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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Abiotic degradation

Na2CO3, Na2S and NaHS are not expected to be released to the air as such because of their low vapour pressure. However, for Na2S and NaHS, in case H2S is formed, H2S may be released to the air. In the atmospheric compartment, sulphur compounds such as H2S will be oxidized to SO2 and, eventually, to sulphate compounds.

When Na2S or NaHS are released to the aquatic compartment, the substances will hydrolyze immediately and a pH dependent equilibrium will be established between H2S, HS- and S2-. However, in aerobic environments, the dissolved sulphide will be oxidised to - eventually - sulphate. In anaerobic environments (e.g., organic-rich sediments) H2S formation will be favoured and no oxidation will occur. However, in these kinds of environments, the dissolved sulphide may be depleted through precipitation with metals. In view of environmental hazard assessment, it should however be kept in mind that typical organisms living in natural reducing environments are often well adapted to living in the fluctuating presence of H2S.

Except in waterlogged and/or highly organic soils, released sulphides are expected to be oxidised relatively rapidly. In soils with reducing conditions, H2S formation will be favoured and similar transformation/removal processes as in sediments will occur. This also holds for deeper layers of well drained soils.

Biodegradation

Biodegradation is not deemed relevant for inorganic compounds. However, it should be kept in mind that any sulphur released to the environment will enter the natural sulphur cycle in which both oxidation and reduction reactions are mediated through abiotic as well as biotic processes. Sulfur oxidising and reducing microorganisms are omnipresent and determine the predominant state of the present sulphur depending on the prevalent conditions.

Environmental distribution

Release to the aquatic environment will be the most relevant route of release for Na2S and NaHS. As mentioned above, the substances will be hydrolysed immediately upon contact with water and depending on the conditions reduced sulphides will stay present in the system or become oxidized to - eventuallly - sulphate. At the moment of release, the sulphur added to the environment enters the natural sulphur cycle and industrially released sulfur will become indistinguishable from naturally present or - overall - formerly present sulfur. Consequently, the environmental distribution of these compounds will be driven by the same reactions driving the natural sulphur cycle. For a thorough description of the sulphur cycle one can refer to the review of Brown (1982).