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 | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| TRICLOPYR | 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 | 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 | |
| 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 | 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 | ||
| HEXAZINONE | no effect | hatching success | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | embryo; midneurulation stage | Laboratory | |
| FENITROTHION | no effect | hatching success | Not Reported | Embryo | 20 animals/replicate; 3 replicates/dose | Toxicity Factor Datasets | embryo; midneurulation stage | 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 | |
| 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 |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| DIELDRIN | 4.0 ug/l | NOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 50 d | Laboratory | |
| DIELDRIN | 52.3 ug/l | LOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 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 | 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 | 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 | 12.3 ug/l | NOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | Toxicity Factor Datasets | 29 d | Laboratory | |
| DIELDRIN | 11.2 ug/l | LOAEL | Not Reported | Tadpole | 20 animals/replicate; 4 replicates/dose | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 | 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 |
| Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Lab |
|---|---|---|---|---|---|---|---|---|
| ENDRIN | > 40 ug/l | EC50; Loss of equilibrium | 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 | 2 ug/l (95% CL: 1-5 ug/l) | LC50 | Not Reported | Tadpole | 220 animals | Toxicity Factor Datasets | Laboratory | |
| TOXAPHENE (POLYCHLORINATED CAMPHENES) | 99 ug/l (95% CL: 71-116 ug/l) | LC50 | Not Reported | Tadpole | 220 animals | Toxicity Factor Datasets | 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 | 1 d after hatching | Laboratory | |
| FENITROTHION | increase at 9 mg/l | Not Reported | Tadpole | 10/replicate; 3 replicates/dose | Toxicity Factor Datasets | 8 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 |
|---|---|---|---|---|---|---|
| TOXAPHENE (POLYCHLORINATED CAMPHENES) | increase at 0.5 lbs/acre | 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 |
| CHLORDECONE (KEPONE) | no effect | 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 |
| HEPTACHLOR | increase at 0.5 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 |
| CHLORDANE | no effect | 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 |
| DIELDRIN | increase at 0.1 and 0.5 lbs/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 |
| ENDOSULFAN | 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 | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| 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) | 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) | effect observed at 1.0 - 3.0 mg/l | growth development arrested | Not Reported | Embryo | Not Reported | Toxicity Factor Datasets | Laboratory | ||
| 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 |
| Chemical | Endpoint Value | Endpoint Description | 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 | ||
| 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 |
| 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 |
|---|---|---|---|---|---|---|---|
| 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 |
| 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 |
| 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 | 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 | decrease at contaminated, compared to reference site | % survival to 80 d posthatching | % | Not Reported | Tadpole | Not Reported | Savannah River | Toxicity Factor Datasets | 80 d |
| 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 |
| 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 | Age-Specific | Lab |
|---|---|---|---|---|---|---|---|---|---|
| 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 | ||
| 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 | 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 | Not Reported | Tadpole | 15 animals/group | Toxicity Factor Datasets | Taylor-Kollros stages I-VII | 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 |
|---|---|---|---|---|---|---|---|---|---|
| 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 | |
| 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 |
| Exposure Endpoint Type | Endpoint Value | Units | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| 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 |
| 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 | 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 |
| Exposure Endpoint Type | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|
| 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 | 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 | 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 | 0.1056 | 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 | ||
| Growth Rate | 0.1353 | mm/d | Male | 46 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 2 yr | CANADA | 0.01079 SE | ||
| Growth Rate | 0.0930 | mm/d | Female | 14 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 3 yr | CANADA | 0.02287 SE | ||
| Growth Rate | 0.0841 | mm/d | Male | 12 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 3 yr | CANADA | 0.01882 SE | ||
| Growth Rate | 0.1250 | mm/d | Female | 10 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 4 yr | CANADA | 0.02155 SE | ||
| Growth Rate | 0.0697 | mm/d | Male | 7 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 4 yr | CANADA | 0.03720 SE | ||
| Growth Rate | 0.0449 | mm/d | Female | 5 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 5 yr | CANADA | 0.00996 SE | ||
| Growth Rate | -0.0043 | mm/d | Male | 4 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 5 yr | CANADA | 0.33534 SE | ||
| Growth Rate | 0.0466 | mm/d | Female | 4 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 6 yr | CANADA | 0.02093 SE | ||
| Growth Rate | 0.0038 | mm/d | Male | 4 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 6 yr | CANADA | 0.01654 SE | ||
| Growth Rate | 0.0304 | mm/d | Female | 4 | Algonquin Provincal Park, Ontario [lat., 45^o35'N; long., 78^o30'W] | Exposure Factor Datasets | 7 yr | CANADA | 0.02256 SE |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Units | Sex | Life Cycle Stage | Sample Size | Location | Type | Error | Lab |
|---|---|---|---|---|---|---|---|---|---|---|
| Metabolic Rate | 15.5 | Oxygen consumption measured at 5C, frogs acclimated at 5C, mean body weight = 646 g (25.5 SE) | ul O2/g/hr | Not Reported | Adult | 8 | Exposure Factor Datasets | 1.2 SE | Laboratory | |
| Metabolic Rate | 53.3 | Oxygen consumption measured at 20C, frogs acclimated at 20C, mean body weight = 621 g (30.5 SE) | ul O2/g/hr | Not Reported | Adult | 8 | Exposure Factor Datasets | 2.1 SE | Laboratory |
| Exposure Endpoint Type | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
|---|---|---|---|---|---|---|---|
| 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 |
