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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.

The new ECHA CHEM database has been released by ECHA, and it now contains all REACH registration data. There are more details on the transition of ECHA's published data to ECHA CHEM here.

Diss Factsheets

Ecotoxicological information

Endpoint summary

Administrative data

Description of key information

Additional information

The relevant data on toxicity on terrestrial organisms for Preventol KMX and the read across substance 4-chloro-3-methylphenol are summarized in the table below. The read across justification and additional data for m-cresol are attached to the Chemical Safety Report in Annex I. In comparison to the chlorocresols, m-cresol is only a minor component of Preventol KMX. Therefore these data are not considered for the assessment of the toxicity on terrestrial organisms of Preventol KMX.

Table 1: Comparison of relevant data on toxicity on terrestrial organisms of Preventol KMX and 4-chloro-3-methylphenol

Endpoint

Preventol KMX

4-chloro-3-methylphenol

Toxicity to soil macroorganisms except arthropods

Read across 4-chloro-3-methylphenol

OECD 207
Eisenia fetida
LC50 (14d): 139.4 mg/kg soil dw

Toxicity to terrestrial plants

Read across 4-chloro-3-methylphenol

OECD 208
Avena sativa
NOEC (14d) = 14.6 mg/kg soil dw

Toxicity to soil microorganisms

Read across 4-chloro-3-methylphenol

OECD216
N-transformation
EC50 (28d): 555.1 mg/kg soil dw
NOEC (28d): 300 mg/kg soil dw

No toxicity studies on terrestrial organisms for the reaction mass are available. The substance is a mixture of four different m-cresols which are similar in physico-chemical properties, environmental fate and metabolism.

For one of the components of the reaction mass (4-chloro-m-cresol, CAS No. 59-50-7) terrestrial toxicity was investigated for plants, soil macroorganisms and soil microorganisms. These studies are used as read across for the reaction mass. The 14-day study with plants revealed an EC50 of 27.7 mg/kg soil dw and a LOEC of 15 mg/kg dw. For earthworms an EC50 (14d) of 139.4 mg/kg soil dw was determined. For the nitrogen transformation of soil microorganisms an NOEC (28d) of 300 mg/kg soil dw was determined.