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6 TESTING STRATEGIES<br />

6.1 INTRODUCTION<br />

TESTING STRATEGIES<br />

In this chapter testing strategies <strong>for</strong> PEC <strong>and</strong> PNEC are given that are in principle to be followed<br />

when the conclusion of the risk characterisation phase is that there is concern <strong>and</strong> there is a need<br />

to ask <strong>for</strong> further in<strong>for</strong>mation to refine the risk assessment. As has been mentioned in the<br />

previous chapter a decision has to be made as to whether PEC, PNEC or both need to be revised.<br />

This decision by the competent authority must be transparent <strong>and</strong> justified <strong>and</strong> should be based<br />

on the principles of lowest cost <strong>and</strong> ef<strong>for</strong>t, highest gain of in<strong>for</strong>mation <strong>and</strong> the avoidance of<br />

unnecessary testing of animals.<br />

Separate from the testing strategies that need to be followed when risks are identified, the PBT<br />

assessment as described in Section 4.4 may identify the need <strong>for</strong> further in<strong>for</strong>mation to clarify<br />

the potential PBT (Persistent, Bioaccumulative, Toxic) or vPvB (very Persistent, very<br />

Bioaccumulative) properties of a substance. When such testing is requested, <strong>and</strong> the substance<br />

turns out not to fulfil the PBT or vPvB criteria, the test results should be used in the subsequent<br />

PEC/PNEC calculations.<br />

6.2 REFINEMENT OF PEC<br />

In order to refine the PEC, in addition to comprehensive in<strong>for</strong>mation on production <strong>and</strong><br />

application, additional tests may lead to a better quantification of the elimination processes of a<br />

substance in the individual environmental compartments or in the sewage treatment plant. The<br />

exact degree of elimination may be determined by measurements in the influent <strong>and</strong> effluent of<br />

sewage treatment plants or by conducting appropriate tests on the degradation behaviour.<br />

The testing strategy <strong>for</strong> biocides can be found in the Technical Notes <strong>for</strong> Guidance <strong>for</strong><br />

Directive 98/8” (TNsG on Data Requirements, 2000, Chapter 3, Section 7.0.2, available on<br />

http://ecb.jrc.it/biocides/). This strategy could also be employed on substances, which potentially<br />

may meet the persistency criteria <strong>for</strong> PBTs. The kind of simulation test asked <strong>for</strong> should depend<br />

on the compartment of highest concern. If the sediment compartment turns out to be the<br />

compartment of highest concern, it could be decided to continue with a sediment simulation test<br />

depending on the physico-chemical properties of the substance as defined in the biocides testing<br />

strategy.<br />

Furthermore it should be noted that a <strong>guidance</strong> document on how to assess <strong>and</strong> test relevant<br />

metabolites <strong>and</strong> trans<strong>for</strong>mation products is under preparation <strong>for</strong> plant protection products under<br />

Directive 91/414. This document could be modified later <strong>for</strong> use <strong>for</strong> biocides, <strong>and</strong> where<br />

appropriate <strong>for</strong> new <strong>and</strong> existing substances.<br />

Guidance in relation to further degradation studies when refining the PEC <strong>for</strong> STP or one or<br />

more of the environmental compartments is given below. In general simulation tests should be<br />

considered based on the likelihood <strong>for</strong> such test data to actually refine the PEC(s) in a way that<br />

may influence the ultimate result of the risk assessment (see Section 2.3.1, sensitivity analysis).<br />

Similarly, the experimental determination of the BCF can be requested in order to refine the<br />

PECoral <strong>for</strong> secondary poisoning (see Section 3.8).<br />

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