Konda L N, Pásztor Z
Institute for Veterinary Medicinal Products, 8 Szállás Street, H-1107 Budapest, Hungary.
J Agric Food Chem. 2001 Aug;49(8):3859-63. doi: 10.1021/jf010187t.
The environmental behavior, movement, distribution, persistence, and runoff by rainfall of the pesticides acetochlor, atrazine, chlorpyrifos, and propisochlor were studied under field conditions during a five-month period at normal weather conditions. The pesticide concentrations in soil depths of 0-5 and 5-20 cm, and in sediment and runoff water samples (collected from an artificial reservoir built in the lower part of the experimental plot) were measured every second week and following every runoff event. The contamination of a stream running across the lowest part of the plot was also monitored. The weather conditions were also recorded at the experimental site. The pesticide residues were quantified by a capillary gas chromatograph equipped with a nitrogen phosphorus selective detector (GC-NPD). There was a consistent decrease in pesticide residues in the 0-5 cm soil layer with time after spaying. At 140 days after treatment only atrazine and chlorpyrifos were present; acetochlor and propisochlor were not detected in this soil layer. Atrazine and chlorpyrifos in the soil at a depth of 5-20 cm were detectable during the whole experimental interval, whereas acetochlor and propisochlor concentrations were below the limit of detection. Pesticide losses by the surface runoff process and the contamination of the stream were closely related to the time of rainfall elapsed after treatment and amount of rain at the experimental plots. Losses were primarily dependent on surface rainfall volume and intensity. The maximum detected residues of atrazine and acetochlor in stream water were 1 order of magnitude higher than the maximum residue limit specified by the European Union (EU) for environmental and drinking water (0.1 microg/L for individual compounds and 0.5 microg/L for total pesticides). Chlorpyrifos and propisochlor were not detected in this matrix.
在正常天气条件下,于田间条件下对农药乙草胺、莠去津、毒死蜱和异丙草胺的环境行为、迁移、分布、持久性及降雨径流情况进行了为期五个月的研究。每隔两周以及每次径流事件后,测量0至5厘米和5至20厘米土壤深度中的农药浓度,以及沉积物和径流水样(从试验区下部建造的人工水库采集)中的农药浓度。还对流经试验区最下部的一条溪流的污染情况进行了监测。同时在试验场地记录天气状况。农药残留通过配备氮磷选择性检测器的毛细管气相色谱仪(GC-NPD)进行定量分析。喷施后,0至5厘米土壤层中的农药残留随时间持续减少。处理后140天时,该土壤层中仅存在莠去津和毒死蜱;未检测到乙草胺和异丙草胺。在整个试验期间,5至20厘米深度土壤中的莠去津和毒死蜱均可检测到,而乙草胺和异丙草胺的浓度低于检测限。通过地表径流过程造成的农药损失以及溪流的污染与处理后降雨时间和试验区降雨量密切相关。损失主要取决于地表降雨量和降雨强度。溪水中检测到的莠去津和乙草胺的最大残留量比欧盟规定的环境和饮用水最大残留限量(单个化合物为0.1微克/升,总农药为0.5微克/升)高1个数量级。在该基质中未检测到毒死蜱和异丙草胺。