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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Biodegradation in soil

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Administrative data

Link to relevant study record(s)

Reference
Endpoint:
biodegradation in soil: simulation testing
Data waiving:
study scientifically not necessary / other information available
Justification for data waiving:
the study does not need to be conducted because the substance is readily biodegradable

Description of key information

Substance is readily biodegradable (according to OECD criteria), therefore no further biodegradation testing required under REACh

Key value for chemical safety assessment

Additional information

Substance is readily biodegradable (according to OECD criteria), therefore no further biodegradation testing required under REACh. The biodegradbility of IBDU in soil, however, was studied in several tests (e.g. Hughes 1976, Markova 1978).

Through its use as slow-release fertilizer, IBDU granules are directly applied on soil. With soil moisture, IBDU may be hydrolized to urea and isobutyraldehyde, dependent on pH, granular size and temperature (Hamamoto, 1966). Both substances are at least inherently biodegradable. Urea is decomposed by urease into NH3 and CO2 (ammonification) and NH3 then protonated into the ammonium ion. The latter volatilizes or is oxidized via nitrite into nitrate (nitrification). Low pH (pH < 6), high temperatures, high soil moisture and small granular size increase solubilisation of IBDU and, hence, mineralization (Hamamoto, 1966; Hughes, 1976; Markova, 1978). Within 24 weeks, the total amount of mineralized nitrogen in 4 different soil types with pH values of 4.8 to 8.3 was between 88 and 99 % of the introduced IBDU (Markova, 1978).