Insect Control: Biological and Synthetic Agents - Index of
Insect Control: Biological and Synthetic Agents - Index of
Insect Control: Biological and Synthetic Agents - Index of
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162 4: <strong>Insect</strong> Growth- <strong>and</strong> Development-Disrupting <strong>Insect</strong>icides<br />
Trialeurodes vaporariorum (De Cock et al., 1995;<br />
De Cock <strong>and</strong> Degheele, 1998; Ishaaya, 2001). It has<br />
no ovicidal activity but suppresses embryogenesis<br />
through adults (Table 14).<br />
Although the exact mode <strong>of</strong> action <strong>of</strong> the IGR<br />
cyromazine, which is predominantly active against<br />
dipteran larvae, is not known, evidence has been<br />
presented to suggest that its target site for interference<br />
with sclerotization is different from that <strong>of</strong><br />
BPUs (Biddington, 1985). In larvae intoxicated<br />
with cyromazine, the cuticle rapidly becomes less<br />
extensible <strong>and</strong> unable to exp<strong>and</strong> compared with<br />
the cuticle <strong>of</strong> untreated larvae. The cuticle may<br />
be stiffer because <strong>of</strong> increased cross-linking between<br />
the various cuticle components, the nature <strong>of</strong> which<br />
remains unknown. As summarized in Table 14,<br />
cyromazine is an IGR with contact action interfering<br />
with molting <strong>and</strong> pupation. It has good systemic<br />
activity. When applied to the leaves, it exhibits a<br />
strong translaminar activity, <strong>and</strong> when applied to<br />
the soil it is taken up by the roots <strong>and</strong> translocated<br />
acropetally (Hall <strong>and</strong> Foehse, 1980; Awad <strong>and</strong><br />
Mulla, 1984; Reynolds <strong>and</strong> Blakey, 1989; Viñuela<br />
<strong>and</strong> Budia, 1994; Tomlin, 2000).<br />
With classical SAR (Hansch-Fujita), the effects <strong>of</strong><br />
different substituents on the benzene rings in BPUs<br />
were analyzed for larvicidal activity against Chilo<br />
suppressalis, S. littoralis, <strong>and</strong> B. mori (Nakagawa<br />
et al., 1987, 1989a, 1989b). For the benzoyl moiety,<br />
the toxicity was higher with a higher total hydrophobicity,<br />
a higher electron withdrawal from the<br />
side chain, <strong>and</strong> a lower steric bulkiness <strong>of</strong> orthosubstituents.<br />
In addition, introduction <strong>of</strong> electronwithdrawing<br />
<strong>and</strong> hydrophobic substituents at<br />
the para-position <strong>of</strong> the phenyl (aniline) moiety enhanced<br />
the larvicidal activity, whereas bulkier<br />
groups were unfavorable. Stacking did not occur<br />
between the two aromatic moieties along the urea<br />
moiety (Sotomatsu et al., 1987). To ascertain the<br />
above results, the relative activity <strong>of</strong> BPUs was<br />
determined by measuring the incorporation <strong>of</strong><br />
[ 14 C]-GlcNAc in larval integuments cultured<br />
in vitro (Nakagawa et al., 1989b). There was a<br />
colinear relationship between in vitro activities <strong>and</strong><br />
in vivo larvicidal toxicities if the hydrophobic factor(s)<br />
participating in transport were considered<br />
separately. In addition, integuments <strong>of</strong> the three<br />
Lepidoptera were incubated in conditions with <strong>and</strong><br />
without the synergists piperonylbutoxide (PB)<br />
<strong>and</strong> S,S,S-tributylphosphorotrithioate (DEF). In the<br />
Qualitative Structure–activity Relation (QSAR)<br />
equation measured without synergist, an electronwithdrawing<br />
effect was favorable to the activity, but<br />
an electron-donating group was favorable to the<br />
activity in the presence <strong>of</strong> PB. These results mean<br />
that electron-withdrawing groups are playing a role<br />
in suppressing the oxidative metabolism. DEF had<br />
no significant effect, suggesting that hydrolytic degradation<br />
<strong>of</strong> the phenyl moiety was not <strong>of</strong> significant<br />
consequence as compared to its oxidative degradation.<br />
In summary, the SAR results suggested that<br />
for BPUs the specific larvicidal spectrum is due<br />
to inherent differences in metabolism in addition<br />
to differences in the physiochemical substituent<br />
effects (Nakagawa et al., 1987, 1989a, 1989b;<br />
Sotomatsu et al., 1987).<br />
4.4.4. Spectrum <strong>of</strong> Activity<br />
Most CSI compounds are very potent against a<br />
variety <strong>of</strong> different pests with the highest activity<br />
towards lepidopterous insects <strong>and</strong> whiteflies. The<br />
main commercial applications are in field crops/<br />
agriculture, forestry, horticulture, <strong>and</strong> in the home<br />
as summarized in Table 14 (Retnakaran <strong>and</strong> Wright,<br />
1987; Tomlin, 2000; Ishaaya, 2001). Novaluron<br />
acts by ingestion <strong>and</strong> contact against lepidopterans<br />
(S. littoralis, S. exigua, S. frugiperda, Tuta absoluta<br />
<strong>and</strong> Helicoverpa armigera), whitefly, B. tabaci, eggs<br />
<strong>and</strong> larvae, <strong>and</strong> different stages <strong>of</strong> the leafminer,<br />
Liriomyza huidobrensis. Bistrifluron is active<br />
against various lepidopteran pests <strong>and</strong> whiteflies<br />
an apple, Brassica leafy vegetables, tomato, persimmon,<br />
<strong>and</strong> other fruits (Kim et al., 2000). Hexaflumuron<br />
<strong>and</strong> the newer noviflumuron are now used in<br />
bait for control <strong>of</strong> subterranean termites (Sheets<br />
et al., 2000; Karr et al., 2004). As a specialty in the<br />
series <strong>of</strong> CSIs, fluazuron is the only ixodicide with a<br />
strong activity against cattle ticks (Kim et al., 2000)<br />
(Table 14).<br />
Bupr<strong>of</strong>ezin has a persistent larvicidal action<br />
against sucking Homoptera, such as the greenhouse<br />
whitefly, T. vaporariorum, the sweet potato whitefly,<br />
B. tabaci, both <strong>of</strong> which are important pests <strong>of</strong><br />
cotton <strong>and</strong> vegetables, the brown planthopper,<br />
N. lugens in rice, the citrus scale insects, Aonidiella<br />
aurantii <strong>and</strong> Sassetia oleae, <strong>and</strong> some Coleoptera<br />
<strong>and</strong> Acarina. In contrast, cyromazine is used for<br />
control <strong>of</strong> dipteran larvae in chicken manure. It is<br />
also used as a foliar spray to control leafminers<br />
(Liriomyza sp.) in vegetables <strong>and</strong> ornamentals, <strong>and</strong><br />
to control flies on animals (Hall <strong>and</strong> Foehse, 1980;<br />
Williams et al., 1980; Kanno et al., 1981; Reynolds<br />
<strong>and</strong> Blakey, 1989; Tomlin, 2000) (Table 14).<br />
4.4.5. Ecotoxicology <strong>and</strong> Mammalian Safety<br />
Overall, CSIs have selective insect toxicities <strong>and</strong> as<br />
such are considered ‘‘s<strong>of</strong>t insecticides.’’ For diflubenzuron,<br />
the harbinger <strong>of</strong> all BPUs, its environmental<br />
fate has been extensively investigated <strong>and</strong> was