PAH
Fish, Estuarine and saltwater fish (Gobiiformes), Longjaw mudsucker (Gillichthys mirabilis)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|---|
PAH | Transplanted to Alamitos from Alamitos: 6090; Ballona: 333; Mugu: 1110 ng/g | Tissue concentration | NR | Not Reported | NR | Three southern CA estuaries | Toxicity Factor Datasets | USA |
PAH | Transplanted to Ballona from Alamitos: 1440; Ballona: 1150; Mugu: 1720 ng/g | Tissue concentration | NR | Not Reported | NR | Three southern CA estuaries | Toxicity Factor Datasets | USA |
PAH | Transplanted to Mugu from Alamitos: 317; Ballona: 5390; Mugu: 2210 ng/g | Tissue concentration | NR | Not Reported | NR | Three southern CA estuaries | Toxicity Factor Datasets | USA |
PAH | Transplanted to Alamitos from Alamitos: 310; Ballona: 124; Mugu: 607 ng/g | Tissue concentration | NR | Not Reported | NR | Three southern CA estuaries | Toxicity Factor Datasets | USA |
PAH | Transplanted to Ballona from Alamitos: 302; Ballona: 0; Mugu: 231 ng/g | Tissue concentration | NR | Not Reported | NR | Three southern CA estuaries | Toxicity Factor Datasets | USA |
PAH | Transplanted to Mugu from Alamitos: <DL; Ballona: 2127; Mugu: <DL ng/g | Tissue concentration | NR | Not Reported | NR | Three southern CA estuaries | Toxicity Factor Datasets | USA |
Chemical | Endpoint Value | Endpoint Description | Life Cycle Stage | Sample Size | Location | Type | Countries |
---|---|---|---|---|---|---|---|
PAH | A: 461.08, B: 266.96, C: 21.20, D1: 27.02, D2: 40.51, D3: 28.82, E1: 118.68 ng/g ww | Egg concentration | Embryo | 9 | Bizkaia | Toxicity Factor Datasets | SPAIN |
Mallard duck (Anas platyrhynchos)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
POLYCYCLIC AROMATIC HYDROCARBONS (PAHs) | increase @ 0.2, 2.0 mg/kg egg | embryonic mortality, compared to controls | Not Reported | Embryo | 22/dose | Toxicity Factor Datasets | 5 d of incubation | Laboratory | |
BENZO[k]FLUORANTHENE | increase @ 0.2, 2.0 mg/kg egg | embryo mortality, compared to controls | Not Reported | Embryo | 20/dose | Toxicity Factor Datasets | 5 d of incubation | Laboratory |
Deer Mouse (Peromyscus maniculatus)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | Lab |
---|---|---|---|---|---|---|---|---|---|
DIBENZ[A]ANTHRACENE (1,2,5,6-) | 0.048 mg/kg/d | ED50 for immunosuppression, measured as suppression of plaque forming cell response | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory | |
DIBENZ[A]ANTHRACENE (1,2,5,6-) | 0.85 mg/kg/d | ED50 for ethoxyresorufin-O-dealkylase (EROD) activity | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory | |
DIMETHYLBENZ[A]ANTHRACENE (7,12-) | 0.026 mg/kg/d | ED50 for immunosuppression, measured as suppression of plaque forming cell response | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory | |
METHYLCHLORANTHRENE (3-) | 0.14 mg/kg/d | ED50 for immunosuppression, measured as suppression of plaque forming cell response | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory | |
METHYLCHLORANTHRENE (3-) | 1.24 mg/kg/d | ED50 for ethoxyresorufin-O-dealkylase (EROD) activity | Male | Juvenile | Not Reported | Toxicity Factor Datasets | 7 - 8 wk | Laboratory |
Alameda Song Sparrow (Melospiza melodia ssp. pusillula)
Chemical | Endpoint Value | Endpoint Description | Sex | Life Cycle Stage | Sample Size | Location | Type | Age-Specific | California Counties | Condition | Lab |
---|---|---|---|---|---|---|---|---|---|---|---|
DIBENZ[A]ANTHRACENE (1,2,5,6-) | 5 | description | Both Male and Female | Adult | sample size | location | Toxicity Factor Datasets | age | Alameda | condition | Laboratory |