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Environmental fate & pathways

Biodegradation in water: screening tests

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Description of key information

not ready biodegradable

Key value for chemical safety assessment

Biodegradation in water:
under test conditions no biodegradation observed

Additional information

In the Klimisch 1 study from Grade (2001) the ready biodegradability of CA 3105 A (purity 93.9%) was determined according to OECD 301 B (CO2 evolution test). A deviation (one instead of 2 CO2 scrubbers) was addressed already in the report and was considered minor and had no impact on the outcome of the study.

The study was performed using sludge from the sewage treatment plant CH-4153 Reinach.

Following flasks (2 L brown glass, filled with 1.5 L test solution) were set up:

Flasks 1 and 2: test medium and inoculum (inoculum blank)

Flasks 3 and 4: reference substance and inoculum (procedure control)

Flasks 5 and 6: test item and inoculum

Flask 7:              reference item, test item and inoculum (control of toxicity of test item)

Flask 8:              distilled water.

The final test item concentration was about 50 mg/L. 

Aeration was performed with 25 m/L CO2-free air. The CO2-scrubbers (250 mL glass vessels filled with 0.05N NaOH) were sampled after 3, 6, 8, 10, 13, 16, 20, 24, 28, 29 days. The last measurement was performed after acidification of the test medium with 1 mL concentrated hydrochloric acid. The test was performed at 22 +/-2°C. The CO2 evolution was determined as inorganic CO2 with a carbon analyser (Shimadzu TOC-5050 A)

After 29 days, the cumulative CO2 evolution in the reference substance flasks (sodium benzoate, 15 mg DOC/L) correspond to a degradation of 79% indicating correct performance of the test procedures. The cumulative CO2 evolution in the reference substance plus test item (toxic control) flasks correspond to a degradation of 85% of the positive control substance sodium benzoate, indicating that the test item had no toxic effect on the organisms at the tested concentration.

After 29 days, the cumulative CO2 evolution in the test item flasks correspond to a degradation of -1%. Negative degradation values were the consequence of the comparison of values obtained in the blanks and the low values obtained in the presence of the test item.

 

It can be concluded that the test item was not readily biodegradable under test conditions.