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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Endpoint summary

Administrative data

Description of key information

Additional information

Experimental studies on potassium methanolate investigating terrestrial toxicity are not available.

In water, potassium methanolate rapidly hydrolyses to methanol and potassium hydroxide (OECD, 2002). Due to the rapid hydrolysis of potassium methanolate, the assessment of the terrestrial toxicity is based on the products of hydrolysis i.e. methanol and potassium hydroxide.

Potassium hydroxide
Potassium hydroxide further dissociates in the environment to potassium (K+) and hydroxyl ions (OH-). Potassium belongs to the alkali metals and is one of the most common elements in the earth crust. Together with sodium ions (Na+), potassium ions (K+) 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 potassium. Thus, potassium 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 potassium hydroxide is considered to be solely caused by a potential change of pH. Potassium 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).

Following NOEC values have been derived for the most sensitive endpoints of the investigated species.

Earthworm (Eisenia andrei)
NOEC (63 d ): 10000 mg/kg dw based on reproduction

 

Terrestrial arthropods (Folsomia candida)
NOEC (28 d) 1000 mg/kg dw based on reproduction

 

Terrestrial plants
NOEC (21 d, Medicago sativa): 1555 mg/kg dw based on shoot dry mass and length
NOEC (14 d, Hordeum vulgare): 1555 mg/kg dw based on shoot dry mass
NOEC (21 d, Elymus lanceolatus): 2592 mg/kg dw based on shoot dry mass and length, root dry mass

All the available data consistently demonstrate the very low terrestrial toxicity of methanol for terrestrial organisms.