Amphibians
Bullfrog (Lithobates catesbeianus formerly Rana catesbeiana)
| 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 | 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 |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | See paper for weight to developmental stage relationship (Gosner stages 27-40) | g | Not Reported | Tadpole | 120 | Crane Pond, E.S. George Reserve, Livingston County [lat., 42.5N] | Exposure Factor Datasets | |
| Age at Fledging, Metamorphosis, Weaning | Referred to as "age at transformation"; range of snout-vent length at transformation = 35-57 mm | mo | Not Reported | Tadpole | 1051 | Crane Pond, E.S. George Reserve, Livingston County [lat., 42.5N] | Exposure Factor Datasets | |
| Time of Fledging or Metamorphosis | July - Sept. | Not Reported | Tadpole | Not Reported | Crane Pond, E.S. George Reserve, Livingston County [lat., 42.5N] | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Population Density | #/m2 | Not Reported | Tadpole | 3 sampling periods, 20,000 animals | Coldstream Pond and Fred Pond, northeast of Lexington, [38o06'23"N, 84o30'08"W] | Exposure Factor Datasets | ||
| Time of Fledging or Metamorphosis | July - Sept. | Not Reported | Tadpole | Not Reported | Coldstream Pond and Fred Pond, northeast of Lexington, [38o06'23"N, 84o30'08"W] | Exposure Factor Datasets | ||
| Age at Fledging, Metamorphosis, Weaning | 1 | yr | Not Reported | Tadpole | Not Reported | Coldstream Pond and Fred Pond, northeast of Lexington, [38o06'23"N, 84o30'08"W] | Exposure Factor Datasets | |
| Body Weight - Mean | see citation | figure of annual variation in weight | g | Not Reported | Tadpole | 27 - 1817 | Coldstream Pond and Fred Pond, northeast of Lexington, [38o06'23"N, 84o30'08"W] | Exposure Factor Datasets |
| Survival/ Mortality | Range of mean survival of larvae | % | Not Reported | Tadpole | 3 sampling periods, 20,000 animals | Coldstream Pond and Fred Pond, northeast of Lexington, [38o06'23"N, 84o30'08"W] | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Dietary Composition | see citation | % occurrence of 44 food items in stomach contents (species level) | Not Reported | Not Reported | 139 | streams, ponds, strip pits in Pulaski, Loanoke and Saline counties | Exposure Factor Datasets | |
| Body Weight - Mean | range of mean body weights | g | Not Reported | Not Reported | 29 - 62 | streams, ponds, strip pits in Pulaski, Loanoke and Saline counties | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Dietary Composition | see citation | % frequency of 26 food items in stomach contents (family level) | Not Reported | Adult | 24 | Cranberry Lake Biological Station, Barber Point, Cranberry Lake | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error |
|---|---|---|---|---|---|---|---|---|---|
| Territory Size | 17.8 | Average distance between male frog and closest male neighbor within a chorus; also reported as a minimum territory radius of 9 ft. | ft | Male | Adult | 94 | Pond in E.S. George Reserve | Exposure Factor Datasets | 5.9 SD |
| Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Clutches or Litters per year | Double clutching observed in 5 out of 73 females | clutches/yr | Female | Adult | 73 | Exposure Factor Datasets |
| Exposure Endpoint Type | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|
| Clutch or Litter Size | eggs/clutch | Female | Adult | Not Reported | Crane Pond, E.S. George Reserve | Exposure Factor Datasets |
| Clutches or Litters per year | clutches/yr | Female | Adult | Not Reported | Crane Pond, E.S. George Reserve | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Growth Rate | mm/yr | Both Male and Female | Adult | 22 | Crane Pond, E.S. George Reserve | Exposure Factor Datasets | ||
| Age at Sexual Maturity | 1 | age after metamorphosis; development of secondary sex characteristics | yr | Male | Adult | Not Reported | Crane Pond, E.S. George Reserve | Exposure Factor Datasets |
| Age at Sexual Maturity | age after metamorphosis when produced eggs | yr | Female | Adult | Not Reported | Crane Pond, E.S. George Reserve | Exposure Factor Datasets | |
| Survival/ Mortality | Non-breeding season survival; measured as # that returned to breed/# known to be alive at end of previous breeding season | % | Both Male and Female | Adult | 25 - 54 | Crane Pond, E.S. George Reserve | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|---|
| Food Ingestion Rate | 7.1 | mean % body weight consumed per day, body weight mean = 17.5 g | % | Not Reported | Juvenile | 25 | Exposure Factor Datasets | 1 mo post-transformation | Laboratory | |
| Food Ingestion Rate | 5.9 | mean % body weight consumed per day, body weight mean = 29.8 g | % | Not Reported | Juvenile | 25 | Exposure Factor Datasets | 2 mo post-transformation | Laboratory | |
| Food Ingestion Rate | 4.0 | mean % body weight consumed per day, body weight mean = 42.4 g | % | Not Reported | Juvenile | 25 | Exposure Factor Datasets | 3 mo post-transformation | Laboratory | |
| Food Ingestion Rate | 3.3 | mean % body weight consumed per day, body weight mean = 55.8 g | % | Not Reported | Juvenile | 25 | Exposure Factor Datasets | 4 mo post-transformation | Laboratory | |
| Body Weight - Mean | 10.7 | g | Not Reported | Juvenile | 25 | Exposure Factor Datasets | newly transformed | Laboratory | ||
| Body Weight - Mean | 17.5 | g | Not Reported | Juvenile | 25 | Exposure Factor Datasets | 1 mo post-transformation | Laboratory | ||
| Body Weight - Mean | 29.8 | g | Not Reported | Juvenile | 25 | Exposure Factor Datasets | 2 mo post-transformation | Laboratory | ||
| Body Weight - Mean | 42.4 | g | Not Reported | Juvenile | 25 | Exposure Factor Datasets | 3 mo post-transformation | Laboratory | ||
| Body Weight - Mean | 55.8 | g | Not Reported | Juvenile | 25 | Exposure Factor Datasets | 4 mo post-transformation | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Dietary Composition | Insecta (92.0%), Crustacea (13.7%), Arachnida (13.7%), Diploda (5.6%), Chilopoda (1.6%), Gastropoda (4.0%), Reptilia (3.2%), Amphibia (9.6%), Aves (1.6%), Osteichthyes (4.0%) | Percent occurrence in stomach contents from frogs collected during day and night | Not Reported | Not Reported | 124 | ponds in north central TX | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Dietary Composition | Coleoptera (43.6%), Notonectidae (10.3%), Diptera (6.6%), Hymenoptera (6.3%), Locustidae (6.0%), Ephemeroptera (4.3%), Gryllidae (4.3%), Protura (3.3%), Chironomidae (2.6%), Culicidae (2.0%), Lepidoptera (1.3%), Odonata (0.3%), Gerridae (0.3%), Mantidae (0.3%), Sepsidae (0.3%), Unidentified parts (21.3%), Decomposed tissue (18.0%), Spiders (16.0%), Rocks, grass, leaves (22.0%), Chitinous material (10%), Snails, Planorbid (9.0%), Frogs (5.6%), Snails, Physid (4.7%), Small fish (4.3%), Unknown vertebrates (2.3%), Tadpoles (1.3%), Salamander (1.0%), Feathers (1.0%), Worms (0.6%), Egg sack (0.3%), Rabbit pellet (0.3%), Peromyscus (0.3%) | % of stomachs in which food item was present at least once, frog weight range 10 - 200 g | Not Reported | Not Reported | 300 | San Joaquin Experimental Range, O'Neals | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|
| Dietary Composition | Review | Both Male and Female | Adult | Not Reported | Exposure Factor Datasets | |
| Time of Fledging or Metamorphosis | Review | Both Male and Female | Tadpole | Not Reported | Exposure Factor Datasets | |
| Time of Mating/ Laying | Review | Both Male and Female | Adult | Not Reported | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Dietary Composition | Newly metamorphosed and larval Rana (87%), Aquatic snails (5%), Adult and larval aquatic Coleoptera (3%), Adult and larval Odonata (3%), Other (2%) | Total percent volume of stomach contents, frog snout-vent length range = 90 - 190 mm | Both Male and Female | Adult | 138 | Wall Lake, southeast Catron County | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Dietary Composition | Gastropoda (0.7%), Arachnida (0.2%), Crustacea (12.8%), Insecta (81.5%), Chilopoda (0.2%), Osteichthyes, Cyprinidae (8.7%), Ictaluridae (10.1%), Centrarchidae (2.9%), Amphibia (0.7%), Mammalia (0.5%) | Percent stomachs containing item | Not Reported | Not Reported | 415 | ponds, Comanche and Kiowa counties | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Dietary Composition | Coleoptera (2.3-6.5%), Wasps and bees (1.1-4.7%), Ants (0-3.5%), Homoptera (2.3-6.0%), Odonata (12.4-17.5%), Larval Lepidoptera (0.5-2.1%), Diptera (3.7-10.5%), Arachnids (0-3.2%), Miscellaneous terrestrial(10.5-11.1%), Hemiptera (19.2-23.2), Larval Odonata (3.4-5.0%), Larval Diptera (4.4-7.2%), Miscellaneous aquatic (1.9-7.4%), Frogs (5.1-14.5%), Metamorphosing Odonates (0-5.7%), Miscellaneous (1.8-7.3) | Percentage of bullfrog diet items | Both Male and Female | Both Adults and Juveniles | 23-46 | Turkey Marsh, Kellogg Biological Station, Kalamazoo County | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
|---|---|---|---|---|---|---|---|---|---|---|
| Surface Area | 15.09 | Mean total skin surface area measured by removing skin; air-breathing tadpole body weight 4.48 g +/- 0.31 SE | cm2 | Not Reported | Tadpole | 20 | Exposure Factor Datasets | 0.85 SE | Laboratory | |
| Metabolic Rate | 5.9 | Mean total oxygen uptake at 20C (summed from skin and gill uptake), aquatic tadpole (stage IV-V) body weight = 3.6 g +/- 1.03 SE | umol O2/g/hr | Not Reported | Tadpole | 6 | Exposure Factor Datasets | 0.3 SE | Laboratory | |
| Metabolic Rate | 6.9 | Mean total oxygen uptake at 20C (summed from skin and gill/lung uptake), air-breathing tadpole (stage XVI-XIX) body weight = 5.3 g +/- 1.2 SE | umol O2/g/hr | Not Reported | Tadpole | 8 | Exposure Factor Datasets | 0.5 SE | Laboratory | |
| Metabolic Rate | 1.1 | Mean total oxygen uptake at 20C (summed from skin and lung uptake), body weight = 228.2 g +/- 70.3 SE | umol O2/g/hr | Not Reported | Adult | 6 | Exposure Factor Datasets | 0.1 SE | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
|---|---|---|---|---|---|---|---|---|---|---|
| Metabolic Rate | 178.2 | Mean total oxygen uptake (skin + gills + lungs) measured at 25C, tadpole mean body weight = 5.74 g | ul O2/g/hr | Not Reported | Tadpole | 5 | Exposure Factor Datasets | 36.7 | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Time of Fledging or Metamorphosis | Aug. - Oct. or Mar. - Apr. of following yr. | time to metamorphosis for second clutch | Not Reported | Tadpole | Not Reported | lower Colorado River between Laguna and Morelos Dams | Exposure Factor Datasets | |
| Age at Sexual Maturity | yr | Not Reported | Adult | Not Reported | lower Colorado River between Laguna and Morelos Dams | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| Metabolic Rate | 17.02 | Pulmonary oxygen uptake at 5C | ul O2/g/hr | Not Reported | 9 | Exposure Factor Datasets | Laboratory | |
| Metabolic Rate | 24.56 | Cutaneous oxygen uptake at 5C | ul O2/g/hr | Not Reported | 9 | Exposure Factor Datasets | Laboratory |
| Exposure Endpoint Type | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|
| Longevity | yr | Not Reported | Adult | Not Reported | Edwin S. George Reserve, Ann Arbor | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Age at Fledging, Metamorphosis, Weaning | yr | Both Male and Female | Tadpole | Not Reported | Ithaca | Exposure Factor Datasets | |
| Time of Fledging or Metamorphosis | July - Oct. | Both Male and Female | Tadpole | Not Reported | Ithaca | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| Growth Rate | review | see citation for review of growth rates based on size estimates | Both Male and Female | Adult, Tadpole | Not Reported | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
|---|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | 142.8 | g | Not Reported | Adult | 39 | York County, New Brunswick [lat., 45^o47'; long., 66^o37'] | Exposure Factor Datasets | CANADA | 77.4 SD |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | California Counties | Error |
|---|---|---|---|---|---|---|---|---|---|---|---|
| Time of Mating/ Laying | July | laying | Female | Adult | Not Reported | Angelo Coast Range Reserve [lat., 39^o44'N; long., 123^o39'W] | Exposure Factor Datasets | Mendocino | |||
| Population Density | 18.2 | #/m2 | Both Male and Female | Tadpole | 17 quadrats | Angelo Coast Range Reserve [lat., 39^o44'N; long., 123^o39'W] | Exposure Factor Datasets | "overwintered" tadpoles | Mendocino | 13.1 SD | |
| Population Density | 90.9 | #/m2 | Both Male and Female | Tadpole | 20 quadrats | Angelo Coast Range Reserve [lat., 39^o44'N; long., 123^o39'W] | Exposure Factor Datasets | "overwintered" tadpoles | Mendocino | 97.7 SD |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
|---|---|---|---|---|---|---|---|---|
| Survival/ Mortality | 0.42 | probability of survival (age x-1 to age x) | Male | Not Reported | Edwin S. George Reserve | Exposure Factor Datasets | 2 or 3 yrs | |
| Survival/ Mortality | 0.52 | probability of survival (age x-1 to age x) | Male | Adult | Not Reported | Edwin S. George Reserve | Exposure Factor Datasets | 4 yrs |
| Survival/ Mortality | 0.23 | probability of survival (age x-1 to age x) | Male | Adult | Not Reported | Edwin S. George Reserve | Exposure Factor Datasets | 5 yrs |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|---|
| Metabolic Rate | see citation | figures of oxygen consumption of submerged tadpoles measured at various oxygen tensions and pre-metamorphic stages | ul/g/hr | Not Reported | Tadpole | 10/group | Exposure Factor Datasets | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Dietary Composition | Decapoda: Astacidae (47.7%); Lepidoptera (19.0%); Coleoptera: Lampryidae (5.8%); Chrysomelidae (5.8%); Carabidae (4.1%); Curculionidae (0.3%); Chilopoda (7.7%); sand, gravel (1.2%); unidentified (1%) | % volume of stomach contents | % | Not Reported | Not Reported | 18 | Breathitt and Perry counties | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|---|
| Dietary Composition | frogs (12.1%); goldfish (30.3%); gastropods (12.4%); crayfish (9.3%); arachnida (4.4%); coleoptera adult (10.6%); hemiptera (8.2%); orthoptera (8.7%) | % of stomachs containing major (>4%) food items | % | Not Reported | Adult | 772 | goldfish pond, Richland | Exposure Factor Datasets |
| Dietary Composition | frogs (13.0%); shiners (27.5%); gastropods (16.1%); crayfish (16.3%); arachnida (4.5%); coleoptera adult (10.5%); hemiptera (13.5%); orthoptera (5.8%); lepidoptera larvae (4.5%); odonata adult (4.2%) | % of stomachs containing major (>4%) food items | % | Not Reported | Adult | 553 | bait minnow pond, Richland | Exposure Factor Datasets |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
|---|---|---|---|---|---|---|---|---|---|---|
| Body Weight - Mean | 175.9 | g | Both Male and Female | Adult | 30 | Exposure Factor Datasets | 8.16 SE | Laboratory | ||
| Inhalation Rate | see citation | figure of breathing frequency (breaths/min) at various seasons, temperatures and oxygen levels | Both Male and Female | Adult | 6/group | Exposure Factor Datasets | Laboratory |
Long-toed Salamander (Ambystoma macrodactylum)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| 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 | |
| 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 |
California Newt (Taricha torosa)
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| 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 | |
| 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 | 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 |
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) | 3.77 mg/l (95% CI; 1.82 - 4.22) | LC50 | Not Reported | Tadpole | 10 tadpoles/replicate; 2 replicates/dose; 5 doses | Toxicity Factor Datasets | 3 wk | Laboratory | |
| 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 | ||
| AMMONIUM SULFATE | 32.4 | 10-d LC50 for embryos | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | 29.7 - 35.4 (95% CI) | Laboratory | |
| AMMONIUM SULFATE | 11.7 | LOAEL for body weight | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | Laboratory | ||
| AMMONIUM SULFATE | 6.1 | NOAEL for body weight | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | Laboratory | ||
| NITRATE, SODIUM | 578.0 | 10-d LC50 for embryos | mg NO3-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | 459.0 - 726.5 (95% CI) | Laboratory | |
| NITRATE, SODIUM | 111.0 | LOAEL for body weight and length | mg NO3-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | Laboratory | ||
| NITRATE, SODIUM | 56.7 | NOAEL for body weight and length | mg NO3-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | Laboratory |
Northern Red-legged Frog (Rana aurora) formerly Rana aurora ssp. aurora
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
|---|---|---|---|---|---|---|---|---|
| Time of Mating/ Laying | Feb. - Apr. | time of breeding and laying | Both Male and Female | Adult | Not Reported | White Rock, British Columbia | Exposure Factor Datasets | CANADA |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries | Error |
|---|---|---|---|---|---|---|---|---|---|---|
| Time of Mating/ Laying | Feb. - Apr. | time of first observance of egg masses | Female | Adult | observations over 3 yrs | Marion Lake, southern British Columbia (elev., 300m) | Exposure Factor Datasets | CANADA | ||
| Time of Hatching or Parturition | May | Not Reported | Embryo | observations over 3 yrs | Marion Lake, southern British Columbia (elev., 300m) | Exposure Factor Datasets | CANADA | |||
| Population Density | 500 | maximum reported density | #/m2 | Not Reported | Tadpole | Not Reported | Marion Lake, southern British Columbia (elev., 300m) | Exposure Factor Datasets | CANADA | |
| Time of Fledging or Metamorphosis | July - Oct. | Not Reported | Tadpole | Not Reported | Marion Lake, southern British Columbia (elev., 300m) | Exposure Factor Datasets | CANADA | |||
| Clutch or Litter Size | 531 | #/egg mass | Female | Adult | 35 egg masses | Marion Lake, southern British Columbia (elev., 300m) | Exposure Factor Datasets | CANADA | 19 SE | |
| Survival/ Mortality | 5 | survival of larval population until metamorphosis | % | Not Reported | Tadpole | Not Reported | Marion Lake, southern British Columbia (elev., 300m) | Exposure Factor Datasets | CANADA |