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User Guide to Thresholds and Classification - Environmental ...

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373<strong>User</strong> <strong>Guide</strong> for <strong>Thresholds</strong> <strong>and</strong> <strong>Classification</strong>sAppendix 19F: Globally Harmonized System of <strong>Classification</strong><strong>and</strong> Labelling of Chemicals – guidance on the bioconcentrationfac<strong>to</strong>r19F.1 IntroductionThis appendix is largely the same as the Globally Harmonized System of <strong>Classification</strong> <strong>and</strong> Labelling ofChemicals, Annex 9.(United Nations, 2007) Section 19F.2 reflects Appendix III <strong>and</strong> section 19F.3 reflectsAppendix IV of Annex 9.19F.2 Basic principles of the experimental <strong>and</strong> estimation methods fordetermination of bioconcentration fac<strong>to</strong>r <strong>and</strong> n-octanol-water partitioncoefficient of organic substancesBioconcentration fac<strong>to</strong>rDefinitionThe bioconcentration fac<strong>to</strong>r (BCF) is defined as the ratio between the concentration of the chemical in biota<strong>and</strong> the concentration in the surrounding medium, here water, at steady state. The BCF can be measuredexperimentally directly under steady-state conditions or calculated by the ratio of the first-order uptake <strong>and</strong>elimination rate constants, a method that does not require equilibrium conditions.Appropriate methods for experimental determination of bioconcentration fac<strong>to</strong>rDifferent test guidelines for the experimental determination of bioconcentration in fish have beendocumented <strong>and</strong> adopted; the most generally applied being the Organisation for Economic Cooperation <strong>and</strong>Development (OECD) test guideline (OECD 305, 1996) <strong>and</strong> the ASTM st<strong>and</strong>ard guide (ASTM E 1022-94)(see Appendix 19A for sources of these guidelines). OECD 305 (1996) was revised <strong>and</strong> replaced theprevious version OECD 305A-E, (1981). Although flow-through test regimes are preferred (OECD 305,1996), semistatic regimes are allowed (ASTM E 1022-94), provided that the validity criteria on mortality <strong>and</strong>maintenance of test conditions are fulfilled. For lipophilic substances (log KOW > 3, where KOW means then-octanol-water partition coefficient), flow-through methods are preferred.The principles of the OECD 305 <strong>and</strong> the ASTM guidelines are similar, but the experimental conditionsdescribed are different, especially concerning:the method of test water supply (static, semi-static or flow through);the requirement for carrying out a depuration study;the mathematical method for calculating BCF;sampling frequency: number of measurements in water <strong>and</strong> number of samples of fish;requirement for measuring the lipid content of the fish; <strong>and</strong>the minimum duration of the uptake phase.January 2012 EPA0109

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