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土壤生物群落对杀虫剂林丹在陆地模型生态系统中的应用的响应。

The response of soil organism communities to the application of the insecticide lindane in terrestrial model ecosystems.

机构信息

Chair of Environmental Biology and Chemodynamics, Institute for Environmental Research (BioV), RWTH Aachen University, Aachen, Germany.

出版信息

Ecotoxicology. 2013 Mar;22(2):339-62. doi: 10.1007/s10646-012-1030-0. Epub 2012 Dec 20.

Abstract

The EU plant protection regulation 1107/2009/EC defines the requirements for active ingredients to be approved, specifically including the assessment of effects on biodiversity and ecosystems. According to that, semi-field methods are expected to be more important in the near future. Therefore, a higher-tier experiment suitable to assess the risk for soil organisms was conducted to further develop the TME (terrestrial model ecosystems) methodology in a dose-response design with the persistent insecticidal model compound lindane (gamma-HCH). The effects of lindane on soil communities such as collembolans, oribatid mites, nematodes, soil fungi and plant biomass were determined in 42 TME. Intact TME-soil cores (diameter 300 mm, height 400 mm) from undisturbed grassland were stored outdoor under natural climatic conditions. Lindane was applied in five concentrations between 0.032 mg active ingredients (ai)/kg dry soil and 3.2 mg ai/kg dry weight soil, six-fold replicated each. Twelve TME served as untreated controls. Abundance and community structures of oribatids, collembolans, enchytraeids, nematodes and fungi were recorded. Oribatid mites' community responded 3 months after treatment, although they were not significantly affected by the overall treatment regimen. Collembolans in total and species-specific abundance as well as the community endpoints (principal response curves, diversity measures) were adversely affected by moderate dosages of lindane. Effects were transient between 3 and 5 months after treatment with a recovery within 1 year. No significant effects could be detected for enchytraeids, nematodes and fungi. The study design and the obtained results allow for calculations of no observed effect concentrations below the highest treatment level for populations and for soil communities as defined entities, as well as effective concentrations. The paper discusses the limits of effect detection in the light of achievable coefficients of variation and by means of minimum detectable differences. Outdoor TME are useful to analyze and assess functional and structural endpoints in soil organisms' communities and their possible recovery after pesticide treatment within 1 year.

摘要

欧盟植保法规 1107/2009/EC 规定了活性成分获得批准的要求,特别是包括对生物多样性和生态系统影响的评估。根据这一规定,半田间方法在不久的将来预计会更加重要。因此,进行了一项更高层次的实验,以评估土壤生物的风险,该实验采用持久性杀虫剂林丹(γ-六氯环己烷)作为模型化合物,采用剂量反应设计进一步开发 TME(陆地模型生态系统)方法。在 42 个 TME 中,测定了林丹对土壤生物群落(如弹尾目、甲螨、线虫、土壤真菌和植物生物量)的影响。完整的 TME-土壤芯(直径 300mm,高 400mm)取自未受干扰的草地,存放在室外自然气候条件下。林丹以 0.032mg 有效成分(ai)/kg 干土和 3.2mg ai/kg 干土的 5 个浓度应用,每个浓度重复 6 次。12 个 TME 作为未处理的对照。记录了甲螨、弹尾目、真蚓、线虫和真菌的丰度和群落结构。处理后 3 个月,甲螨群落发生了反应,尽管它们没有受到整个处理方案的显著影响。总的来说,弹尾目生物的丰度和物种特异性丰度以及群落终点(主要响应曲线、多样性测量)受到中等剂量林丹的不利影响。处理后 3 至 5 个月内出现了短暂的效应,1 年内恢复。真蚓、线虫和真菌未检测到明显的影响。该研究设计和获得的结果允许计算种群和土壤群落作为定义实体的无观察效应浓度,以及有效浓度。本文讨论了在可达到的变异系数范围内以及通过最小可检测差异,在检测效应方面的局限性。户外 TME 可用于分析和评估土壤生物群落的功能和结构终点,以及在 1 年内农药处理后可能的恢复情况。

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