Registration Dossier

Data platform availability banner - registered substances factsheets

Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

In general, phototransformation and hydrolysis are the main abiotic degradation pathways for a substance. Mn(II)IDHA is neither susceptible for phototransformation in air, water and soil nor for hydrolysis under environmental conditions. Only the cation (Mn2+) will undergo hydrolysis at pH < 7 resulting in the formation of metal hydroxides [Mn(OH)2]. In general, experimental investigations are not triggered for a registration under REACH.

Biotic degradation

Mn(2Na)IDHA was identified to be "inherently biodegradable" (Chojnacka, 2014). In addition to that, the substance was found to be potentially biodegradable by Cokese et al. (2004). Conclusively, the substance will be degraded when entering the environmental compartment and therefore will not be persistent.

Bioaccumulation

Bioaccumulation in aquatic organisms is not expected for Mn(II)IDHA. The first indication for that conclusion is given by the substance specific logPow of -2.69 at 23 °C (experimentally determined; Stegient-Nowicka, 2013). Bioaccumulation is expected for substances possessing a partition coefficient in the range of 4.5 to 6 according to ECHA Guidance R.11, PBT Assessment).

Transport and distribution

Soil adsorption is not expected for Mn(II)IDHA based on the intrinsic physico-chemical properties, i.e. logPow of -2.69 (Stegient-Nowicka, 2013).

The QSAR prediction with KOCWIN v2.00 (logKoc = 1.00 L/kg; Chemservice S.A., 2014) reveals that the substance possesses no strong binding capacity towards soil.

Henry´s Law constant was manually calculated and amounts to 2.37 E-8 Pa*m3*mol-1 at 20 °C (Chemservice S.A., 2014). This value, as well as the key value of the Koc determination, will be taken into account for the chemical safety assessment (CSA), i.e. PNECsediment and PNECsoil derivation via the equilibrium partitioning method (EPM).