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hal.structure.identifierUnité de recherche Zoologie Forestière [URZF]
dc.contributor.authorROBINET, Christelle
hal.structure.identifierInstitut Sophia Agrobiotech [ISA]
dc.contributor.authorCASTAGNONE-SERENO, Philippe
hal.structure.identifierUniversidade de Évora
dc.contributor.authorMOTA, Manuel
hal.structure.identifierUnité de recherche Zoologie Forestière [URZF]
dc.contributor.authorROUX, Géraldine
hal.structure.identifierAgence nationale de sécurité sanitaire de l'alimentation, de l'environnement et du travail [ANSES]
dc.contributor.authorSARNIGUET, Corinne
hal.structure.identifierAgence nationale de sécurité sanitaire de l'alimentation, de l'environnement et du travail [ANSES]
dc.contributor.authorTASSUS, Xavier
hal.structure.identifierBiodiversité, Gènes & Communautés [BioGeCo]
dc.contributor.authorJACTEL, Herve
dc.date.issued2016
dc.date.conference2016-12-12
dc.description.abstractEnFollowing the detection of a pine wood nematode outbreak, Implementing Decision 2012/535/EU imposes eradication measures for at least four years, mainly consisting of the establishment of: i) clear-cuts with a radius of 500 m around the infested plants and ii) intensive surveillance within a radius varying from 6 to 20 km around the infested zone. To estimate the effectiveness of these measures, a simulation model was developed and calibrated using experimental data specifying the dispersal capabilities of the insect vector Monochamus galloprovincialis. These data were obtained in the laboratory (on a flight mill) and in natura (mark-and-recapture experiments) in the context of the Landes de Gascogne forest (David, 2014 and David et al., 2014), one of the forest areas most exposed to the risk of introduction of the pine wood nematode in France. The simulations that were then carried out under different scenarios (preventive or curative) showed that the clear-cuts currently requested by European and French regulations would not be effective in a landscape configuration of continuous plantations of maritime pine. Indeed, with the recommended radius of 500 m, at best 11% of nematode transmissions by the insect vector would be avoided. Moreover, to obtain a pine wood nematode transmission rate lower than 0.1%, it would be necessary to implement clear-cuts with a radius of 15 - 38 km (Anses, 2015). These simulations, carried out in the context of a continuous forest, should however be supplemented by a scenario involving highly fragmented pine forests. In this regard, it would be interesting to include biological data from Spanish forest managers, as they are directly involved in implementing nematode eradication measures in this type of landscape. Alternative management measures to control the spread of the pine wood nematode were also assessed by the Working Group.
dc.language.isoen
dc.title.enModelling the dispersal of Monochamus galloprovincialis, the vector of the pine wood nematode, and assessing the effectiveness of clear-cutting measures
dc.typeCommunication dans un congrès
dc.subject.halSciences de l'environnement/Biodiversité et Ecologie
dc.subject.halSciences de l'environnement/Milieux et Changements globaux
bordeaux.conference.titleJoint EFSA/EPPO Workshop: Modelling in Plant Health
bordeaux.countryIT
bordeaux.conference.cityParme
bordeaux.peerReviewednon
hal.identifierhal-02740376
hal.version1
hal.invitedoui
hal.conference.organizerEuropean Food Safety Authority (EFSA). ITA.
hal.conference.end2016-12-14
hal.popularnon
hal.audienceInternationale
hal.origin.linkhttps://hal.archives-ouvertes.fr//hal-02740376v1
bordeaux.COinSctx_ver=Z39.88-2004&rft_val_fmt=info:ofi/fmt:kev:mtx:journal&rft.date=2016&rft.au=ROBINET,%20Christelle&CASTAGNONE-SERENO,%20Philippe&MOTA,%20Manuel&ROUX,%20G%C3%A9raldine&SARNIGUET,%20Corinne&rft.genre=unknown


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