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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

For the indirect photodegradation of isovaleric acid in air by the reaction with OH-radicals, a half-life of approx. 31.3 hours (2.6 days) was calculated (GUBDH, 2012, US EPA EPI Suite v4.10).

Hydrolysis

Due to its chemical structure and reactivity, isovaleric acid will not hydrolyse under environmental conditions. The structure of the molecule does not contain hydrolysable constituents (GUBDH, 2008).

 

Biodegradation

Biodegradation in water: screening test

Isovaleric acid has been shown to be readily biodegradable in two tests for ready biodegradability.

1. - test similar to OECD TG 301 C (Urano, 1986; RL2; KS)

2. - test similar to OECD TG 301 D (Dias, 1971; RL2; SS)

Biodegradation in water and sediment: simulation test

Tests need not be conducted, as isovaleric acid is readily biodegradable.

In addition, data are not required as only Annex VII data requirements have to be fulfilled.

Biodegradation in soil

Tests need not be conducted, as isovaleric acid is readily biodegradable. In addition, data are not required as only Annex VII data requirements have to be fulfilled.

 

Bioaccumulation

Bioaccumulation: aquatic/sediment

Not required as the substance is registered under provisions of Article 12(1)(c) of REACH.

As the log Kow of isovaleric acid is low (log Kow = 1.7, Sect. 4.7, OXEA, 2010) and the substance is readily biodegradable (Urano, 1986 and Dias 1971), the potential for bioaccumulation of isovaleric acid is low.

In addition, calculated Log BCF and log BAF (upper trophic) values of 0.5 and 0.748 respectively (US EPA EPI Suite v4.10, program component BCFBAF v3.01) indicate a low potential of isovaleric acid for bioaccumulation in aquatic organisms (GUBDH, 2012).

Terrestrial

No data available (data are not required as only Annex VII data requirements have to be fulfilled).

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Transport and Distribution

Adsorption/Desorption

In accordance with column 2 of REACH Annex VIII Nr 9.3.1, the study does not need to be conducted as the substance has a low potential for adsorption (log Kow < 3, see Sect. 4.7) and is readily biodegradable (see Sect. 5.2.1).

Based on a calculated Koc of 4.022 (log Koc = 0.6045), isovaleric acid is expected to have a high mobility in soil (GUBDH, 2012).

Henry’s Law constant

For isovaleric acid, a Henry's law constant of 8.333E-7 atm m³/mol was determined in an experimental study using equilibrium partial pressure measurements over aqueous solutions at 298.15 K (25°C) (Khan, 1992).

Calculations (GUBDH, 2012; US EPA EPI Suite v4.10) resulted in

Bond contribution method: HLC (25°C) = 1.28E-006 atm m³/mole

Group contribution method: HLC (25°C) = 9.96E-007 atm m³/mole

Isovaleric acid will volatilize from water only to a low degree.