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ECOFUN-MICROBIODIV: an FP7 European project for developing and evaluating innovative tools for assessing the impact of pesticides on soil functional microbial diversity- towards new pesticide registration regulation?

机译:ECOFUN-MICROBIODIV:一个FP7欧洲项目,用于开发和评估创新工具,以评估农药对土壤功能微生物多样性的影响-朝着新的农药注册法规发展?

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Conventional agriculture is still relying on the use of fertil izers and pesticides, with consequent toxicological pressure on the environment and on human through food chain accumulation and reproductive repercussions under "the thematic strategy for soil protection"; the European Soil Framework Directive (COM(2006)232) clearly identifies agricultural practices as a major threat for soil biodiversity and functioning (Van Camp et al. 2004). The issue was also highlighted by the Millennium Ecosystem Assessment (2005), an international effort to draw an inventory of global ecosystems, which identified agriculture as a major threat for soil ecosystemic services such as nutrient cycling. Depending on agricultural practices, farmers can either con tribute to increasing or decreasing carbon storage inagricultural soils (Fontaine et al. 2007). In addition, the nitrogen and phosphorous deposited onto agricultural lands through fertilization can be transported to the atmosphere or leach to groundwater (Gregoire et al. 2009). The natural attenuation capacity of soils via the biotransformation of pollutants significantly decreases the persistence of pesticides in the different environmental compartments (Udikovic-Kolic et al. 2012). The successive revisions (2455/2001/CE, 2008/32/CE, 2008/105/CE et 2009/31/ CE) of the European Union (EU) water framework (Directive 2000/60/CE) have led to the definition of new guidelines not only to ensure the high quality of drinking water (EU limit for drinking water 0.1 μg of pesticide per liter) but also to preserve the ecological quality of natural water resources, including surface water systems such as rivers and lakes which are subjected to chemical pollution from cultivated lands, at least in agricultural landscapes. In response to the implementation of the water framework directive, agrochemical companies developed new classes of pesticides which are particularly effective at low doses (i.e., only a few grams per hectare), show high affinity for their target and are characterized by reduced dispersion into the environment (Cessna et al. 2006). As they have been used in low amounts and over a relatively short time period, few environmental data are yet available for these new pesticide classes and one of the major limitations to these studies is that the detection limit of current chemical analyses, although improved within the last few years, still remains too high for this kind of compounds.
机译:传统农业仍然依靠肥料和杀虫剂的使用,在“土壤保护主题战略”下,通过食物链的积累和生殖影响,对环境和人类产生毒理学压力;欧洲土壤框架指令(COM(2006)232)明确地将农业实践视为对土壤生物多样性和功能的主要威胁(Van Camp等,2004)。千年生态系统评估(2005年)也强调了这个问题,这是一项国际工作,旨在绘制全球生态系统清单,该报告将农业确定为对土壤生态系统服务(如养分循环)的主要威胁。根据农业实践,农民可以增加或减少农业土壤中的碳储量(Fontaine等人,2007)。此外,通过施肥沉积在农田上的氮和磷可以运到大气中或浸出到地下水中(Gregoire et al。2009)。通过污染物的生物转化,土壤的自然衰减能力显着降低了农药在不同环境区室中的持久性(Udikovic-Kolic et al。2012)。欧盟(EU)水框架(第2000/60 / CE号指令)的连续修订版(2455/2001 / CE,2008/32 / CE,2008/105 / CE和2009/31 / CE)导致了定义新指南不仅要确保饮用水的质量(欧盟对饮用水的限制为每升农药0.1μg农药),而且还要维护自然水资源的生态质量,包括受到污染的地表水系统,如河流和湖泊至少在农业景观中来自耕地的化学污染。为响应水框架指令的实施,农药公司开发了新型农药,这些农药在低剂量(即每公顷仅几克)时特别有效,对目标具有高度亲和力,并且具有减少向农药中分散的特点。环境(Cessna et al。2006)。由于它们的使用量很少且使用时间相对较短,因此这些新农药类别的环境数据仍然很少,这些研究的主要局限之一是当前化学分析的检出限,尽管在检测范围内有所改善。最近几年,对于这类化合物仍然过高。

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