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User Guide to Thresholds and Classification - Environmental ...

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283<strong>User</strong> <strong>Guide</strong> for <strong>Thresholds</strong> <strong>and</strong> <strong>Classification</strong>sbased on reduction in biomass is available, or it is not indicated which EC50 is reported, these values maybe used.Ideally, data on all three st<strong>and</strong>ard taxa will be available for classification purposes, with classification basedon the most sensitive test result.19.1.2. Chronic aquatic <strong>to</strong>xicityChronic effects usually include a range of sublethal endpoints <strong>and</strong> are generally expressed in terms of a noobservable effect concentration (NOEC) or an equivalent ECx. Endpoints typically include survival, growth,<strong>and</strong>/or reproduction. Exposure durations vary widely, depending on the endpoint being assessed <strong>and</strong> thetest species being used.Chronic <strong>to</strong>xicity data are generally less available than are acute data, so for classification purposes thepotential for chronic or long-term <strong>to</strong>xicity is often assessed through a combination of acute <strong>to</strong>xicity, lack ofrapid degradability, <strong>and</strong> potential or actual bioaccumulation. Where chronic data do exist, these are takenin<strong>to</strong> account in assigning a classification <strong>to</strong> a substance.Use of chronic data <strong>to</strong> reduce a classificationWhere a substance is acutely <strong>to</strong>xic, not rapidly degradable, <strong>and</strong>/or has potential <strong>to</strong> bioconcentrate, chronictest data > 1 mg/L can be used <strong>to</strong> ‗de-classify‘ or reduce the classification of a substance from 9.1B or 9.1C<strong>to</strong> the less restrictive classification of 9.1D. Several aspects of the chronic data must be considered before aclassification can be reduced.The general approach is <strong>to</strong> demonstrate the chronic NOEC > 1 mg/L for the most sensitive species identifiedby the acute <strong>to</strong>xicity data. For example, if the classification has been applied on the basis of acute <strong>to</strong>xicity <strong>to</strong>fish, it would generally not be possible <strong>to</strong> reduce the classification based on a NOEC for an aquaticinvertebrate. If the classification has resulted from acute <strong>to</strong>xicity <strong>to</strong> more than one taxa, a NOEC > 1 mg/L foreach would be needed <strong>to</strong> reduce the classification.Tests with algae <strong>and</strong> Lemna cannot be used <strong>to</strong> reduce the classification of a substance because the:duration of the studies is not long term;acute <strong>to</strong> chronic ratio is generally narrow; <strong>and</strong>endpoints are more consistent with those for other organisms.Combined acute <strong>and</strong> chronic classificationsWhile the current HSNO Act classification system will continue <strong>to</strong> rely on the use of acute <strong>to</strong>xicity data incombination with a lack of rapid degradation <strong>and</strong>/or a potential <strong>to</strong> bioaccumulate as the basis for aquatichazard classification, actual chronic <strong>to</strong>xicity data form a better basis for classification where these data areavailable. The OECD is developing a chronic aquatic hazard classification system based on chronic aquatictest data. It is anticipated that under the United Nations Globally Harmonized System of <strong>Classification</strong> <strong>and</strong>Labelling of Chemicals (GHS) (United Nations, 2007) the available chronic <strong>to</strong>xicity data would be used <strong>to</strong>assign a chronic hazard classification in preference <strong>to</strong> that derived from acute <strong>to</strong>xicity in combination with aJanuary 2012 EPA0109

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