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Fate of chlorpyrifos, atrazine, and metolachlor from nonpoint sources in wetland mesocosms.

机译:毒死rif,阿特拉津和甲草胺的命运来自湿地中观世界的非点源。

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Constructed wetland mesocosms (59--73 m x 14 m) were amended on two different occasions (one for the insecticide chlorpyrifos, the other for a mixture of the herbicides atrazine and metolachlor). Following each pesticide amendment, a simulated cropland runoff and rainfall event equal to three volume additions was imposed on each wetland. Targeted concentrations of chlorpyrifos were 73 mug/L, 147 mug/L, and 733 mug/L, while targeted concentrations for both atrazine and metolachlor were 73 mug/L and 147 mug/L in addition to an unamended control (0 mug/L). Water, sediment, and plant samples were collected weekly for the duration of each experiment (chlorpyrifos, 84 d; atrazine and metolachlor, 35 d). Samples were collected from sites longitudinally distributed within each wetland and analyzed for the respective pesticides using gas chromatography.; Chlorpyrifos rapidly sorbed to sediment and plant material, and the half-life in water, in this research, ranged from 5--13 d. Approximately 47--65% of measured chlorpyrifos was within the first 30--36 m (from inflow) of wetland mesocosms. Approximately 55% and 25% of measured chlorpyrifos mass were retained by sediments and plant material, respectively. Between 17 and 42% of the measured atrazine mass was within the first 30--36 m (from inflow) of wetlands. Atrazine concentrations were below analytical limits of quantification (0.05 mug/L) in all sediment and plant samples collected for this research. Atrazine aqueous half-lives ranged from 16--48 d. Between 7--25% of measured metolachlor mass was in the first 30--36 m (from inflow) of wetlands immediately following application and simulated rainfall. Approximately 10% of measured metolachlor mass was in plant samples.; According to results from this research, downstream or receiving system impacts could be mitigated by using constructed wetlands as "buffers" for agricultural pesticide runoff. This research provides fundamental answers concerning constructed wetland capabilities that are necessary for constructing field-scale systems within agricultural watersheds.
机译:在两种不同的情况下修改了人工湿地的中观世界(59--73 m x 14 m)(一种用于杀虫剂毒死,,另一种用于除草剂r去津和甲草胺的混合物)。每次修改农药后,在每个湿地上施加相当于三个体积增加量的模拟农田径流和降雨事件。毒死rif的目标浓度为73杯/升,147杯/升和733杯/升,而阿特拉津和甲草胺的目标浓度除未经修正的对照(0杯/升外)分别为73杯/升和147杯/升。 )。在每个实验期间,每周都要收集水,沉积物和植物样品(毒死rif,84 d;阿特拉津和甲草胺,35 d)。从每个湿地内纵向分布的地点收集样品,并使用气相色谱法分析相应的农药。毒死rif迅速吸收到沉积物和植物材料上,在本研究中,水中的半衰期为5--13 d。大约47--65%的毒死rif在湿地中观世界的前30--36 m(来自流入)之内。沉积物和植物材料分别保留了约55%和25%的毒死material质量。测得的at去津质量的17%至42%在湿地的前30--36 m(来自流入)之内。本研究收集的所有沉积物和植物样品中的r去津浓度均低于定量分析极限(0.05杯/升)。阿特拉津的水性半衰期为16--48 d。在施用和模拟降雨后的头30--36 m(来自流入)湿地中,测得的异丙甲草胺质量在7--25%之间。大约有10%的异丙甲草胺质量存在于植物样品中。根据这项研究的结果,可以通过使用人工湿地作为农业农药径流的“缓冲”来减轻下游或接收系统的影响。这项研究提供了有关人工湿地能力的基本答案,这对于在农业流域内构建田间规模系统是必需的。

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