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Taricha torosa

Citation:

Residues of cutthroat trout (Salmo clarkii) and California newts (Tarichia torosa) from a lake treated with technical chlordane

Author(s)
Albright, L.J., P.C. Oloffs and S.Y Szeto
Pages
333-349
Year
Issue
4
Volume
815
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

Pseudacris regilla

Citation:

Comparative Toxicity of Guthion and Guthion 2S to Xenopus laevis and Pseudacris regilla tadpoles

Author(s)
Schuytema, G.S., A.V. Nebeker and W.L. Griffis
Pages
382-388
Year
Volume
54
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
Citation:

Comparative toxicity of diuron on survival and growth of Pacific treefrog, bullfrog, red-legged frog and African clawed frog embryos and tadpoles

Author(s)
Schuytema, G.S. and A.V. Nebeker
Pages
370-376
Year
Volume
34
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
Citation:

Comparative effects of ammonium and nitrate compounds on Pacific treefrog and African clawed frog embryos

Author(s)
Schuytema, G.S. and A.V. Nebeker
Pages
200-206
Year
Volume
36
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

Lithobates catesbeianus

Citation:

Behavioral and histopathological effects of fluoranthene on bullfrog larvae (Rana catesbeiana)

Author(s)
Walker, Sean E., Douglas H. Taylor and James T. Oris
Pages
734-739
Year
Volume
17
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
FLUORANTHENE increase @ 10.97 - 59.48 ug/l incidence of structural disorganization and necrosis of the integument Not Reported Tadpole 20/group 0, 10.97, 37.97, 59.48 ug/l with simulated solar UV radiation TOX-Non-Repro-Sublethal - organ/system effects 96 hr water-borne; flow-through Toxicity Factor Datasets
FLUORANTHENE increase @ 37.97 ug/l total distance travelled Not Reported Tadpole 20/group 0, 10.97, 37.97, 59.48 ug/l with simulated solar UV radiation TOX-Non-Repro-Sublethal - behavioral effects 96 hr water-borne; flow-through Toxicity Factor Datasets
Citation:

Comparative toxicity of diuron on survival and growth of Pacific treefrog, bullfrog, red-legged frog and African clawed frog embryos and tadpoles

Author(s)
Schuytema, G.S. and A.V. Nebeker
Pages
370-376
Year
Volume
34
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DIURON 12.7 mg/l (95% CI; 9.8 - 16.4) 21 d LC50 Not Reported Tadpole 5/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 21 d waterborne Toxicity Factor Datasets
DIURON 7.6 mg/l lowest NOAEL based on body weight endpoint Not Reported Tadpole 5/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 21 d waterborne Toxicity Factor Datasets
Citation:

The use of simultaneous multiple species acute toxicity test to compare the relative sensitivities of aquatic organisms to mercury

Author(s)
McCrary, J.E. and M.G. Heagler
Pages
73-81
Year
Volume
A32
Chemical Endpoint Value Endpoint Description Range Units Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
MERCURIC CHLORIDE 63.36 96 hour LC50 (95% Confidence Interval); based on measured concentrations 37.02 - 108.30 (95% CI) ug Hg/L Not Reported Not Reported 10/dose 0, 1.4, 3.9, 12.0, 110.0 and 487 ug Hg/L (mean daily measured concn.) TOX-MORT - toxicity benchmarks 96 hr waterborne Toxicity Factor Datasets
Citation:

Elevated maintenance costs in an anuran (Rana catesbeiana) exposed to a mixture of trace elements during the embryonic and early larval periods

Author(s)
Rowe, Christopher L., Owen M. Kinney, Roy D. Nagle and Justin D. Congdon
Pages
27-35
Year
Volume
71
Chemical Endpoint Value Endpoint Description Units Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
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 Savannah River 8-11 80-d tadpole residue levels (ppm dry wt) at contaminated (C) vs reference (R) sites: Chromium, C=27.25 +/- 6.22, R=8.58 +/- 0.35; Copper, C=55.12 +/- 5.05, R=17.40 +/- 1.74; Arsenic C=25.95 +/- 3.08, R=0.75 +/- 0.20; Selenium, C=25.27 +/- 1.67, R=0.83 +/- TOX-Non-Repro-Sublethal - whole animal NR site contamination Toxicity Factor Datasets
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 Savannah River Not Reported 80-d tadpole residue levels (ppm dry wt) at contaminated (C) vs reference (R) sites: Chromium, C=27.25 +/- 6.22, R=8.58 +/- 0.35; Copper, C=55.12 +/- 5.05, R=17.40 +/- 1.74; Arsenic C=25.95 +/- 3.08, R=0.75 +/- 0.20; Selenium, C=25.27 +/- 1.67, R=0.83 +/- TOX-REPRO - reproductive success NR site contamination Toxicity Factor Datasets
Citation:
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
METHYLPARATHION 79.5 in loco heart rate Not Reported Tadpole NR 36 10 µg/L TOX-MORT - dose-response data 48 h Toxicity Factor Datasets
PENOXSULAM 7.52 mg/L LC50 Not Reported Tadpole Experimental Frog Farm, São Paulo 6 (+ vegetable oil adjuvant): 2.88 + 55.80; 4.32 + 83.70; 5.76 + 111.60; 7.20 mg/L C 139.50; 8.64 + 167.40 TOX-MORT - toxicity benchmarks 96 hr Waterborne Toxicity Factor Datasets

Rana aurora

Citation:

Comparative toxicity of diuron on survival and growth of Pacific treefrog, bullfrog, red-legged frog and African clawed frog embryos and tadpoles

Author(s)
Schuytema, G.S. and A.V. Nebeker
Pages
370-376
Year
Volume
34
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DIURON 22.2 mg/l (95% CI; 19.8 - 25.0) 14 d LC50 Not Reported Tadpole 5/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 7.6 mg/l lowest NOAEL based on body weight endpoint Not Reported Tadpole 5/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

Anaxyrus boreas

Citation:

Toxicity of mine drainage to embryonic and larval boreal toads (Bufonidae: Bufo boreas)

Author(s)
Porter, Kenneth R and Dean E. Hakanson
Pages
327-331
Year
Issue
2
Volume
1976
Chemical Endpoint Value Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
IRON SULFATE increase @ 30-288 mg/l Not Reported Juvenile 5-25/dose 0, 3, 10, 20, 30, 35, 40, 72, 144, 288 mg/l Fe++ TOX-MORT - dose-response data 39 d waterborne Toxicity Factor Datasets

Ambystoma macrodactylum

Citation:

Methoxychlor alters hatching and larval startle response in the salamander Ambystoma macrodactylum

Author(s)
Ingermann, R.L., D.C. Bencic and V.P. Eroschenko
Pages
815-821
Year
Volume
59
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
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

Dicamptodon tenebrosus, Ensatina eschscholtzii

Citation:

Response of amphibians to clearcutting, burning, and glyphosate application in the Oregon Coast Range

Author(s)
Cole, Elizabeth C., William C. McComb, Michael Newton, Carol L. Chambers, J.P. Leeming
Pages
656-664
Year
Volume
61
Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
no effect capture rates between logged and burned units and the logged, burned and sprayed units during the year after spraying Not Reported Not Reported Oregon Coast Range 3 units/treatment control or 1.3 kg/ha TOX-POP - size effects single field application Toxicity Factor Datasets
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