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66<br />

J.A. JACAS & A. URBANEJA<br />

Since the cost of production of these natural enemies is relatively low, the current<br />

use of these IBCAs involves augmentative releases against their respective target pests<br />

(Table 3). These strategies are also in use in other Mediterranean countries<br />

(Katsoyannos, 1996), as well as in areas with a similar climate, such as Australia,<br />

California, or South Africa (Charleston et al., 2003; UC, 1991; Smith et al., 1997).<br />

As shown in Table 3, augmentative releases include both exotic <strong>and</strong> native<br />

natural enemies. Consistent with latest trends in EU agriculture, which emphasizes<br />

the role of indigenous natural enemies, Anagyrus pseudococci (Girault)<br />

(Hymenoptera: Encyrtidae), a native parasitoid of the citrus mealybug, Planococcus<br />

citri Risso (Hemiptera: Pseudococcidae), has been recently studied <strong>and</strong> could<br />

successfully substitute the exotic L. dactylopii in the future (Campos & Martínez-<br />

Ferrer, 2003). Similarly, studies are in progress to establish conditions for using the<br />

native predatory mite Phytoseiulus persimilis Athias-Henriot (Acari: Phytoseiidae)<br />

against the two spotted spider mite, Tetranychus urticae Koch (Acari:<br />

Tetranychidae) another native mite which is considered a key pest for clementine<br />

m<strong>and</strong>arins in Spain (Aucejo, Gómez-Cadenas, & Jacas, 2004; Ansaloni, Pascual-<br />

Ruiz, Hurtado, & Jacas, 2008). Likewise, releases of Neoseiulus californicus<br />

(McGregor) (Acari: Phytoseiidae) <strong>and</strong> P. persimilis have also been proposed against<br />

the citrus mite, Panonychus citri, <strong>and</strong> T. urticae, respectively, in nurseries (Table 3)<br />

(Abad-Moyano, Pina, Pérez-Panadés, Carbonell, & Urbaneja, 2009).<br />

4. FORTUITOUS BIOLOGICAL CONTROL<br />

Anagyrus pseudococci is not the only example of an indigenous natural enemy<br />

having a significant impact on an exotic pest. Although such pests are usually the<br />

target of the Classical BC strategy, indigenous natural enemies can sometimes result<br />

in excellent BC, which is then called fortuitous BC.<br />

The native predator E. stipulatus provides a good example of such a situation in<br />

Spain. This species is the most abundant Phytoseiidae in Spanish citrus (Ferragut et al.,<br />

1988). If undisturbed, its populations are usually able to regulate Panonychus citri<br />

populations below their economic threshold (Ripollés, Marsá, & Martínez, 1995).<br />

Therefore E. stipulatus is considered as one of the most relevant natural enemies in<br />

Spanish citrus orchards <strong>and</strong> its conservation is a key factor for IPM success (Urbaneja<br />

et al., 2008). Most other indigenous natural enemies do not have such a dramatic<br />

impact on their host/prey pests (Table 1). However, both the increasing legal<br />

restrictions for importing exotic natural enemies into the EU (Bigler et al., 2005) <strong>and</strong><br />

the disappearance of many pesticides in the EU following the process of re-evaluation<br />

of all pesticide active ingredients under EU Directive 91/414/EEC, have lead to a<br />

renewed interest on these native species <strong>and</strong> their conservation (Table 1).<br />

5. THE CORNERSTONE: CONSERVATION<br />

Conservation biological control exploits resident, either native or naturalized,<br />

natural enemies. This strategy is especially useful in permanent ever-green crops<br />

(Barbosa, 1998; L<strong>and</strong>is, Wratten, & Gurr, 2000), such as citrus, where both pests<br />

<strong>and</strong> their natural enemies are active <strong>and</strong> abundant throughout the year (Garrido &

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