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Please be aware that this old REACH registration data factsheet is no longer maintained; it remains frozen as of 19th May 2023.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

Environmental fate & pathways

Biodegradation in water: screening tests

Currently viewing:

Administrative data

Link to relevant study record(s)

Reference
Endpoint:
biodegradation in water: ready biodegradability
Type of information:
read-across from supporting substance (structural analogue or surrogate)
Adequacy of study:
key study
Justification for type of information:
Please refer to the analogue justification attached to IUCLID section 13.
Reason / purpose for cross-reference:
read-across source
Reason / purpose for cross-reference:
read-across source
Reason / purpose for cross-reference:
read-across source
Reason / purpose for cross-reference:
read-across source
Reason / purpose for cross-reference:
read-across source
Parameter:
% degradation (O2 consumption)
Value:
8
Sampling time:
28 d
Remarks on result:
other: Balk, 1989, Closed Bottle
Parameter:
% degradation (O2 consumption)
Value:
23
Sampling time:
28 d
Remarks on result:
other: Balk, 1989, RDA
Parameter:
% degradation (O2 consumption)
Value:
< 10
Sampling time:
28 d
Remarks on result:
other: van Ginkel 1988;Closed Bottle
Parameter:
% degradation (O2 consumption)
Value:
16
Sampling time:
28 d
Remarks on result:
other: 0.15% SSA dipersion
Remarks:
Kolvenbach 1989; Closed Bottle
Parameter:
% degradation (O2 consumption)
Value:
20
Sampling time:
28 d
Remarks on result:
other: 0.020% SSA dispersion
Remarks:
Kolvenbach 1989, Closed Bottle
Parameter:
% degradation (O2 consumption)
Value:
24
Sampling time:
28 d
Remarks on result:
other: Maximum degree of degradation with non-adapted inoculum
Remarks:
Kolvenbach 1989, Sturm test
Parameter:
% degradation (O2 consumption)
Value:
19
Sampling time:
28 d
Remarks on result:
other: Maximum degree of degradation with non-adapted inoculum
Remarks:
Kolvenbach 1989, Sturm test
Conclusions:
Not readily biodegradable: < 10% - 24% degradation (OECD 301 D, 301 F, DGXI/400/84 EEC 19984, L251, 1984.09.19, Part C, EEC 1984)
Executive summary:

Studies on the ready biodegradability of (Z)-N-octadecyldocos-13-enamide (CAS No. 10094-45-8) are not available. Therefore data of the analogue substance N-octadecylstearamide (stearyl stearamide, CAS 13276 -08 -9) were used as read-across. The ready biodegradability of N-octadecylstearamide (stearyl stearamide, CAS 13276 -08 -9) was investigated in five tests.

The first study comprises a test according to OECD guideline 301 D and a repetitive die away test following DGXI/400/84, EEC 1984 (Balk, 1989). Both tests were carried out under GLP and have a test duration of 6 weeks. In the OECD closed bottle test 2.04 mg/L of the substance was incubated with domestic activated sludge. The substance reached 8% degradation after 28 days and 9% degradation after 42 days. In the die away test 40 mg/L of the substance was incubated with industrial non-adapted activated sludge as inoculum. Degradation rates were 23% after 28 days and 29% after 42 days. The second study is a closed bottle test equivalent to the guideline L251, 1984.09.19, Part C, EEC 1984 (van Ginkel, 1988). Domestic activated sludge was used as inoculum and incubated with 2 mg/L of the substance. The degradation after 28 days was < 10%. The third study comprises two tests according to OECD guidelines 301 D and 301 F (Kolvenbach, 1989) using effluent from a municipal waste water treatment plant as inoculum. The closed bottle test applying 1.8 ppm of the substance resulted in 20% degradation after 28 days. The CO2 evolution test applying 10 and 20 ppm of the substance resulted in maximum degradation rates of 24% with non-adapted inoculum and 19% with adapted inoculum. Altogether it is stated that the substance can be regarded as not readily biodegradable under OECD criteria.

Description of key information

Not readily biodegradable: < 10% - 24% degradation (OECD 301 D, 301 F, DGXI/400/84 EEC 19984, L251, 1984.09.19, Part C, EEC 1984)

Key value for chemical safety assessment

Biodegradation in water:
not biodegradable
Type of water:
freshwater

Additional information

Studies on the ready biodegradability of (Z)-N-octadecyldocos-13-enamide (CAS No. 10094-45-8) are not available. Therefore data of the analogue substanceN-octadecylstearamide (stearyl stearamide, CAS 13276-08-9) were used as read-across.The read-across is justified due to the structural similarity of the analogue substances and similar physico-chemical properties resulting in a similar environmental fate and ecotoxicity profile.This read-across is in accordance with Regulation (EC) No. 1907/2006 Annex XI, 1.5 and justified in detail in the overall summary (IUCLID Chapter 6.1) and within the category justification attached in IUCLID Section 13. The ready biodegradability of N-octadecylstearamide (stearyl stearamide, CAS 13276-08-9) was investigated in five tests.

The first study comprises a test according to OECD guideline 301 D and a repetitive die away test following DGXI/400/84, EEC 1984 (Balk, 1989). Both tests were carried out under GLP and have a test duration of 6 weeks. In the OECD closed bottle test 2.04 mg/L of the substance was incubated with domestic activated sludge. The substance reached 8% degradation after 28 days and 9% degradation after 42 days. In the die away test 40 mg/L of the substance was incubated with industrial non-adapted activated sludge as inoculum. Degradation rates were 23% after 28 days and 29% after 42 days. The second study is a closed bottle test equivalent to the guideline L251, 1984.09.19, Part C, EEC 1984 (van Ginkel, 1988). Domestic activated sludge was used as inoculum and incubated with 2 mg/L of the substance. The degradation after 28 days was < 10%. The third study comprises two tests according to OECD guidelines 301 D and 301 F (Kolvenbach, 1989) using effluent from a municipal waste water treatment plant as inoculum. The closed bottle test applying 1.8 ppm of the substance resulted in 20% degradation after 28 days. The CO2 evolution test applying 10 and 20 ppm of the substance resulted in maximum degradation rates of 24% with non-adapted inoculum and 19% with adapted inoculum. Altogether it is stated that the substance can be regarded as not readily biodegradable under OECD criteria.