage | Laboratory | |
FENITROTHION | no effect | avoidance response assessed by daily prodding of newly hatched tadpoles | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | embryo; midneurulation stage | Laboratory | |
TRICLOPYR | no effect | hatching success | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | embryo; midneurulation stage | Laboratory | |
TRICLOPYR | no effect | avoidance response assessed by daily prodding of newly hatched tadpoles | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | embryo; midneurulation stage | Laboratory | |
HEXAZINONE | no effect | hatching success | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | embryo; midneurulation stage | Laboratory | |
HEXAZINONE | no effect | Not Reported | Tadpole | 10 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | 1-2 d after hatching | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
MEXACARBATE | 283 - 800 mg/kg | LD50, estimated | Male | Not Reported | 14 | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
HEPTACHLOR | increase at 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
ENDOSULFAN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
CHLORDANE | no effect | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
CHLORDECONE (KEPONE) | no effect | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
CHLORDANE | increase at 0.5 lb/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
DDT (Technical Grade Mixture) | increase at 1.0 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
ENDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
PERMETHRIN | 7,033 ug/l (95% CL: 4,129-8,735 ug/l) | LC50 | Not Reported | Tadpole | 10 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
TRIFLUOROMETHYL-4-NITROPHENOL (3-, LAMPRECIDE) | 11.62 mg/kg bw (95% CL: 10.71-13.14) | LD50 | Not Reported | Tadpole | 5 | Toxicity Factor Datasets | Gossner stages 33-38 | Laboratory |
Western Toad (Anaxyrus boreas formerly Bufo boreas)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
FENTHION | decrease @ 60 ppb | temperature tolerance, estimated by heating water at 1C/3min and using onset of spasms in frogs as the endpoint | Not Reported | Juvenile | 10 animals/replicate; 2 replicates/dose | Toxicity Factor Datasets | Laboratory | |
CHLORPYRIFOS | decrease @ 30 and 60 ppb | temperature tolerance, estimated by heating water at 1C/3min and using onset of spasms in frogs as the endpoint | Not Reported | Juvenile | 10 animals/replicate; 2 replicates/dose | Toxicity Factor Datasets | Laboratory | |
METHYLPARATHION | decrease @ 25 and 50 ppb | temperature tolerance, estimated by heating water at 1C/3min and using onset of spasms in frogs as the endpoint | Not Reported | Juvenile | 10 animals/replicate; 2 replicates/dose | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
ZINC SULFATE | increase @ 39 mg/l | 100% mortality reported | Not Reported | Juvenile | 5-25/dose | Toxicity Factor Datasets | larvae | Laboratory | |
COPPER SULFATE | increase @ 3.7 mg/l | 100% mortality reported | Not Reported | Juvenile | 5-25/dose | Toxicity Factor Datasets | larvae | Laboratory | |
IRON SULFATE | increase @ 30-288 mg/l | Not Reported | Juvenile | 5-25/dose | Toxicity Factor Datasets | larvae | Laboratory |
Pacific Treefrog (Pseudacris regilla formerly Hyla regilla)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
AZINPHOS-METHYL (GUTHION) | 1.78 mg/l | NOAEL | Not Reported | Tadpole | 10 tadpoles/replicate; 2 replicates/dose; 5 doses | Toxicity Factor Datasets | 3 wk | Laboratory | |
AZINPHOS-METHYL (GUTHION) | 9.67 mg/l | LOAEL | Not Reported | Tadpole | 10 tadpoles/replicate; 2 replicates/dose; 5 doses | Toxicity Factor Datasets | 3 wk | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIURON | 15.2 mg/l | 14-d LC50 value; mean of 2 tests | Not Reported | Tadpole | 8/replicate; 3 replicates/dose | Toxicity Factor Datasets | 12 - 24 d | Laboratory | |
DIURON | 14.5 mg/l | lowest NOAEL based on body length/weight endpoints | Not Reported | Tadpole | 8/replicate; 3 replicates/dose | Toxicity Factor Datasets | 12 - 24 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
---|---|---|---|---|---|---|---|---|---|---|
AMMONIUM NITRATE | 25.0 | 10-d LC50 value for embryos | mg/L as NH4-N | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | 21.9-28.7 (95% CI) | Laboratory | |
AMMONIUM NITRATE | 6.9 | LOAEL for body weight and length | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | Laboratory | ||
AMMONIUM NITRATE | 3.3 | NOAEL for body weight and length | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | Laboratory | ||
AMMONIUM CHLORIDE | 30.3 | 10-d LC50 for embryos | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | 27.0 - 33.4 (95% CI) | Laboratory | |
AMMONIUM CHLORIDE | 24.9 | LOAEL for body weight and length and deformities | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | Laboratory | ||
AMMONIUM CHLORIDE | 12.8 | NOAEL for body weight and length and deformities | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | Laboratory |
Pacific Giant Salamander (Dicamptodon tenebrosus), Ensatina (Ensatina eschscholtzii)
Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
no effect | capture rates between logged and burned units and the logged, burned and sprayed units during the year after spraying | Not Reported | Not Reported | 3 units/treatment | Oregon Coast Range | Toxicity Factor Datasets |
no effect | capture rates between logged and burned units and the logged, burned and sprayed units during the year after spraying | Not Reported | Not Reported | 3 units/treatment | Oregon Coast Range | Toxicity Factor Datasets |
Long-toed Salamander (Ambystoma macrodactylum)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
METHOXYCHLOR | no appreciable mortality | embryo and larvae (10 d post-hatch) mortality | Not Reported | Embryo, Juvenile | 30-34 eggs/dose | Toxicity Factor Datasets | Laboratory | |
METHOXYCHLOR | decrease @ 0.1, 0.3, 1, 3, 10 mg/L | mean day of hatch, compared to controls | Not Reported | Embryo, Juvenile | 30-34 eggs/dose | Toxicity Factor Datasets | Laboratory | |
METHOXYCHLOR | decrease @ 0.3, 1, 3, 10 mg/l | responsiveness to startle and distance travelled post-startle in larvae | Not Reported | Juvenile | 30-34 eggs exposed/dose; 14-27 larvae tested/dose | Toxicity Factor Datasets | Laboratory | |
METHOXYCHLOR | decrease @ 0.3 and 10 mg/L | mean body weight of larvae | Not Reported | Embryo, Juvenile | 30-38 eggs/dose | Toxicity Factor Datasets | Laboratory |
California Newt (Taricha torosa)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
CHLORDANE | 8,906 ppb, range; 4,954 - 15, 609 ppb | mean and range of total technical chlordane residues in newt carcasses (without liver and stomach) 14 days after application | Both Male and Female | Both Adults and Juveniles | 4 | Toxicity Factor Datasets | CANADA | |
CHLORDANE | 2,116 ppb, range; 1,354 - 3,783 ppb | mean and range of total technical chlordane residues in newt carcasses (without liver and stomach) 451 days after application | Both Male and Female | Both Adults and Juveniles | 6 | Toxicity Factor Datasets | CANADA | |
CHLORDANE | 176 ppb, range; 29 - 272 ppb | mean and range of total technical chlordane residues in newt carcasses (without liver and stomach) 1036 days after application | Both Male and Female | Both Adults and Juveniles | 8 | Toxicity Factor Datasets | CANADA |
Northern Red-legged Frog (Rana aurora) formerly Rana aurora ssp. aurora
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIURON | 22.2 mg/l (95% CI; 19.8 - 25.0) | 14 d LC50 | Not Reported | Tadpole | 5/replicate; 3 replicates/dose | Toxicity Factor Datasets | 7 d | Laboratory |