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Long-term effects of imidacloprid on the abundance of surface- and soil-active nontarget fauna in turf

机译:吡虫啉对草皮中表面活性和土壤活性非目标动物数量的长期影响

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Abstract1 Outbreaks of root-feeding scarab larvae in turfgrass are widely managed through preventive applications of imidacloprid. Long-residual activity and application before feasible scouting probably lead to its overuse and overexposure.2 Recent investigations revealed a selective impact of imidacloprid (not trichlorfon or halofenozide) on certain nontarget turf arthropods, motivating the present study on the persistence of abundance effects over 6 years of annual applications.3 Arthropods were sampled monthly (July to October) in replicated plots using soil core heat extraction and pitfall traps to quantify soil- and surface-active arthropods. Captures were identified to class, order or family. The most represented taxa were analysed to test for cumulative effects and their change over season and year.4 Imidacloprid had no impact on pitfall captures, although the abundance of Hemiptera, Thysanoptera, Coleoptera and Collembola was suppressed in soil core captures. Among beetles, impact was expressed in adults (not larvae), and in Carabidae and Staphylinidae (not Chrysomelidae or Curculionidae). Among springtails, impact was expressed in Entomobryomorpha (not Poduromorpha or Symphypleona). Impact did not diminish with year but there was variable recovery between applications.5 There may therefore be a diverging response of soil- and surface-active fauna to the nontarget impacts of imidacloprid. The suppression of predaceous (not phytophagous) beetles indicates an indirect effect mediated through declines in prey populations.6 The magnitude of abundance effects confirms that the balance between target and nontarget impact should be explicitly examined. Implications are discussed with respect to functional relevance for nutrient cycling and the natural regulation of pests.
机译:摘要1预防性应用吡虫啉可广泛控制草根草中以根为食的金龟子幼虫的暴发。 2在最近的调查中发现吡虫啉(不是敌百虫或氟苯乙脲)对某些非目标草皮节肢动物有选择性影响,这促使本研究对6种以上丰度效应的持久性进行了研究。 3每月(7月至10月)对节肢动物进行采样,使用土壤芯热提取和陷阱陷阱对重复的样地进行采样,以量化土壤和表面活性节肢动物。捕获物被识别为分类,订购或家庭。分析了最具代表性的分类单元,以测试其累积效应及其随季节和年份的变化。4吡虫啉对陷阱捕获没有影响,尽管土壤核心捕获中抑制了半翅目,Th翅目,鞘翅目和Collembola的丰度。在甲虫中,影响是在成年动物(不是幼虫),在甲壳动物和葡萄球菌(不是金眼科或弯孢科)中表达的。在跳尾中,冲击波以昆虫突触核表达(而不是单突触目或对称突触)。影响并没有随着年的减少而减少,但是两次施用之间的恢复有所不同。5因此,土壤和表面活性动物对吡虫啉的非目标性影响可能会有不同的反应。捕食早((非食草性)甲虫表明间接作用是由猎物种群减少所介导的。6丰度影响的程度证实,应明确检验目标和非目标甲虫之间的平衡。讨论了有关养分循环和害虫自然调控的功能相关性的含义。

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