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394<br />

P. Genovesi<br />

11 years (Panzacchi et al. 2006). The Ruddy duck eradication campaign<br />

launched in the United Kingdom is predicted to cost € 5–13 million. Even<br />

small-scale eradications can sometimes be very costly: for example, the<br />

removal of only twelve Himalayan porcupines from Devon cost a staggering<br />

€ 230,000.<br />

One of the problems in assessing how much eradications have cost on average<br />

is that the available literature (either scientific or “grey”) often does not<br />

report such data, and the results of prompt eradication projects (cf. removals<br />

carried out in the early stages of invasions) are often not published at all. If it<br />

is complex to assess costs, it is even more difficult to compare costs with benefits<br />

of eradications, because these depend on parameters which have very<br />

high levels of uncertainty, such as the probability of the target species, if not<br />

removed, to establish, expand and cause damage. The eradication of the Canadian<br />

beaver (Castor canadensis) from France required only one operator<br />

working for a limited amount of time but likely prevented very costly impacts<br />

if the species had been allowed to expand (Rouland 1985). In an attempt to<br />

compare costs of eradication vs. permanent control, Panzacchi and coauthors<br />

(2006) showed that the successful eradication of the coypu from East<br />

Anglia, costing about € 5 million in 11 years, may have prevented much more<br />

severe economic impacts in the long term, considering that permanent control<br />

of the species in Italy causes losses of over € 3.4 million per year and that<br />

future annual costs are predicted to exceed € 12 million (see also Chaps. 18<br />

and 19).<br />

In the case of the invading alga C. taxifolia, successful eradication from<br />

California required (converted into €) over € 2.5 million in 3 years, and additional<br />

costs will be necessary for medium-term monitoring. In Europe, when<br />

the species was initially detected, it could have been removed within a few<br />

days of work (cf. above) – nowadays, it is widespread, and permanent control<br />

in many areas of the Mediterranean basin is costing huge amounts of money.<br />

In the case of the black-striped mussel from Cullen Bay in Australia, the decision<br />

of eradicating the invasive – at a cost of (converted into €) over € 1.3 million<br />

“only” – was taken because of the risk that an expansion of the alien mollusc<br />

could have impacted the local € 24 million pearl fishery.<br />

More comprehensive economic assessments of eradications are evidently<br />

needed, in order to provide state governments with critical data for revising<br />

their policies on the issue, and to assist the authorities competent of taking<br />

decision about when to start an eradication (see also Chaps. 18 and 19).<br />

22.2.5 Legal and Organizational Constraints<br />

Invasive alien species are a cross-cutting issue, involving many different<br />

aspects (such as agriculture, forestry, horticulture, aquaculture and hunting),<br />

and implementation of eradications is often regulated by different laws. For

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