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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Ecotoxicological information

Toxicity to microorganisms

Currently viewing:

Administrative data

Link to relevant study record(s)

Description of key information

NOEC (14 d) ≥ 100 mg/L (from ready biodegradation test, 67.3% biodegradation within 14 days in toxicity control); read-across

Key value for chemical safety assessment

Additional information

Since no studies investigating the toxicity of Lauric acid ester with hydroxypropanediyl diacetate (CAS 30899-62-8) to activated sludge microorganisms are available, in accordance to Regulation (EC) No 1907/2006 Annex XI, 1.5 a read-across to the structurally related source substance Glycerides, C8-21 and C8-21-unsatd. mono- and di-, acetates (CAS 97593-30-1) was conducted.

The target substance is mainly characterized as a triester of glycerol esterified with acetic acid and lauric acid. A structurally very similar substance was selected as source substance. Glycerides, C8-21 and C8-21-unsatd. mono- and di-, acetates (CAS 97593-30-1) is a multi-constituent substance described as a triester of glycerol with acetic acid and lauric acid in a slightly different composition compared to the target substance. This read-across is justified in detail in the overall summary (IUCLID Section 6.1) and within the analogue justification in IUCLID Section 13. In this case of read-across, the best suited (highest degree of structural similarity, nearest physico-chemical properties) read-across substance was used for the assessment.

No standard studies evaluating the effects of the source substance Glycerides, C8-21 and C8-21-unsaturated, mono- and di-, acetates (CAS 97593-30-1) on respiration inhibition of activated sludge microorganisms are available. Therefore, a ready biodegradability study is used to derive a NOEC for this endpoint. If a compound degrades well in a ready biodegradability test, or does not inhibit the degradation of a positive control at a certain concentration, this concentration can be used as a NOEC value. This approach is in accordance with the Guidance on information requirements and chemical safety assessment (Chapter R.7b: Endpoint specific guidance, ECHA 2016). A substance can be assumed to be not inhibitory of the activity of aquatic microorganisms if, in the toxicity control of a ready biodegradation test, more than 25% biodegradation occurs within a period of 14 days (OECD Guideline 301). For Glycerides, C8-21 and C8-21-unsaturated, mono- and di-, acetates a biodegradation screening test according to OECD 301F is available (Weyers, 2007). This test includes a toxicity control containing 100 mg/L of test material and reference substance (sodium benzoate). Within 14 days, 67.3% biodegradation took place in this toxicity control clearly indicating the lack of toxic potential of Glycerides, C8-21 and C8-21-unsaturated, mono- and di-, acetates to aquatic microorganisms, and therefore, the test item concentration of 100 mg/L can be used as a NOEC (NOEC (14 d) ≥ 100 mg/L).

Based on the available result from one structurally related source substance (in accordance to Regulation (EC) No 1907/2006 Annex XI, 1.5) which is characterized by a comparable structure and composition, it can be concluded that Lauric acid ester with hydroxypropanediyl diacetate will not inhibit the degradation process in sewage treatment plants.