Schulz Ralf, Moore Matt T, Bennett Erin R, Farris Jerry L, Smith Sammie, Cooper Charles M
U.S. Department of Agriculture-Agricultural Research Service, National Sedimentation Laboratory, PO. Box 1157, Oxford, Mississippi 38655, USA.
Environ Toxicol Chem. 2003 Jun;22(6):1262-8.
Methyl parathion (MeP) was introduced into constructed wetlands for the purpose of assessing the influence of emergent vegetation on transport and toxicity of the pesticide. Two vegetated (90% cover, mainly Juncus effusus) and two nonvegetated wetland cells (each with a water body of 50 x 5.5 x 0.2 m) were each dosed with 6.5 m3 of water containing active ingredient of MeP at 6.6 mg/L associated with suspended soil at 400 mg/L to simulate a storm runoff event. Acute toxicity was assessed by sampling benthic macroinvertebrates at 5, 10, 20, and 40 m from the inlet before and 96 h after contamination and by in situ exposure of Chironomus tentans (Diptera) up to 24 h after contamination. Methyl parathion was detected throughout the nonvegetated wetland cells (70 microg/L at 20 m, 8 microg/L at 40 m), whereas the pesticide was not transported through the vegetated wetland cells (20 microg/L at 20 m, < 0.1 microg/L at 40 m). A three-way analysis of variance using contamination (repeated measure variable), location, and vegetation indicated significant negative effects of contamination on various insect taxa, such as mayfly nymphs and caddisfly larvae. Seven out of the total of 15 species revealed a significant contamination x vegetation effect, with individuals in the vegetated wetlands being less affected. Four species showed a significant contamination x location effect, confirming a higher toxicity in the inlet area of the wetlands. A significant three-way interaction of contamination x vegetation x location was detected in Chironomus sp., which was most strongly affected at the inlet area of the nonvegetated wetland cells. The in situ bioassay employing C. tentans confirmed the positive effect of wetland vegetation on MeP toxicity. These results demonstrate the importance of vegetation for pesticide mitigation in constructed wetlands.
为了评估挺水植物对农药迁移和毒性的影响,将甲基对硫磷(MeP)引入人工湿地。两个种植了植物(覆盖率90%,主要为灯心草)的湿地单元和两个未种植植物的湿地单元(每个单元有一个50×5.5×0.2米的水体)分别加入6.5立方米含有6.6毫克/升MeP活性成分且伴有400毫克/升悬浮土壤的水,以模拟暴雨径流事件。通过在污染前和污染后96小时从进水口起5米、10米、20米和40米处采集底栖大型无脊椎动物样本,以及在污染后长达24小时原位暴露摇蚊(双翅目)来评估急性毒性。在未种植植物的湿地单元中全程检测到甲基对硫磷(20米处为70微克/升,40米处为8微克/升),而该农药未通过种植了植物的湿地单元迁移(20米处为20微克/升,40米处<0.1微克/升)。使用污染(重复测量变量)、位置和植被进行的三因素方差分析表明,污染对各种昆虫类群有显著负面影响,如蜉蝣若虫和毛翅目幼虫。总共15个物种中有7个显示出显著的污染×植被效应,种植了植物的湿地中的个体受影响较小。4个物种显示出显著的污染×位置效应,证实湿地进水口区域毒性更高。在摇蚊属中检测到污染×植被×位置的显著三因素交互作用,在未种植植物的湿地单元进水口区域受影响最大。使用摇蚊进行的原位生物测定证实了湿地植被对MeP毒性的积极影响。这些结果证明了植被对人工湿地减轻农药污染的重要性。