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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Toxicity to terrestrial plants

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Administrative data

Link to relevant study record(s)

Description of key information

Key value for chemical safety assessment

Additional information

According to Regulation (EC) 1907/2006, Annex IX, Section 9.4.1 to 9.4.3, Column 2, studies on the toxicity to terrestrial organisms do not need to be conducted if direct and indirect exposure of the soil compartment is unlikely.
For tripropylamine only industrial and professional uses with adequate risk mitigating measures are foreseen. Environmental exposure through widespread uses by consumers is excluded. Widespread uses by professionals will mostly take place indoors. In case of outdoor scenarios, risk mitigating measures are implemented to reduce unintended exposure to insignificant amounts. The substance is not supposed to be directly applied to soil.
Tripropylamine is considered not readily biodegradable according OECD criteria, however shown to be easily eliminated from water, after an extended lag phase (see IUCLID Ch. 5.2.1). Therefore, an indirect exposure to soil via sewage sludge transfer may be reduced since it can be assumed that the substance will partly be biodegraded within the STP process and as a consequence a transfer to the soil compartment is minimized. Additionally, adsorption to sewage sludge is not expected based on the low adsorption potential (see IUCLID Ch. 5.4.1); therefore, further reducing the risk of indirect transfer of the substance via sewage sludge.

In Annex XI, Section 3, it is laid down that testing in accordance with Annex IX may be omitted, based on the exposure scenario(s) developed in the Chemical Safety Report (“Substance-Tailored Exposure-Driven Testing”). In accordance with Annex XI, Section 3, it can be demonstrated in the risk assessment that the manufacture and the use of the substance do not pose an unacceptable risk for all environmental compartments as the risk characterization ratios (RCRs) of the chemical safety assessment are well below 1 for all compartments (see Chemical Safety Report Ch. 10).
Consequently, no tests on soil organisms are performed. The equilibrium partitioning method has been used for assessing the hazard to soil organisms in accordance with Annex IX, Section 9.4, Column 2 of Regulation (EC) No 1907/2006.