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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Stability

Formic acid is hydrolytically stable (BASF AG, 2002).

In air, formic acid is expected to be photodegraded by OH-radicals with a half-life of 30.1 d (BASF AG, 2006).

Rate constants for photoransformation in water (selected values; Buxton et al., 1988):

k = 4.4E+05 M-1 * sec-1 (formic acid at pH 0.4 - 1)

k = 2.1E+08 M-1 * sec-1 (formate ion at pH 7)

Biodegradation

Formic acid and the formate ion are readily biodegradable (EU method C.4-B; OECD TG 301D) (BASF AG, 1988; HRC, 1992; NIVA, 2000).

Formic acid and the formate ion are readily biodegradable in seawater (Closed Bottle Test, OECD TG 306) (Price et al., 1974; Binnie, 1994).

Bioaccumulation

Formic acid has a measured log Kow of -2.1 (23 °C, pH 7), which is < 3 (BASF AG; 2007). The correspondingly calculated BCF is 3.2 (ECT, 2007). Therefore, significant bioaccumulation is not to be expected.

Transport and distribution

Formic acid (uncharged): Adsorption to the solid soil phase is not expected (BASF AG, 2002).

Formate ion: Adsorption to the solid soil phase is possible (BASF SE, 2009).

The Henry's Law Constant (HLC) of formic acid was determined to be 0.019 Pa m³/mol at 25 °C (Khan & Brimblecomb, 1992).

Following the Mackay Level I calculations, formic acid will preferentially distribute into the water (93.5 %)(ECT, 2007).