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414User Guide for Thresholds and ClassificationsFigure 21.2: Terrestrial vertebrate hazard classification of mixturesStep 1 (9.3A)% x M ≥ 25%YesClassify as 9.3ANoStep 2 ((9.3A)% x M x 10) + (9.3B)% ) ≥ 25%YesClassify as 9.3BNoStep 3 ((9.3A)% x M x 100) + (%9.3B x 10) + (9.3C)%) ≥ 25%YesClassify as 9.3CNoNo terrestrial vertebrate classification ifsubstance is a biocide. See chapter 23.ReferencesEC 2002. Guidance Document on Risk Assessment for Birds and Mammals under Council Directive91/414/EEC, SANCO/4145/2000 – final. European Commission.http://ec.europa.eu/food/plant/protection/evaluation/guidance/wrkdoc19_en.pdfJanuary 2012 EPA0109
415User Guide for Thresholds and ClassificationsAppendix 21A: Classification notes for avian studiesAppendix contents21A.1 Avian acute oral toxicityRegurgitation can substantially reduce the dose absorbed by birds in acute oral toxicity tests. Therefore,evaluation of avian acute oral tests should include whether regurgitation or emesis has occurred. If so, it maybe appropriate to repeat the study using birds that do not regurgitate, in particular if a high-risk use such asseed treatment is being assessed.For example, if regurgitation is observed in an acute oral toxicity test at 500, 1,000, and 2,000 mg activesubstance/kg body weight (bw), but not at 200 mg a.s./kg bw, and if there is no mortality at 200 mg a.s./kgbw, then the conclusion is valid that the median lethal dose (LD 50 ) is > 200 mg/kg bw. Although this figurecannot be used for classification purposes it may be used in the initial risk assessment. If this assessmentraises concern, then either an acute or a dietary study would be requested using a bird species that does notregurgitate. If the initial assessment does not raise concern, no further data will be requested. Sometimesregurgitation may occur in all doses while mortality occurs only in the top doses, that is, regurgitation is notsufficient to protect birds. Also, in this situation, a further study with a non-regurgitating species would berequired.21A.2 Avian short-term dietary toxicityWhen the test diet has been analysed the results should be reported in the monograph. According to OECDguideline 205, a deviation up to 20% between measured feed concentrations and nominal values isconsidered acceptable. In the case of larger deviations, toxicity figures should be recalculated using effectiveconcentrations.21A.3 Avian reproductionIt should be noted that low acute and dietary avian toxicity are not sufficient to indicate a low reproductivetoxicity. A reproductive toxicity study should always be conducted unless it can be demonstrated that theexposure of birds (adults and young) does not occur during the breeding season. When all relevant speciesare considered, the breeding season could be rather long and even short exposure periods may give rise toconcern about potential reproductive effects. Thus, in the case of foliar applications during the breedingseason, for example, the test should normally be required even if only one treatment per season is intended.Reproductive data are always required for substances that are generally persistent or have a bioaccumulationpotential.January 2012 EPA0109
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