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Application for the Reassessment of a Hazardous Substance under ...

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5.18 The Task Specific Factors (TSF), suggested in <strong>the</strong> UK CRD model, are not thatappropriate <strong>for</strong> out-door activities as <strong>the</strong>y were designed <strong>for</strong> <strong>the</strong> first tier <strong>of</strong> anexposure assessment relating to harvesting ornamentals and to <strong>the</strong> re-entry <strong>of</strong>greenhouses approximately 8-16 hours after treatment, but no better model isavailable. The indicative TSFs were 0.1 <strong>for</strong> cutting ornamentals; 0.01 <strong>for</strong> sorting& bundling ornamentals; 0.03 <strong>for</strong> re-entering greenhouses after low-volume-mistapplication; and, 0.15 <strong>for</strong> re-entering greenhouses after ro<strong>of</strong> fogger application.As <strong>the</strong> tasks in <strong>the</strong>se Scenarios are outside tending Berries/Fruit andVegetables/Cereals <strong>the</strong> lowest TSF 0.01 is proposed (assuming that inhalationexposure would be similar, or less, than that while bundling ornamentals indoors).5.19 Using <strong>the</strong> data from Casida et al. (1962), 20 minutes after application to <strong>the</strong> leafsurfaces <strong>of</strong> maize, cotton and peas about 50% was volatilised, while 5% remainson <strong>the</strong> leaf surfaces and 45% absorbed by <strong>the</strong> plant (in APVMA, 2008b). It isassumed <strong>the</strong>re<strong>for</strong>e that only 50% <strong>of</strong> <strong>the</strong> application rate is available <strong>for</strong> possibleinhalation (See Appendix 5).Dichlorvos reassessment – application Page 312 <strong>of</strong> 436

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