Bullfrog (Lithobates catesbeianus formerly Rana catesbeiana)
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 | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|
FENITROTHION | increase at 9 mg/l | Not Reported | Tadpole | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | 8 d after hatching | Laboratory | |
FENITROTHION | increase at 9 mg/l | Not Reported | Tadpole | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | 1 d after hatching | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
ARSENIC COMPOUNDS, BARIUM COMPOUNDS, CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, SELENIUM COMPOUNDS | increase | incidence of oral deformities at coal ash contaminated site, relative to reference site | Not Reported | Tadpole | 575-1048 | Savannah River, Aiken | Toxicity Factor Datasets |
ARSENIC COMPOUNDS, BARIUM COMPOUNDS, CADMIUM COMPOUNDS, CHROMIUM COMPOUNDS, COPPER COMPOUNDS, SELENIUM COMPOUNDS | increase at contaminated (C) compared to reference (R) site: Arsenic, C=48.9 +/- 2.6SE, R=2.5 +/-0.2SE; Barium, C=211.5 +/- 14.9SE, R=81.2 +/- 5.2SE; Cadmium, C=1.71 +/- 0.5SE, R=0.15 +/- 0.04SE; Chromium, C=17.2 +/- 0.5SE, R=1.4 +/- 0.3SE; Copper, C=31.4 +/- 1.5SE, R=17.5 +/- 6.6SE; Selenium, C=25.70 +/- 3.60SE, R=3.37 +/- 0.09SE. | mean whole body metal concentrations (ppm, dry mass) | Not Reported | Tadpole | 3 animals/site | Savannah River, Aiken | Toxicity Factor Datasets |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIELDRIN | 12.0 ug/g at 30.3 ug/l | whole body dieldrin concentration (ug/g, wet wt.) at the LC50 | Not Reported | Tadpole | Not Reported | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 19.0 ug/g at 52.3 ug/l | whole body dieldrin concentration (ug/g, wet wt.) | Not Reported | Tadpole | Not Reported | Toxicity Factor Datasets | 29 d | Laboratory | |
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 | |
DIELDRIN | 36,000 - 54,000 | 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 | 50 d | Laboratory | |
DIELDRIN | 30.3 ug/l (95% CL: 26.2 - 35.2 ug/l) | LC50 | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 52.3 ug/l | LOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 d | Laboratory | |
DIELDRIN | 12.3 ug/l | NOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 d | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
FLUORANTHENE | increase @ 10.97 - 59.48 ug/l | incidence of structural disorganization and necrosis of the integument | Not Reported | Tadpole | 20/group | Toxicity Factor Datasets | Laboratory | |
FLUORANTHENE | increase @ 37.97 ug/l | total distance travelled | Not Reported | Tadpole | 20/group | Toxicity Factor Datasets | Laboratory |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
SULFURIC ACID | significant decrease at pH 3.5 and 4.0 | hatching success | Not Reported | 50 eggs/replicate, 6 replicates/group (n=294-312) | Toxicity Factor Datasets | Laboratory | ||
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 |
---|---|---|---|---|---|---|---|---|---|
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 | 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 |
Exposure Endpoint Type | Chemical | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Error | Lab |
---|---|---|---|---|---|---|---|---|---|---|---|---|
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 | |||
Metabolic Rate | 0.1582 | resting oxygen consumption at 23C | ml O2/hr/tadpole | Not Reported | Tadpole | 19 | Exposure Factor Datasets | 0.009 SE | Laboratory |
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 | ||
TRICLOPYR | increase at 2.4 and 4.8 mg/l | Not Reported | Tadpole | 10 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | 1-2 d after hatching | Laboratory | ||
TRICLOPYR | decrease response at 1.2 mg/l | avoidance response assessed by daily prodding | Not Reported | Tadpole | 10 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | 1-2 d after hatching | Laboratory | |
FENITROTHION | decrease response at 0.5 - 8 mg/l | avoidance response assessed by daily prodding | 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 |
DIELDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
ALDRIN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
TOXAPHENE (POLYCHLORINATED CAMPHENES) | increase at 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
LINDANE | increase at 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 | |
TRIFLUOROMETHYL-4-NITROPHENOL (3-, LAMPRECIDE) | 15.35 mg/kg bw (95% CL: 8.72-21.98) | LD50 | Not Reported | Adult | 7 | Toxicity Factor Datasets | Laboratory | ||
TRIFLUOROMETHYL-4-NITROPHENOL (3-, LAMPRECIDE) | 0.95 mg/l (95% CL: 0.72 - 1.14) | LC50 | Not Reported | Tadpole | 5 | Toxicity Factor Datasets | Gossner stages 33-38 | Laboratory | |
TRIFLUOROMETHYL-4-NITROPHENOL (3-, LAMPRECIDE) | 12.99 mg/l (95% CL: 6.75 - 19.22) | LC50 | Not Reported | Adult | 7 | Toxicity Factor Datasets | Laboratory | ||
TRIFLUOROMETHYL-4-NITROPHENOL (3-, LAMPRECIDE) | effect observed at 1.0 - 3.0 mg/l | growth development arrested | Not Reported | Embryo | Not Reported | Toxicity Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
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 | 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 | Age-Specific | Countries | Error |
---|---|---|---|---|---|---|---|---|---|---|---|
Longevity | Maximum estimated age | yr | Both Male and Female | Adult | 567 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | CANADA | |||
Growth Rate | 0.0653 | mm/d | Both Male and Female | 16 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 0 yr | CANADA | 0.01465 SE | ||
Growth Rate | 0.1056 | mm/d | Both Male and Female | 34 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 1 yr | CANADA | 0.01427 SE | ||
Growth Rate | 0.1322 | mm/d | Female | 44 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 2 yr | CANADA | 0.1109 SE |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|---|
Surface Area | SA = 0.953W^0.725 | Area of removed skin measured, equation based on weight (W) in grams | cm2 | Not Reported | Not Reported | Not Reported | Exposure Factor Datasets | ||
Metabolic Rate | 29.36 | Pulmonary oxygen uptake at 15C | ul O2/g/hr | Not Reported | 4 | Exposure Factor Datasets | Laboratory | ||
Metabolic Rate | 27.74 | Cutaneous oxygen uptake at 15C | ul O2/g/hr | Not Reported | Not Reported | 4 | Exposure Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific |
---|---|---|---|---|---|---|---|---|
Body Weight - Mean | 0.80 | lbs | Not Reported | 5 | Ridge Lake, Charleston, Coles County | Exposure Factor Datasets | end of 6th yr | |
Age at Fledging, Metamorphosis, Weaning | mo | Not Reported | Tadpole | Not Reported | Ridge Lake, Charleston, Coles County | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Age at Fledging, Metamorphosis, Weaning | time to metamorphosis from first breeding clutch | mo | Not Reported | Tadpole | Not Reported | lower Colorado River between Laguna and Morelos Dams | Exposure Factor Datasets | |
Time of Fledging or Metamorphosis | Aug. - Oct. | metamorphosis period for first breeding clutch | Not Reported | Tadpole | Not Reported | lower Colorado River between Laguna and Morelos Dams | Exposure Factor Datasets | |
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 |
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 | Lab |
---|---|---|---|---|---|---|---|---|
Metabolic Rate | see citation | figure of oxygen consumption at various body temperatures within seasons | Both Male and Female | Adult | 6/group | Exposure Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
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 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 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
---|---|---|---|---|---|---|---|---|
Metabolic Rate | see citation | figures of aerial activity oxygen consumption and body weights at different developmental stages | Not Reported | Tadpole | 59 | Exposure Factor Datasets | Laboratory |
Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
Time of Torpor or Hibernation | Oct. - April | Not Reported | Adult | 6 | Seiberling Naturealm, Summit County | 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 | 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 |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|---|
Territory Size | 4.1 | Mean distance between territorial males | m | Male | Adult | 31 | Basking Pond, Great Swamp National Wildlife Refuge, Morris County | Exposure Factor Datasets |
Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
---|---|---|---|---|---|---|---|---|---|---|
Water Ingestion Rate | 0.18 | "drinking" measured as 125I-iothalamate uptake in gut after 2 hrs | ml/100 g/hr | Not Reported | Tadpole | 8 | Exposure Factor Datasets | 0.02 SE | Laboratory |