Registration Dossier
Registration Dossier
Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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.
Use of this information is subject to copyright laws and may require the permission of the owner of the information, as described in the ECHA Legal Notice.
EC number: 307-055-2 | CAS number: 97489-15-1
Endpoint summary
Administrative data
Description of key information
Additional information
Abiotic degradation in air
Direct photolysis in air
SAS does not absorb light > 290 nm (ozone band) and therefore a direct photolysis in air will not occur.
Indirect photolysis in air
OH-radical induced indirect photolysis of SAS can be calculated with US EPA AOPWIN program estimating a low degradation half-life of 0.9d. But as SAS has a Henry’s Law Constant of 4.7*10 -7Pa*m3/mole (see IUCLID Sections 4.6 & 4.8), volatilisation is not an exposure route which has to be considered.
Abiotic degradation in water
Hydrolysis
SAS has no functional groups which could be hydrolysed under environmental conditions as stated in OECD guideline 111. In addition, SAS is readily biodegradable.
Direct photolysis in water
SAS does not absorb light > 290 nm (ozone band) and therefore a direct photolysis in water will not occur.
Indirect photolysis in water
OH-radical induced indirect photolysis of SAS in air can be estimated with US EPA AOPWIN program estimating a low degradation half-life of 0.9 d. Therefore, SAS may also be degraded in water by indirect photolysis if sufficient OH radicals were available. As SAS is rapidly biodegraded in surface water (see IUCLID Section 5.2.2) indirect photolysis will play a minor role in degradation.
Abiotic degradation in soil
Direct photolysis in soil
SAS does not absorb light > 290 nm (ozone band) and therefore a direct photolysis on soil surface will not occur.
Indirect photolysis in soil
OH-radical induced indirect photolysis of SAS in air can be estimated with US EPA AOPWIN Program estimating a low degradation half-life of 0.9 d. Therefore, SAS may be degraded on soil surface by indirect photolysis but as SAS is rapidly biodegraded in aerobic soils (see IUCLID Section 5.2.3) indirect photolysis will play a minor role in degradation.
Information on Registered Substances comes from registration dossiers which have been assigned a registration number. The assignment of a registration number does however not guarantee that the information in the dossier is correct or that the dossier is compliant with Regulation (EC) No 1907/2006 (the REACH Regulation). This information has not been reviewed or verified by the Agency or any other authority. The content is subject to change without prior notice.
Reproduction or further distribution of this information may be subject to copyright protection. Use of the information without obtaining the permission from the owner(s) of the respective information might violate the rights of the owner.
