An extended summary of the study Menezes Oliveiras et al., 2013 and a certified translation of Strumpf et al.. Further data to refine the risk to soil macro‐organisms (relevant for all the representative uses evaluated, submission date proposed by the applicants: unknown; see Section 5). Performance & security by Cloudflare, Please complete the security check to access. There are many formulations of copper products on the market, differing widely in the amount of copper, active ingredients, rate of application, and other factors. In accordance with Article 13 of the Regulation, unless formally informed by the European Commission that a conclusion is not necessary, EFSA is required to adopt a conclusion on whether the active substance can be expected to meet the approval criteria provided for in Article 4 of Regulation (EC) No 1107/2009 within 5 months from the end of the period provided for the submission of written comments, subject to an extension of an additional 3 months where additional information is required to be submitted by the applicants in accordance with Article 13(3). SANCO/10329/2002‐rev. A low risk was concluded for secondary poisoning and from consumption of contaminated water. 2002, 41, 2341. Most of the published findings date back to the 1970s and 1980s. omnivorous and frugivorous birds and large herbivorous and frugivorous mammals (data gap). When N a O H solution is added a bluish precipitate of copper (II) hydroxide is formed. Considering the major data gaps identified for grapes, tomatoes, cucurbits with edible peel and cucurbits with inedible peel, the consumer risk assessment resulting from the representative uses could not be finalised. The resulting weak bonding between the sheets accounts for the perfect (100) cleavage and the typical platy habit of botallackite (Figure 2). Upon foliar application, transportation and distribution of copper in plants are limited. Occurrence. 1997, 75 (Suppl. (relevant for all the representative uses evaluated, submission date proposed by the applicants: unknown; see Section, ILV for the residue method for drinking water (relevant for all the representative uses evaluated, submission date proposed by the applicants: unknown; see Section, Toxicological information on the stabilisers used in the technical concentrates by some manufacturers of copper hydroxide, copper oxychloride, tribasic copper sulfate and copper I oxide, relevant for all representative uses evaluated; submission date proposed by the applicants: unknown; see Section, Full residue data sets supporting the northern and southern outdoor GAPs with post‐flowering applications on grapes (relevant for the representative uses on grapes; submission date proposed by the applicants: unknown; see Section, Residue data sets supporting the GAPs with preflowering applications on grapes (relevant for the representative uses on grapes; submission date proposed by the applicants: unknown; see Section, Full residue data sets supporting the outdoor (NEU and SEU) and indoor GAPs on tomatoes (relevant for the representative uses on tomatoes); submission date proposed by the applicants: unknown; see Section, Full residue data sets supporting the outdoor (NEU and SEU) and indoor GAPs on cucurbits with edible peel (relevant for the representative uses on cucumber, gherkins and courgettes); submission date proposed by the applicants: unknown; see Section, Full residue data sets supporting the northern and southern outdoor GAPs on cucurbits with inedible peel (relevant for the representative uses on melons, pumpkins and watermelons; submission date proposed by the applicants: unknown; see Section, Two additional residue trials supporting the indoor GAP on cucurbits with inedible peel (relevant for the representative uses on melons, pumpkins and watermelons; submission date proposed by the applicants: unknown; see Section, Applicants to submit information against the data requirement on residue levels in pollen and in bee products for human consumption resulting from residues taken up by honeybees from crops at blossom (submission date proposed by the applicants: unknown; see Section, Further information was not provided to update information describing the speciation of copper in natural water (relevant for all the representative uses evaluated, submission date proposed by the applicants: unknown; see Section, Further information was not provided in order to investigate if natural background levels of copper increased and consequently to assess the relevance of the median concentrations of copper in European stream sediment (relevant for all the representative uses evaluated, submission date proposed by the applicants: unknown; see Section, Further information to address the acute and long‐term risk to birds and mammals (relevant for all the representative uses evaluated, submission date proposed by applicants: unknown; see Section, Further information to address the risk to aquatic invertebrates and algae (relevant for the uses on grapes), fish and sediment dwellers (relevant for all the representative uses evaluated, submission date proposed by the applicants: unknown; see Section, Further data to address the chronic toxicity to honeybees (adult and larvae) (relevant for all the representative uses evaluated, submission date proposed by the applicants: unknown; see Section, A risk assessment for honeybees in line with EFSA (, Further information to address the risk to non‐target arthropods (relevant for the representative uses of Copper hydroxide (Funguran‐OH), copper oxychloride (Curenox 50) and tribasic copper sulfate (Cuproxat SC), submission date proposed by the applicants: unknown; see Section, Further data to refine the risk to earthworms (relevant for all the representative uses except the use on grapes up to an application of 3.75 kg/ha, submission date proposed by the applicants: unknown; see Section.

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