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Limits and Potentialities of Eradication as a Tool for Addressing Biological Invasions 395<br />

example, a common legal constraint to eradication is that several national<br />

and supra-national legislations automatically protect alien species, and often<br />

do not explicitly include eradication as a management tool (Shine et al.<br />

2000).<br />

This complex situation causes an unclear repartition of roles and responsibilities<br />

in eradication, and equivocal decision and authorisation processes.<br />

As a result of these legal and organizational constraints, eradications are often<br />

delayed for too long or, in many cases, never even start. For example, an<br />

attempt to eradicate the American grey squirrel from Italy failed also because<br />

of the unclear legal status of alien species under the Italian legal framework,<br />

and the inadequate repartition of responsibilities between the national and<br />

local institutions (Genovesi and Bertolino 2001).<br />

One of the reasons for the successful eradication of C. taxifolia from California<br />

(cf. above) is the extraordinary commitment by all competent authorities<br />

in the invaded area. These formed a contingency body and ensured adequate<br />

powers and funds to the program, thereby enabling a prompt and<br />

effective response to the invasion. Similarly, the eradication of the coypu from<br />

East Anglia was also made possible by the strong commitment and the relevant<br />

resources mobilised by the decision makers.<br />

More generally, eradications should be integrated into national strategies,<br />

and particular attention should be paid to the coordination of all involved<br />

departments and agencies. For example, the many eradications carried out in<br />

New Zealand are also the result of a coordinated policy, with a clear repartition<br />

of roles and authorisation process under the Hazardous Substances and<br />

New Organisms Act of 1996. The successful eradication of over 53 infestations<br />

of 16 weed species in California has also been made possible by the coordinated<br />

policy to prevent and control weeds, formalised in 2005 through the<br />

adoption of a Noxious and Invasive Weed Action Plan (Rejmánek and Pitcairn<br />

2002; Shoenig 2005).<br />

In order to enable the competent agencies to carry out eradications and,<br />

more generally, to mitigate the impacts caused by invasive alien species, state<br />

authorities should review national institutional and legal frameworks, and<br />

develop coherent, comprehensive and consistent policies on biological invasions.<br />

In particular, legal constraints to the application of the necessary mitigation<br />

measures should be removed, legal tools should adopt terminology<br />

consistent with international definitions, and the competent authorities<br />

should be equipped with adequate powers to take the appropriate actions<br />

(Shine et al. 2000; Genovesi and Shine 2004). Establishing a coordination<br />

body, with access to adequate contingency funds, can be a critical element for<br />

resolving the institutional fragmentation of competencies on the different<br />

issues related to eradications.

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