Test system | Exposure method (exposure method, concentration, vehicle, solution exchange time, and the others) | Organism characteristics (age, developmental stages) | PFAA type | Exposure time (sampling time, refresh time, generation) | Effects |
Fish | |||||
Fathead minnow (Pimephales promelas) | Flow-through exposure; 45 ml/min solution supply; 0, 0.03, 0.1, 0.3, 1 mg/L PFOS | F0: Six-to-seven-month adult fish F1: From embryo to fry 24 dpf | PFOS | 14 d (at 1 mg/L), 21 d, and 24 d | Reproductive toxicity, endocrine disruption, PFOS accumulation |
Juvenile atlantic salmon (Salmo salar) | Dietary exposure; 0.2 mg/kg PFOA, PFOS; 0.01% methanol solvent | Juvenile fish (sexually immature), average mass of 70 ± 20 g | PFOA, PFOS | Sampling at 0, 2, 5, 8, and 14 d 0, 3, 6 d food spike exposure and 7 d recovery | Beta-oxidation, oxidative stress |
Rainbow trout (Oncorhynchus mykiss) | Dietary exposure; PFC mixture exposure (in the ratio of 1:1:1:1, mix A composed of 5 mg/L individual PFC (PFOA, PFNA, PFDA, PFUnDA), mix B composed of 50 mg/L individual PFC, mix C composed of 250 mg/L individual PFC). For VTG, PFOA and PFDA exposure, 0.026, 0.128, 0.64, 3.2, 16, 80, 400, 2000 mg/L PFOA or PFDA; DMSO vehile (≤0.05 mg/L) | Subchronic PFC exposure: 11 month old juvenile trout; PFOA and PFDA exposure for VTG analysis: 5 month old juvenile trout | PFOA, PFNA, PFDA, PFUnDA, PFPA, PFHxA, PFHpA, PFDoDA, PFTrDA, PFTDA, PFBS, PFOS, PFDS, E2 | 14 d (feeding every 5 d per a week) | Endocrine disruption |
Zebrafish (Danio rerio) | Static-exposure; 0.1% DMSO(v/v); 8, 16, 32 µM PFOS for sensitive period screening; 16 µM PFOS for histological examination, transmission electron microscopic examination, NimbleGen microarray | Embryo within 0.5 h of spawning | PFOS | 0 to 48 hpf or 48 - 96 hpf for sensitive period screening; 48 - 96 hpf for histological examination and transmission electron microscopic examination; from 48 hpf during 48 h for NimbleGen microarray | Developmental toxicity, microassay gene profiles |
Zebrafish (Danio rerio) | Semi-static exposure (50% renewals every 5 d, except for initial 5 d when embryo hatching occur); 0.01% DMSO; 0.5 µM PFOS (250 µg/L) | 8 hpf | PFOS | From 8 hpf to 120 dpf | Thryoid toxicity |
Marine medaka (Oryzias melastigma) | Semi-static exposure (25‰ saline water); 1, 3, 10 µg/L PFBS; daily exchange | Eggs | PFBS | From egg state to sexual maturity state (6 month old) | Ocular toxicity, neuronal toxicity, protein profilings |
Zebrafish (Danio rerio) | Semi-static exposure (50% renewals every 5 d, except for initial 5 d when embryo hatching occur); 0.01% DMSO; 0.5 µM PFOS | Developmental stage from 8 h dpf to 150 dpf | PFOS | 5 month exposure (from 8 h dpf to 150 dpf), followed by 5 d spawning time, hatching, and others | Lipid metabolism change, ATP content, gross index, histological changes, endocrine disruption |
Pseudokirchneriella subcapitata, Daphnia magna, Oncorhynchus mykiss | Acute toxicity test: Static exposure; APFO (PFOA + salt); to D. magna, 0, 100, 178, 316, 562, 1000 mg/L APFO; to O. mykiss, 0, 31.3, 62.5, 125, 250, 500, 1000 mg/L APFO; to P. subcapitata, 5.76, 11.37, 22, 70, 46.33, 95.87, 180, 67, 369.67 mg/L APFO); Chronic toxicity test: To D. magna (Semi-static exposure: 0, 4.31, 9.16, 20, 44.2, 88.6 mg/L); to O. mykiss (Flow-through exposure (5.76 replacement per day, ELS test, 0, 2.18, 4.48, 10.7, 20.9, 40 mg/L)-OECD 201, 202, 203; EU commission directive 92/69 EEC, OECD 210, 211 | Acute test: 6 h - 24 h neonate D. magna, 40 mm - 50 mm O. mykiss, 104 cells/ml inoculation P. subcapitata, Chronic test: 6 h - 24 h neonate D. magna, Fertilized egg to 85 d O. mykiss | APFO (PFOA + salt) | Acute toxicity test: D. magna: 48 h, O. mykiss: 96 h, P. subcapitata: 96 h; Chronic toxicity test: D. magna 21 d, O. mykiss 85 d | Acute toxicity, reproductive toxicity(ex. 95 d-O. mykiss ELS test) |
Zebrafish (Danio rerio) | Semi-static exposure, replaced 50% at every 5 days; 8 hpf to 180 dpf exposure period; 0.01% DMSO; 0, 0.02, 0.1, 0.5 µM PFOS | 8 hpf embryo | PFOS | 8 hpf to 180 dpf | Lipid metabolism disturbance, oxidative stress |
Thicklip grey mullets (Chelon labrosus), | Static exposure; 2 mg/L PFOS dissolved in seawater | Juvenile fish | PFOS | 2 and 16 d | Transport gene expression change |
European bullhead (Cottus gobio) | Semi-static exposure; a half of water was replenished every 24 h; 0.1 and 1 mg/L PFOS | Adult fish, 10.4 ± 4.1 g; catching organism in Samson river and acclimated in tap water | PFOS | 96 h | Enzyme activity, protein expression change (ex.: HSPA4, HSC70-2 etc.) |
Zebrafish (Danio rerio) | Semi-static exposure, replenished half every day, 0.002% DMSO; 0, 10, 50, 250 µg/L PFOS | F0 fish: 14 dpf zebrafish fry | PFOS | F0 fish: 70 d PFOS exposure and 30 d only water exposure, (100 d) F1 fish: Offspring of PFOS treated female and nonchemical treated male fish | F0: Gross index, thyroid toxicity, endocrine disruption F1: Reproductive toxicity endocrine disruption |