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2454 final report.pdf - Agra CEAS Consulting

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Evaluation of the Community Plant Health Regime: Final Report<br />

DG SANCO Evaluation Framework Contract Lot 3 (Food Chain)<br />

The reduction of active substances available for control measures may also lead to a situation<br />

where for a certain pest or even group of pests, only one family of products is likely to be<br />

available creating a risk of the development of pesticide resistance, as it becomes almost<br />

impossible to rotate the PPP used.<br />

For example, as illustrated in the National Audit Office (NAO, 2003) <strong>report</strong> on protecting<br />

England and Wales from plant pests and diseases, the main pesticides used to combat Thrips<br />

palmi, are no longer available because they are prohibited from use in the EU. The study<br />

concludes that any outbreak might therefore be more difficult to contain and eradicate in<br />

future. The <strong>report</strong> concludes that the relevant competent authorities need to work more closely<br />

together to co-ordinate the phasing out of key pesticides alongside the development and use of<br />

other means of control, such as pest-resistant crops. Similar recommendations were indicated<br />

by several respondents to the general survey and during the interviews.<br />

Another potential issue to consider is that the framework Directive on the sustainable use of<br />

PPP in principle prohibits aerial treatment 252 , and defines buffer zones around aquatic areas<br />

(rivers, lake, etc...) in which the use of PPPs may be forbidden. These two elements may<br />

create refuge zones for some HOs, and this could put at risk eradication measures in certain<br />

cases. In particular, aerial treatments are in some cases the only solution if particular action is<br />

required in forestry.<br />

An adverse effect of the increasing prohibitions on usage of PPPs in Europe, as mentioned by<br />

one interviewee representing farmers, is that the cultivation of some crops is moving to third<br />

countries, where less strict rules apply to the use of pesticides. The problem in this case is that<br />

some substances are detectable only for a limited period only after harvest (i.e. 15 days, but<br />

not one month); therefore when products on which such substances have been used are<br />

imported, the controls may fail to detect these substances.<br />

Biological control measures may be an alternative to the reduction and/or ban on use of PPPs,<br />

However such measures are by definition never fully and immediately effective, particularly<br />

to address quarantine pests. Also, the availability of these alternative methods at large<br />

commercial scale is rather limited at the moment.<br />

Due to the recent entry into force of the new PPP legislation, FCEC considers that it is<br />

premature to judge on the inconsistencies between PPP legislation and CPHR. The extent to<br />

which the possibility for derogation in case of minor crops and in case of serious danger for<br />

plant health will be used and granted in practice as well as the extent to which the PPPs for<br />

which derogation are requested are likely to be available to farmers (there is the risk that PPP<br />

manufacturers will not be producing products that would not be authorised just in case there<br />

may be a need for them) are not known at this stage.<br />

252 Aerial treatment is forbidden by the new Framework Directive 2009/128 (art.9 (1)) but case by case<br />

derogations can be granted by MS (art. 9 (2 and following)). For example in FR, aerial treatment is authorized in<br />

some cases, e.g. Bacillus thuringiensis against Thaumetopoea pityocampa in forests.<br />

Food Chain Evaluation Consortium 261

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