Registration Dossier

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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Environmental fate & pathways

Endpoint summary

Administrative data

Description of key information

Additional information

Stability

Phototransformation in air

This is not a standard information requirement for a registration under the REACH Regulation.

 

Hydrolysis

According to Annex VIII (Paragraph 9.2.2, Column 2) of the REACh regulation 1907/2006 a test on hydrolysis does not need to be conducted if the substance is readily biodegradable or highly insoluble in water. In addition alcohols are generally resistant to aqueous environmental hydrolysis. Therefore, 2-methylbutan-1-ol is not expected to hydrolyze in the environment.

 

Phototransformation in water

This is not a standard information requirement for a registration under the REACH Regulation.

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Phototransformation in soil

This is not a standard information requirement for a registration under the REACH Regulation.

 

Biodegradation

Biodegradation in water: screening test:

The ready biodegradability of the test substance was investigated according to OECD Guideline 310 (Ready Biodegradability - CO2 in Sealed Vessels (Headspace Test). The test substance was degraded 93 % in 18 days, therefore the test substance was found to be readily-biodegradable under the test conditions.

The ready biodegradability of the test item was also assessed in a read across category approach based on grouping of substances. The surrogate test substances were found to be readily biodegradable.

 

Biodegradation in water and sediment

The substance is considered as readily biodegradable. Therefore, no further testing on biodegradation is required according to Annex IX (Paragraph 9.2.1, Column 2) of the REACh regulation 1907/2006. 

 

Biodegradation in soil

The substance is considered as readily biodegradable. Therefore, no further testing on biodegradation is required according to Annex IX (Paragraph 9.2.1, Column 2) of the REACh regulation 1907/2006. 

 

Bioaccumulation

Bioaccumulation: aquatic/sediment

For 2 -methylbutan-1 -ol was determined a log Kow= 1.29 (25°C) according to Valvani SC et al., 1981 (HSDB, 2008).In accordance with Column 2 of REACH Annex IX, the study need not be conducted if the substance has a low potential for bioaccumulation (for instance a log Kow < 3) and/or a low potential to cross biological membranes. The substance has a log Kow < 3 and a low potential for bioaccumulation. Testing of bioconcentration in an aquatic species is therefore not required.

 

Bioaccumulation terrestrial

Data on terrestrial bioaccumulation in soil are not required for REACh registration.

 

Transport and distribution

Adsorption/Desorption

Based upon a calculated log Koc = 0.75 adsorption to solid soil phase is not expected.

 

Henry´s Law constant

2 -methylbutan-1-ol will slowly evaporate from the water surface into the atmosphere. Henry´s law constant at 25°C was estimated to be 1.34 Pa*m3/mole by SRC HENRYWIN v3.10 [BASF SE 2010].