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Environmental fate & pathways

Biodegradation in water: screening tests

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Reference
Endpoint:
biodegradation in water: ready biodegradability
Type of information:
experimental study
Adequacy of study:
key study
Reliability:
2 (reliable with restrictions)
Rationale for reliability incl. deficiencies:
guideline study without detailed documentation
Qualifier:
according to guideline
Guideline:
OECD Guideline 301 B (Ready Biodegradability: CO2 Evolution Test)
Version / remarks:
adopted 17 July 1992
Deviations:
no
Qualifier:
according to guideline
Guideline:
EU Method C.4-C (Determination of the "Ready" Biodegradability - Carbon Dioxide Evolution Test)
Version / remarks:
29 December 1992
Deviations:
no
Principles of method if other than guideline:
20
GLP compliance:
no
Remarks:
ISO 17025
Oxygen conditions:
aerobic
Inoculum or test system:
activated sludge, domestic, non-adapted
Details on inoculum:
- Source of inoculum/activated sludge (e.g. location, sampling depth, contamination history, procedure): Activated sludge from the aeration tank of a municipal waste water treatment plant, not adapted, not pre-conditioned; ARA Werdhölzli. CH-8048 Zürich (21 February 2007; 10.30 a.m.)
- Concentration of sludge: 30 mg/L suspended solids

The activated sludge was used without adaptation. Prior to the test the sludge was washed twice with tap water.
Duration of test (contact time):
28 d
Initial conc.:
20 mg/L
Based on:
TOC
Parameter followed for biodegradation estimation:
CO2 evolution
Details on study design:
TEST CONDITIONS
- Medium: Aerobic mineral salts medium prepared with deionised water (conductivity : <1.5 µS/cm; DOC: <0.3 mg/L)
- Additional substrate: no
- Test temperature: 22 ±0.5°C
- Suspended solids concentration: 30 mg/L
- Continuous darkness: yes

TEST SYSTEM
- Culturing apparatus: 2500 mL closed glass bottle containing a total volume of test solution of 2000 ml; aerated with CO2-free air and fitted to gas-absorption bottles containing 125 ml of 0.13 M KOH
- Number of culture flasks/concentration: 2

CONTROL AND BLANK SYSTEM
- Inoculum blank: containing inoculum and test medium (two replicates)
- Abiotic sterile control: no
- Toxicity control: no
- Procedure control: containing inoculum, test medium and sodium benzoate es ready biodegradable reference compound (one replicate)

Reference substance:
benzoic acid, sodium salt
Parameter:
% degradation (CO2 evolution)
Value:
47
Sampling time:
10 d
Parameter:
% degradation (CO2 evolution)
Value:
79.4
Sampling time:
28 d
Results with reference substance:
The positive control, sodium benzoate. reached 96% biodegradation after 14 days.
Validity criteria fulfilled:
yes
Interpretation of results:
readily biodegradable, but failing 10-day window
Conclusions:
ISOTRIDECYL METHACRYLATE did not reach the pass level of 60 % for ready biodegradability in the CO2 Evolution Test within the 10 -d window and. therefore, cannot be termed as readily biodegradable. However, the pass level of 60 % was reached after 28 days of incubation .
Executive summary:

The biodegradability ot Isotridecyl methacrylate exposed to microorganisms derived from the activated sludge of a municipal sewage treatment plant was investigated under aerobic staitc exposure conditions.

The biodegradabitity based on CO2 evolution of Isotridecyl methacrylate was calculaled to be 79 % of the theoretical value (ThCO2) atter an incubation time of 28 days. The biodegradation of Isotridecyl methacrylate reached 47 % at the end of the 10-d window. Significant biodegradation of the test substance was observed after a lag phase of about 4 days.

The positive control, sodium benzoate, reached 96 % biodegradation after 14 days, thus confirming suitability of inoculum and test conditions.

The calculated biodegradation based on DOC measurement reached 93 % for Isotridecyl methacrylate and 98 % for sodium benzoate.

Isotridecyl methacrylate did not reach the pass level of 60 % for ready biodegradability in the CO2 Evolution Test within the 10 -d window and. therefore, cannot be termed as readily biodegradable. However, the pass level of 60 % was reached after 28 days of incubation.

In accordance with the OECD "Guidelines for the Testing of Chemicals, Revised Introduction To The OECD Guidelines For Testing Of Chemicals, Section 3 Part I: Principles And Strategies Related To The Testing Of Degradation Of Organic Chemicals" the 10 day window does not apply to UVCB substances ("it is anticipated that a sequential biodegradation of the individual structures is taking place,

then the 10-day window should not be applied to interpret the results of the test").

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Description of key information

readily biodegradable but failing 10-day window (47% at the end of 10 day window; 79% after 28 d)

Key value for chemical safety assessment

Biodegradation in water:
readily biodegradable but failing 10-day window

Additional information

The biodegradability ot Isotridecyl methacrylate exposed to micro-organisms derived from the activated sludge of a municipal sewage treatment plant was investigated under aerobic static exposure conditions according to OECD Guideline 301B.

The biodegradabitity based on CO2 evolution of Isotridecyl methacrylate was calculaled to be 79 % of the theoretical value (ThCO2) atter an incubation time of 28 days. The biodegradation of Isotridecyl methacrylate reached 47 % at the end of the 10-d window. Significant biodegradation of the test substance was observed after a lag phase of about 4 days.

The positive control, sodium benzoate, reached 96 % biodegradation after 14 days, thus confirming suitability of inoculum and test conditions.

The calculated biodegradation based on DOC measurement reached 93 % for Isotridecyl methacrylate and 98 % for sodium benzoate.

Isotridecyl methacrylate did not reach the pass level of 60 % for ready biodegradability in the CO2 Evolution Test within the 10 -d window and. therefore, cannot be termed as readily biodegradable. However, the pass level of 60 % was reached after 28 days of incubation.

In accordance with the OECD "Guidelines for the Testing of Chemicals, Revised Introduction To The OECD Guidelines For Testing Of Chemicals, Section 3 Part I: Principles And Strategies Related To The Testing Of Degradation Of Organic Chemicals" the 10 day window does not apply to UVCB substances ("it is anticipated that a sequential biodegradation of the individual structures is taking place,

then the 10-day window should not be applied to interpret the results of the test").

[Type of water: freshwater]