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 Arthropoda: Invert (insects, crustaceans) and Pharm. Personal Care Products
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 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Chironomus riparius | 6172 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 2.2 mg/L | N/I | N/I | 382 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Dead midges used for bioassay | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6173 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 0.75 mg/L | N/I | N/I | 15.02 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | Live midges used for bioassay Weight | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6174 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 0.75 mg/L | N/I | N/I | 14.37 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | Live midges used for bioassay Weight | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6175 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 1.72 mg/L | N/I | N/I | 46.36 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | Live midges used for bioassay Weight | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6176 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 1.72 mg/L | N/I | N/I | 65.3 | whole body | growth | N/I | N/I | N/I | N/I | NOEC | Live midges used for bioassay Weigh | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6177 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 2.2 mg/L | N/I | N/I | 235.1 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Live midges used for bioassay | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6178 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 1.3 mg/L | N/I | N/I | 130.6 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Dead midges used for bioassay | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6179 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 1.3 mg/L | N/I | N/I | 58.77 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Live midges used for bioassay | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6180 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 0.8 mg/L | N/I | N/I | 58.77 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Live midges used for bioassay | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6181 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 1.2 mg/L | N/I | N/I | 68.56 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | Live midges used for bioassay | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6182 | L | midge | larvae | N/I | dodecylbenzenesulfonic acid | 25155-30-0 | N | N/I | N/I | aqueous | 1.72 mg/L | N/I | N/I | 124.07 | whole body | morphology | N/I | N/I | N/I | N/I | LOEC | Live midges used for bioassay Deformities | Hwang et al. 2003. Assessing the toxicity of dodecylbenzene.... Environ Toxicol Chem 22:302-312. |
Chironomus riparius | 6272 | L | midge | larvae | N/I | Galaxolide | 1222-05-5 | N | N/I | N/I | aqueous | 288 µg/L | N/I | N/I | 5.16 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | LC50 was less than lowest reported concentration | Artola-Garciano et al. 2003. Bioconcentration and acute toxicity of p.... Environ Toxicol Chem 22:1086-1092. |
Chironomus riparius | 14295 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | aqueous | 11.425 µmol/L | N/I | N/I | 290 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | N/I | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14296 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | 1.062 mmol/L | N/I | N/I | 18.9 | whole body | mortality | N/I | N/I | N/I | N/I | LD 8 | N/I | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14297 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | 1.686 mmol/L | N/I | N/I | 31 | whole body | mortality | N/I | N/I | N/I | N/I | NOEC | N/I | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14298 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | 2.503 mmol/L | N/I | N/I | 89.4 | whole body | mortality | N/I | N/I | N/I | N/I | LD 16 | N/I | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14299 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | 3.034 mmol/L | N/I | N/I | 128 | whole body | mortality | N/I | N/I | N/I | N/I | LD 86 | N/I | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14300 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | 2.503 mmol/L | N/I | N/I | 89.4 | whole body | growth | N/I | N/I | N/I | N/I | ED 31 | growth (head capsule) | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14301 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | 3.034 mmol/L | N/I | N/I | 128 | whole body | growth | N/I | N/I | N/I | N/I | ED 45 | growth (head capsule) | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14302 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | 2.503 mmol/L | N/I | N/I | 89.4 | whole body | growth | N/I | N/I | N/I | N/I | ED 45 | growth (weight) | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14303 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | 3.034 mmol/L | N/I | N/I | 128 | whole body | growth | N/I | N/I | N/I | N/I | ED 50 | growth (weight) | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14304 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | 1.69 mmol/L | N/I | N/I | 89.4 | whole body | growth | N/I | N/I | N/I | N/I | LOEC | growth (weight) | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14305 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | N/I | N/I | N/I | 103 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | N/I | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14306 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | N/I | N/I | N/I | 91.1 | whole body | growth | N/I | N/I | N/I | N/I | ED 50 | growth (head capsule) | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 14307 | L | midge | larvae | N/I | Sodium alkylbenzene sulfonate | 68411-30-3 | N | N/I | N/I | sediment | N/I | N/I | N/I | 61.2 | whole body | growth | N/I | N/I | N/I | N/I | ED 50 | growth (weight) | Maenpaa and Kukkonen. 2006. Bioaccumulation and toxicity of 4-nonylp.... Aquat Toxicol 77:329-338. |
Chironomus riparius | 6275 | L | midge | larvae | N/I | Tonalide | 21145-77-7 | N | N/I | N/I | aqueous | 460 µg/L | N/I | N/I | 5.16 | whole body | mortality | N/I | N/I | N/I | N/I | LD 50 | LC50 was less than lowest reported concentration | Artola-Garciano et al. 2003. Bioconcentration and acute toxicity of p.... Environ Toxicol Chem 22:1086-1092. |