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User Guide to Thresholds and Classification - Environmental ...

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243<strong>User</strong> <strong>Guide</strong> for <strong>Thresholds</strong> <strong>and</strong> <strong>Classification</strong>s<strong>to</strong>xicokinetic differences are so marked that it is certain the hazardous property will not be expressed inhumans, then a substance that produces an adverse effect on reproduction in experimental animals shouldnot be classified.Studies involving routes of administration such as intravenous or intraperi<strong>to</strong>neal injection, which may result inexposure of the reproductive organs <strong>to</strong> unrealistically high levels of the test substance or elicit local damage<strong>to</strong> the reproductive organs (for example, by irritation), must be interpreted with extreme caution <strong>and</strong> on theirown would not normally be the basis for classification.There is general agreement about the concept of a limit dose, above which the production of an adverseeffect may be considered <strong>to</strong> be outside the criteria that lead <strong>to</strong> classification. Some Test <strong>Guide</strong>lines specify alimit dose; other Test <strong>Guide</strong>lines qualify the limit dose with a statement that higher doses may be necessaryif expected human exposure is sufficiently high that an adequate margin of exposure would not be achieved.Also, due <strong>to</strong> species differences in <strong>to</strong>xicokinetics, establishing a specific limit dose may not be adequate forsituations where humans are more sensitive than the animal model.In principle, adverse effects on reproduction seen only at very high dose levels in animal studies (forexample, doses that induce prostration, severe inappetence, or excessive mortality) would not normally lead<strong>to</strong> classification, unless other information were available (for example, <strong>to</strong>xicokinetic information, indicatingthat humans may be more susceptible than animals) <strong>to</strong> suggest that classification is appropriate. See alsosection 16.2.4.However, specification of the actual ‗limit dose‘ will depend on the test method that has been used <strong>to</strong> providethe test results (for example, in OECD Test <strong>Guide</strong>line 408 for repeated dose <strong>to</strong>xicity studies by the oralroute, an upper dose of 1,000 milligrams per kilogram unless the expected human response indicates theneed for a higher dose level, has been recommended as a limit dose).16.3. <strong>Classification</strong> of mixtures16.3.1. <strong>Classification</strong> of mixtures when data are available for the complete mixture<strong>Classification</strong> of mixtures is based on the available test data of the individual constituents of the mixtureusing cut-off values or concentration limits for the components of the mixture. The classification may bemodified on a case-by case basis based on the available test data for the mixture as a whole. In such cases,the test results for the mixture as a whole must be shown <strong>to</strong> be conclusive, taking in<strong>to</strong> account dose <strong>and</strong>other fac<strong>to</strong>rs such as duration, observations, <strong>and</strong> analysis (for example, statistical analysis <strong>and</strong> testsensitivity) of reproduction test systems.16.3.2. <strong>Classification</strong> of mixtures when data are not available for the complete mixture:bridging principlesWhere the mixture itself has not been tested <strong>to</strong> determine its reproductive or developmental <strong>to</strong>xicity, butthere are sufficient data on the individual ingredients <strong>and</strong> similar tested mixtures <strong>to</strong> adequately characterisethe hazards of the mixture, these data are used in accordance with the following agreed bridging rules. ThisJanuary 2012 EPA0109

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