OECD Guidelines for the Testing of Chemicals, Section 3

Environmental fate and behaviour

English
ISSN: 
2074-577x (online)
http://dx.doi.org/10.1787/2074577x
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The OECD Guidelines for the Testing of Chemicals is a collection of about 150 of the most relevant internationally agreed testing methods used by government, industry and independent laboratories to identify and characterise potential hazards of chemicals. They are a set of tools for professionals, used primarily in regulatory safety testing and subsequent chemical and chemical product notification, chemical registration and in chemical evaluation. They can also be used for the selection and ranking of candidate chemicals during the development of new chemicals and products and in toxicology research. This group of tests covers environmental fate and behaviour. In 2017, the section 3 “Degradation and Accumulation” was renamed to “ Environmental fate and behaviour”  to take into account Test Guidelines measuring endpoints such as dispersion, aggregation.

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Test No. 302B: Inherent Biodegradability: Zahn-Wellens/ EVPA Test

Test No. 302B: Inherent Biodegradability: Zahn-Wellens/ EVPA Test You or your institution have access to this content

English
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    http://oecd.metastore.ingenta.com/content/97302b1e.pdf
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Author(s):
OECD
17 July 1992
Pages:
8
ISBN:
9789264070387 (PDF)
http://dx.doi.org/10.1787/9789264070387-en

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This Test Guideline describes the Zahn-Wellens/EMPA Test. It is used to determine inherent biodegradability.

A mixture containing the non-volatile and water soluble test substance, mineral nutrients and a relatively large amount of activated sludge in aqueous medium is agitated and aerated at 20-25°C in the dark or in diffuse light, for up to 28 days. Blank controls, containing activated sludge and mineral nutrients but no test substance, are run in parallel. The functional capability of the activated sludge is tested using a reference compound (ethylene glycol, diethylene glycol, lauryl sulfonate or aniline). In a typical run 1 or 2 vessels for the test suspension and for the inoculum blank, 1 for procedure control are used. The biodegradation process is monitored by determination of DOC, Dissolved Organic Carbon, (or COD, Chemical Oxygen Demand) in filtered samples, taken at daily or other time intervals. It is mandatory to follow DOC in the test suspension and inoculum blanks in parallel. The ratio of eliminated DOC (or COD), corrected for the blank, after each time interval, to the initial DOC value is expressed as the percentage biodegradation at the sampling time. The percentage biodegradation is plotted against time to give the biodegradation curve. The test is considered valid if the procedural control shows the removal of the reference compound by at least 70% within 14d and if DOC (or COD) in the test suspension is removed relatively gradually over days or weeks, since this indicates biodegradation.

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