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Commission Regulation (EU) No 544/2011 of 10 June 2011 implementing Regulation (EC) No 1107/2009 of the European Parliament and of the Council as regards the data requirements for active substances (Text with EEA relevance) (repealed)
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The test shall provide sufficient data to evaluate the mobility and leaching potential of the active substance and if possible of relevant metabolites, degradation and reaction products.
Studies in four soils must be carried out where in the adsorption and desorption studies provided for under point 7.1.2 it is not possible to obtain reliable adsorption coefficient values.
SETAC — Procedures for assessing the environmental fate and ecotoxicity of pesticides.
The test shall provide sufficient data to estimate the mobility and leaching potential of relevant metabolites, degradation and reaction products.
The studies must be performed except:
where the nature and manner of use of preparations containing the active substance, preclude soil contamination such as uses on stored products or wound healing treatments for trees, or
where a separate study for the metabolite, degradation or reaction product in accordance with point 7.1.2 or point 7.1.3.1 was performed.
The period(s) of ageing shall be determined from inspection of the degradation patterns of active substance and metabolites to ensure that a relevant spectrum of metabolites is present at the time of leaching.
SETAC — Procedures for assessing the environmental fate and ecotoxicity of pesticides.
The test shall provide data on:
the mobility in soil,
the potential for leaching to ground water,
the potential distribution in soil.
Expert judgement will be necessary to decide whether lysimeter studies or field leaching studies shall be carried out, taking into account the results of degradation and other mobility studies and the predicted environmental concentrations in groundwater (PECGW), calculated in accordance with Section 9 of the Annex to Regulation (EU) No 545/2011. The type and conditions of the study to be conducted shall be discussed with the competent authorities.
Great care is necessary in design of both experimental installations and individual studies, to ensure that results obtained can be used for assessment purposes. Studies shall cover the realistic worst case situation, taking into account the soil type, climatic conditions, the application rate and the frequency and period of application.
Water percolating from soil columns must be analysed at suitable intervals, while residues in plant material must be determined at harvest. Residues in the soil profile in at least five layers must be determined on termination of experimental work. Intermediate sampling must be avoided, since removal of plants (except for harvesting in accordance with normal agricultural practice) and soil cross influences the leaching process.
Precipitation, soil and air temperatures have to be recorded at regular intervals (at least on a weekly base).
The minimal depth of the lysimeters shall be 100 cm; their maximal depth shall be 130 cm. The soil monolith must be undisturbed. Soil temperatures must be similar to those pertaining in the field. Where necessary, supplementary irrigation must be provided to ensure optimal plant growth and to ensure that the quantity of infiltration water is similar to that in the regions for which authorisation is sought. When during the study the soil has to be disturbed for agricultural reasons it must not be disturbed deeper than 25 cm.
Information on the groundwater table in the experimental fields must be submitted. If soil cracking is observed during the study this must be fully described.
Great attention shall be given to the number and the location of water collection devices. The placement of these devices in the soil shall not result in preferential flow paths.
SETAC — Procedures for assessing the environmental fate and ecotoxicity of pesticides.
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