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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

BIODEGRATDATION IN WATER: SCREENING TESTS

The registration substance is readily biodegradable in an OECD Tests 301B.

BIODEGRADATION IN WATER AND SEDIMENT: SIMULATION TESTS

SEWAGE TREATMENT PLANT

C12 -18. 18u alkyl amines were tested in two OECD 303A Sewage treatment plant simulation test. The test substance showed very high elimination after having reached the plateau phase. The elimination was >99.8 % (removal via adsorption expected in the range of 2 - 5 % based on the discussed publication of Geerts et al (2015) results in primary biodegradation of 95 - 98 %) and this can be attributed to ultimate biodegradation as in the ready tests no recalcitrant metabolites were formed.

FRESHWATER AND MARINE WATER

No simulation tests are available but according the REACH Guidance R.16.5.4.5 Half-lives can be assigned based on the ready test result:

Half-life Freshwater 15d

Half-life Marine water 50d

BIODEGRADATION IN SOIL & SEDIMENT

Based on an OECD 307 test on Aerobic transformation in soil with 1 -Hexadecanamine the median half-life over the three soils tested is 16.9 d at the environmental temperature of 12 deg Celsius. This soil biodegradation half-life is used for freshwater sediment as well (see REACH Guidance R16). The value for bulk sediment is set at 169 d.

BIOTRANSFORMATION IN FISH

The registration substance is also rapidly metabolized in fish. Metabolic rates in fish were measured for 1-Hexadecanamine (C16 amine) using an in vitro method with carp hepatocytes (Perdu-Durand, 2006, http://www.erasm.org/Study/INRA_report-subcellular-C16PA-060701.pdf). For a carp with a mass of 438 g the kM was estimated to be 0.152 1/d for a fish assuming only arterial blood supply to the liver, whereas a rate of 1.024 d-1 was estimated considering both arterial and a portal blood supplies.

METABOLISM IN MICROOGRANISM

The registration substance is rapidly biodegraded by microorganisms available in water, sediment and soil. The first step is the oxidative fission of the nitrogen alkyl bond leading to the corresponding alkanal and subsequently alkanoic (fatty) acid as well as ammonium. The fatty acid is rapidly metabolised by beta oxidation (van Ginkel, Handbook of Detergents, Volume F, Environmental Impact, 2003, CRC).

Additional Literature

  • Perdu-Durand et al (2006): Hexadecylamine biotransformation rates in carp and rainbow trout liver subcellular fractions, ERASM (http://www.erasm.org/Study/INRA_report-subcellular-C16PA-060701.pdf), 2006

Additional information