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User Guide to Thresholds and Classification - Environmental ...

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362<strong>User</strong> <strong>Guide</strong> for <strong>Thresholds</strong> <strong>and</strong> <strong>Classification</strong>sThe OPPTS 835.5270 screening test concerns indirect pho<strong>to</strong>lysis of chemicals in waters that contain humicsubstances. The principle of the test is that in natural waters exposed <strong>to</strong> natural sunlight a measuredpho<strong>to</strong>transformation rate will include both direct <strong>and</strong> indirect pho<strong>to</strong>transformation, whereas only directpho<strong>to</strong>transformation will take place in pure water. Therefore, the difference between the directpho<strong>to</strong>degradation rate in pure water <strong>and</strong> the <strong>to</strong>tal pho<strong>to</strong>degradation in natural water is the sum of indirectpho<strong>to</strong>lysis <strong>and</strong> secondary pho<strong>to</strong>degradation. In the practical application of the test, commercial humicsubstances are used <strong>to</strong> make up a synthetic humic water, which mimics a natural water. It should be notedthat the indirect pho<strong>to</strong>transformation rate determined is only valid for the season <strong>and</strong> latitude for which it isdetermined <strong>and</strong> it is not possible <strong>to</strong> transfer the results <strong>to</strong> other latitudes <strong>and</strong> seasons.Biotic degradabilityOnly a brief overview of the test methods is given below. For more information, consult the comprehensivepaper Detailed Review Paper on Biodegradability Testing (OECD, 1995).Ready biodegradabilitySt<strong>and</strong>ard tests for determination of the ready biodegradability of organic substances aredeveloped by a number of organisations including OECD (OECD Test <strong>Guide</strong>lines 301A-F), European Union(EU) (C.4 tests), OPPTS (835.3110) <strong>and</strong> International Organization for St<strong>and</strong>ardization (ISO) (9408, 9439,10707).The ready biodegradability tests are stringent tests, which provide limited opportunity for biodegradation <strong>and</strong>acclimatisation <strong>to</strong> occur. The basic test conditions ensuring these specifications are:high concentration of test substance (2–100 mg/L);the test substance is the sole carbon <strong>and</strong> energy source;low <strong>to</strong> medium concentration of inoculum (104–108 cells/mL);no pre-adaptation of inoculum is allowed;28-day test period with a 10-days time window (except for the MITI I method (OECD Test <strong>Guide</strong>line301C)) for degradation <strong>to</strong> take place;test temperature < 25°C; <strong>and</strong>pass levels of 70% (DOC removal) or 60% (O2 dem<strong>and</strong> or CO2 evolution) demonstrating completemineralisation (as the remaining carbon of the test substance is assumed <strong>to</strong> be built in<strong>to</strong> the growingbiomass).It is assumed that a positive result in one of the ready biodegradability tests demonstrates that the substancewill degrade rapidly in the environment (OECD 301 Test <strong>Guide</strong>lines).Also the traditional BOD5 tests (for example, the EU C.5 test) may demonstrate whether a substance isreadily biodegradable. In this test, the relative biochemical oxygen dem<strong>and</strong> in a period of 5 days is compared<strong>to</strong> the theoretical oxygen dem<strong>and</strong> (ThOD) or, when this is not available, the chemical oxygen dem<strong>and</strong>(COD). The test is completed within 5 days <strong>and</strong> consequently, the pass level defined in the proposed hazardclassification criteria at 50% is lower than in the ready biodegradability tests.January 2012 EPA0109

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