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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

MTBE is resistant to hydrolysis within environmentally relevant pH ranges as demonstrated in an OECD guideline, GLP-compliant study. Strong acids can contribute to the hydrolysis of MTBE, but the pH range in which this would occur is below typical ranges found in natural soil and water ( Lyman et al. 1982).

The degradation half-life of MTBE in the air is calculated to range between 3-6 days depending on environmental conditions (primarily OH-radical concentration).

The atmospheric half-life of MTBE is estimated at 5.65 days, based on degradation rate constant of 2.84E-12 cm3/molecule/s and a radical concentration of 5E05 radicals/cm3. The half-life represents a degradation rate in non-polluted air, rather than polluted air where half-lives typically are shorter due to a higher concentration of reactive radical components.

Direct photolysis will not be an important removal process of MTBE in water because aliphatic ethers do not absorb light at wavelengths, >290 nm, that are responsible for this process. The MTBE UV-spectrum, max t 289 nm, indicates that there is a low potential for direct photolysis in water.

The rate constant used in the assessment are:

Degradation for hydrolysis

0 d-1

Degradation for photolysis

0 d-1

Degradation in air

0.123 d-1