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). |
Source: Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046.
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 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
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 |
Salvelinus fontinalis | 1416 | L | Brook Trout | juvenile | N/I | Lindane | 58-89-9 | N | N/I | N/I | aqueous | 16.6 µg/L | N/I | 261 | 1.2 | carcass | growth | N/I | N/I | N/I | N/I | ED 32 | note: control failed | 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 |
Salvelinus fontinalis | 1419 | L | Brook Trout | juvenile | N/I | Lindane | 58-89-9 | N | N/I | N/I | aqueous | 16.6 µg/L | N/I | 261 | 1.2 | carcass | growth | N/I | N/I | N/I | N/I | ED 9 | note: control failed | 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 |
Pimephales promelas | 1424 | L | fathead Minnow | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 23.4 µg/L | N/I | 304 | 9.533 | carcass | reproduction | N/I | N/I | N/I | N/I | NOEC | hatch success | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Pimephales promelas | 1425 | L | fathead Minnow | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 23.4 µg/L | N/I | 304 | 9.533 | carcass | reproduction | N/I | N/I | N/I | N/I | NOEC | Growth; caution: variability in data | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Salvelinus fontinalis | 1426 | L | Brook Trout | juvenile | N/I | Lindane | 58-89-9 | N | N/I | N/I | aqueous | 16.6 µg/L | N/I | 261 | 1.2 | carcass | survival | N/I | N/I | N/I | N/I | NOEC | controls failed to spawn | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |
Pimephales promelas | 1427 | L | fathead Minnow | juvenile | N/I | Lindane | 58-89-9 | N | N/I | FW | aqueous | 23.4 µg/L | N/I | 304 | 9.533 | carcass | survival | N/I | N/I | N/I | N/I | NOEC | % F1 survival | Macek et al. 1976. Chronic toxicity of lindane to selected ....EPA 600/3-76-046 |