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Insect Control: Biological and Synthetic Agents - Index of

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22 1: Pyrethroids<br />

used. Organophosphates <strong>and</strong> carbamates were used in<br />

Stage III <strong>and</strong> also if required for additional sprays<br />

during Stages I <strong>and</strong> II.<br />

The use <strong>of</strong> a ‘‘s<strong>of</strong>ter’’ insecticide (endosulfan) in<br />

the early season was deliberate to minimize disruption<br />

<strong>of</strong> beneficial parasitoids <strong>and</strong> predators <strong>and</strong> to<br />

avoid a potential upsurge <strong>of</strong> secondary pests such as<br />

mites, aphids, <strong>and</strong> whiteflies, which were not controlled<br />

by the pyrethroids available at the time.<br />

Examples <strong>of</strong> nonchemical countermeasures incorporated<br />

in the strategy to reduce selection pressure<br />

included the use <strong>of</strong> early-maturing crops, avoiding<br />

early-growing crops (e.g., maize) in adjacent fields,<br />

which may act as early-season nurseries for resistant<br />

H. armigera, <strong>and</strong> utilization <strong>of</strong> host plants in refugia<br />

to maintain a large pool <strong>of</strong> susceptible individuals,<br />

which would continually dilute the resistant<br />

population in the crop. Resistance was monitored<br />

on a weekly basis using a discriminating dose <strong>of</strong><br />

fenvalerate with <strong>and</strong> without the synergist PBO.<br />

Later monitoring showed a rise in metabolic resistance<br />

attributed to MFOs <strong>and</strong> this resulted in the<br />

inclusion <strong>of</strong> PBO in the last <strong>of</strong> the maximum <strong>of</strong> three<br />

pyrethroid sprays. This strategy was successful for<br />

many years but the underlying trend <strong>of</strong> upward<br />

increase in the proportion <strong>of</strong> resistant insects continued<br />

<strong>and</strong> finally led to a complete reorganization <strong>of</strong><br />

the strategy in the mid 1990s with a shift away from<br />

reliance on pyrethroids.<br />

Initial resistance to pyrethroids was thought to be<br />

due to the presence <strong>of</strong> the knockdown site-insensivity<br />

resistance (kdr) mechanism probably as a direct<br />

result <strong>of</strong> cross-resistance to DDT. Over the years <strong>of</strong><br />

the IRM strategy, metabolic resistance mechanisms<br />

appear to have taken over. However, there is still<br />

controversy over whether it is primarily due to elevated<br />

levels <strong>of</strong> esterases or mixed-function oxidases<br />

(MFOs). The main reason for the uncertainty concerns<br />

the role <strong>of</strong> synergists used in the studies. For<br />

example, PBO is now thought to inhibit both these<br />

types <strong>of</strong> enzymes. Furthermore, it has been suggested<br />

that such inhibitors may themselves have<br />

become resisted in the field over time (McCaffery,<br />

1998), thus obscuring the mechanism <strong>of</strong> resistance.<br />

The second IRM strategy involved the whitefly,<br />

B. tabaci, a representative sucking pest on a wide<br />

range <strong>of</strong> crops (Denholm et al., 1998). In 1995, overreliance<br />

on a limited range <strong>of</strong> pyrethroids in Arizona<br />

had led to a classic treadmill scenario, with farmers<br />

responding to rising levels <strong>of</strong> resistance by increasing<br />

the number <strong>of</strong> sprays (as many as 8–12 applications<br />

per season). In this pest, the haplodiploid<br />

breeding system encourages rapid selection <strong>and</strong><br />

fixation <strong>of</strong> resistance genes. Males are produced<br />

uniparentally from unfertilized, haploid eggs, <strong>and</strong><br />

females are produced biparentally from fertilized<br />

diploid eggs. In addition, for this (<strong>and</strong> other) highly<br />

polyphagous species, the interaction between pest<br />

ecology <strong>and</strong> resistance is complex <strong>and</strong> generally<br />

not well understood, making formulation <strong>of</strong> IRM<br />

strategies even more difficult. The strategy <strong>of</strong><br />

Dennehy <strong>and</strong> Williams (1997) implemented in<br />

1996 had several features in common with that for<br />

H. armigera. It too relies on the continuous availability<br />

<strong>of</strong> a pool <strong>of</strong> susceptible whiteflies in refugia<br />

(e.g., Brassica crops) throughout the year <strong>and</strong> alteration<br />

<strong>of</strong> agronomic practices (e.g., timing <strong>of</strong> planting)<br />

in crops to minimize whitefly numbers whilst<br />

still maintaining the level <strong>of</strong> natural enemies. The<br />

first <strong>of</strong> the three-stage IRM strategy involved use <strong>of</strong><br />

a single spray each <strong>of</strong> pyriproxyfen <strong>and</strong> bupr<strong>of</strong>ezin<br />

(then newly available insect-growth regulators) with<br />

a 14- or a 21-day gap. The second stage allowed<br />

nonpyrethroid conventional insecticides <strong>and</strong> the<br />

third used pyrethroids synergized with acephate as<br />

late as possible in the season. A threshold <strong>of</strong> infestation<br />

was defined to initiate insecticide applications.<br />

Mixtures were limited to no more than two compounds<br />

<strong>and</strong> any one active ingredient was restricted<br />

to no more than two applications in one season.<br />

This strategy has been extremely successful in reducing<br />

the number <strong>of</strong> sprays required <strong>and</strong> regaining<br />

susceptibility both to synergized pyrethroids <strong>and</strong><br />

key nonpyrethroid insecticides.<br />

As for H. armigera, the need for monitoring,<br />

establishing threshold levels to trigger spray applications,<br />

<strong>and</strong> cooperation <strong>of</strong> the growers was key to<br />

the strategy. Long-term success <strong>of</strong> any IRM strategy<br />

depends on many factors because, even when an<br />

IRM strategy has been successful (McCaffery,<br />

1998), effectiveness <strong>of</strong> synergized pyrethroids can<br />

be lost after just two applications in areas with a<br />

history <strong>of</strong> resistance to pyrethroids.<br />

In conclusion, the key requirement for the development<br />

<strong>and</strong> sustainability <strong>of</strong> an IRM strategy is<br />

diagnosis <strong>of</strong> the resistance mechanism(s) in field<br />

populations. This is especially important when<br />

assessing the relative importance <strong>of</strong> individual<br />

mechanisms when several are present, which influences<br />

changes to the strategy with time. As alluded<br />

to earlier, there is still much uncertainty in the diagnosis<br />

<strong>of</strong> mechanisms. The use <strong>of</strong> established inhibitors<br />

or just in vitro bioassay data has been shown<br />

to be unreliable in this regard. For example in<br />

M. persicae, elevated esterase was considered for<br />

many years to be the main resistance mechanism. It<br />

was only recently shown (Devonshire et al., 1998) that<br />

this mechanism made only a minor contribution to the

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