m-Cresol - ipcs inchem

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OECD SIDS m- / p-CRESOL Table 12: Tests on Acute Toxicity of m-and p-Cresol to Invertebrates Species Test type Exposure period Daphnia magna Effects [mg/l] m-Cresol p-Cresol Reference Static 24 h EC50 = 4.9 (n) Kühn et al. (1988, 1989a) * Static 48 h EC50 = 7.7 (n) Kühn et al. (1989b) Static 24 h EC50 =19.2 (n) EC50 =12.4 (n) Devillers et al. (1987, 1988) static 24 h EC50 = 25 (n) Bringmann and Kühn (1982) * static 24 h EC50 = 8.9 (n) Bringmann and Kühn (1977a) * Daphnia pulicaria flow through 48 h EC50 > 99.5 (e) EC50 = 22.7 (e) DeGraeve et al. (1980) * (n): nominal concentration (e): effective concentration *: studies which are flagged as key studies Table 13: Tests on Long-term Toxicity of m-and p-Cresol to Fish and Invertebrates Species Test type Exposure period Effects [mg/l] m-Cresol p-Cresol Reference Pimephales promelas Early life stage 32 d NOEC = 1.35 (n) Barron and Adelmann (1984)* Daphnia magna semistatic 21 d NOEC = 1.0 (n) Kühn et al. (1988, 1989a) * Dugesia tigrina (aquatic flatworm) (n): nominal concentration (e): effective concentration *: studies which are flagged as key studies semistatic 80 d LC10 =2.0 (n) LC0 = 1.0 (n) Solski and Piontek (1987) 38 UNEP PUBLICATIONS
OECD SIDS m- / p-CRESOL Table 14: Toxicity of m- and p-Cresol to Aquatic Plants Species Exposure period Effects [mg/l] m-Cresol p-Cresol Scenedesmus subspicatus 48 h E b C10 = 2.3 (n) E r C10 = 4.6 (n) E b C50 = 7.8 (n) E r C50 = 21 (n) Endpoint Biomass Growth rate Reference Kühn and Pattard (1990) * Chlorella pyrenoidosa 72 h EC50 = 127 (n) EC50 = 116(n) Chlorophyll content Huang and Gloyna (1968) (n): nominal concentration (e): effective concentration *: studies which are flagged as key studies UNEP PUBLICATIONS 39
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