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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Ecotoxicological information

Toxicity to soil microorganisms

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Administrative data

Link to relevant study record(s)

Reference
Endpoint:
toxicity to soil microorganisms
Data waiving:
other justification
Justification for data waiving:
other:

Description of key information

Key value for chemical safety assessment

Additional information

In contact with water, sodium methanolate rapidly hydrolyses to methanol and sodium hydroxide (OECD, 2002). Thus, the degradation products of sodium methanolate are of relevance for the assessment of environmental toxicity.

No studies on the toxicity to soil microorganisms are available for sodium methanolate or the degradation products methanol and sodium hydroxide. All available data on terrestrial organisms as well as activated sludge microorganisms do not indicate a need to investigate the effects of the substance and relevant degradation products on soil microorganisms.

Sodium hydroxide
Sodium hydroxide further dissociates in the environment to sodium (K+) and hydroxyl ions (OH-). Sodium belongs to the alkali metals and is one of the most common elements in the earth crust. Together with potassium ions (K+), sodium ions (Na+) are responsible for maintaining the cell membrane potential and essential for the function of all living cells (Clausen&Poulsen, 2013). Many physiological processes in organisms are driven by the influence of sodium. Thus, sodium ions are not considered to be relevant for aquatic toxicity. Hydroxyl ions may cause a change (increase) of pH of the receiving environmental compartment. This may result in effects on aquatic organisms in case the pH is changed outside of the tolerable pH-range. Thus, hydroxyl ions do not have an intrinsic toxicity but may cause physical effects depending on the buffer capacity of the aqueous medium (OECD, 2002). It has to be noted that effluents from sewage treatment plants are measured frequently for its pH and are appropriately adapted before release if needed. In addition, due to the dilution effects and buffer capacity of natural aquatic ecosystems significant pH changes followed by effects on aquatic species are not expected (OECD, 2002). In conclusion, any observed effects after exposure of terrestrial organisms to sodium hydroxide is considered to be solely caused by a potential change of pH. Sodium ions are not considered to contribute to terrestrial toxicity.

Methanol
Data on methanol investigating the long-term toxicity to soil organisms are available for terrestrial plants, earthworms and terrestrial arthropods (Stantec 2006).

All available studies indicate a low toxicity of methanol to terrestrial organisms with NOEC values≥1000 mg/kg.

 

Thus, no further testing on soil microorganisms is deemed necessary for sodium methanolate.