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Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Type |
---|---|---|---|---|---|
Time of Mating/ Laying | review | Both Male and Female | Adult | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Population Density | range of mean larval density estimates over 2 yrs | 1.44 - 3.0 | # larvae/m2 | Both Male and Female | Juvenile | Cold Creek, Santa Monica Mountains | Not Reported | Exposure Factor Datasets | |
Dietary Composition | see citation | figure of % of stomachs containing prey items over several yrs | Not Reported | Adult | Cold Creek and Trancas Creek, Santa Monica Mountains | 17-52 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Population Density | range of mean density estimates for six pools without crayfish over two time periods | 0.67 - 1.84 | #/10m2 | Not Reported | Adult | Trancas Creek, Santa Monica Mountains | Not Reported | Exposure Factor Datasets |
Population Density | range of mean density estimates for six pools with crayfish over two time periods | 0 - 0.22 | #/10 m2 | Not Reported | Adult | Trancas Creek, Santa Monica Mountains | Not Reported | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Time of Mating/ Laying | Apr. - May | time of breeding | Both Male and Female | Adult | Santa Monica Mountains | Not Reported | Exposure Factor Datasets | ||
Clutch or Litter Size | 1-4 masses of 5-30 eggs | #/clutch | 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 |
---|---|---|---|---|---|---|---|---|---|---|
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 | aerial application; water residues, 4.6 ppb (day 7), 0.29 ppb (day 52), 0.009 ppb (day 421); sediment residues, 35 ppb (day 7), 34 ppb (day 52), 20 ppb (day 1014) | TOX-EXP IND - accumulation | 14 d | field application | Toxicity Factor Datasets |
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 | aerial application; water residues, 4.6 ppb (day 7), 0.29 ppb (day 52), 0.009 ppb (day 421); sediment residues, 35 ppb (day 7), 34 ppb (day 52), 20 ppb (day 1014) | TOX-EXP IND - accumulation | 451 d | field application | Toxicity Factor Datasets |
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 | aerial application; water residues, 4.6 ppb (day 7), 0.29 ppb (day 52), 0.009 ppb (day 421); sediment residues, 35 ppb (day 7), 34 ppb (day 52), 20 ppb (day 1014) | TOX-EXP IND - accumulation | 1036 d | field application | Toxicity Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 0.26 | 0.05 - 0.49 | g | Not Reported | Juvenile | Portland, Multnomah County | 23 | Exposure Factor Datasets | |
Body Weight - Mean | 1.60 | 0.70 - 3.28 | g | Both Male and Female | Juvenile | Portland, Multnomah County | 37 | Exposure Factor Datasets | |
Body Weight - Mean | 4.30 | 2.58 - 5.08 | g | Female | Adult | Portland, Multnomah County | 11 | Exposure Factor Datasets | |
Body Weight - Mean | 2.80 | 1.45 - 5.80 | g | Male | Adult | Portland, Multnomah County | 19 | Exposure Factor Datasets | |
Dietary Composition | Crustacea (1); Arachnida (19); Diplopoda (5); Chilopoda (3); Hexapoda (32) | number of each item in stomach contents | Both Male and Female | Both Adults and Juveniles | Portland, Multnomah County | 21 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Home Range | 17.3 | average distance moved between recaptures | 2.5 - 63.7 | ft | Female | Adult | Pinehurst Madrone Grove Park | 13 | Exposure Factor Datasets |
Home Range | 32.8 | average distance moved between recaptures | 5.2 - 106.6 | ft | Male | Adult | Pinehurst Madrone Grove Park | 17 | Exposure Factor Datasets |
Population Density | estimated maximum density | 170 - 200 | #/acre | Both Male and Female | Adult | Pinehurst Madrone Grove Park | 25 | Exposure Factor Datasets | |
Population Density | estimated maximum density | 600 - 700 | #/acre | Both Male and Female | Both Adults and Juveniles | Pinehurst Madrone Grove Park | Not Reported | Exposure Factor Datasets | |
Clutches or Litters per year | 1 | clutch/yr | Female | Adult | Pinehurst Madrone Grove Park | Not Reported | Exposure Factor Datasets | ||
Clutch or Litter Size | 11 | # large ovarian eggs/female | 8 - 17 | #/clutch | Female | Adult | Pinehurst Madrone Grove Park | 26 | Exposure Factor Datasets |
Growth Rate | see citation | figure of growth rates based on changes in snout-vent length | Both Male and Female | Juvenile | Pinehurst Madrone Grove Park | Not Reported | Exposure Factor Datasets | ||
Longevity | range of oldest individuals recorded | 6 - 8 | yrs | Both Male and Female | Adult | Pinehurst Madrone Grove Park | 3 | Exposure Factor Datasets | |
Age at Sexual Maturity | 3 - 4 | yrs | Both Male and Female | Adult | Pinehurst Madrone Grove Park | Not Reported | Exposure Factor Datasets | ||
Dietary Composition | earthworm (1); sowbugs (14); amphipod (1); centipede (1); millipede (4); spiders (6); springtail (1); thysanuran (1); camel crickets (15); lepidopterous larva (1); dipteran (1); beetles (5); ant (1) | number of each food item in stomachs | # | Not Reported | Both Adults and Juveniles | Pinehurst Madrone Grove Park | 27 | Exposure Factor Datasets | |
Body Weight - Mean | 6 | 5 - 7 | g | Both Male and Female | Adult | Pinehurst Madrone Grove Park | 9 | Exposure Factor Datasets | |
Duration of Incubation or Gestation | 4 - 5 | mo | Female | Adult | Pinehurst Madrone Grove Park | Not Reported | Exposure Factor Datasets | ||
Time of Mating/ Laying | late spring - early summer | time of laying | Female | Adult | Pinehurst Madrone Grove Park | Not Reported | Exposure Factor Datasets | ||
Time of Mating/ Laying | Oct. - Mar. | time of breeding | Both Male and Female | Adult | Pinehurst Madrone Grove Park | Not Reported | Exposure Factor Datasets | ||
Time of Hatching or Parturition | fall - early winter | Not Reported | Embryo | Pinehurst Madrone Grove Park | Not Reported | Exposure Factor Datasets | |||
Dietary Composition | sowbug (1); centipede (1); millipede (6); spiders (7); wood ticks (2); scavenger mite (1); solpugid (1); springtails (5); worker termites (15); hemipteran (1); fly (1); beetles (11); ants (2) | number of each food item in stomachs | # | Not Reported | Both Adults and Juveniles | Madelia Canyon | 8 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|
Dietary Composition | Collembola (68%); Coleoptera adults (49%); Coleoptera larvae (11%); Diptera adults (14%); Diptera larvae (16%); Hymenoptera (22%); Acarina (19%); Araneae (57%); Diplopoda (38%); Isopoda (32%) | % frequency of major food items | % | Not Reported | Both Adults and Juveniles | 1-2 mi WSW of Pepperwood, Humboldt Co. | 37 | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Range | Units | Sex | Life Cycle Stage | Location | Sample Size | Type |
---|---|---|---|---|---|---|---|---|---|
Population Density | range of larval density estimates in 8 fishless lakes utilizing 3 survey methodologies during day and night | 0 - 383 | larvae/100 m shoreline | Both Male and Female | Juvenile | North Cascades National Park Service Complex | Not Reported | Exposure Factor Datasets | |
Dietary Composition | Benthic macroinvertebrates (75%): Diptera (66.7); Chironomidae (41.7%); Coleoptera (58.3%); Trichoptera (50%); Ephemeroptera (25%); Amphipoda (16.7%); Plecoptera (8.3%); Pelecypoda (8.3%); Crustacean zooplankton (41.7%): Cladocerans (41.7%); Unidentified (41.7%); Imm. Daphnids (25.0%); Daphnia rosea (25%); Ceriodaphnia quadrangula (16.7%); Chydorus spaericus (8.3%); Copepods (16.7%); Cylopoids (16.7%); Calanoids (8.3%); Harpactacoids (8.3%) | % larvae stomachs that contained prey item | % | Not Reported | Juvenile | North Cascades National Park Service Complex | 13 | Exposure Factor Datasets |
Chemical | Exposure Endpoint Type | Endpoint Value | Endpoint Description | Error | Units | Sex | Life Cycle Stage | Sample Size | Tox Exposure | Toxicity Endpoint Type | Tox Exposure Duration | Tox Exposure Technique | Type |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 15.4 | 0.3 SE | mg | Not Reported | Juvenile | 3 | Exposure Factor Datasets | ||||||
METHOXYCHLOR | no appreciable mortality | embryo and larvae (10 d post-hatch) mortality | Not Reported | Embryo, Juvenile | 30-34 eggs/dose | 0, 0.03, 0.1, 0.3, 1.0, 3.2, 10.0 mg/L (DMSO carrier) | TOX-MORT - dose-response data | 45 d | waterborne | Toxicity Factor Datasets | |||
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 | 0, 0.03, 0.1, 0.3, 1.0, 3.2, 10.0 mg/L (DMSO carrier) | TOX-REPRO - development | 35 d | waterborne | Toxicity Factor Datasets | |||
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 | 0, 0.03, 0.1, 0.3, 1.0, 3.2, 10.0 mg/L (DMSO carrier) | TOX-REPRO - behavior | 45 d | waterborne | Toxicity Factor Datasets | |||
METHOXYCHLOR | decrease @ 0.3 and 10 mg/L | mean body weight of larvae | Not Reported | Embryo, Juvenile | 30-38 eggs/dose | 0, 0.03, 0.1, 0.3, 1.0, 3.2, 10.0 mg/L (DMSO carrier) | TOX-Non-Repro-Sublethal - whole animal | 37 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 |