ENDOSULFAN
Amphibians, Frogs and toads (Anura), Foothill Yellow-Legged Frog (Rana boylii)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries |
---|---|---|---|---|---|---|---|---|---|
ENDOSULFAN | No effect | Time to metamorphosis | B | Tadpole | 18/treatment | Eggs from Soda Creek | Toxicity Factor Datasets | Lake | USA |
ENDOSULFAN | Decreased | Cholinesterase activity | B | Tadpole | 18/treatment | Eggs from Soda Creek | Toxicity Factor Datasets | Lake | USA |
ENDOSULFAN | Decreased | Snout-vent length | B | Tadpole | 18/treatment | Eggs from Soda Creek | Toxicity Factor Datasets | Lake | USA |
ENDOSULFAN | Logistic: 0.233 ug/L; SK: 0.55 ug/L | LC50 | B | Tadpole | 18/treatment | Eggs from Soda Creek | Toxicity Factor Datasets | Lake | USA |
ENDOSULFAN | Decreased | Body mass | B | Tadpole | 18/treatment | Eggs from Soda Creek | Toxicity Factor Datasets | Lake | USA |
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | California Counties | Countries | Lab |
---|---|---|---|---|---|---|---|---|---|---|
ENDOSULFAN | I: 0.11, II: 0.19 µg/g ww | Feather concentration | NR | Both Adults and Juveniles | 45 | Rio Negro Province; rural site: Bariloche; ag site: Valle | Toxicity Factor Datasets | ARGENTINA | ||
ENDOSULFAN | 8.2 ± 22.25 ng/g ww | Ʃendosulphan liver concentration | NR | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL | ||
ENDOSULFAN | Not detected | Plasma concentration of endosulfan I | B | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO | ||
ENDOSULFAN | Not detected | Plasma concentration of endosulfan II | B | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO | ||
ENDOSULFAN | 1,147 [623-2,726 (84% CI)] | LC90 | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | |
ENDOSULFAN | 7 | LOEC | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | |
ENDOSULFAN | 172 [117-283 (84% CI)] ppb | LC90 | NR | Embryo | 10 | Pymatuning Laboratory of Ecology, Pittsburgh, PA | Toxicity Factor Datasets | Lab | USA | |
ENDOSULFAN | 7 ppb | LOEC | NR | Embryo | 10 | Pymatuning Laboratory of Ecology, Pittsburgh, PA | Toxicity Factor Datasets | Lab | USA | |
ENDOSULFAN | 1.7 [1.1-2.4 (84% CI)] ppb | LC10 | NR | Embryo | 10 | Pymatuning Laboratory of Ecology, Pittsburgh, PA | Toxicity Factor Datasets | Lab | USA | |
ENDOSULFAN | 13.9 [11.1-17.5 (84% CI)] ppb | LC50 | NR | Embryo | 10 | Pymatuning Laboratory of Ecology, Pittsburgh, PA | Toxicity Factor Datasets | Lab | USA | |
ENDOSULFAN | 114 [79.0-187 (84% CI)] ppb | LC90 | NR | Embryo | 10 | Pymatuning Laboratory of Ecology, Pittsburgh, PA | Toxicity Factor Datasets | Lab | USA | |
ENDOSULFAN | 7 | LOEC | NR | Embryo | 10 | Pymatuning Laboratory of Ecology, Pittsburgh, PA | Toxicity Factor Datasets | Lab | USA | |
ENDOSULFAN | 21.4 [17.0-27.0 (84%CI)] ppb | LC50 | NR | Embryo | 10 | Pymatuning Laboratory of Ecology, Pittsburgh, PA | Toxicity Factor Datasets | Lab | USA | |
ENDOSULFAN | 2.7 [1.7-3.7 (84% CI)] ppb | LC10 | NR | Embryo | 10 | Pymatuning Laboratory of Ecology, Pittsburgh, PA | Toxicity Factor Datasets | Lab | USA | |
ENDOSULFAN | 7 | LOEC | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | Laboratory |
ENDOSULFAN | 2.8 ±11.75 ng/g ww | Endosuphan sulphate liver concentration | NR | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL | ||
ENDOSULFAN | 0.10 µg/g lw | Blubber concentration | B | Not Reported | 18 | Todos Santos Bay, Ensenada, Baja California | Toxicity Factor Datasets | MEXICO | ||
ENDOSULFAN | 10.6 ng/g lw | Blood concentration | B | Pup | 5 | 3 sites in eastern AK | Toxicity Factor Datasets | USA | ||
ENDOSULFAN | 0.0 ng/g lw | Blood concentration | B | Juvenile | 6 | 3 sites in eastern AK | Toxicity Factor Datasets | USA | ||
ENDOSULFAN | 7.2 ng/g lw | Blood concentration | F | Adult | 18 | 3 sites in eastern AK | Toxicity Factor Datasets | USA | ||
ENDOSULFAN | 15.5 ng/g lw | Blood concentration | M | Adult | 11 | 3 sites in eastern AK | Toxicity Factor Datasets | USA | ||
ENDOSULFAN | Not detected | Plasma concentration of endosulfan sulfate | B | Juvenile | 19 | Punta Abreojos | Toxicity Factor Datasets | MEXICO | ||
ENDOSULFAN | 0.005-1.22 ng/mL | Plasma concentration of endosulfan I | B | Juvenile | 13 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO | ||
ENDOSULFAN | 0.005-7.54 ng/mL | Plasma concentration of endosulfan II | B | Juvenile | 13 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO | ||
ENDOSULFAN | 0.005-12.99 ng/mL | Plasma concentration of endosulfan sulfate | B | Juvenile | 12 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO | ||
ENDOSULFAN | No effect | Hatching success | NR | Embryo | 375 | South Okanagan Valley, British Columbia | Toxicity Factor Datasets | CANADA | Laboratory | |
ENDOSULFAN | 5.2 ± 19.52 ng/g ww | α isomer fat concentration | NR | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL | ||
ENDOSULFAN | 5.0 [2.9-7.6 (84% CI)] | LC10 | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | Laboratory |
ENDOSULFAN | Max: 38.6 ng/g ww | β isomer fat concentration | NR | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL | ||
ENDOSULFAN | 76.1 [56.3-109 (84% CI)] | LC50 | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | Laboratory |
ENDOSULFAN | 3.4 ± 9.81 ng/g ww | Endosuphan sulfate fat concentration | NR | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL | ||
ENDOSULFAN | 4.9 [3.1-7.0 (84% CI)] | LC10 | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | Laboratory |
ENDOSULFAN | 8.1 ± 26.15 ng/g ww | Ʃendosulphan fat concentration | NR | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL | ||
ENDOSULFAN | 46.8 [36.5-61.5 (84% CI)] | LC50 | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | Laboratory |
ENDOSULFAN | 6.7 ± 16.37 ng/g ww | α isomer liver concentration | NR | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL | ||
ENDOSULFAN | 446 [282-832 (84% CI)] | LC90 | NR | Tadpole | 120 | University of Pittsburgh | Toxicity Factor Datasets | Lab | USA | Laboratory |
ENDOSULFAN | 1.7 ± 3.92 ng/g ww | β isomer liver concentration | NR | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL |
Pacific Green Turtle (Chelonia mydas)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
ENDOSULFAN | Not detected | Plasma concentration of endosulfan I | Both Male and Female | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
ENDOSULFAN | Not detected | Plasma concentration of endosulfan II | Both Male and Female | Juvenile | 39 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
ENDOSULFAN | Not detected | Plasma concentration of endosulfan sulfate | Both Male and Female | Juvenile | 19 | Punta Abreojos | Toxicity Factor Datasets | MEXICO |
ENDOSULFAN | 0.005-1.22 ng/mL | Plasma concentration of endosulfan I | Both Male and Female | Juvenile | 13 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO |
ENDOSULFAN | 0.005-7.54 ng/mL | Plasma concentration of endosulfan II | Both Male and Female | Juvenile | 13 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO |
ENDOSULFAN | 0.005-12.99 ng/mL | Plasma concentration of endosulfan sulfate | Both Male and Female | Juvenile | 12 | Bahía Magdalena | Toxicity Factor Datasets | MEXICO |
ENDOSULFAN | 5.2 ± 19.52 ng/g ww | ? isomer fat concentration | Not Reported | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL |
ENDOSULFAN | Max: 38.6 ng/g ww | ? isomer fat concentration | Not Reported | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL |
ENDOSULFAN | 3.4 ± 9.81 ng/g ww | Endosuphan sulfate fat concentration | Not Reported | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL |
ENDOSULFAN | 8.1 ± 26.15 ng/g ww | ?endosulphan fat concentration | Not Reported | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL |
ENDOSULFAN | 6.7 ± 16.37 ng/g ww | ? isomer liver concentration | Not Reported | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL |
ENDOSULFAN | 1.7 ± 3.92 ng/g ww | ? isomer liver concentration | Not Reported | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL |
ENDOSULFAN | 2.8 ±11.75 ng/g ww | Endosuphan sulphate liver concentration | Not Reported | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL |
ENDOSULFAN | 8.2 ± 22.25 ng/g ww | ?endosulphan liver concentration | Not Reported | Juvenile | 64 | SE coast | Toxicity Factor Datasets | BRAZIL |
Bullfrog (Lithobates catesbeianus formerly Rana catesbeiana)
Chemical | Endpoint Value | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|
ENDOSULFAN | increase at 0.1 and 0.5 lbs/acre | Not Reported | Tadpole | 10 animals/dose | ponds, southern San Joaquin Valley | Toxicity Factor Datasets |
Mourning Dove (Zenaida macroura)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type |
---|---|---|---|---|---|---|---|
AZINPHOS-METHYL (GUTHION), DIMETHOATE, ENDOSULFAN, METHYLPARATHION, PARATHION, PERMETHRIN, THIRAM, ZIRAM | decreased in conventional orchards | daily survival rates | Not Reported | Nestling | 29 conventional nests | York Springs, Adams Co. | Toxicity Factor Datasets |
AZINPHOS-METHYL (GUTHION), DIMETHOATE, ENDOSULFAN, METHYLPARATHION, PARATHION, PERMETHRIN, THIRAM, ZIRAM | decreased in conventional orchards | hatching success | Not Reported | Nestling | 29 conventional nests | York Springs, Adams Co. | Toxicity Factor Datasets |
AZINPHOS-METHYL (GUTHION), DIMETHOATE, ENDOSULFAN, METHYLPARATHION, PARATHION, PERMETHRIN, THIRAM, ZIRAM | no effect | numbers of eggs laid or number of fledglings produced | Not Reported | Both Adults and Juveniles | 29 conventional nests | York Springs, Adams Co. | Toxicity Factor Datasets |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
ENDOSULFAN | 27.8 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 36 hours | Laboratory | |
ENDOSULFAN | 6.47 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 7 days | Laboratory | |
ENDOSULFAN | 7.89 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 30 days | Laboratory | |
ENDOSULFAN | 34.4 mg/kg | LD50 | Both Male and Female | Juvenile | 5 | Toxicity Factor Datasets | 6 mos | Laboratory |