PEER REVIEW DRAFT. DO NOT CITE OR QUOTE \vEPA United States Office of Chemical Safety and Environmental Protection Agency Pollution Prevention Draft Risk Evaluation for Perchloroethylene (Ethene, 1,1^2,2-Tetrachloro) Systematic Review Supplemental File: Data Extraction Tables for Environmental Hazard Studies CASRN: 127-18-4 CI CI CI CI April 2020 1 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Environmental Hazard Data Extraction Table for Perchloroethylene (PCE) Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Fish Rainbow trout Fresh 96-hour LCso - Not reported Flow- Mortality Shubat et High (Oncorhynchu s mvkiss) 5.84 mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 96-hour LCso = Not reported Flow- Mortality Shubat et High ('Oncorhynchu s mvkiss) 4.99 mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 1-hour LCso = Not reported Flow- Mortality Shubat et High ('Oncorhynchu s mvkiss) -15 mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 3-hour LCso = Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) >11, <12 mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 6-hour LCso = ~7 Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 12-hour LCso = ~6 Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 24-hour LCso = ~5 Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) mg AI/L through, Measured al„ 1982 Rainbow trout {Oncorhynchu s mvkiss) Fresh 48-hour LCso = ~5 mg AI/L Not reported Flow- through, Measured Mortality Shubat et al„ 1982 High Rainbow trout Fresh 72-hour LCso = ~5 Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 1-hour LCso = Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) >11, <12 mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 3-hour LCso = >8, Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) <9 mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 6-hour LCso = >7, Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) <8 mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 12-hour LCso = ~7 Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 24-hour LCso = >6, Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) <7 mg AI/L through, Measured al„ 1982 Rainbow trout Fresh 48-hour LCso = >6, Not reported Flow- Mortality Shubat et High {Oncorhynchu s mvkiss) <7 mg AI/L through, Measured al„ 1982 2 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Rainbow trout (Oncorhynchu s mvkiss) Fresh 72-hour LCso = >6, <7 mg AI/L Not reported Flow- through, Measured Mortality Shubat et al„ 1982 High Rainbow trout Fresh 24-hour LCso = Not reported Flow- Mortality Call et al„ High ('Oncorhynchu s mvkiss) 4.99 mg AI/L through, Measured 1983 Rainbow trout Fresh 48-hour LCso = Not reported Flow- Mortality Call et al„ High ('Oncorhynchu s mvkiss) 4.99 mg AI/L through, Measured 1983 Rainbow trout Fresh 72-hour LCso = Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) 4.99 mg AI/L through, Measured 1983 Rainbow trout Fresh 24-hour LCso = Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) 6.31 mg AI/L through, Measured 1983 Rainbow trout Fresh 48-hour LCso = Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) 5.95 mg AI/L through, Measured 1983 Rainbow trout Fresh 72-hour LCso = Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) 5.81 mg AI/L through, Measured 1983 Rainbow trout Fresh 96-hour ECso = Not reported Flow- Equilibrium Call et al„ High {Oncorhynchu s mvkiss) 5.38 mg AI/L through, Nominal 1979 Rainbow trout Fresh 96-hour ECso = Not reported Flow- Equilibrium Call et al„ High {Oncorhynchu s mvkiss) 4.68 mg AI/L through, Nominal 1979 Rainbow trout Fresh <20-hour LCso = >9, Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) <12 mg AI/L through, Measured 1979 Rainbow trout Fresh <20-hour LCso = >6, Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) <9 mg AI/L through, Measured 1979 Rainbow trout Fresh <20-hour LCso = >6, Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) <9 mg AI/L through, Measured 1979 Rainbow trout Fresh >20-< LCso = ~6 Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) 40-hour mg AI/L through, Measured 1979 Rainbow trout Fresh >40-, LCso = >3, Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) <60-hour <6 mg AI/L through, Measured 1979 Rainbow trout Fresh >60-, LCso = >3, Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) <80-hour <6 mg AI/L through, Measured 1979 Rainbow trout Fresh 96-hour LCso = >3, Not reported Flow- Mortality Call et al„ High {Oncorhynchu s mvkiss) <6 mg AI/L through, Measured 1979 Rainbow trout Fresh <20-hour LCso = >6, Not reported Flow- Mortality Call et al.. High {Oncorhynchu s mvkiss) <9 mg AI/L through, Measured 1979 3 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Duration End-point Concentration(s) Test Effect(s) References Data Quality Salt Analysis Evaluation Water Rainbow trout Fresh <20-hour LCso = >3, Not reported Flow- Mortality Ca et al.. High (Oncorhynchu s mvkiss) <6 mg AI/L through, Measured 979 Rainbow trout Fresh <20-hour LCso = >3, Not reported Flow- Mortality Ca et al.. High ('Oncorhynchu s mvkiss) <6 mg AI/L through, Measured 979 Rainbow trout Fresh >20-, LCso = >3, Not reported Flow- Mortality Ca et al.. High ('Oncorhynchu s mvkiss) <40-hour <6 mg AI/L through, Measured 979 Rainbow trout Fresh >40-, LCso = >3, Not reported Flow- Mortality Ca et al.. High {Oncorhynchu s mvkiss) <60-hour <6 mg AI/L through, Measured 979 Rainbow trout Fresh >60-, LCso = >3, Not reported Flow- Mortality Ca et al.. High {Oncorhynchu s mvkiss) <80-hour <6 mg AI/L through, Measured 979 Rainbow trout Fresh <20-hour ECso = >6, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <9 mg AI/L through, Measured 979 Rainbow trout Fresh <20-hour ECso = >6, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <9 mg AI/L through, Measured 979 Rainbow trout Fresh <20-hour ECso = >6, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <9 mg AI/L through, Measured 979 Rainbow trout Fresh >20-, ECso = >3, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <40-hour <6 mg AI/L through, Measured 979 Rainbow trout Fresh >40-, ECso = >3, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <60-hour <6 mg AI/L through, Measured 979 Rainbow trout Fresh >60-, ECso = >3, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <80-hour <6 mg AI/L through, Measured 979 Rainbow trout Fresh 96-hour ECso = >3, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <6 mg AI/L through, Measured 979 Rainbow trout Fresh <20-hour ECso = >3, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <6 mg AI/L through, Measured 979 Rainbow trout Fresh <20-hour ECso = >3, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <6 mg AI/L through, Measured 979 Rainbow trout Fresh <20-hour ECso = >3, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <6 mg AI/L through, Measured 979 Rainbow trout Fresh >20-, ECso = >3, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <40-hour <6 mg AI/L through, Measured 979 Rainbow trout Fresh >40-, ECso = >3, Not reported Flow- Equilibrium Ca et al.. High {Oncorhynchu s mvkiss) <60-hour <6 mg AI/L through, Measured 1979 4 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Rainbow trout (Oncorhynchu s mvkiss) Fresh >60-, <80-hour ECso = >3, <6 mg AI/L Not reported Flow- through, Measured Equilibrium Call et al„ 1979 High Rainbow trout ('Oncorhynchu s mvkiss) Fresh <20-hour LCso = >8, <10 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout ('Oncorhynchu s mvkiss) Fresh <20-hour LCso = >8, <10 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh <20-hour LCso = >6, <8 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh <20-hour LCso = >6, <8 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh <20-hour LCso = >6, <8 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >20-, <40-hour LCso = ~6 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >20-, <40-hour LCso = >6, <8 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >40-, <60-hour LCso = >4, <6 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >40-, <60-hour LCso = >6, <8 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >60-, <80-hour LCso = >6, <8 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >60-, <80-hour LCso = >4, <6 mg AI/L Not reported Flow- through, Measured Mortality Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >60-, <80-hour ECso = >4, <6 mg AI/L Not reported Flow- through, Measured Equilibrium Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >60-, <80-hour ECso = >4, <6 mg AI/L Not reported Flow- through, Measured Equilibrium Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >40-, <60-hour ECso = >4, <6 mg AI/L Not reported Flow- through, Measured Equilibrium Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >40-, <60-hour ECso = >4, <6 mg AI/L Not reported Flow- through, Measured Equilibrium Call et al„ 1979 High Rainbow trout {Oncorhynchu s mvkiss) Fresh >20-, <40-hour ECso = ~6 mg AI/L Not reported Flow- through, Measured Equilibrium Call et al., 1979 High 5 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Rainbow trout (Oncorhynchu s mvkiss) Fresh >20-, <40-hour ECso = >4, <6 mg AI/L Not reported Flow- through, Measured Equilibrium Call et al„ 1979 High Rainbow trout Fresh <20-hour m p o II ck Not reported Flow- Equilibrium Call et al„ High ('Oncorhynchu s mvkiss) mg AI/L through, Measured 1979 Rainbow trout Fresh <20-hour m p o II V p Not reported Flow- Equilibrium Call et al„ High ('Oncorhynchu s mvkiss) <8 mg AI/L through, Measured 1979 Rainbow trout Fresh <20-hour m p o II V p Not reported Flow- Equilibrium Call et al„ High {Oncorhynchu s mvkiss) <8 mg AI/L through, Measured 1979 Rainbow trout Fresh <20-hour m p o II V 00 Not reported Flow- Equilibrium Call et al„ High {Oncorhynchu s mvkiss) <10 mg AI/L through, Measured 1979 Bluegill Fresh 24-hour LCso = 46 Not reported Static, Mortality Buccafusco Medium {Lepomis macrochirus) mg AI/L Nominal etal., 1981 Bluegill Fresh 96-hour LCso = 13 Not reported Static, Mortality Buccafusco Medium {Lepomis macrochirus) mg AI/L Nominal etal., 1981 Bluegill Fresh 1-21 day BCF = 49 0.00343 mg AI/L Flow- Bioconcentratio Barrows et Medium {Lepomis macrochirus) through, Measured n al„ 1978 Fathead Fresh 32-day NOAF.L = Not reported Flow- Mortality Ahmad et High minnow {Pimephales promelas) 1.4 mg AI/L through, Measured al„ 1984 Fathead Fresh 32-day MATC = Not reported Flow- Growth: Wet Alunad et High minnow {Pimephales promelas) 0.5, 1.4 mg AI/L through, Measured weight al„ 1984 Fathead Fresh 32-day NOAF.L = Not reported Flow- Growth: Wet Alunad et High minnow {Pimephales promelas) 0.5 mg AI/L through, Measured weight al„ 1984 Fathead Fresh 32-day LOAEL = Not reported Flow- Growth: Wet Alunad et High minnow {Pimephales promelas) 1.4 mg AI/L through, Measured weight al„ 1984 Fathead Fresh 32-day LCioo = Not reported Flow- Mortality Alunad et High minnow {Pimephales promelas) 4.1 mg AI/L through, Measured al„ 1984 Fathead Fresh 96-hour r p o II Not reported Flow- Mortality Geiger et High minnow {Pimephales promelas) 13.4 mg AI/L through, Measured al„ 1985 6 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Fathead minnow (Pimephales promelas) Fresh 96-hour LCso = 20.3 mg/L Not reported Flow- through, Measured Mortality Geiger et al„ 1985 High Fathead Fresh 96-hour LCso = Not reported Flow- Mortality Broderius High minnow 23.8 mg through, and Kahl, (Pimephales promelas) AI/L Not reported 1985 Fathead Fresh 96-hour LCso = Not reported Static, Mortality Brooke, High minnow 10.8 mg Measured 1987 (Pimephales promelas) AI/L Fathead Fresh 32-day LCioo = Not reported Flow- Mortality De Foe, Medium minnow (Pimephales promelas) 4.1 mg AI/L through, Measured 1980 rFathead Fresh 24-hour LCso = Not reported Flow- Mortality Alexander High minnow (Pimephales promelas) 23.5 mg AI/L through, Measured et al„ 1978 Fathead Fresh 48-hour LCso = Not reported Flow- Mortality Alexander High minnow (Pimephales promelas) 19.6 mg AI/L through, Measured et al„ 1978 Fathead Fresh 72-hour LCso = Not reported Flow- Mortality Alexander High minnow (Pimephales promelas) 18.9 mg AI/L through, Measured et al„ 1978 Fathead Fresh 96-hour LCso = Not reported Flow- Mortality Alexander High minnow (Pimephales promelas) 18.4 mg AI/L through, Measured et al„ 1978 Fathead Fresh 96-hour LCso = Not reported Static, Mortality Alexander High minnow 21.4 mg Nominal et al„ 1978 (Pimephales promelas) AI/L Fathead Fresh 24-hour ECso = Not reported Flow- Immobilization Alexander High minnow (Pimephales promelas) 14.4 mg AI/L through, Measured et al„ 1978 Fathead Fresh 48-hour ECso = Not reported Flow- Immobilization Alexander High minnow (Pimephales promelas) 14.4 mg AI/L through, Measured et al„ 1978 Fathead Fresh 72-hour ECso = Not reported Flow- Immobilization Alexander High minnow (Pimephales promelas) 14.4 mg AI/L through, Measured et al„ 1978 7 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Fathead minnow (Pimephales promelas) Fresh 96-hour ECso = 14.4 mg AI/L Not reported Flow- through, Measured Immobilization Alexander et al„ 1978 High Fathead minnow (Pimephales promelas) Fresh 96-hour LCso = 23.8 mg AI/L Not reported Flow- through, Measured Mortality Envtl Research Laboratory, 1985 High Flagfish (Jordanella floridae) Fresh 96-hour LCso = 8.43 mg AI/L Not reported Flow- through, Measured Mortality Smith et al„ 1991 High Flagfish (Jordanella floridae) Fresh 10-day LOEC = 3.1 mg AI/L Not reported Flow- through, Measured Mortality Smith et al„ 1991 High Flagfish (Jordanella floridae) Fresh 28-day LOEC = 3.69 mg AI/L Not reported Flow- through, Measured Mortality Smith et al„ 1991 High Flagfish (Jordanella floridae) Fresh 28-day LOEC >9.3 mg AI/L Not reported Flow- through, Measured Growth: general Smith et al„ 1991 High Japanese medaka (Oryzias latipes) Fresh 10-day LCso = 25 mg AI/L Not reported Renewal, Nominal Mortality Schell, 1987 High Japanese medaka (Oryzias latipes) Fresh 10-day LCioo = 40 mg AI/L Not reported Renewal, Nominal Mortality Schell, 1987 High Japanese medaka (Oryzias latipes) Fresh 10-day NOEC = 17 mg AI/L Not reported Renewal, Nominal Mortality Schell, 1987 High Japanese medaka (Oryzias latipes) Not reporte d 96-hour NOEL = 2.19 mg AI/L LOEL = 4.37 mg AI/L 0, 20, 40, 60, 80 mg/L Renewal, Measured Mortality Spencer et al„ 2002 High Japanese medaka (Oryzias latipes) Not reporte d 96-hour LC50 = 26.8 mg AI/L 0, 20, 40, 60, 80 mg/L Renewal, Measured Mortality Spencer et al„ 2002 High Japanese medaka (Oryzias latipes) Not reporte d 96-hour LC95 = 96.53 mg AI/L 0, 20, 40, 60, 80 mg/L Renewal, Measured Mortality Spencer et al„ 2002 High Japanese medaka (Oryzias latipes) Not reporte d <17 days LOAEL = 1.5 mg AI/L 0, 1.5,3,6, 12, 25 mg/L Static, Nominal Reproduction: Hatch Spencer et al„ 2002 unacceptable 8 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Japanese medaka Fresh 96-hour LOAEL = 10 mg 0, 10 mg/L Static, Nominal Growth: Weight Spencer et al„ 2006 unacceptable (Orvzias latipes) AI/L Japanese medaka Fresh 96-hour LOAEL= 10 mg 0, 10 mg/L Static, Nominal Growth: Weight Spencer et al„ 2006 unacceptable (Orvzias latipes) AI/L Japanese medaka Fresh 96-hour LOAEL= 10 mg 0, 10 mg/L Static, Nominal Growth: Weight Spencer et al„ 2006 unacceptable (Orvzias latipes) AI/L Japanese medaka Fresh 96-hour LOAEL= 10 mg 0, 10 mg/L Static, Nominal Growth: Weight Spencer et al„ 2006 unacceptable (Orvzias latipes) AI/L Japanese medaka Fresh 96-hour LOAEL= 10 mg 0, 10 mg/L Static, Nominal Growth: Weight Spencer et al„ 2006 unacceptable (Orvzias latipes) AI/L Japanese medaka Fresh 96-hour LOAEL= 10 mg 0, 10 mg/L Static, Nominal Growth: Weight Spencer et al„ 2006 unacceptable (Orvzias latipes) AI/L Japanese medaka Fresh 96-hour LOAEL= 10 mg 0, 10 mg/L Static, Nominal Growth: Weight Spencer et al„ 2006 unacceptable (Orvzias latipes) AI/L Japanese medaka Fresh 96-hour LOAEL= 10 mg 0, 10 mg/L Static, Nominal Growth: Weight Spencer et al„ 2006 unacceptable (Orvzias latipes) AI/L Molly (Poecilia sphenops) Not reporte d 59-day LCioo = 0.005 mg AI/L Not reported Renewal, Nominal Mortality Loekle et al„ 1983 Unacceptable Sheepshead minnow Salt 24-hour LCso >52 mg AI/L Not reported Static, Nominal Mortality Heitmuller etal., 1981 Unacceptable (Cvprinodon variegatus) Sheepshead minnow Salt 48-hour LCso >52 mg AI/L Not reported Static, Nominal Mortality Heitmuller etal., 1981 Unacceptable (Cvprinodon variegatus) Sheepshead minnow Salt 96-hour LCso = >29, <52 Not reported Static, Nominal Mortality Heitmuller etal., 1981 Unacceptable (Cvprinodon variegatus) mg AI/L Sheepshead minnow Salt 96-hour NOEC = 29 mg Not reported Static, Nominal Mortality Heitmuller etal., 1981 Unacceptable (Cvprinodon variegatus) AI/L 9 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Sheepshead minnow Salt 24-hour LCioo = 31.63 mg Not reported Static, Nominal Mortality Home et al„ 1983 High (Cvprinodon variegatus) AI/L Sheepshead minnow Salt 24-hour LCioo = 31.63 mg Not reported Static, Nominal Mortality Home et al„ 1983 High (Cvprinodon variegatus) AI/L Sheepshead minnow Salt 96-hour LCso = 9.8 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High (Cvprinodon variegatus) Inland silverside Salt 96-hour LCso = 28.1 mg Not reported Static, Nominal Mortality Home et al„ 1983 High (Menidia bervllina) AI/L Aquatic Invertebrates Water flea Fresh 48-hour LCso = 18 Not reported Static, Mortality Richter et High (Daphnia mg AI/L Measured al„ 1983 magna) Water flea Fresh 48-hour LCso = 9.1 Not reported Static, Mortality Richter et High (Daphnia mg AI/L Measured al„ 1983 magna) Water flea Fresh 48-hour EC5o=8.5 Not reported Static, Immobilization Richter et High (Daphnia mg AI/L Measured al„ 1983 magna) Water flea Fresh 48-hour EC5o=7.5 Not reported Static, Immobilization Richter et High (Daphnia mg AI/L Measured al„ 1983 magna) Water flea Fresh 24-hour LCso = Not reported Static, Mortality LeBlanc, High (Daphnia magna) 14.4 mg AI/L Nominal 1980 Water flea Fresh 48-hour LCso = Not reported Static, Mortality LeBlanc, High (Daphnia magna) 14.4 mg AI/L Nominal 1980 Water flea Fresh 48-hour NOEC = 8 Not reported Static, Mortality LeBlanc, High (Daphnia mg AI/L Nominal 1980 magna) Water flea Fresh 28-day NOEC = Not reported Renewal, Growth: Length Call et al„ High (Daphnia magna) 0.505 mg AI/L Measured 1980 Water flea (Daphnia magna) Fresh 28-day NOEC = 0.505 mg AI/L Not reported Renewal, Measured Reproduction: Reproductive success (general) Call et al„ 1980 High Water flea Fresh 48-hour LCso = Not reported Static, Mortality Call et al„ High (Daphnia magna) 18.1 mg AI/L Measured 1980 Water flea Fresh 48-hour ECso = 8.5 Not reported Static, Immobilization Call et al„ High (Daphnia mg AI/L Measured 1980 magna) 10 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Water flea (Daphnia magna) Fresh 48-hour LCso = 9.09 mg AI/L Not reported Static, Measured Mortality Call et al„ 1980 High Water flea Fresh 48-hour ECso = Not reported Static, Immobilization Call et al„ High (Daphnia magna) 7.49 mg AI/L Measured 1980 Water flea Fresh 2-day LCso = 0,0.17, 0.33,0.66, Renewal, Mortality Niederlehn High {Ceriodaphnia dubia) 2.48751 mg AI/L 0.99, 1.5 mg/L Measured eret al., 1998 Water flea Fresh 7-day LCso = 0,0.17, 0.33,0.66, Renewal, Mortality Niederlehn High {Ceriodaphnia dubia) 0.82917 mg AI/L 0.99, 1.5 mg/L Measured er et al., 1998 Water flea Fresh 7-day NOEL = 0,0.17, 0.33,0.66, Renewal, Reproduction: Niederlehn High ('Ceriodaphnia dubia) 0.331668 mg AI/L LOEL = 0.663336 mg AI/L 0.99, 1.5 mg/L Measured Progeny counts/numbers er et al., 1998 Water flea Fresh 7-day IC50 = 0,0.17, 0.33,0.66, Renewal, Reproduction: Niederlehn High {Ceriodaphnia dubia) 0.663336 mg AI/L 0.99, 1.5 mg/L Measured Progeny counts/numbers er et al., 1998 Brine shrimp {Artemia Salt 24-hour LCso = 23.21676 Not reported Aquatic- not Mortality Sanchez- Fortun et Low salina) mg AI/L reported. Nominal al., 1997 Brine shrimp {Artemia Salt 24-hour LCso = 6.63336 Not reported Aquatic- not Mortality Sanchez- Fortun et Low salina) mg AI/L reported. Nominal al., 1997 Brine shrimp {Artemia Salt 24-hour LCso = 0.331668 Not reported Aquatic- not Mortality Sanchez- Fortun et Low salina) mg AI/L reported. Nominal al., 1997 Opossum shrimp {Americamysis bahia) Salt 96-hour LC50 = 2.85 mg AI/L Not reported Flow- through, Measured Mortality Hollister et al., 1968 High Opossum shrimp {Americamysis bahia) Salt 6-day NOAF.L = 1.4 mg AI/L Not reported Flow- through, Measured Mortality Hollister et al., 1968 High Opossum shrimp {Americamysis bahia) Salt 7-day LOAEL = 1.4 mg AI/L Not reported Flow- through, Measured Mortality Hollister et al., 1968 High Opossum shrimp {Americamysis bahia) Salt 28-day NOAF.L = 0.37 mg AI/L, LOAEL= 0.67 ppm Not reported Flow- through, Measured Mortality Hollister et al., 1968 High 11 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Opossum shrimp (Americamvsis bahia) Salt 28-day NOAF.L = 1.39 mg AI/L Not reported Flow- through, Measured Reproduction: progeny counts/ numbers Hollister et al„ 1968 High Opossum shrimp (Americamvsis bahia) Salt 28-day MATC = >0.3, <0.67 mg AI/L Not reported Flow- through, Measured Endpoint reported without a specific effect Hollister et al„ 1968 High Scud (Gammarus minus) Fresh 24-hour LCioo= 60 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Scud ('Gammarus minus) Fresh 96-hour LCo = 21.6 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Stonefly (Tallaperia maria) Fresh 96-hour LCso = 3.6 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Pond snail, pneumonate snail (Phvsa heterostropha) Fresh 96-hour LCso = 93.4 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Scud (Gammarus minus) Fresh 96-hour LCso = 28.6 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Scud (Gammarus annulatus) Salt 24-hour LCioo = 21 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Scud (Gammarus annulatus) Salt 24-hour LCioo = 24.7 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Scud (Gammarus annulatus) Salt 96-hour LCso = 9.1 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Daggerblade grass shrimp (Palaemonetes pugio) Salt 24-hour LCo = 2.5 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Daggerblade grass shrimp (Palaemonetes pugio) Salt 24-hour LCo = 2.5 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Daggerblade grass shrimp (Palaemonetes pugio) Salt 24-hour LCioo = 18.85 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Calanoid copepod (Acartia tonsa) Salt 96-hour LCso = 13.2 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High 12 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Bay shrimp, sand shrimp (Cragnon septemspinosa ) Salt 96-hour LCso = 17.4 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Daggerblade grass shrimp (Palaemonetes pugio) Salt 96-hour LCso= 1.3 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Polychaete wo mi (Neanthes arenaceodenta ta) Salt 96-hour LCso= 1.3 mg AI/L Not reported Static, Nominal Mortality Home et al„ 1983 High Flatworm (Dugesia japonica) Fresh 7-day LCso= 1.4 mg AI/L Not reported Renewal, Nominal Mortality Yosliioka et al„ 1986 Low Flatworm (Dugesia japonica) Fresh 7-day ECso = 0.9 mg AI/L Not reported Renewal, Nominal Limb/body part regeneration Yosliioka et al„ 1986 Low Ciliate (Tetrahymena pvriformis) Not reporte d 24-hour ECso = 100 mg AI/L Not reported Static, Nominal Population growth rate Yosliioka et al„ 1985 Unacceptable Midge (Tany tarsus dissimilis) Fresh 24-hour LCso = 54.6 mg AI/L Not reported Static, Measured Mortality Call et al„ 1983 High Midge (Tany tarsus dissimilis) Fresh 48-hour LCso = 30.8 mg AI/L Not reported Static, Measured Mortality Call et al„ 1983 High Midge (Tany tarsus dissimilis) Fresh 48-hour ECso = 7 mg AI/L Not reported Aquatic- not reported. Nominal Equilibrium Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >0, <10- hour LCso = >60, <80 mg AI/L Not reported Aquatic- not reported. Measured Mortality Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >0, <10- hour LCso = >60, <80 mg AI/L Not reported Aquatic- not reported. Measured Mortality Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >0, <10- hour LCso = ~60 mg AI/L Not reported Aquatic- not reported. Measured Mortality Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >10, <20-hour LCso = ~60 mg AI/L Not reported Aquatic- not reported. Measured Mortality Call et al„ 1979 High 13 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Midge (Tany tarsus dissimilis) Fresh >20, <30-hour LCso = >40, <60 mg AI/L Not reported Aquatic- not reported. Measured Mortality Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >20, <30-hour LCso = >40, <60 mg AI/L Not reported Aquatic- not reported. Measured Mortality Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >30-, <40-hour LCso = >40, <60 mg AI/L Not reported Aquatic- not reported. Measured Mortality Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >30-, <40-hour LCso = >20, <40 mg AI/L Not reported Aquatic- not reported. Measured Mortality Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >30-, <40-hour ECso = >0, <20 mg AI/L Not reported Aquatic- not reported. Measured Equilibrium Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >30-, <40-hour ECso = >0, <20 mg AI/L Not reported Aquatic- not reported. Measured Equilibrium Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >20, <30-hour ECso = >0, <20 mg AI/L Not reported Aquatic- not reported. Measured Equilibrium Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >20, <30-hour ECso = >0, <20 mg AI/L Not reported Aquatic- not reported. Measured Equilibrium Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >10, <20-hour ECso = >0, <20 mg AI/L Not reported Aquatic- not reported. Measured Equilibrium Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >10, <20-hour ECso = >0, <20 mg AI/L Not reported Aquatic- not reported. Measured Equilibrium Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >0, <10- hour ECso = ~20 mg AI/L Not reported Aquatic- not reported. Measured Equilibrium Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh >0, <10- hour ECso = ~20 mg AI/L Not reported Aquatic- not reported. Measured Equilibrium Call et al., 1979 High 14 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Midge (Tany tarsus dissimilis) Fresh >0, <10- hour ECso = >20, <40 mg AI/L Not reported Aquatic- not reported. Measured Equilibrium Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh 9-hour LCioo = 101.8 mg/AI/L Not reported Aquatic- not reported. Measured Mortality Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh <10 hour LCso = >60, <80 mg AI/L Not reported Aquatic- not reported. Measured Mortality Call et al„ 1979 High Midge (Tany tarsus dissimilis) Fresh <10 hour ECso = >20, <40 mg AI/L Not reported Aquatic- not reported. Measured Equilibrium Call et al„ 1979 High Algae Green algae (Chlamvdomo nas reinhardtii) Fresh 2-hour EC20 = 8.1 mg AI/L Not reported Static, Nominal Fluorescence Brack and Frank, 1980 Unacceptable Green algae (Chlamvdomo nas reinhardtii) Fresh 72-hour ECso = 3.64 mg AI/L Not reported Static, Nominal Biomass Brack and Rottler, 1994 High Green algae (Chlamvdomo nas reinhardtii) Fresh 72-hour EC10 = 1.77 mg AI/L Not reported Static, Nominal Biomass Brack and Rottler, 1994 High Green algae (Pseudokirchn eriella subcapitata) Fresh 48-hour ECso = 10.54 mg AI/L Not reported Static, Nominal Population growth rate Tsai and Chen, 2007 High Green algae (Pseudokirchn eriella subcapitata) Fresh 24-hour NOAF.L = 0.01 mg AI/L LOAEL = 0.02 mg AI/L 0, 0.01, 0.02, 0.05, 0.2, 0.5 mg/L Static, Nominal Abundance Labra et al., 2010 Medium Green algae (Pseudokirchn eriella subcapitata) Fresh 48-hour NOAF.L = 0.01 mg AI/L LOAEL= 0.02 mg AI/L 0, 0.01, 0.02, 0.05, 0.2, 0.5 mg/L Static, Nominal Abundance Labra et al., 2010 Medium Green algae (Pseudokirchn eriella subcapitata) Fresh 72-hour NOAF.L = 0.01 mg AI/L LOAEL= 0.02 mg AI/L 0, 0.01, 0.02, 0.05, 0.2, 0.5 mg/L Static, Nominal Abundance Labra et al., 2010 Medium 15 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Green algae Fresh 72-hour NOAEL = 0, 0.01, 0.02, 0.05, Static, Damage Labra et al.. Medium (Pseudokirchn eriella 0.02 mg AI/L 0.2, 0.5 mg/L Nominal 2010 subcapitatd) LOAEL = 0.05 mg AI/L Green algae Fresh 48-hour NOAEL= 0, 0.01, 0.02, 0.05, Static, Damage Labra et al.. Medium (Pseudokirchn eriella 0.02 mg AI/L 0.2, 0.5 mg/L Nominal 2010 subcapitatd) LOAEL= 0.05 mg AI/L Green algae Fresh 24-hour NOAEL= 0, 0.01, 0.02, 0.05, Static, Damage Labra et al.. Medium (Pseudokirchn eriella 0.02 mg AI/L 0.2, 0.5 mg/L Nominal 2010 subcapitatd) LOAEL= 0.05 mg AI/L Blue-green Fresh 24-hour LOAEL= 0, 23 |iL Static, Peroxidase Bacsi et al.. Unacceptable algae (Synechococcu s elongatus) 23 |iL Nominal activity 2013 Blue-green Fresh 24-hour LOAEL= 0, 23 |iL Static, Abundance Bacsi et al.. Unacceptable algae 23 |iL Nominal 2013 (Synechococcu s elongatus) Blue-green Fresh 4-hour LOAEL= 0, 23 |iL Static, Chlorophyll A Bacsi et al.. Unacceptable algae 23 |iL Nominal concentration 2013 (Synechococcu s elongatus) Blue-green Fresh 24-hour NOAEL= 0, 23 |iL Static, Chlorophyll A Bacsi et al.. Unacceptable algae 23 |iL Nominal concentration 2013 (Synechococcu s elongatus) Blue-green Fresh 4-hour NOAEL= 0, 23 |iL Static, Peroxidase Bacsi et al.. Unacceptable algae (Synechococcu s elongatus) 23 |iL Nominal activity 2013 Blue-green Fresh 8-hour LOAEL= 0, 23 |iL Static, Peroxidase Bacsi et al.. Unacceptable algae (Synechococcu s elongatus) 23 |iL Nominal activity 2013 Blue-green Fresh 12-hour LOAEL= 0, 23 |iL Static, Peroxidase Bacsi et al.. Unacceptable algae (Synechococcu s elongatus) 23 |iL Nominal activity 2013 Blue-green Fresh 24-hour LOAEL= 0, 23 |iL Static, Thiobarbituric Bacsi et al.. Unacceptable algae 23 |iL Nominal acid reactive 2013 (Synechococcu s elongatus) substances 16 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Blue-green algae {Synechococcu s elongatus) Fresh 12-hour LOAEL = 23 |iL 0, 23 |iL Static, Nominal Thiobarbituric acid reactive substances Bacsi et al., 2013 Unacceptable Blue-green algae {Synechococcu s elongatus) Fresh 8-hour LOAEL= 23 |iL 0, 23 |iL Static, Nominal Thiobarbituric acid reactive substances Bacsi et al., 2013 Unacceptable Blue-green algae {Synechococcu s elongatus) Fresh 4-hour LOAEL= 23 |iL 0, 23 |iL Static, Nominal Thiobarbituric acid reactive substances Bacsi et al., 2013 Unacceptable Algae (not reported) Fresh 24-hour LOAEL= 92 uL 0, 0, 92 |iL Lentic, Nominal Abundance Bacsi et al., 2013 Unacceptable Algae (not reported) Fresh 48-hour LOAEL= 92 uL 0, 0, 92 |iL Lentic, Nominal Abundance Bacsi et al., 2013 Unacceptable Algae (not reported) Fresh 72-hour LOAEL= 92 uL 0, 0, 92 |iL Lentic, Nominal Chlorophyll A concentration Bacsi et al., 2013 Unacceptable Algae (not reported) Fresh 48-hour LOAEL= 92 |iL 0, 0, 92 |iL Lentic, Nominal Thiobarbituric acid reactive substances Bacsi et al., 2013 Unacceptable Algae (not reported) Fresh 1-day LOAEL= 150 mg AI/L 0, 150 mg/L Lentic, Nominal Chlorophyll A concentration Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 2-day LOAEL= 150 mg AI/L 0, 150 mg/L Lentic, Nominal Chlorophyll A concentration Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 3-day NOAF.L = 150 mg AI/L 0, 150 mg/L Lentic, Nominal Chlorophyll A concentration Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 3-day NOAF.L = 150 mg AI/L 0, 150 mg/L Lentic, Nominal Abundance Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 2-day NOAF.L = 150 mg AI/L 0, 150 mg/L Lentic, Nominal Abundance Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 1-day LOAEL= 150 mg AI/L 0, 150 mg/L Lentic, Nominal Abundance Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 1-day LOAEL= 150 mg AI/L 0, 150 mg/L Lentic, Nominal Diversity, evenness Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 2-day LOAEL= 150 mg AI/L 0, 150 mg/L Lentic, Nominal Diversity, evenness Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 3-day NOAF.L = 150 mg AI/L 0, 150 mg/L Lentic, Nominal Diversity, evenness Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 1-day LOAEL= 150 mg AI/L 0, 150 mg/L Lentic, Nominal Chlorophyll A concentration Bacsi et al., 2015 Unacceptable 17 ------- INTERAGENCY DRAFT. DO NOT CITE OR QUOTE Table X. On-topic aquatic toxicity studies that were evaluated for Tetrachloroethylene Test Species Fresh/ Salt Water Duration End-point Concentration(s) Test Analysis Effect(s) References Data Quality Evaluation Algae (not reported) Fresh 2-day LOAEL = 150 mg AI/L 0, 150 mg/L Lentic, Nominal Abundance Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 3-day NOAF.L = 150 mg AI/L 0, 150 mg/L Lentic, Nominal Abundance Bacsi et al., 2015 Unacceptable Algae (not reported) Fresh 3-day NOAF.L = 150 mg AI/L 0, 150 mg/L Lentic, Nominal Diversity, Evenness Bacsi et al., 2015 Unacceptable Amphibians Wood frog (Lithobates svlvaticus) Fresh 96-hour ECso = 7.8 mg AI/L 0,2.5, 7.5, 12.5, 20, 30, 45 mg/L Renewal, Measured Deformation McDaniel et al., 2004 High Bronze frog (Lithobates clamitans ssp. Clamitans) Fresh 96-hour ECso = 7.9 mg AI/L 0,2.5, 7.5, 12.5, 20, 30, 45 mg/L Renewal, Measured Deformation McDaniel et al., 2004 High American toad (Bufo americanus) Fresh 96-hour ECso >45 mg AI/L 0,2.5, 7.5, 12.5, 20, 30, 45 mg/L Renewal, Nominal Deformation McDaniel et al., 2004 High Spotted salamander (Ambvstoma maculatum) Fresh 96-hour ECso = 14.5 mg AI/L 0,2.5, 7.5, 12.5, 20, 30, 45 mg/L Renewal, Measured Deformation McDaniel et al., 2004 Medium Fungi Fungi (Aspergillus versicolor) Fresh ~30-hour LTso = 1,900 mg AI/L 0, 1,900 mg/L Static, Not reported Mortality Steiman et al., 1995 Low Fungi (Aspergillus cejpii) Fresh ~20-hour LTso = 1,900 mg AI/L 0, 1,900 mg/L Static, Not reported Mortality Steiman et al., 1995 Low Fungi (Coniothrium sp.) Fresh ~30-hour LTso = 1,900 mg AI/L 0, 1,900 mg/L Static, Not reported Mortality Steiman et al., 1995 Low Fungi (Acremonium tubakii) Fresh ~30-hour LTso = 1,900 mg AI/L 0, 1,900 mg/L Static, Not reported Mortality Steiman et al., 1995 Low Fungi Class: Basidiomycete s Fresh ~20-hour LTso = 1,900 mg AI/L 0, 1,900 mg/L Static, Not reported Mortality Steiman et al., 1995 Low Fungi Class:, Basidiomycete s Fresh ~10-hour LTso = 1,900 mg AI/L 0, 1,900 mg/L Static, Not reported Mortality Steiman et al., 1995 Low Fungi (Phoma putaminum) Fresh ~30-hour LTso = 1,900 mg AI/L 0, 1,900 mg/L Static, Not reported Mortality Steiman et al., 1995 Low 18 ------- |