Identification of point and nonpoint emission sources of neonicotinoid pollution in regional surface water

被引:26
作者
Chen, Yuanchen [1 ,2 ]
Ling, Jun [1 ]
Yu, Wenfei [1 ]
Zhang, Li [1 ]
Wu, Ruxin [1 ]
Yang, Dan [1 ]
Qu, Jiajia [1 ]
Jin, Hangbiao [1 ,2 ]
Tao, Zhen [1 ]
Shen, Yuexin [1 ]
Meng, Ruirui [1 ]
Yu, Jingtong [1 ]
Zheng, Qingyi [1 ]
Shen, Guofeng [3 ]
Du, Wei [4 ]
Sun, Haitong [5 ,6 ]
Zhao, Meirong [1 ]
机构
[1] Zhejiang Univ Technol, Coll Environm, Key Lab Microbial Technol Ind Pollut Control Zheji, Hangzhou 310032, Zhejiang, Peoples R China
[2] Ecoind Innovat Inst ZJUT, Innovat Res Ctr Adv Environm Technol, Quzhou 324018, Peoples R China
[3] Peking Univ, Coll Urban & Environm Sci, Minist Educ, Lab Earth Surface Proc, Beijing 100871, Peoples R China
[4] Kunming Univ Sci &Technol, Fac Environm Sci & Engn, Yunnan Prov Key Lab Soil Carbon Sequestrat & Pollu, Kunming 650500, Yunnan, Peoples R China
[5] Univ Cambridge, Yusuf Hamied Dept Chem, Cambridge CB2 1EW, England
[6] Univ Cambridge, Dept Earth Sci, Cambridge CB2 3EQ, England
基金
浙江省自然科学基金; 中国国家自然科学基金;
关键词
Insecticides; Farmland; WWTPs; Emission source; Migration; Distribution; WASTE-WATER; TREATMENT PLANTS; INSECTICIDES; RIVER; PESTICIDES; LAKES;
D O I
10.1016/j.watres.2023.120863
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Neonicotinoid insecticides are widely applied in farmland, with high detection rates in soils and surface waters, posing potential risks to biodiversity and human health. As a nonpoint emission, surface runoff is widely regarded as the major source of neonicotinoid pollution in surface waters, but few studies have determined the point source contribution to rivers that may be primarily from wastewater treatment plants (WWTPs). Here, we collected the surface water from eight river basins in Zhejiang Province of China and quantified residual con-centrations of eight widely commercialized neonicotinoids. Four of these were detected in all samples, with concentrations of dinotefuran and nitenpyram of 119 +/- 166 and 87.6 +/- 25.3 ng/L, respectively, representing more than 90 % of the total (282 +/- 174 ng/L). Neonicotinoid residues were higher in tributaries due to nearby farmland and more dilution effects in the mainstream, and the residues were higher in lower reaches which can be explained by the water flow direction. Significant spatial differences in neonicotinoid distribution between surface water and agricultural soils result from environmental factors (e.g., water turbidity, precipitation, temperature) impacting migration and transport processes. Neonicotinoid residues in surface water showed a significant positive correlation with total WWTP emissions after adjusting for environmental factors. Conversely, no significant association was observed with cropland density (a nonpoint emission source), indicating that point emission source (contributing 20.6 %) predominantly influenced neonicotinoid residue spatial variation in river basin-scale surface water.
引用
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页数:9
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