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388<br />

100000<br />

Area of islands successfully eradicated<br />

from brown rats (log ha)<br />

10000<br />

1000<br />

100<br />

10<br />

P. Genovesi<br />

Fig. 22.3 Eradications<br />

of Rattus<br />

rattus in New<br />

Zealand: increasing<br />

size of islands<br />

successfully eradicated<br />

(modified<br />

from Veitch 1995)<br />

1<br />

1955<br />

1960<br />

1965<br />

1970<br />

1975<br />

1980<br />

1985<br />

1990<br />

1995<br />

2000<br />

2005<br />

igate the impacts of invasive alien species and also significant advances in<br />

technical aspects of eradications (Veitch and Clout 2002). For example, the<br />

development of second-generation anti-coagulant poisons has made it possible<br />

to increase the size of islands from which rats have been successfully eradicated.<br />

This was confirmed by the successful removal, completed in 2003, of<br />

the Norway rat (Rattus norvegicus) from sub-Antarctic Campbell Island (over<br />

11,000 ha), by far the largest area in the world successfully eradicated from<br />

rats (Fig. 22.3).<br />

22.1.3 Outcomes<br />

Successful eradications can lead to significant effects in terms of recovery of<br />

native species and habitats. Rat eradications from islands have promoted the<br />

recovery of many colonial nesting seabirds, including the storm petrel<br />

(Hydrobates pelagicus) and the Cory’s shearwater (Calonectris diomedea) in<br />

the Mediterranean (Martín et al. 2000), or of terrestrial bird species such as<br />

the dunnock (Prunella modularis), the wren (Troglodytes troglodytes) and the<br />

rock pipit (Anthus petrosus) (Kerbiriou et al. 2003).<br />

In many cases, the removal of alien species is an essential prerequisite for<br />

subsequent recovery programs. For example, the recently completed rat eradication<br />

from Campbell Island was considered an essential condition for starting<br />

a recovery program for the endemic Campbell Island teal (Anas nesiotis),

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