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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 />

Type of benefit<br />

environmental<br />

benefits<br />

* chinensis and glabripennis<br />

CPHR successful for<br />

avoiding:<br />

Introduction /<br />

establishment<br />

Containment / slowing<br />

spread<br />

Countries Plant<br />

Susceptible area (in number<br />

of plants/trees, ha)<br />

Belgium deciduous trees 350000 ha<br />

Czech Republic ornamental trees 627500 ha<br />

Italy deciduous trees public area, private gardens:<br />

No data available<br />

Lithuania Not specified No data available<br />

Netherlands deciduous trees, No data available<br />

in particular Acer<br />

spp.<br />

Germany deciduous trees, No data available<br />

Acer campestris,<br />

Salix caprea,<br />

Aesculus and<br />

Betula<br />

Source: compiled by FCEC based on specific cost survey results<br />

Anoplophora is a wood-boring pest which was imported from Asia into the EU. Host plants<br />

are various deciduous trees, such as Acer, Corylus, Prunus, Citrus, Malus, Populus and Salix.<br />

These trees are widely distributed in the EU. Adults lay their eggs in the bark and eggs hatch<br />

after about 10 days. Trees die or are weakened due to the high number of larval tunnels in the<br />

wood.<br />

Imports of host plants are important, especially in the Netherlands where 1.6-2 million Acer<br />

were imported per year during the period 2005 – 2007, with an estimated total value of these<br />

plants (wholesale price) of about € 3 – 6 million. Solid wood (including wood products, wood<br />

packaging material) is a recognized pathway for Anoplophora glabripennis. Infested wood,<br />

chipped into pieces larger than 1.5 cm can enable larvae of Anoplophora to survive.<br />

Anoplophora is mainly present in Italy, and it could easily establish in other southern MS with<br />

similar climatic conditions, though there is also evidence that it can establish in northern parts<br />

of the EU, such as the Netherlands. In Southern Europe, the impact of Anoplophora chinensis<br />

may be higher than that of Anoplophora glabripennis since the first one has a broader host<br />

range. However, the climate in Northern Europe is possibly more favourable to Anoplophora<br />

glabripennis and its impact may, therefore, be higher despite the wider host range of<br />

Anoplophora chinensis.<br />

Economic benefits<br />

In countries where the CPHR avoided the introduction of Anoplophora, costs for surveys,<br />

eradication and replanting were spared. These can be high in case of infestation, as illustrated<br />

with the case of the infested area in Lombardy-Italy, where € 1.2 million has been spent from<br />

2004 to 2007 and € 10 million for the period 2008 – 2010.<br />

Moreover, it avoided crop losses and losses of export markets for tree nurseries and fruit<br />

orchards (Citrus, Malus, Pyrus) due to die back or weakening of trees as well as the negative<br />

impact on consumer demand. Large outbreaks that also include agricultural areas may indeed<br />

FCEC 211

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