Glyphosate application may influence the transfer of trace elements from soils to both soil solutions and plants

IF 8.1 2区 环境科学与生态学 Q1 ENVIRONMENTAL SCIENCES
Nathan Bemelmans, Rosalie Dejardin, Bryan Arbalestrie, Yannick Agnan
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Abstract

Trace element dynamics in the soil-plant system depends on multiple parameters, including chelating organic compounds from natural or synthetic organic matters. In this study, we evaluated the influence of one of the most common pesticides—glyphosate—on the mobility of trace elements considering contrasted soils (uncontaminated, anthropogenically contaminated, and naturally-enriched) in a greenhouse experiment. Four modalities have been tested: one control without any application, two with different glyphosate doses (1 and 3 times the authorised field dose), and one with compost addition to evaluate its potential ability to mitigate the impact of glyphosate on trace element mobility. Both, trace element and glyphosate concentrations were measured in the soil solutions and trace element contents were determined in plants at the end of the experiment. The results showed that, although glyphosate concentrations rapidly decreased in soil solutions, glyphosate application still influenced the transfer of trace elements to both soil solution (up to 12-times higher) and plant (up to 5.2-times higher). This influence was highly dependent on both the specific elements and the type of soils considered. For instance, in uncontaminated soils, glyphosate especially increased the mobilization of Mn, Co, Zn, Mo, and Pb to soil solution. This effect diminished of 2.5 times on average with increasing soil contamination. A similar trend was observed for the transfer of trace elements from soil to plant (i.e., on average 2.2-times lower in the most contaminated compared to the uncontaminated soil). However, in the naturally-enriched soil, opposing trends were noticed between soil solution and plant. The impact of compost addition on the transfer of trace elements to plants remains unclear: compost enhanced the transfer of trace elements to soil solution in uncontaminated and naturally-enriched soils likely due to trace element input through the compost, but decreased the transfer in anthropogenically-contaminated soils likely due to adsorption processes. Therefore, glyphosate could potentially increase the exposure of trace elements through food consumption and their transfer to the ecosystem, particularly in uncontaminated and weakly contaminated soils. In highly contaminated soils, compost could mitigate the glyphosate-induced enhancement of trace element mobility to soil solution.

Abstract Image

施用草甘膦可能会影响微量元素从土壤向土壤溶液和植物的转移。
土壤-植物系统中微量元素的动态取决于多个参数,包括来自天然或合成有机物的螯合有机化合物。在这项研究中,我们在温室实验中评估了最常见的农药之一草甘膦对微量元素流动性的影响,并考虑了对比土壤(未受污染、人为污染和天然富集土壤)。试验采用了四种模式:一种是不施用草甘膦的对照组,两种是施用不同剂量草甘膦的对照组(分别为田间授权剂量的 1 倍和 3 倍),一种是添加堆肥的对照组,以评估堆肥减轻草甘膦对微量元素迁移率影响的潜在能力。在土壤溶液中测量了微量元素和草甘膦的浓度,并在实验结束时测定了植物中的微量元素含量。结果表明,虽然草甘膦在土壤溶液中的浓度迅速下降,但草甘膦的施用仍然影响了微量元素向土壤溶液和植物的转移(分别增加了 12 倍和 5.2 倍)。这种影响在很大程度上取决于所考虑的特定元素和土壤类型。例如,在未受污染的土壤中,草甘膦尤其会增加土壤溶液中锰、钴、锌、钼和铅的移动。随着土壤污染程度的增加,这种效应平均降低了 2.5 倍。微量元素从土壤向植物的转移也呈现出类似的趋势(即与未受污染的土壤相比,受污染最严重的土壤中的微量元素平均减少了 2.2 倍)。然而,在天然富集土壤中,土壤溶液和植物之间的转移趋势相反。堆肥的添加对微量元素向植物转移的影响尚不清楚:在未受污染和天然富集的土壤中,堆肥增强了微量元素向土壤溶液的转移,这可能是由于通过堆肥输入了微量元素,但在人为污染的土壤中,堆肥减少了微量元素向土壤溶液的转移,这可能是由于吸附过程。因此,草甘膦可能会通过食物摄入增加微量元素的暴露量,并将其转移到生态系统中,特别是在未受污染和受轻度污染的土壤中。在高度污染的土壤中,堆肥可以减轻草甘膦引起的微量元素在土壤溶液中流动性的增强。
本文章由计算机程序翻译,如有差异,请以英文原文为准。
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来源期刊
Chemosphere
Chemosphere 环境科学-环境科学
CiteScore
15.80
自引率
8.00%
发文量
4975
审稿时长
3.4 months
期刊介绍: Chemosphere, being an international multidisciplinary journal, is dedicated to publishing original communications and review articles on chemicals in the environment. The scope covers a wide range of topics, including the identification, quantification, behavior, fate, toxicology, treatment, and remediation of chemicals in the bio-, hydro-, litho-, and atmosphere, ensuring the broad dissemination of research in this field.
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