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Fortuitous biological control of insect pests and ... - THE BIOSCAN

Fortuitous biological control of insect pests and ... - THE BIOSCAN

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BABASAHEB B. FAND et al.,Table 3: <strong>Fortuitous</strong> <strong>biological</strong> <strong>control</strong> <strong>of</strong> nontarget <strong>pests</strong> by purposefully imported natural enemiesNontarget pest/ s Host plant/ Country <strong>of</strong> Controlled by Imported from Target pest/ s Year Referenceutility invasion natural enemyOpuntia vulgaris Miller Terrestrial India Dactylopius Brazil Opuntia cactii 1795 Tryon, 1910; Ramakrishnainvasive weed ceylonicus (Green) Ayyar,1931Citrus mealybug Planococcus CitrusGrape India Cryptolaemus Australia C<strong>of</strong>fe green scale 1898 Sankaran, 1974citri (Risso), Pink hibiscus mealy montrouzieri Coccus viridis (Green) Singh, 1994bug Maconellicoccus hirsutus Mulsant(Green)Spodoptera litura (Fabricius) Tobacco India Telenomus Papua New Castor semilooper, Achaea 1964 Sankaran, 1974remus Nixon Guinea janata LinnaeusRed-b<strong>and</strong>ed whitefly Avocado California Cales noacki Howard Brazil Mulberry whitefly Tetraleurodes 1982 Rose <strong>and</strong> Wooly, 1984Tetraleurodes sp. (Hymenoptera: mori (Quaintance), Acacia whitefly(Homoptera: Aleyrodidae) Aphelinidae) Tetraleurodes acaceae (Quaintance)also results in fortuitous <strong>biological</strong> <strong>control</strong> (Nechols, 2003).We quote here specifically the instances regardingpurposefully imported natural enemies recruited on nontarget<strong>pests</strong>, which can be regarded as fortuitous as well as fortunate<strong>biological</strong> <strong>control</strong> since unplanned <strong>pests</strong> attacked by theintroduced natural enemies were <strong>of</strong> economic concern (Table3). The fortuitous <strong>control</strong> <strong>of</strong> one <strong>of</strong> the invasive <strong>and</strong> noxiousweeds Opuntia vulgaris Miller in North <strong>and</strong> Central India byDactylopius ceylonicus (Green), an <strong>insect</strong> bioagent native <strong>of</strong>Brazil introduced in 1795 mistakenly in place <strong>of</strong> D. cocciCosta, a true carmine dye producing scale feeding on O. cacti(Tryon, 1910; Ramakrishna Ayyar, 1931) is one <strong>of</strong> the bestexamples <strong>of</strong> purposefully imported natural enemies<strong>control</strong>ling nontarget but economically important <strong>pests</strong>. TheAustralian Ladybird beetle Cryptolaemus montrouzieriMulsant was imported to India in 1898 against C<strong>of</strong>fe greenscale Coccus viridis (Green). Though it has established underIndian conditions but failed to <strong>control</strong> the target pest <strong>and</strong> nowis a common predator <strong>of</strong> variety <strong>of</strong> mealybug species includingcitrus mealybug Planococcus citri (Risso) <strong>and</strong> pink hibiscusmealybug Maconellicoccus hirsutus (Green) in South India(Rao et al., 1971; Sankaran, 1974; Singh, 1994). Similarly, inanother case an egg parasitoid, Telenomus remus Nixon,basically imported from Papua New Guinea to India in 1964against castor semilooper Achoea janata Linnaeus (Sankaran,1974) has turned to be an important regulator <strong>of</strong> anothernon-target but one <strong>of</strong> the destructive <strong>pests</strong> i.e. tobacco leafeating caterpillar Spodoptera litura (Fabricius). Suppression<strong>of</strong> red b<strong>and</strong>ed whitefly Tetraleurodes sp., an invasive species<strong>of</strong> avocado in California by Cales noacki Howard, an earlierintroduced parasitoid for <strong>control</strong> <strong>of</strong> mulberry whiteflyTetraleurodes mori (Quaintance) <strong>and</strong> acacia whiteflyTetraleurodes acaceae (Quaintance), preventing the dispersal<strong>of</strong> the pest to uninfested areas has been reported (Rose <strong>and</strong>Wooly, 1984).Do really fortuitous introductions are beneficial ecologically<strong>and</strong> economically?Historically, invasive alien species <strong>of</strong> worldwide importancehave been <strong>control</strong>led successfully through classical <strong>biological</strong><strong>control</strong> approach involving importation, mass rearing <strong>and</strong>release <strong>of</strong> several species <strong>of</strong> exotic natural enemies (VanLenteren et al., 2000; 2003). By its very nature, classical<strong>biological</strong> <strong>control</strong> involves the introduction <strong>of</strong> <strong>biological</strong><strong>control</strong> agents into the new areas outside their native range; ithas every possibility <strong>of</strong> accidental introduction <strong>of</strong> otherunintended organisms too. The literature says that most <strong>of</strong> thecases <strong>of</strong> accidental introductions <strong>of</strong> unintended species <strong>of</strong>natural enemies were invariably associated with the purposefulimportations <strong>of</strong> exotic natural enemies for classical <strong>biological</strong><strong>control</strong> (De Bach, 1971; Ooi, 1987; Nechols, 2003; VanLenteren et al., 2003, 2006).Regardless <strong>of</strong> when <strong>and</strong> how they entered into the newlocalities, the fortuitous introductions <strong>and</strong> establishments <strong>of</strong>exotic <strong>biological</strong> <strong>control</strong> agents resulted in incredible amount<strong>of</strong> natural <strong>biological</strong> <strong>control</strong> <strong>of</strong> <strong>pests</strong> <strong>of</strong> economic importance(Table 1) <strong>and</strong> are still going on in nature. Similarly, therecruitment <strong>of</strong> indigenous natural enemies onto invasive <strong>pests</strong>(Table 2) has very little or no environmental risk thanintroducing natural enemies from original area (Lasalle <strong>and</strong>6

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