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 Polyaromatic Hydrocarbons (PAHs)
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 |
---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|---|
Fundulus heteroclitus | 9755 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | whole body | cellular | N/I | N/I | N/I | N/I | IP 570 | Fry (70-80 mm, 6.5-7.5 g] | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9756 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | blood | cellular | N/I | N/I | N/I | N/I | IP 187 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9757 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | blood | cellular | N/I | N/I | N/I | N/I | IP 381 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9758 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | liver | cellular | N/I | N/I | N/I | N/I | IP 600 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9759 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | liver | cellular | N/I | N/I | N/I | N/I | IP 3550 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9760 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | liver | cellular | N/I | N/I | N/I | N/I | IP 9900 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9761 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | liver | cellular | N/I | N/I | N/I | N/I | IP 2700 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9762 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | kidney | cellular | N/I | N/I | N/I | N/I | IP 200 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9763 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | kidney | cellular | N/I | N/I | N/I | N/I | IP 1300 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9764 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | kidney | cellular | N/I | N/I | N/I | N/I | IP 1300 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9765 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | spleen | cellular | N/I | N/I | N/I | N/I | IP 500 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9766 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | spleen | cellular | N/I | N/I | N/I | N/I | IP 750 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9767 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | spleen | cellular | N/I | N/I | N/I | N/I | IP 1000 | form B[a]P-DNAadducts,nmol adducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 9768 | L | mummichog | fry | W | Benzo[a]pyrene | 50-32-8 | N | Y | FW | injection | 12 mg/kg bw | N/I | N/I | 1710 | spleen | cellular | N/I | N/I | N/I | N/I | IP 750 | form B[a]P-DNAadducts, nmoladducts/mol nucleotides | Rose et al. 2001. Persistence of benzo [a] pyrene–DNA addu.... Aquat Toxicol 52:319-328. |
Fundulus heteroclitus | 4888 | L | mummichog | adult | W | Naphthalene | 91-20-3 | N | Y | SW | aqueous | 4 mg/L | N/I | 0.5 | 12 | whole body | biochemistry | INC | N/I | Yes | N/I | LOEC | Increased serum cortisol | Levitan and Taylor. 1979. Physiology of salinity-dependent naphtha.... J Fish Res Board Can 36:615-622. |
Fundulus heteroclitus | 4889 | L | mummichog | adult | W | Naphthalene | 91-20-3 | N | Y | SW | aqueous | 4 mg/L | N/I | 0.5 | 17 | whole body | mortality | INC | N/I | Yes | N/I | LOEC | at 23 and 33 ppt salinity | Levitan and Taylor. 1979. Physiology of salinity-dependent naphtha.... J Fish Res Board Can 36:615-622. |
Fundulus heteroclitus | 4890 | L | mummichog | adult | W | Naphthalene | 91-20-3 | N | Y | SW | aqueous | 4 mg/L | N/I | 0.08 | 5 | whole body | physiological | INC | N/I | Yes | N/I | LOEC | oxygen consumption | Levitan and Taylor. 1979. Physiology of salinity-dependent naphtha.... J Fish Res Board Can 36:615-622. |
Fundulus heteroclitus | 4891 | L | mummichog | adult | W | Naphthalene | 91-20-3 | N | Y | SW | aqueous | 4 mg/L | N/I | 0.5 | 23 | whole body | biochemistry | NEF | N/I | N/I | N/I | NOEC | No sig diff hematocrits | Levitan and Taylor. 1979. Physiology of salinity-dependent naphtha.... J Fish Res Board Can 36:615-622. |
Poecilia reticulata | 7901 | L | guppy | adult | N/I | Quinoline | 91-22-5 | N | N/I | N/I | aqueous | N/I | N/I | N/I | 269.9 | whole body | mortality | N/I | N/I | N/I | N/I | LD 100 | fish killed during the experiment used for LBB | Ramos et al. 1998. Acute toxicity of polar narcotics to thr.... Chemosphere 37:633-650. |
Poecilia reticulata | 7902 | L | guppy | adult | N/I | Quinoline | 91-22-5 | N | N/I | N/I | aqueous | N/I | N/I | N/I | 153.7 | whole body | mortality | N/I | N/I | 100% | N/I | LD 100 | Low exposure | Ramos et al. 1998. Acute toxicity of polar narcotics to thr.... Chemosphere 37:633-650. |
Poecilia reticulata | 8495 | L | guppy | adult | N/I | Quinoline | 91-22-5 | N | N/I | N/I | aqueous | N/I | N/I | N/I | 269.95 | whole body | mortality | N/I | N/I | N/I | N/I | LD 100 | high dose | Ramos et al. 1998. Acute toxicity of polar narcotics to thr.... Chemosphere 37:633-650. |
Poecilia reticulata | 8504 | L | guppy | adult | N/I | Quinoline | 91-22-5 | N | N/I | N/I | aqueous | N/I | N/I | N/I | 153.7 | whole body | mortality | N/I | N/I | N/I | N/I | LD 100 | Low dose | Ramos et al. 1998. Acute toxicity of polar narcotics to thr.... Chemosphere 37:633-650. |