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User Guide to Thresholds and Classification - Environmental ...

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323<strong>User</strong> <strong>Guide</strong> for <strong>Thresholds</strong> <strong>and</strong> <strong>Classification</strong>sTime windowThe harmonised criteria include a general requirement for all of the ready biodegradability tests onachievement of the pass level within 10 days. This is not in line with the OECD Test <strong>Guide</strong>line 301 in whichthe 10-days time window applies <strong>to</strong> the OECD ready biodegradability tests except <strong>to</strong> the MITI I test (OECDTest <strong>Guide</strong>line 301C). In the Closed Bottle test (OECD Test <strong>Guide</strong>line 301D), a 14-days window may beused instead when measurements have not been made after 10 days. Moreover, often only limitedinformation is available in references of biodegradation tests. Thus, as a pragmatic approach the percentageof degradation reached after 28 days may be used directly for assessment of ready biodegradability when noinformation on the 10-days time window is available. This should, however, only be accepted for existing testdata <strong>and</strong> data from tests where the 10-days window does not apply.(Note that the HSNO Act regulations have no requirement for a pass within a specified window.)BOD 5 /CODInformation on the five-day biochemical oxygen dem<strong>and</strong> (BOD 5 ) will be used for classification purposes onlywhen no other measured degradability data are available. Thus, priority is given <strong>to</strong> data from readybiodegradability tests <strong>and</strong> from simulation studies regarding degradability in the aquatic environment. TheBOD 5 test is a traditional biodegradation test that is now replaced by the ready biodegradability tests.Therefore, this test should not be performed <strong>to</strong>day for assessment of the ready biodegradability ofsubstances. Older test data may, however, be used when no other degradability data are available. Forsubstances where the chemical structure is known, the theoretical oxygen dem<strong>and</strong> (ThOD) can becalculated <strong>and</strong> this value should be used instead of the chemical oxygen dem<strong>and</strong> (COD).Other convincing scientific evidenceRapid degradation in the aquatic environment may be demonstrated by other data than referred <strong>to</strong> in HSNOAct criteria (a) <strong>and</strong> (b). These may be data on biotic <strong>and</strong>/or abiotic degradation. Data on primary degradationcan only be used where it is demonstrated that the degradation products shall not be classified as hazardous<strong>to</strong> the aquatic environment, that is, that they do not fulfil the classification criteria.The fulfilment of HSNO Act criterion (c), requires that the substance is degraded in the aquatic environment<strong>to</strong> a level of > 70% within a 28-day period. If first-order kinetics are assumed, which is reasonable at the lowsubstance concentrations prevailing in most aquatic environments, the degradation rate will be relativelyconstant for the 28-day period. Thus, the degradation requirement will be fulfilled with an averagedegradation rate constant, k > -(ln 0.3 - ln 1)/28 = 0.043 day-1. This corresponds <strong>to</strong> a degradation half-life,t½ < ln 2/0.043 = 16 days.Moreover, as degradation processes are temperature dependent, this parameter should also be taken in<strong>to</strong>account when assessing degradation in the environment. Data from studies employing environmentallyrealistic temperatures should be used for the evaluation. When data from studies performed at differenttemperatures need <strong>to</strong> be compared, the traditional Q10 approach could be used, that is, that the degradationrate is halved when the temperature decreases by 10°C.January 2012 EPA0109

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