Spatial and temporal trends and flow dynamics of glyphosate and other pesticides within an agricultural watershed in Argentina

环境科学 分水岭 草甘膦 氨基甲基膦酸 杀虫剂 水文学(农业) 地表径流 地表水 空间变异性 弹簧(装置) 农学 生态学 生物 环境工程 地质学 机械工程 统计 机器学习 工程类 计算机科学 数学 岩土工程
作者
Débora Jesabel Pérez,Elena Okada,Eduardo De Gerónimo,Mirta L. Menone,Virginia Aparicio,José Luís Costa
出处
期刊:Environmental Toxicology and Chemistry [Wiley]
卷期号:36 (12): 3206-3216 被引量:97
标识
DOI:10.1002/etc.3897
摘要

Abstract In the present study, we evaluated the spatial and temporal trends of current‐use pesticides in surface water and sediments as well as their relationship with hydrological stream dynamics within the agricultural watershed of El Crespo stream (Buenos Aires Province, Argentina). We sampled 2 contrasting sites: site 1 (upstream), surrounded by agricultural lands, and site 2 (downstream), surrounded by natural grasslands. Most of the applied pesticides (glyphosate, 2,4‐D, atrazine, tebuconazole, and imidacloprid) were detected at high frequencies in surface water samples at both sites. However, only glyphosate and aminomethylphosphonic acid (AMPA) were present at high concentrations and had a significant spatial–temporal trend. The highest concentrations were found during spring 2014 at site 1, in association with the intense rains that occurred in that season. The fact that glyphosate and AMPA concentrations were higher than the rest of the studied compounds is closely related to the land use within the watershed, as glyphosate was the most applied herbicide during the fallow period of glyphosate‐resistant crops (soybean, maize). The pesticide mixture had a significant spatial–temporal trend, reaching the highest levels during storm flow events in spring 2014. The intensive rains in spring 2014 could be the main factor influencing stream hydrology and pesticide behavior at El Crespo watershed. The estimated annual pesticide losses were 3.11 g/ha at site 1 and 0.72 g/ha at site 2. This result indicates that an attenuation process could be decreasing pesticide loads during downstream transport from site 1 to site 2. Environ Toxicol Chem 2017;36:3206–3216. © 2017 SETAC
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