Field Name | Description |
---|---|
% Effect | The magnitude of the effect (e.g., % mortality; change in weight; change in length; percent hatch; etc.). |
Analyte | The chemical substance used to create the exposure. |
CAS | CAS registry number is a unique numerical identifier assigned by Chemical Abstract Service (CAS) to a chemical substance. |
COLL | Where the animal was obtained: C (cultured-reared in laboratory); W (collected from wild); N/I (No Information); N/R (Not Reported). |
Comments | Commonly supports the effects data. |
Common name | Common name of the test animal. |
Control | The control response for the observed effect (e.g., survival, growth, reproduction; etc.). |
Dose | The frequency with which the contaminant was applied during the test. |
Duration | The duration of the exposure period: hr (hours); d (days) wk (weeks), mo (months), yr (years). |
Effect | The type of toxicological effect observed in the test animal (e.g., survival, growth, reproduction). |
ERED ID | Unique identification number autogenerated by database. |
ExpConc | The exposure concentration and units. |
Fraction | The test animal tissue used to determine tissue residue (e.g., whole body, soft tissue, liver, etc.). |
Genus Species | Scientific name of the test animal. |
Media | Type of water used to test animal: FW (freshwater); SW (saltwater) |
Mix | Whether the analyte was tested as part of a mixture of analytes or individually: yes (part of mixture), no (single), or N/I (No information). |
Risk | Summary of the risk (e.g., ED, NOED, LOED) an analyte might pose to the test animal. Previously, many risk numbers were assigned to results. Going forward ERED will not report a risk number unless it is reported in the study. |
Route | The route by which the analyte was intended to enter the body: aquatic; diet; injection. |
Signif | Whether the effect was significantly different, usually compared to the control for laboratory studies: Yes (significant); No (not significant). |
Source | Reference from which data was obtained. |
Spiked | Whether the analyte was spiked into the route (aquatic, diet, sediment, injection): yes (analyte spiked), no (analyte not spiked) |
ST | Study type: L (Lab); F (Field); L/F (Lab/Field); Meso (Mesocosm); Micro (Microcosm); N/I (No Information). |
Stage | Life stage of the test animal (e.g., egg, larval, juvenile, adult). |
Tissue ww (mg/kg) | Tissue residue of analyte in the test animal tissue (mg/kg wet weight). |
Trend | The trend of the effect, usually compared to the control for laboratory studies: INC (increase); DEC (decrease), NEF (No effect). |
You are viewing Chordata: Vert (fishes; non-salmonid) and Pesticides-insecticides
Genus Species | ERED ID | ST | Common | Stage | COLL | Analyte | CAS | MX | SPK | H2O | Route | CONC | Dose | DUR | Residue mg/kg ww |
Fraction | Effect | Trend | Signif | % Effect | Control | Risk | Comments | Source |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Lagodon rhomboides | 19767 | L | Pinfish | N/R | W | Chlordane | 57-74-9 | N | Y | SW | aqueous | 5.4 µg/L | continuous | 96 hr | 16.6 | whole body | mortality | INC | N/R | 30% | 0% | N/R | increase in mortality; no stats | Parrish et al. 1976. Chlordane: effects on several estuarine .... J Toxicol Environ Health 1:485-494, 1976. |
Lagodon rhomboides | 19768 | L | Pinfish | N/R | W | Chlordane | 57-74-9 | N | Y | SW | aqueous | 7.3 µg/L | continuous | 96 hr | 55 | whole body | mortality | INC | N/R | 70% | 0% | N/R | increase in mortality; no stats | Parrish et al. 1976. Chlordane: effects on several estuarine .... J Toxicol Environ Health 1:485-494, 1976. |
Lagodon rhomboides | 19769 | L | Pinfish | N/R | W | Chlordane | 57-74-9 | N | Y | SW | aqueous | 8.7 µg/L | continuous | 96 hr | 61 | whole body | mortality | INC | N/R | 70% | 0% | N/R | increase in mortality; no stats | Parrish et al. 1976. Chlordane: effects on several estuarine .... J Toxicol Environ Health 1:485-494, 1976. |
Lagodon rhomboides | 19770 | L | Pinfish | N/R | W | Chlordane | 57-74-9 | N | Y | SW | aqueous | 9.6 µg/L | continuous | 96 hr | 70 | whole body | mortality | INC | N/R | 85% | 0% | N/R | increase in mortality; no stats | Parrish et al. 1976. Chlordane: effects on several estuarine .... J Toxicol Environ Health 1:485-494, 1976. |
Lagodon rhomboides | 19771 | L | Pinfish | N/R | W | Chlordane | 57-74-9 | N | Y | SW | aqueous | 15.2 µg/L | continuous | 96 hr | N/R | mortality | INC | N/R | 95% | 0% | N/R | increase in mortality; no stats | Parrish et al. 1976. Chlordane: effects on several estuarine .... J Toxicol Environ Health 1:485-494, 1976. | |
Leiostomus xanthurus | 22397 | L | spot croaker | juvenile | W | Chlordecone | 143-50-0 | N | Y | SW | diet | 0.30 µg/g | N/I | 56 d | 0.33 | whole body | growth | NEF | N/R | N/R | N/R | N/R | no relationship between body burden and fish weight observed; no comparison to the control | Stehlik and Merriner. 1983. Effects of accumulated dietary Kepone on.... Aquat Toxicol 3:345-358. |
Leiostomus xanthurus | 3888 | L | spot croaker | juvenile | W | Chlordecone | 143-50-0 | N | Y | SW | diet | 3.3 µg/g | N/I | 28 d | 2.7 | whole body | mortality | INC | N/R | 78% | N/R | N/R | 19 spot alive out of 90 spot; no comparison made to the control | Stehlik and Merriner. 1983. Effects of accumulated dietary Kepone on.... Aquat Toxicol 3:345-358. |
Leiostomus xanthurus | 3889 | L | spot croaker | juvenile | W | Chlordecone | 143-50-0 | N | Y | SW | diet | 0.59 µg/g | N/I | 56 d | 0.7 | whole body | growth | NEF | N/R | N/R | N/R | N/R | no relationship between body burden and fish weight observed; no comparison to the control | Stehlik and Merriner. 1983. Effects of accumulated dietary Kepone on.... Aquat Toxicol 3:345-358. |
Oreochromis mossambicus | 11324 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 13.3 | carcass | histopathology | N/I | N/I | N/I | N/I | LOEC | Large sub-epithelial spaces in secondary lamellae | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11325 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 24 | carcass | histopathology | N/I | N/I | N/I | N/I | LOEC | gill raker elongation and thinning | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11326 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 40 | carcass | histopathology | N/I | N/I | N/I | N/I | LOEC | Lamellae buldging | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11327 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 40 | carcass | histopathology | N/I | N/I | Yes | N/I | LOEC | Lesions and erosions at the base of lamellae | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11328 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 182.3 | carcass | histopathology | N/I | N/I | N/I | N/I | LOEC | Fusion of secondary lamellae and mucus coat | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11329 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 12.9 | head | histopathology | N/I | N/I | N/I | N/I | LOEC | Large sub-epithelial spaces in secondary lamellae | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11330 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 126 | viscera | histopathology | N/I | N/I | N/I | N/I | LOEC | Large sub-epithelial spaces in secondary lamellae | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11331 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 24 | head | histopathology | N/I | N/I | N/I | N/I | LOEC | gill raker elongation and thinning | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Micropterus salmoides | 1445 | Meso | largemouth bass | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 1 ng/L | N/I | 7 | 0.23 | whole body | biochemistry | DEC | N/I | 20 | N/I | ED 20 | inhibition of acetylcholinesterase activity | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Lepomis macrochirus | 1446 | Meso | Bluegill | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 1 ng/L | N/I | 7 | 0.2 | whole body | biochemistry | DEC | N/I | 60 | N/I | ED 60 | inhibition of acetylcholinesterase activity | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Micropterus salmoides | 1447 | Meso | largemouth bass | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 2.38 ng/L | N/I | 7 | 0.99 | whole body | biochemistry | DEC | N/I | 80 | N/I | ED 80 | inhibition of acetylcholinesterase activity | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Lepomis macrochirus | 1448 | Meso | Bluegill | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 2.38 ng/L | N/I | 7 | 2.12 | whole body | biochemistry | DEC | N/I | 90 | N/I | ED 90 | inhibition of acetylcholinesterase activity | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Micropterus salmoides | 1449 | Meso | largemouth bass | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 2.38 ng/L | N/I | 63 | 1.15 | whole body | mortality | N/I | N/I | 46% | N/I | LD 46 | 2 applications 30 ds apart | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Micropterus salmoides | 1450 | Meso | largemouth bass | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 2.38 ng/L | N/I | 37 | 1.15 | whole body | behavior | N/I | N/I | N/I | N/I | LOEC | erratic swimming, loss of equilibrium | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Lepomis macrochirus | 1451 | Meso | Bluegill | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 2.38 ng/L | N/I | 3 | 2.06 | whole body | behavior | N/I | N/I | N/I | N/I | LOEC | erratic swimming, loss of equilibrium | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Micropterus salmoides | 1452 | Meso | largemouth bass | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 1 ng/L | N/I | 63 | 0.41 | whole body | mortality | N/I | N/I | 10% | N/I | LOEC | 2 applications 30 ds apart | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Lepomis macrochirus | 1453 | Meso | Bluegill | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 2.38 ng/L | N/I | 63 | 2.06 | whole body | mortality | N/I | N/I | 55% | N/I | LOEC | 2 applications 30 ds apart | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Micropterus salmoides | 1454 | Meso | largemouth bass | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 1 ng/L | N/I | 37 | 0.27 | whole body | behavior | NEF | N/I | N/I | N/I | NOEC | behavior (swimming) | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Lepomis macrochirus | 1455 | Meso | Bluegill | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 1 ng/L | N/I | 63 | 0.42 | whole body | behavior | NEF | N/I | N/I | N/I | NOEC | behavior (swimming) | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Lepomis macrochirus | 1456 | Meso | Bluegill | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | Y | FW | aqueous | 1 ng/L | N/I | 63 | 0.42 | whole body | mortality | NEF | N/I | N/I | N/I | NOEC | 2 applications 30 ds apart | Macek et al. 1972. Toxicity of the insecticide Dursban (R) .... T Am Fish Soc 3:420-427. |
Oreochromis mossambicus | 11332 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 154 | viscera | histopathology | N/I | N/I | N/I | N/I | LOEC | gill raker elongation and thinning | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11333 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 26 | head | histopathology | N/I | N/I | N/I | N/I | LOEC | Lamellae buldging | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11334 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 144 | viscera | histopathology | N/I | N/I | N/I | N/I | LOEC | Lamellae buldging | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11335 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 26 | head | histopathology | N/I | N/I | Yes | N/I | LOEC | Lesions and erosions at the base of lamellae | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11336 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 144 | viscera | histopathology | N/I | N/I | Yes | N/I | LOEC | Lesions and erosions at the base of lamellae | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11337 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 39 | head | histopathology | N/I | N/I | N/I | N/I | LOEC | Fusion of secondary lamellae and mucus coat | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Oreochromis mossambicus | 11338 | L | Mozambique tilapia | juvenile | N/I | Chlorpyrifos | 2921-88-2 | N | N/I | N/I | aqueous | 10.4 µg/L | N/I | N/I | 150 | viscera | histopathology | N/I | N/I | N/I | N/I | LOEC | Fusion of secondary lamellae and mucus coat | Rao et al. 2003. Toxicity of chlorpyrifos to the fish Ore.... B Environ Contam Tox 70:985-992. |
Micropterus salmoides | 22522 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.1 mg/kg | 1% bw/day | 30 d | 0.02 | whole body | mortality | NEF | N | 0% | 0% | N/R | no effect on mortality of exposure group or control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22523 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.64 mg/kg | 1% bw/day | 30 d | 0.1 | whole body | mortality | NEF | N | 0% | 0% | N/R | no effect on mortality of exposure group or control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22524 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 4.69 mg/kg | 1% bw/day | 30 d | 1.01 | whole body | mortality | NEF | N | 0% | 0% | N/R | no effect on mortality of exposure group or control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22528 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.1 mg/kg | 1% bw/day | 30 d | 0.02 | whole body | growth | NEF | N | N/R | N/R | N/R | no effect on growth (weight, length, K) of exposure group as compared to the control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22529 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.64 mg/kg | 1% bw/day | 30 d | 0.1 | whole body | growth | NEF | N | N/R | N/R | N/R | no effect on growth (weight, length, K) of exposure group as compared to the control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22530 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 4.69 mg/kg | 1% bw/day | 30 d | 1.01 | whole body | growth | NEF | N | N/R | N/R | N/R | no effect on growth (weight, length, K) of exposure group as compared to the control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22534 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.4 mg/kg | 1% bw/day | 120 d | 0.2 | whole body | mortality | NEF | N | 0% | 0% | N/R | no effect on mortality of exposure group or control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22535 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.81 mg/kg | 1% bw/day | 120 d | 0.26 | whole body | mortality | NEF | N | 0% | 0% | N/R | no effect on mortality of exposure group or control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22539 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.4 mg/kg | 1% bw/day | 120 d | 0.2 | whole body | growth | NEF | N | N/R | N/R | N/R | no effect on growth (weight, length, K) of exposure group as compared to the control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22540 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.81 mg/kg | 1% bw/day | 120 d | 0.26 | whole body | growth | NEF | N | N/R | N/R | N/R | no effect on growth (weight, length, K) of exposure group as compared to the control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22544 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.1 mg/kg | 1% bw/day | 30 d | 0.02 | whole body | reproduction | NEF | N | 100% | 100% | N/R | 100% of males in exposure group and control showing high degree of proliferation and sperm maturation | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22545 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.64 mg/kg | 1% bw/day | 30 d | 0.1 | whole body | reproduction | NEF | N | 100% | 100% | N/R | 100% of males in exposure group and control showing high degree of proliferation and sperm maturation | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22546 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 4.69 mg/kg | 1% bw/day | 30 d | 1.01 | whole body | reproduction | NEF | N | 100% | 100% | N/R | 100% of males in exposure group and control showing high degree of proliferation and sperm maturation | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22551 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.1 mg/kg | 1% bw/day | 30 d | 0.02 | whole body | reproduction | NEF | N | N/R | N/R | N/R | no effect on female GSI of exposure group as compared to the control; GSI% not reported | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22552 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.64 mg/kg | 1% bw/day | 30 d | 0.1 | whole body | reproduction | NEF | N | N/R | N/R | N/R | no effect on female GSI of exposure group as compared to the control; GSI% not reported | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22553 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 4.69 mg/kg | 1% bw/day | 30 d | 1.01 | whole body | reproduction | NEF | N | N/R | N/R | N/R | no effect on female GSI of exposure group as compared to the control; GSI% not reported | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22557 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.4 mg/kg | 1% bw/day | 120 d | 0.2 | whole body | reproduction | NEF | N | N/R | N/R | N/R | no difference detected in female gonadal stage of exposure group as compared to the control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Micropterus salmoides | 22558 | L | largemouth bass | adult | C | Dieldrin | 60-57-1 | N | Y | FW | diet | 0.81 mg/kg | 1% bw/day | 120 d | 0.26 | whole body | reproduction | NEF | N | N/R | N/R | N/R | no difference detected in female gonadal stage of exposure group as compared to the control | Johnson et al. 2007. Influence of seasonality and exposure on.... Environ Toxicol Chem 26:927-934. |
Lepomis macrochirus | 20035 | L | Bluegill | N/R | N/R | Dieldrin | 60-57-1 | N | Y | FW | aqueous | 0.026 mg/L | 1x | 5 hr | 3.7 | whole body | physiological | N/R | N/R | N/R | N/R | N/R | equilibrium loss and convulsions | Gakstatter and Weiss. 1967. The elimination of DDT-C14, Dieldrin-C14.... T Am Fish Soc 96:301-307. |
Tilapia (No GS!) | 1527 | F | Tilapia | N/I | N/I | Endosulfan | 115-29-7 | N | Y | FW | in situ | N/I | N/I | 3d | 1.1 | whole body | mortality | N/I | N/I | N/I | N/I | LD | N/I | Matthiessen et al. 1982. Accumulation of endosulfan residues in f.... Pest Manag Sci 13:39-48. |
Sarotherodon sp. | 1528 | F | Cichlids | N/I | N/I | Endosulfan | 115-29-7 | N | Y | FW | in situ | N/I | N/I | 3d | 1.1 | whole body | mortality | N/I | N/I | N/I | N/I | LD | N/I | Matthiessen et al. 1982. Accumulation of endosulfan residues in f.... Pest Manag Sci 13:39-48. |
Serranochromis sp. | 1529 | F | yellow fis | N/I | N/I | Endosulfan | 115-29-7 | N | Y | FW | in situ | N/I | N/I | 3d | 1.15 | whole body | mortality | N/I | N/I | N/I | N/I | LD | N/I | Matthiessen et al. 1982. Accumulation of endosulfan residues in f.... Pest Manag Sci 13:39-48. |
Pseudocrenilabrus philander | 1530 | F | Southern mouthbrooder | N/I | N/I | Endosulfan | 115-29-7 | N | Y | FW | in situ | N/I | N/I | 3d | 1.46 | whole body | mortality | N/I | N/I | N/I | N/I | LD | N/I | Matthiessen et al. 1982. Accumulation of endosulfan residues in f.... Pest Manag Sci 13:39-48. |
Haplochromis sp. | 1526 | F | Mouthbrooders | N/I | N/I | Endosulfan | 115-29-7 | N | Y | FW | in situ | N/I | N/I | 3d | 1.08 | whole body | mortality | N/I | N/I | N/I | N/I | LD | N/I | Matthiessen et al. 1982. Accumulation of endosulfan residues in f.... Pest Manag Sci 13:39-48. |
Leiostomus xanthurus | 2331 | L | spot croaker | N/I | N/I | Endosulfan | 115-29-7 | N | N/I | SW | aqueous | 0.75 µg/L | N/I | 96 hr | 465 | whole body | mortality | N/I | N/I | N/I | N/I | LD 28 | 620 BCF | Schimmel et al. 1977. Acute toxicity to and bioconcentration o... |
Lagodon rhomboides | 2333 | L | Pinfish | N/I | N/I | Endosulfan | 115-29-7 | N | N/I | SW | aqueous | 0.42 µg/L | N/I | 96 hr | 439.32 | whole body | mortality | N/I | N/I | N/I | N/I | LD 35 | 1046 BCF | Schimmel et al. 1977. Acute toxicity to and bioconcentration o... |
Leiostomus xanthurus | 2334 | L | spot croaker | N/I | N/I | Endosulfan | 115-29-7 | N | N/I | SW | aqueous | 0.135 µg/L | N/I | 96 hr | 120.8 | whole body | mortality | N/I | N/I | N/I | N/I | LD 39 | 895 BCF | Schimmel et al. 1977. Acute toxicity to and bioconcentration o... |
Lagodon rhomboides | 2336 | L | Pinfish | N/I | N/I | Endosulfan | 115-29-7 | N | N/I | SW | aqueous | 0.24 µg/L | N/I | 96 hr | 311.76 | whole body | mortality | N/I | N/I | N/I | N/I | LD 5 | 1299 BCF | Schimmel et al. 1977. Acute toxicity to and bioconcentration o... |
Leiostomus xanthurus | 2338 | L | spot croaker | N/I | N/I | Endosulfan | 115-29-7 | N | N/I | SW | aqueous | 0.42 µg/L | N/I | 96 hr | 369.9 | whole body | mortality | N/I | N/I | N/I | N/I | LD 89 | 822 BCF | Schimmel et al. 1977. Acute toxicity to and bioconcentration o... |
Leiostomus xanthurus | 3754 | L | spot croaker | mature | N/I | Endosulfan | 115-29-7 | N | N/I | SW | aqueous | 0.05 µg/L | N/I | 4 | 0.031 | whole body | mortality | N/I | N/I | N/I | N/I | ED 35 | Sum Of Detected Endo I, Il, And Sulfate | Schimmel et al. 1977. Acute toxicity to and bioconcentration o... |
Lagodon rhomboides | 3756 | L | Pinfish | mature | N/I | Endosulfan | 115-29-7 | N | N/I | SW | aqueous | 0.26 µg/L | N/I | 4 | 0.272 | whole body | mortality | N/I | N/I | N/I | N/I | ED 35 | Sum Of Detected Endo I, Il, And Sulfate | Schimmel et al. 1977. Acute toxicity to and bioconcentration o... |
Leiostomus xanthurus | 3758 | L | spot croaker | mature | N/I | Endosulfan | 115-29-7 | N | N/I | SW | aqueous | 0.076 µg/L | N/I | 4 | 0.068 | whole body | mortality | N/I | N/I | N/I | N/I | ED 45 | Sum Of Detected Endo I, Il, And Sulfate | Schimmel et al. 1977. Acute toxicity to and bioconcentration o... |
Leiostomus xanthurus | 3761 | L | spot croaker | mature | N/I | Endosulfan | 115-29-7 | N | N/I | SW | aqueous | 0.31 µg/L | N/I | 4 | 0.255 | whole body | mortality | N/I | N/I | N/I | N/I | ED 90 | Sum Of Detected Endo I, Il, And Sulfate | Schimmel et al. 1977. Acute toxicity to and bioconcentration o... |
Lagodon rhomboides | 3765 | L | Pinfish | mature | N/I | Endosulfan | 115-29-7 | N | N/I | SW | aqueous | 0.15 µg/L | N/I | 4 | 0.195 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | Sum Of Detected Endo I, Il, And Sulfate | Schimmel et al. 1977. Acute toxicity to and bioconcentration o... |
Micropterus salmoides | 247 | L | largemouth bass | juvenile | N/I | Endrin | 72-20-8 | N | N/I | FW | aqueous | 0.1 µg/L | N/I | 29 | 0.0115 | whole body | mortality | N/I | N/I | 40% | N/I | LOEC | Residue in dead fish | Fabacher. 1976. Toxicity of endrin and an endrin-methyl .... B Environ Contam Tox 16:376-378. |
Lepomis macrochirus | 799 | L | Bluegill | N/I | N/I | Endrin | 72-20-8 | N | N/I | FW | aqueous | 2 µg/L | N/I | 1 | 0.12 | muscle | mortality | INC | N/I | Yes | N/I | LOEC | N/I | Bennett and Day. 1970. Absorption of endrin by the bluegill sun.... Pestic Monit J 3:201-203. |
Lepomis macrochirus | 800 | L | Bluegill | N/I | N/I | Endrin | 72-20-8 | N | N/I | FW | aqueous | 2 µg/L | N/I | 1 | 0.3 | whole body | mortality | INC | N/I | Yes | N/I | LOEC | N/I | Bennett and Day. 1970. Absorption of endrin by the bluegill sun.... Pestic Monit J 3:201-203. |
Lepomis macrochirus | 801 | L | Bluegill | N/I | N/I | Endrin | 72-20-8 | N | N/I | FW | aqueous | 2 µg/L | N/I | 1 | 0.7 | gastrointestinal | mortality | INC | N/I | Yes | N/I | LOEC | N/I | Bennett and Day. 1970. Absorption of endrin by the bluegill sun.... Pestic Monit J 3:201-203. |
Lepomis macrochirus | 802 | L | Bluegill | N/I | N/I | Endrin | 72-20-8 | N | N/I | FW | aqueous | 2 µg/L | N/I | 1 | 1 | liver | mortality | INC | N/I | Yes | N/I | LOEC | N/I | Bennett and Day. 1970. Absorption of endrin by the bluegill sun.... Pestic Monit J 3:201-203. |
Lepomis macrochirus | 803 | L | Bluegill | N/I | N/I | Endrin | 72-20-8 | N | N/I | FW | aqueous | 0.2 µg/L | N/I | 1 | 0.04 | muscle | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Bennett and Day. 1970. Absorption of endrin by the bluegill sun.... Pestic Monit J 3:201-203. |
Lepomis macrochirus | 804 | L | Bluegill | N/I | N/I | Endrin | 72-20-8 | N | N/I | FW | aqueous | 0.2 µg/L | N/I | 1 | 0.08 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Bennett and Day. 1970. Absorption of endrin by the bluegill sun.... Pestic Monit J 3:201-203. |
Lepomis macrochirus | 805 | L | Bluegill | N/I | N/I | Endrin | 72-20-8 | N | N/I | FW | aqueous | 0.2 µg/L | N/I | 1 | 0.5 | gastrointestinal | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Bennett and Day. 1970. Absorption of endrin by the bluegill sun.... Pestic Monit J 3:201-203. |
Lepomis macrochirus | 806 | L | Bluegill | N/I | N/I | Endrin | 72-20-8 | N | N/I | FW | aqueous | 0.2 µg/L | N/I | 1 | 0.8 | liver | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Bennett and Day. 1970. Absorption of endrin by the bluegill sun.... Pestic Monit J 3:201-203. |
Lepomis macrochirus | 2473 | L | Bluegill | juvenile | N/I | Fenvalerate | 51630-58-1 | N | Y | FW | injection | N/I | N/I | 2 | 0.67 | whole body | mortality | N/I | N/I | 50% | N/I | LD 50 | i.p. injection of .67 mg/kg. | Bradbury et al. 1987. Toxicity of fenvalerate and its constitu.... B Environ Contam Tox 38:727-735. |
Leiostomus xanthurus | 19843 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 0.5 µg/L | continuous | 96 hr | 1.5 | whole body | mortality | INC | N/R | 25% | 5% | N/R | tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Leiostomus xanthurus | 19844 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 0.65 µg/L | continuous | 96 hr | 2.3 | whole body | mortality | INC | N/R | 35% | 5% | N/R | tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Leiostomus xanthurus | 19845 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 0.77 µg/L | continuous | 96 hr | 7.6 | whole body | mortality | INC | N/R | 40% | 5% | N/R | tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Leiostomus xanthurus | 19846 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 1.25 µg/L | continuous | 96 hr | 17.3 | whole body | mortality | INC | N/R | 70% | 5% | N/R | tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Leiostomus xanthurus | 19847 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 1.4 µg/L | continuous | 96 hr | 9.8 | whole body | mortality | INC | N/R | 85% | 5% | N/R | tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Lagodon rhomboides | 19848 | L | Pinfish | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 0.2 µg/L | continuous | 96 hr | 0.55 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | no effect on mortality; tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Lagodon rhomboides | 19849 | L | Pinfish | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 0.44 µg/L | continuous | 96 hr | 1.8 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | no effect on mortality; tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Lagodon rhomboides | 19850 | L | Pinfish | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 1.1 µg/L | continuous | 96 hr | 5.7 | whole body | mortality | INC | N/R | 5% | 0% | N/R | tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Lagodon rhomboides | 19851 | L | Pinfish | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 4.4 µg/L | continuous | 96 hr | 34 | whole body | mortality | INC | N/R | 50% | 0% | N/R | tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Lagodon rhomboides | 19852 | L | Pinfish | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 11 µg/L | continuous | 96 hr | N/R | mortality | INC | N/R | 100% | 0% | N/R | tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. | |
Leiostomus xanthurus | 19858 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | N | Y | SW | aqueous | 0.47 µg/L | continuous | 96 hr | 1.7 | whole body | mortality | NEF | N/R | 0% | 0% | N/R | no effect on mortality; analytic grade 99.8% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Leiostomus xanthurus | 19859 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | N | Y | SW | aqueous | 0.93 µg/L | continuous | 96 hr | 5.3 | whole body | mortality | INC | N/R | 85% | 0% | N/R | analytic grade 99.8% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Leiostomus xanthurus | 19860 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | N | Y | SW | aqueous | 1.1 µg/L | continuous | 96 hr | 11 | whole body | mortality | INC | N/R | 70% | 0% | N/R | analytic grade 99.8% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. |
Leiostomus xanthurus | 19861 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | N | Y | SW | aqueous | 2 µg/L | continuous | 96 hr | N/R | mortality | INC | N/R | 100% | 0% | N/R | analytic grade 99.8% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. | |
Leiostomus xanthurus | 19862 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | N | Y | SW | aqueous | 2.3 µg/L | continuous | 96 hr | N/R | mortality | INC | N/R | 100% | 0% | N/R | analytic grade 99.8% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. | |
Lagodon rhomboides | 19872 | L | Pinfish | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 3.77 µg/L | continuous | 96 hr | N/R | mortality | INC | N/R | 50% | N/A | LC 50 | tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. | |
Leiostomus xanthurus | 19873 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | Y | Y | SW | aqueous | 0.85 µg/L | continuous | 96 hr | N/R | mortality | INC | N/R | 50% | N/A | LC 50 | tech grade 65% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. | |
Leiostomus xanthurus | 19875 | L | spot croaker | N/R | W | Heptachlor | 76-44-8 | N | Y | SW | aqueous | 0.86 µg/L | continuous | 96 hr | N/R | mortality | INC | N/R | 50% | N/A | LC 50 | analytic grade 99.8% | Schimmel et al. 1976. Heptachlor: Toxicity to and uptake by s.... J Toxicol Environ Health 1:955-965. | |
Lepomis macrochirus | 20038 | L | Bluegill | N/R | N/R | Lindane | 58-89-9 | N | Y | FW | aqueous | 0.03 mg/L | 1x | 19 hr | 1.5 | whole body | physiological | N/R | N/R | N/R | N/R | N/R | no symptoms of poisoning | Gakstatter and Weiss. 1967. The elimination of DDT-C14, Dieldrin-C14.... T Am Fish Soc 96:301-307. |
Lagodon rhomboides | 2327 | L | Pinfish | N/I | N/I | Lindane | 58-89-9 | N | N/I | N/I | aqueous | 31.3 µg/L | N/I | 96 hr | 5.22 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Lindane (gamma-BHC) | Schimmel et al. 1977. TToxicity and bioconcentration of BHC an.... Arch Environ Con Tox 6:355-363. |
Lagodon rhomboides | 2328 | L | Pinfish | N/I | N/I | Lindane | 58-89-9 | N | N/I | N/I | aqueous | 81.5 µg/L | N/I | 96 hr | 38.6 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | BHC | Schimmel et al. 1977. TToxicity and bioconcentration of BHC an.... Arch Environ Con Tox 6:355-363. |
Lepomis macrochirus | 4934 | L | Bluegill | immature | N/I | Lindane | 58-89-9 | N | Y | FW | aqueous | 9.1 µg/L | N/I | 735 | 0.297 | muscle | growth | N/I | N/I | N/I | N/I | NOEC | N/I | Macek et al. 1976. Chronic toxicity of atrazine to selected....EPA-600/3-76-047 |
Lepomis macrochirus | 4936 | L | Bluegill | immature | N/I | Lindane | 58-89-9 | N | Y | FW | aqueous | 9.1 µg/L | N/I | 735 | 0.297 | muscle | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Macek et al. 1976. Chronic toxicity of atrazine to selected....EPA-600/3-76-047 |
Lepomis macrochirus | 1413 | L | Bluegill | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 0.6 µg/L | N/I | 735 | 0.016 | muscle | reproduction | N/I | N/I | N/I | N/I | ED 10 | % hatch; lack of spawning in control conc | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Lepomis macrochirus | 1414 | L | Bluegill | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 1.1 µg/L | N/I | 735 | 0.025 | muscle | reproduction | N/I | N/I | N/I | N/I | ED 12 | % hatch; lack of spawning in control conc | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Lepomis macrochirus | 1415 | L | Bluegill | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 4.4 µg/L | N/I | 735 | 0.196 | muscle | reproduction | N/I | N/I | N/I | N/I | ED 30 | % hatch; lack of spawning in control conc | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Lepomis macrochirus | 1417 | L | Bluegill | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 2.3 µg/L | N/I | 735 | 0.062 | muscle | reproduction | N/I | N/I | N/I | N/I | ED 35 | % hatch; lack of spawning in control conc | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Lepomis macrochirus | 1418 | L | Bluegill | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 4.4 µg/L | N/I | 735 | 0.196 | muscle | reproduction | N/I | N/I | N/I | N/I | ED 70 | % hatch; lack of spawning in control conc | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Lepomis macrochirus | 1420 | L | Bluegill | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 0.6 µg/L | N/I | 90 | 0.016 | muscle | mortality | N/I | N/I | N/I | N/I | LD 100 | F1 fry survival @90 d | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Lepomis macrochirus | 1421 | L | Bluegill | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 2.3 µg/L | N/I | 90 | 0.062 | muscle | mortality | N/I | N/I | N/I | N/I | LD 41 | F1 fry survival @90 d | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Lepomis macrochirus | 1422 | L | Bluegill | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 4.4 µg/L | N/I | 90 | 0.196 | muscle | mortality | N/I | N/I | N/I | N/I | LD 86 | F1 fry survival @90 d | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Lepomis macrochirus | 1423 | L | Bluegill | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 1.1 µg/L | N/I | 90 | 0.025 | muscle | mortality | N/I | N/I | N/I | N/I | LD 88 | F1 fry survival @90 d | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Lagodon rhomboides | 3220 | L | Pinfish | N/I | N/I | Malathion | 121-75-5 | N | N/I | N/I | aqueous | 30 µg/L | N/I | 8 hr | 0.96 | gut | physiological | DEC | N/I | Yes | N/I | ED 26 | Acetylcholinesterase inhibition | Cook et al. 1976. The relationship of malathion and its me.... B Environ Contam Tox 16:283-290. |
Lagodon rhomboides | 3221 | L | Pinfish | N/I | N/I | Malathion | 121-75-5 | N | N/I | N/I | aqueous | 20 µg/L | N/I | 24 hr | 1.44 | gut | physiological | DEC | N/I | Yes | N/I | ED 29 | Acetylcholinesterase inhibition | Cook et al. 1976. The relationship of malathion and its me.... B Environ Contam Tox 16:283-290. |
Lagodon rhomboides | 3222 | L | Pinfish | N/I | N/I | Malathion | 121-75-5 | N | N/I | N/I | aqueous | 30 µg/L | N/I | 48 hr | 2.18 | gut | physiological | DEC | N/I | Yes | N/I | ED 48 | Acetylcholinesterase inhibition | Cook et al. 1976. The relationship of malathion and its me.... B Environ Contam Tox 16:283-290. |
Lagodon rhomboides | 3223 | L | Pinfish | N/I | N/I | Malathion | 121-75-5 | N | N/I | N/I | aqueous | 30 µg/L | N/I | 24 hr | 2.22 | gut | physiological | DEC | N/I | Yes | N/I | ED 55 | Acetylcholinesterase inhibition | Cook et al. 1976. The relationship of malathion and its me.... B Environ Contam Tox 16:283-290. |
Lagodon rhomboides | 3224 | L | Pinfish | N/I | N/I | Malathion | 121-75-5 | N | N/I | N/I | aqueous | 30 µg/L | N/I | 72 hr | 3.8 | gut | physiological | DEC | N/I | Yes | N/I | ED 79 | Acetylcholinesterase inhibition | Cook et al. 1976. The relationship of malathion and its me.... B Environ Contam Tox 16:283-290. |
Lagodon rhomboides | 3225 | L | Pinfish | N/I | N/I | Malathion | 121-75-5 | N | N/I | N/I | aqueous | 30 µg/L | N/I | 72 hr | 3.8 | gut | mortality | N/I | N/I | N/I | N/I | LD 60 | N/I | Cook et al. 1976. The relationship of malathion and its me.... B Environ Contam Tox 16:283-290. |
Lagodon rhomboides | 3226 | L | Pinfish | N/I | N/I | Malathion | 121-75-5 | N | N/I | N/I | aqueous | 30 µg/L | N/I | 24 hr | 2.22 | gut | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Cook et al. 1976. The relationship of malathion and its me.... B Environ Contam Tox 16:283-290. |
Lagodon rhomboides | 3227 | L | Pinfish | N/I | N/I | Malathion | 121-75-5 | N | N/I | N/I | aqueous | 30 µg/L | N/I | 4 hr | 0.42 | gut | physiological | DEC | N/I | N/I | N/I | NOEC | Acetylcholinesterase inhibition | Cook et al. 1976. The relationship of malathion and its me.... B Environ Contam Tox 16:283-290. |
Lagodon rhomboides | 3228 | L | Pinfish | N/I | N/I | Malathion | 121-75-5 | N | N/I | N/I | aqueous | 20 µg/L | N/I | 6 hr | 0.6 | gut | physiological | DEC | N/I | N/I | N/I | NOEC | Acetylcholinesterase inhibition | Cook et al. 1976. The relationship of malathion and its me.... B Environ Contam Tox 16:283-290. |
Lepomis spp. | 18119 | Meso | fish | N/R | C | Mirex | 2385-85-5 | N | Y | FW | aqueous | N/I | 1x 1.4 kg/ha | 107 d | 0.01 | whole body | growth | NEF | N | 18.3 g | 21.07 g | N/R | no effect on weight; dry/wet weight N/R; use w/caution | Hyde et al. 1974. The effect of mirex on channel catfish p.... T Am Fish Soc 2:366-369. |
Lepomis spp. | 18120 | Meso | fish | N/R | C | Mirex | 2385-85-5 | N | Y | FW | aqueous | N/I | 2x 1.4 kg/ha | 216 d | 0.06 | whole body | growth | NEF | N | 15.4 g | 21.20 g | N/R | no effect on weight; dry/wet weight N/R; use w/caution | Hyde et al. 1974. The effect of mirex on channel catfish p.... T Am Fish Soc 2:366-369. |
Lepomis spp. | 18121 | Meso | fish | N/R | C | Mirex | 2385-85-5 | N | Y | FW | aqueous | 0.3 mg/L | 3x 1.4 kg/ha | 292 d | 0.02 | whole body | growth | NEF | N | 25.82 g | 35.11 g | N/R | no effect on weight; dry/wet weight N/R; use w/caution | Hyde et al. 1974. The effect of mirex on channel catfish p.... T Am Fish Soc 2:366-369. |
Lepomis macrochirus | 5271 | Meso | Bluegill | immature | N/R | Mirex | 2385-85-5 | N | Y | FW | diet | 5 mg/kg | N/I | 168 | 14 | whole body | growth | DEC | N/I | 34 | N/I | LOEC | weight gain | van Valin et al. 1968. Some effects of mirex on two warm-water .... T Am Fish Soc 97:185-196. |
Lepomis macrochirus | 5272 | Meso | Bluegill | immature | N/R | Mirex | 2385-85-5 | N | Y | FW | aqueous | 1 mg/L | N/I | 168 | 30 | whole body | cellular | NEF | N/I | N/I | N/I | NOEC | no evidence of histopathology | van Valin et al. 1968. Some effects of mirex on two warm-water .... T Am Fish Soc 97:185-196. |
Lepomis macrochirus | 5273 | Meso | Bluegill | immature | N/R | Mirex | 2385-85-5 | N | Y | FW | diet | 3 mg/kg | N/I | 168 | 10 | whole body | growth | NEF | N/I | N/I | N/I | NOEC | growth (weight) | van Valin et al. 1968. Some effects of mirex on two warm-water .... T Am Fish Soc 97:185-196. |
Lepomis macrochirus | 5275 | Meso | Bluegill | immature | N/R | Mirex | 2385-85-5 | N | Y | FW | diet | 5 mg/kg | N/I | 168 | 14 | whole body | morphology | N/I | N/I | N/I | N/I | NOEC | N/I | van Valin et al. 1968. Some effects of mirex on two warm-water .... T Am Fish Soc 97:185-196. |
Lepomis macrochirus | 5276 | Meso | Bluegill | immature | N/R | Mirex | 2385-85-5 | N | Y | FW | diet | 5 mg/kg | N/I | 168 | 14 | whole body | mortality | NEF | N/I | N/I | N/I | NOEC | N/I | van Valin et al. 1968. Some effects of mirex on two warm-water .... T Am Fish Soc 97:185-196. |
Lepomis macrochirus | 5277 | Meso | Bluegill | immature | N/R | Mirex | 2385-85-5 | N | Y | FW | aqueous | 1 mg/L | N/I | 168 | 30 | whole body | mortality | NEF | N/I | N/I | N/I | NOEC | Mirex bait added to outdoor ponds | van Valin et al. 1968. Some effects of mirex on two warm-water .... T Am Fish Soc 97:185-196. |
Lepomis macrochirus | 5278 | Meso | Bluegill | immature | N/R | Mirex | 2385-85-5 | N | Y | FW | aqueous | 1 mg/L | N/I | 168 | 30 | whole body | reproduction | NEF | N/I | N/I | N/I | NOEC | on reproductive success (no measurements given) | van Valin et al. 1968. Some effects of mirex on two warm-water .... T Am Fish Soc 97:185-196. |
Oreochromis aureus | 625 | L | Blue tilapia | N/I | N/I | Permethrin | 52645-53-1 | N | N/I | N/I | aqueous | 8.31 µg/L | N/I | 24 hr | 0.74 | whole body | mortality | N/I | N/I | N/I | N/I | LD 100 | 10.5 g initial avg weight | Herzberg. 1988. Toxicity and accumulation of permethrin .... Isr J Aquacult-Bamid 40:35-39. |
Oreochromis aureus | 626 | L | Blue tilapia | N/I | N/I | Permethrin | 52645-53-1 | N | N/I | N/I | aqueous | 6.2 µg/L | N/I | 24 hr | 0.41 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | 10.5 g initial avg weight | Herzberg. 1988. Toxicity and accumulation of permethrin .... Isr J Aquacult-Bamid 40:35-39. |
Oreochromis aureus | 627 | L | Blue tilapia | N/I | N/I | Permethrin | 52645-53-1 | N | N/I | N/I | aqueous | 8.31 µg/L | N/I | 24 hr | 0.74 | whole body | mortality | N/I | N/I | N/I | N/I | LOEC | 10.5 g initial avg weight | Herzberg. 1988. Toxicity and accumulation of permethrin .... Isr J Aquacult-Bamid 40:35-39. |
Oreochromis aureus | 628 | L | Blue tilapia | N/I | N/I | Permethrin | 52645-53-1 | N | N/I | N/I | aqueous | 6.7 µg/L | N/I | 24 hr | 0.48 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | 10.5 g initial avg weight | Herzberg. 1988. Toxicity and accumulation of permethrin .... Isr J Aquacult-Bamid 40:35-39. |
Lepomis macrochirus | 2288 | Meso | Bluegill | N/I | C | Temephos | 3383-96-8 | N | Y | FW | aqueous | 180 g/ha | N/I | 55 d | 0.16 | whole body | reproduction | N/I | N/I | N/I | N/I | ED 50 | # of Fry total | Sanders et al. 1981. Abate: Effects of the organophosphate in....Technical Paper 104 |
Lepomis macrochirus | 2289 | Meso | Bluegill | N/I | C | Temephos | 3383-96-8 | N | Y | FW | aqueous | 180 g/ha | N/I | 55 d | 0.16 | whole body | reproduction | N/I | N/I | N/I | N/I | ED 58 | # of Fry per female | Sanders et al. 1981. Abate: Effects of the organophosphate in....Technical Paper 104 |
Lepomis macrochirus | 2290 | Meso | Bluegill | N/I | C | Temephos | 3383-96-8 | N | Y | FW | aqueous | 180 g/ha | N/I | 55 d | 0.16 | whole body | reproduction | N/I | N/I | N/I | N/I | LOEC | # of Fry per female | Sanders et al. 1981. Abate: Effects of the organophosphate in....Technical Paper 104 |
Lepomis macrochirus | 2291 | Meso | Bluegill | N/I | C | Temephos | 3383-96-8 | N | Y | FW | aqueous | 180 g/ha | N/I | 55 d | 0.16 | whole body | reproduction | N/I | N/I | N/I | N/I | LOEC | # of Fry total | Sanders et al. 1981. Abate: Effects of the organophosphate in....Technical Paper 104 |
Oreochromis mossambicus | 1531 | L | Mozambique tilapia | juvenile | N/I | Temephos | 3383-96-8 | N | N/I | N/I | diet | 2210 mg/kg | N/I | 28 | 300 | whole body | morphology | N/I | N/I | N/I | N/I | NOEC | N/I | Matthiessen and Johnson. 1978. Accumulation of the organophosphate blac.... J Fish Biol 13:575-586. |
Oreochromis mossambicus | 1532 | L | Mozambique tilapia | adult | N/I | Temephos | 3383-96-8 | N | N/I | N/I | aqueous | 0.05 mg/L | N/I | 69 | 8.86 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Matthiessen and Johnson. 1978. Accumulation of the organophosphate blac.... J Fish Biol 13:575-586. |
Oreochromis mossambicus | 1533 | L | Mozambique tilapia | juvenile | N/I | Temephos | 3383-96-8 | N | N/I | N/I | diet | 2210 mg/kg | N/I | 28 | 300 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Matthiessen and Johnson. 1978. Accumulation of the organophosphate blac.... J Fish Biol 13:575-586. |
Lagodon rhomboides | 4069 | L | Pinfish | adult | N/I | Toxaphene | 8001-35-2 | N | N/I | N/I | aqueous | 0.5 µg/L | N/I | 4 | 1.9 | whole body | mortality | N/I | N/I | N/I | N/I | LD 25 | N/I | Schimmel et al. 1977. Uptake and toxicity of toxaphene in seve.... Arch Environ Con Tox 5:353-367. |
Lagodon rhomboides | 4082 | L | Pinfish | adult | N/I | Toxaphene | 8001-35-2 | N | N/I | N/I | aqueous | 0.41 µg/L | N/I | 4 | 1.6 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Schimmel et al. 1977. Uptake and toxicity of toxaphene in seve.... Arch Environ Con Tox 5:353-367. |