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Lithobates catesbeianus

Citation:

Oral deformities in tadpoles (Rana catesbeiana) associated with coal ash deposition: Effects on grazing ability and growth

Author(s)
Rowe, Christopher L., Owen M. Kinney, Alison P. Fiori and Justin D. Congdon
Pages
723-730
Year
Volume
36
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique 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 Savannah River, Aiken 575-1048 mean whole body concn. at contaminated (C) compared to reference (R) site: As, C=48.9 +/- 2.6SE, R=2.5 +/-0.2SE; Ba, C=211.5 +/- 14.9SE, R=81.2 +/- 5.2SE; Cd, C=1.71 +/- 0.5SE, R=0.15 +/- 0.04SE; Cr, C=17.2 +/- 0.5SE, R=1.4 +/- 0.3SE; Cu, C=31.4 +/- 1.5SE TOX-REPRO - development NR site contamination 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 Savannah River, Aiken 3 animals/site sediment concn. at contaminated (C) compared to reference (R) site: As, C=70.8 +/- 12.5SE, R=<1.0; Ba, C=418.7 +/- 34.0SE, R=11.8 +/- 0.6SE; Cd, C=0.57 +/- 0.05SE, R=0.03 +/- 0.00SE; Cr, C=70.8 +/- 12.5SE, R=<1.0; Cu, C=71.8 +/- 12.3SE, R=<1.0; Se, C=6.21 TOX-EXP IND - accumulation NR site contamination Toxicity Factor Datasets
Citation:

Teratogenesis, toxicity and bioaccumulation in frogs exposed to dieldrin

Author(s)
Schuytema, Gerald S., Alan V. Nebeker, William L. Griffis and Karsten N. Wilson
Pages
332-350
Year
Volume
21
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DIELDRIN 34.4 ug/l (95% CL: 31.1 - 38.1 ug/l) LC50 Not Reported Embryo 20 animals/replicate; 4 replicates/dose 0, 0.8, 2.0, 4.9, 11.0, 25.4, 64.8, 154.8 ug/l TOX-MORT - toxicity benchmarks 21 d waterborne Toxicity Factor Datasets
DIELDRIN 25.1 ug/l LOAEL, based on mortality but gross spinal deformities also observed Not Reported Embryo 20 animals/replicate; 4 replicates/dose 0, 0.8, 2.0, 4.9, 11.0, 25.4, 64.8, 154.8 ug/l TOX-MORT - toxicity benchmarks 21 d waterborne Toxicity Factor Datasets
DIELDRIN 11.0 ug/l NOAEL Not Reported Embryo 20 animals/replicate; 4 replicates/dose 0, 0.8, 2.0, 4.9, 11.0, 25.4, 64.8, 154.8 ug/l TOX-MORT - toxicity benchmarks 21 d waterborne Toxicity Factor Datasets
DIELDRIN 8.7 ug/l (95% CL: 7.8-9.7 ug/l) LC50 Not Reported Tadpole 20 animals/replicate; 4 replicates/dose 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l TOX-MORT - toxicity benchmarks 4 d waterborne Toxicity Factor Datasets
DIELDRIN 11.2 ug/l LOAEL Not Reported Tadpole 20 animals/replicate; 4 replicates/dose 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l TOX-MORT - toxicity benchmarks 4 d waterborne Toxicity Factor Datasets
DIELDRIN 4.0 ug/l NOAEL Not Reported Tadpole 20 animals/replicate; 4 replicates/dose 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l TOX-MORT - toxicity benchmarks 4 d waterborne Toxicity Factor Datasets
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 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l TOX-EXP IND - accumulation 4 d waterborne Toxicity Factor Datasets
DIELDRIN 6.0 ug/g at 11.2 ug/l whole body dieldrin concentration (ug/g, wet wt.) Not Reported Tadpole Not Reported 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l TOX-EXP IND - accumulation 4 d waterborne Toxicity Factor Datasets
DIELDRIN 2.0 ug/g at 4.0 ug/l whole body dieldrin concentration (ug/g, wet wt.) Not Reported Tadpole Not Reported 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l TOX-EXP IND - accumulation 4 d waterborne Toxicity Factor Datasets
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 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l TOX-EXP IND - accumulation 4 d waterborne Toxicity Factor Datasets
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 0, 2.2, 4.0, 11.2, 46.5, 179.9 ug/l TOX-EXP IND - accumulation 4 d waterborne Toxicity Factor Datasets
DIELDRIN 30.3 ug/l (95% CL: 26.2 - 35.2 ug/l) LC50 Not Reported Tadpole 20 animals/replicate; 4 replicates/dose 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l TOX-MORT - toxicity benchmarks 4 d waterborne Toxicity Factor Datasets
DIELDRIN 52.3 ug/l LOAEL Not Reported Tadpole 20 animals/replicate; 4 replicates/dose 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l TOX-MORT - toxicity benchmarks 4 d waterborne Toxicity Factor Datasets
DIELDRIN 12.3 ug/l NOAEL Not Reported Tadpole 20 animals/replicate; 4 replicates/dose 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l TOX-MORT - toxicity benchmarks 4 d waterborne Toxicity Factor Datasets
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 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l TOX-EXP IND - accumulation 4 d waterborne Toxicity Factor Datasets
DIELDRIN 19.0 ug/g at 52.3 ug/l whole body dieldrin concentration (ug/g, wet wt.) Not Reported Tadpole Not Reported 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l TOX-EXP IND - accumulation 4 d waterborne Toxicity Factor Datasets
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 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l TOX-EXP IND - accumulation 4 d waterborne Toxicity Factor Datasets
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 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l TOX-EXP IND - accumulation 4 d waterborne Toxicity Factor Datasets
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 0, 1.0, 3.8, 12.3, 52.3, 182.0 ug/l TOX-EXP IND - accumulation 4 d waterborne Toxicity Factor Datasets
Citation:

Behavior of tadpoles of the bullfrog, Rana catesbeiana, in response to sublethal lead exposure

Author(s)
Steele, Craig W., Shari Strickler-Shaw and Douglas H. Taylor
Pages
331-344
Year
Volume
14
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
LEAD NITRATE no effect preference/avoidance behavior and spontaneous locomotor activity Not Reported Tadpole 8 animals/dose 0, 500, 625, 750, 1000 ug/l TOX-REPRO - behavior 6 d waterborne Toxicity Factor Datasets
Citation:

Toxicity of Zectran insecticide to several wildlife species

Author(s)
Tucker, Richard K. and D. Glen Crabtree
Pages
1307-1310
Year
Issue
6
Volume
62
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
MEXACARBATE 283 - 800 mg/kg LD50, estimated Male Not Reported 14 NR TOX-MORT - toxicity benchmarks single gavage Toxicity Factor Datasets

Falco sparverius

Citation:

Tissue lead distribution and hematologic effects in American kestrels (Falco sparverius L.) fed biologically incorporated lead

Author(s)
Custer, Thomas W., J.Christian Franson, and Oliver H. Pattee
Pages
39-43
Year
Issue
1
Volume
20
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
LEAD COMPOUNDS 7.84 ppm femur at 120 ppm; 16.60 ppm femur at 212 ppm; 18.44 ppm femur at 448 ppm mean lead concentration in femur Both Male and Female Adult 8-14/group 0.5, 120, 212, 448 ppm (dry wt) TOX-EXP IND - accumulation 60 d diet Toxicity Factor Datasets
LEAD COMPOUNDS no effect packed cell volume, hemoglogin concentration, erythrocyte counts Both Male and Female Adult 8-14/group 0.5, 120, 212, 448 ppm (dry wt) TOX-Non-Repro-Sublethal - cellular/biochemical effects 60 d diet Toxicity Factor Datasets
Citation:

Methyl mercury: Its effect on eggshell thickness

Author(s)
Peakall, David B. and Jefferey L. Lincer
Pages
89-90
Year
Issue
2
Volume
8
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DIMETHYLMERCURY no effect eggshell thickness Female Adult Not Reported 0, 10 ppm TOX-REPRO - physiology 3 mo diet Toxicity Factor Datasets
Citation:

Enzymatic changes in the oviduct associated with DDE-induced eggshell thinning in the kestrel, Falco sparverius

Author(s)
Bird, David M., David B. Peakall and David S. Miller
Pages
22-24
Year
Volume
31
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DDE (4,4'-) decrease eggshell thickness Female Adult 8/group 6 mg/kg bw/d TOX-REPRO - physiology NR diet Toxicity Factor Datasets
DDE (4,4'-) decrease Calcium ATPase activity of shell gland Female Adult 8/group 6 mg/kg bw/d TOX-REPRO - physiology NR diet Toxicity Factor Datasets
DDE (4,4'-) decrease carbonic anhydrase activity of shell gland Female Adult 8/group 6 mg/kg bw/d TOX-REPRO - physiology NR diet Toxicity Factor Datasets
DDE (4,4'-) no effect calcium concentration in blood Female Adult 8/group 6 mg/kg bw/d TOX-REPRO - physiology NR diet Toxicity Factor Datasets
Citation:

DDE-induced eggshell thinning in the American kestrel: A comparison of the field situation and laboratory results

Author(s)
Lincer, Jeffrey L.
Pages
781-793
Year
Issue
3
Volume
12
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DDE (4,4'-) decrease at all doses (15.1-29.2%) eggshell thickness Female Adult 2-5 pairs/dose 0, 0.3, 3, 6, 10 ppm (wet wt) TOX-REPRO - physiology 6 mo diet Toxicity Factor Datasets
Citation:

Organochlorine contaminants in a terrestrial foodweb on the Niagara Peninsula, Ontario, Canada 1987 - 89

Author(s)
Hebert, C.E., D.V. Weseloh, L. Kot and V. Glooschenko
Pages
356-366
Year
Volume
26
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Location Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
DDE (4,4'-) 5.53 mg/kg egg (wet wt) mean DDE concentration in eggs (pooled analyses) Both Male and Female Embryo N. Niagra Peninsula, Ontario 10 eggs 0.009 mg/kg plant; 0.343 mg/kg soil; 0.605 mg/kg worm; 0.016 mg/kg vole TOX-EXP IND - accumulation NR diet Toxicity Factor Datasets
Citation:

Eggshell thickness and reproduction in American kestrels exposed to chronic dietary lead

Author(s)
Pattee, Oliver H.
Pages
29-34
Year
Volume
13
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
LEAD (elemental) no effect eggshell thickness Female Adult 16 pairs/group 0, 10, 50 ppm TOX-REPRO - physiology 5-7 mo diet Toxicity Factor Datasets
LEAD (elemental) no effect lead concentration in eggshell Female Adult 16 pairs/group 0, 10, 50 ppm TOX-EXP IND - accumulation 5-7 mo diet Toxicity Factor Datasets
LEAD (elemental) 62.0 ppm tibia, 13.5 ppm humeri at 50 ppm lead concentrations in bones Female Adult 16 pairs/group 0, 10, 50 ppm TOX-EXP IND - accumulation 5-7 mo diet Toxicity Factor Datasets
Citation:

Methyl parathion and fenvalerate toxicity in American kestrels: acute physiological responses and effects of cold

Author(s)
Rattner, Barnett A. and J. Christian Franson
Pages
787-792
Year
Volume
62
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
METHYLPARATHION increased at 2, 3 mg/kg bw abnormal posture, ataxia, paresis Both Male and Female Adult 5/dose 0, 0.375, 1.0, 2.0, 3.0 mg/kg bw TOX-Non-Repro-Sublethal - behavioral effects single gavage Toxicity Factor Datasets
METHYLPARATHION increase at 3 mg/kg bw mortality rate 2 hr post-dose Both Male and Female Adult 5/dose 0, 0.375, 1.0, 2.0, 3.0 mg/kg bw TOX-MORT - dose-response data single gavage Toxicity Factor Datasets
METHYLPARATHION decrease at 2, 3 mg/kg bw cloacal temperature Both Male and Female Adult 5/dose 0, 0.375, 1.0, 2.0, 3.0 mg/kg bw TOX-Non-Repro-Sublethal - whole animal single gavage Toxicity Factor Datasets

Anas platyrhynchos

Citation:

Toxicity of Zectran insecticide to several wildlife species

Author(s)
Tucker, Richard K. and D. Glen Crabtree
Pages
1307-1310
Year
Issue
6
Volume
62
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
MEXACARBATE 3.0 mg/kg LD50 Both Male and Female Not Reported 12 NR TOX-MORT - toxicity benchmarks single gavage Toxicity Factor Datasets

Zenaida macroura

Citation:

Toxicity of Zectran insecticide to several wildlife species

Author(s)
Tucker, Richard K. and D. Glen Crabtree
Pages
1307-1310
Year
Issue
6
Volume
62
Chemical Endpoint Value Endpoint Description Sex Life Cycle Stage Sample Size Tox Exposure Toxicity Endpoint Type Tox Exposure Duration Tox Exposure Technique Type
MEXACARBATE 2.83 mg/kg LD50 Both Male and Female Not Reported 8 NR TOX-MORT - toxicity benchmarks single gavage Toxicity Factor Datasets
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