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Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|
Time of Torpor or Hibernation | July - Oct. | Not Reported | Not Reported | Gorman (elev., 4000 ft) and Palmdale (elev., 2000 ft) | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Collembola (8.2%); Lepidoptera larvae (14.8%); Hymenoptera (6.6%); Diptera adult (14.5%); Diptera larvae (8.2%); Coleoptera adults (32.8%); Coleoptera larvae (19.7%); Aranea (9.9%); Acarina (3.3%); Isopoda (9.9%); Chilopoda (4.9%); Pulmonata (11.3%); Megadrili (4.9%) | % frogs in which each item occurred in stomach contents | % | Not Reported | Not Reported | Lakeport (elev., 1300 ft) | 61 | Exposure Factor Datasets |
Dietary Composition | Collembola (1.4%); Lepidoptera larvae (4.1%); Hymenoptera (4.1%); Diptera adult (8.1%); Diptera larvae (1.4%); Coleoptera adults (14.9%); Coleoptera larvae (4.1%); Plecoptera (2.7%); Hemiptera (6.8%); Aranea (6.8%); Acarina (1.4%) | % frogs in which each item occurred in stomach contents | % | Both Male and Female | Not Reported | Eureka | 74 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | May - Aug. | time of breeding | Both Male and Female | Adult | South Fork Eel River, Branscomb [lat., 39^o44' N; long., 123^o39'W] | Not Reported | Exposure Factor Datasets | ||
Body Weight - Mean | range of average weight at metamorphosis, tadpoles fed green algae in field enclosures | 251 - 294 | mg | Both Male and Female | Juvenile | South Fork Eel River, Branscomb [lat., 39^o44' N; long., 123^o39'W] | 16-24/group | Exposure Factor Datasets | |
Body Weight - Mean | range of average weight at metamorphosis, tadpoles fed seston, detritus or blue green algae in field enclosures | 132-152 | mg | Both Male and Female | Juvenile | South Fork Eel River, Branscomb [lat., 39^o44' N; long., 123^o39'W] | 7-12/group | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Jan. - June | time of breeding | Both Male and Female | Adult | San Diego | 85 pairs in amplexus | Exposure Factor Datasets | |||
Clutches or Litters per year | estimated by number of times a female was found in amplexus with palpable eggs | 1 - 5 | clutches/yr | Female | Adult | San Diego | Not Reported | Exposure Factor Datasets | ||
Clutch or Litter Size | 267.7 | 128.7 SD | 62 - 633 | eggs/clutch | Female | Adult | San Diego | 40 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Time of Fledging or Metamorphosis | July - Sept. | Not Reported | Juvenile | Moscow, Latah County (elev., 850m) | Not Reported | Exposure Factor Datasets | |
Time of Hatching or Parturition | May | Not Reported | Hatchling | Moscow, Latah County (elev., 850m) | Not Reported | Exposure Factor Datasets | |
Time of Mating/ Laying | Apr. - May | time of laying | Female | Adult | Moscow, Latah County (elev., 850m) | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Growth Rate | range of average increase in snout-vent length for 7 size classes (snout vent length; 28.0 - 35.9 mm) | 4.20 - 10.80 | mm/yr | Not Reported | Adult | Washington County | 13 - 52 | Exposure Factor Datasets | |
Survival/ Mortality | 13.3 | % surviving their first year | % | Not Reported | Juvenile | Washington County | 15 | Exposure Factor Datasets | |
Age at Sexual Maturity | 8 | mo | Not Reported | Adult | Washington County | Not Reported | Exposure Factor Datasets | ||
Survival/ Mortality | 11 | % surviving one year | % | Not Reported | Adult | Washington County | 373 | Exposure Factor Datasets | |
Growth Rate | 2 | increase in snout-vent length | mm/wk | Not Reported | Juvenile | Washington County | 30 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Metabolic Rate | range of mean oxygen consumption rates measured at 20C | 0.304 - 0.524 | mm3 O2/g/hr | Both Male and Female | Not Reported | captured in San Diego, Julian and Willows, CA | 7/location and sex | Exposure Factor Datasets | |
Body Weight - Mean | 2.27 | g | Both Male and Female | Adult | 90 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | spring - summer | breeding | Both Male and Female | Adult | Angelo Coast Range Reserve [lat., 39^o44'N; long., 123^o39'W] | Not Reported | Exposure Factor Datasets | |||
Population Density | 16.25 | 7 SD | 0 - 350 | #/m2 | Both Male and Female | Tadpole | Angelo Coast Range Reserve [lat., 39^o44'N; long., 123^o39'W] | 27 quadrats | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Feb. - June | time of breeding | Both Male and Female | Adult | Santa Monica Mountains | Not Reported | Exposure Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
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 | 0.01-9.67 mg/l | TOX-MORT - toxicity benchmarks | 8 d | waterborne | Toxicity Factor Datasets |
AZINPHOS-METHYL (GUTHION) | 1.78 mg/l | NOAEL | Not Reported | Tadpole | 10 tadpoles/replicate; 2 replicates/dose; 5 doses | 0.01-9.67 mg/l | TOX-MORT - toxicity benchmarks | 8 d | waterborne | Toxicity Factor Datasets |
AZINPHOS-METHYL (GUTHION) | 9.67 mg/l | LOAEL | Not Reported | Tadpole | 10 tadpoles/replicate; 2 replicates/dose; 5 doses | 0.01-9.67 mg/l | TOX-MORT - toxicity benchmarks | 8 d | waterborne | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|
DIURON | 15.2 mg/l | 14-d LC50 value; mean of 2 tests | Not Reported | Tadpole | 8/replicate; 3 replicates/dose | 0, 0.5, 1.0, 3.8, 7.6, 14.5, 21.1, 29.1 mg/l | TOX-MORT - toxicity benchmarks | 14 d | waterborne | Toxicity Factor Datasets |
DIURON | 14.5 mg/l | lowest NOAEL based on body length/weight endpoints | Not Reported | Tadpole | 8/replicate; 3 replicates/dose | 0, 0.5, 1.0, 3.8, 7.6, 14.5, 21.1, 29.1 mg/l | TOX-Non-Repro-Sublethal - whole animal | 14 d | waterborne | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|---|
AMMONIUM NITRATE | 25.0 | 10-d LC50 value for embryos | 21.9-28.7 (95% CI) | mg/L as NH4-N | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.3, 3.3, 6.9, 13.3, 25.1, 50.9, 101.2 mg/L NH4-N, mean measured concentration | TOX-MORT - toxicity benchmarks | 10 d | waterborne | Toxicity Factor Datasets |
AMMONIUM NITRATE | 6.9 | LOAEL for body weight and length | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.3, 3.3, 6.9, 13.3, 25.1, 50.9, 101.2 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
AMMONIUM NITRATE | 3.3 | NOAEL for body weight and length | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.3, 3.3, 6.9, 13.3, 25.1, 50.9, 101.2 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
AMMONIUM CHLORIDE | 30.3 | 10-d LC50 for embryos | 27.0 - 33.4 (95% CI) | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.2, 2.8, 7.3, 12.8, 24.9, 49.7, 102.9 mg/L NH4-N, mean measured concentration | TOX-MORT - toxicity benchmarks | 10 d | waterborne | Toxicity Factor Datasets |
AMMONIUM CHLORIDE | 24.9 | LOAEL for body weight and length and deformities | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.2, 2.8, 7.3, 12.8, 24.9, 49.7, 102.9 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
AMMONIUM CHLORIDE | 12.8 | NOAEL for body weight and length and deformities | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.2, 2.8, 7.3, 12.8, 24.9, 49.7, 102.9 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
AMMONIUM SULFATE | 32.4 | 10-d LC50 for embryos | 29.7 - 35.4 (95% CI) | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.04, 2.6, 6.1, 11.7, 23.1, 45.4, 91.5 mg/L NH4-N, mean measured concentration | TOX-MORT - toxicity benchmarks | 10 d | waterborne | Toxicity Factor Datasets |
AMMONIUM SULFATE | 11.7 | LOAEL for body weight | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.04, 2.6, 6.1, 11.7, 23.1, 45.4, 91.5 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
AMMONIUM SULFATE | 6.1 | NOAEL for body weight | mg NH4-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.04, 2.6, 6.1, 11.7, 23.1, 45.4, 91.5 mg/L NH4-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
NITRATE, SODIUM | 578.0 | 10-d LC50 for embryos | 459.0 - 726.5 (95% CI) | mg NO3-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.1, 24.8, 56.7, 111.0, 230.4, 470.4, 979.2, 2716 mg/L NO3-N, mean measured concentration | TOX-MORT - toxicity benchmarks | 10 d | waterborne | Toxicity Factor Datasets |
NITRATE, SODIUM | 111.0 | LOAEL for body weight and length | mg NO3-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.1, 24.8, 56.7, 111.0, 230.4, 470.4, 979.2, 2716 mg/L NO3-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets | |
NITRATE, SODIUM | 56.7 | NOAEL for body weight and length | mg NO3-N/L | Not Reported | Embryo | 10/replicate; 3 replicates/dose | 0.1, 24.8, 56.7, 111.0, 230.4, 470.4, 979.2, 2716 mg/L NO3-N, mean measured concentration | TOX-REPRO - development | 10 d | waterborne | Toxicity Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|
Time of Hatching or Parturition | see citation | figure of mean duration from fertilization to hatching in field enclosures | Both Male and Female | Embryo | Santa Monica Mountains | 8 replicates of 150 (frogs) or 16-12 (newts) embryos | Exposure Factor Datasets |