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Management of the Diamondback Moth and Other Crucifer Insect ...

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were applied to control DBM in 1992 <strong>and</strong> 1994, <strong>the</strong>losses <strong>of</strong> summer cabbage were 99% <strong>and</strong> 80%,respectively compared with <strong>the</strong> insecticide-treated plots(Zhao et al. 1996).In 1953, DBM was reported by Ankersmith as <strong>the</strong> firstcrop pest in <strong>the</strong> world to develop resistance to DDT inJava, Indonesia (Ankersmith 1953). The resistancedevelopment to several insecticides had been reported in<strong>the</strong> Philipines (Barroga 1974), Australia (Altman 1988),Hawaii (Tabashnik et al. 1987), Malaysia (Syed, 1992),Japan (Hama, 1992), North America (Shelton et al.1993), Thail<strong>and</strong> (Kuwahara et al. 1995). In 1992, Cheng<strong>and</strong> Tang reported <strong>the</strong> resistance <strong>of</strong> DBM to insecticidesin PR China. Up to now, because <strong>of</strong> <strong>the</strong> extensiveselection pressure <strong>and</strong> its high potential for developingresistance, DBM had developed resistance to <strong>the</strong> majortypes <strong>of</strong> insecticides, including organophosphates,organochlorines, carbamates, syn<strong>the</strong>tic pyrethroids, someinsect growth regulators, <strong>and</strong> microbial insecticides suchas Bacillus thuringiensis (Liu et al. 1981; Miyata et al.1992; Tabashnik et al. 1990; Talekar <strong>and</strong> Shelton 1993).In PR China, chemical control is still <strong>the</strong> main way tomanage <strong>the</strong> DBM. The massive abuse <strong>of</strong> chemicalinsecticides was leading to <strong>the</strong> rapid development <strong>of</strong>insecticide resistance. Due to insecticide resistance <strong>and</strong>eventual control failure <strong>of</strong> DBM, economical production<strong>of</strong> crucifers had become almost impossible in certainChinese areas (Liang et al. 2001; Liu et al. 2005).In <strong>the</strong> past two decades, Chinese entomologists hadcarried out more research on DBM in PR China,including occurrence, resistance, molecular geneticmechanism <strong>and</strong> IPM, etc. Some measures had beendeveloped in cultural control, chemical control, physicalcontrol <strong>and</strong> biological control, although systematicdemonstration was lacking. In order to produce betterquality brassica vegetables <strong>and</strong> canola, it is necessary tobuild <strong>and</strong> demonstrate new integrated technologiesaccording to <strong>the</strong> local conditions <strong>of</strong> different areas. In2008, a national project, <strong>the</strong> Special Fund for AgroscientificResearch in <strong>the</strong> Public Interest, supported <strong>the</strong>research on sustainable management <strong>of</strong> DBM. Theproject is a group effort involving 117 entomologistsfrom ten institutes or universities, including nearly allDBM experts in PR China. The group covers fivegeographic areas, viz., south, south-west, east, north <strong>and</strong>center. The significant progress made in <strong>the</strong> projectduring <strong>the</strong> past three years is presented here.Investigation on population dynamics infive geographic regionsPopulation dynamics <strong>of</strong> DBM in 14 locations from 10provinces in south, south-west, east, north <strong>and</strong> centerChina were investigated. The results showed that <strong>the</strong>rewere more than 20 generations in south China <strong>and</strong> it wasonly 2-3 generations in north-east China. There were oneor two population peaks in different areas during springor autumn. The time <strong>of</strong> initial peak occurred duringFebruary – March in South China <strong>and</strong> May – June inNorth-East China. The spring peak was higher than <strong>the</strong>autumn one in North China, whereas <strong>the</strong> two peaks weresimilar in South China.In 2010, <strong>the</strong> Chinese DBM population was significantlylow, <strong>and</strong> it could be due to <strong>the</strong> changes in climate, naturalenemy population <strong>and</strong> cropping systems. In terms <strong>of</strong> <strong>the</strong>climate, mean spring low temperature <strong>and</strong> summer hightemperature was one <strong>of</strong> <strong>the</strong> reasons. At <strong>the</strong> same time,<strong>the</strong> population was also controlled by a tremendousamount <strong>of</strong> rainfall. In addition, <strong>the</strong> natural enemiesincluding Diadegma semiclausum, Can<strong>the</strong>onideafurcellata <strong>and</strong> Erigonidium graminicola) <strong>and</strong> <strong>the</strong>cropping systems including rotating rice, corn <strong>and</strong> shallotin summer were effective in managing <strong>the</strong> DBM.Current status <strong>of</strong> insecticide resistancein DBM in PR ChinaDBM field populations were monitored for <strong>the</strong>irresistance to 11 selected pesticides (Table 1) in 34locations in south, south-west, east, north <strong>and</strong> centerChina following a st<strong>and</strong>ard method. The results showedthat <strong>the</strong> resistance was serious in all locations. Therewere significant differences in resistance to an insecticideamong <strong>the</strong> study sites. The resistance was more seriousin south, south-west <strong>and</strong> east China than o<strong>the</strong>r parts. Theresistance in Danzhou (Hainan Province) was <strong>the</strong> mostserious. High resistance is correlated to <strong>the</strong> populationdifferences <strong>and</strong> over-use <strong>of</strong> insecticides. It is verydifficult to plant vegetable brassicas in south Chinaduring summer because <strong>of</strong> high resistance in DBM. So,<strong>the</strong> farmers in <strong>the</strong> north or west China prefer plantingvegetable brassicas during summer. However, it is aremarkable fact that <strong>the</strong> insecticide resistance in DBM indifferent geographical regions is gradually decreasingyear by year from 2008 to 2010, which proves that <strong>the</strong>IPM technologies demonstrated <strong>and</strong> promoted through<strong>the</strong> project are effective.Over-wintering <strong>and</strong> migrationSome research work was also carried out on <strong>the</strong> nature<strong>and</strong> north limit <strong>of</strong> over-wintering. The super-coolingpoint was high with <strong>the</strong> growth <strong>of</strong> larva, <strong>and</strong> <strong>the</strong> meanwas -13.72°C. The super-cooling point was lowest for<strong>the</strong> pupa. The freezing point had <strong>the</strong> same trend as <strong>the</strong>super-cooling point. The research on <strong>the</strong> north limit <strong>of</strong>hibernation in PR China showed that <strong>the</strong> north limit was<strong>the</strong> area from Wuhan to Zhu-ma-dian based on <strong>the</strong>investigation on over-wintering in 19 locations.The genetic differences among 10 geographic DBMpopulations were lower. Hence, DBM could migratefrom south to north. The adult migration <strong>and</strong> climatecondition were monitored in 19 locations. The resultsshowed that <strong>the</strong>re were two models <strong>of</strong> migration, viz.,move in <strong>and</strong> move out (e.g., in Wuhan <strong>and</strong> Nanjing) <strong>and</strong>move in <strong>and</strong> settle down (e.g., Datong <strong>and</strong> Shenyang).Simultaneously, <strong>the</strong> resistance <strong>of</strong> DBM in differentlocations was analyzed <strong>and</strong> found that it was very similarto different insecticides among Wuxue (eastern Hubeiprovince), Luoyang (western Henan province) <strong>and</strong>Beijing (nor<strong>the</strong>rn China), which could be due tomigration.16 AVRDC - The World Vegetable Center

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