Laboratory assessment of atrazine and fluometuron degradation in soils from a constructed wetland

被引:54
作者
Weaver, MA
Zablotowicz, RM
Locke, MA
机构
[1] USDA ARS, So Weed Sci Res Unit, Stoneville, MS 38776 USA
[2] USDA ARS, Water Qual & Ecol Proc Res Unit, Oxford, MS 38655 USA
关键词
atrazine; fluometuron; wetland soils; herbicide fate; herbicide sorption; herbicide degradation;
D O I
10.1016/j.chemosphere.2004.08.013
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Constructed wetlands offer promise for removal of nonpoint source contaminants such as herbicides from agricultural runoff. Laboratory studies assessed the potential of soils to degrade and sorb atrazine and fluometuron within a recently constructed wetland. The surface 3 cm of soil was sampled from two cells of a Mississippi Delta constructed wetland; one shallow area disturbed only hydrologically, and the second excavated to provide greater water-holding capacity. The excavated area was more acidic on average (pH 4.85 versus 5.21), but otherwise the physical properties and general microbial enzyme activities in the two areas were similar. Soils were treated with 84 and 68 mug kg(-1) soil C-14-ring labeled atrazine and fluometuron, respectively, and incubated under either saturated (88%,, moisture, w:w) or flooded (1 cm standing water) conditions. Soils were sampled over 32 days and extracted for herbicide and metabolite analysis. Under saturated conditions, fluometuron metabolized to desmethylfluometuron (DMF) with a half-life equal 25-27 days. However, under flooded conditions, the half-life of fluometuron was more than 175 days. Atrazine dissipated rapidly in saturated and flooded soil with a half-life of approximately 23 days, but only 10% of atrazine was mineralized to CO2. The overall atrazine and fluometuron dissipation rates were similar between the two cells, but each area had a different pattern of metabolite accumulation. The major route of atrazine dissipation was incorporation of atrazine residues into methanol-nonextractable (soil-bound) components, with minimal extractable metabolite accumulation. A mixed-mode extractant (potassium phosphate: acetonitrile) recovered greater amounts of C-14-residues from atrazine-treated soils, suggesting that hydrolysis of atrazine to hydroxylated metabolites was a major component of the bound residues. These studies indicate the potential for herbicide dissipation in wetland soils and a differential effect of flooding on the fate of these herbicides. Published by Elsevier Ltd.
引用
收藏
页码:853 / 862
页数:10
相关论文
共 45 条
[1]   Atrazine mineralization potential in two wetlands [J].
Anderson, KL ;
Wheeler, KA ;
Robinson, JB ;
Tuovinen, OH .
WATER RESEARCH, 2002, 36 (19) :4785-4794
[2]  
BARTHA RICHARD, 1965, SOIL SCI, V100, P68, DOI 10.1097/00010694-196507000-00011
[3]   CHEMICAL VERSUS MICROBIAL-DEGRADATION OF CYANAZINE AND ATRAZINE IN SOILS [J].
BLUMHORST, MR ;
WEBER, JB .
PESTICIDE SCIENCE, 1994, 42 (02) :79-84
[4]   Pollutant removal from municipal sewage lagoon effluents with a free-surface wetland [J].
Cameron, K ;
Madramootoo, C ;
Crolla, A ;
Kinsley, C .
WATER RESEARCH, 2003, 37 (12) :2803-2812
[5]   MICROBIAL METABOLIC-ACTIVITY IN SOIL AS MEASURED BY DEHYDROGENASE DETERMINATIONS [J].
CASIDA, LE .
APPLIED AND ENVIRONMENTAL MICROBIOLOGY, 1977, 34 (06) :630-636
[6]   DIFFERENCES IN HERBICIDE ADSORPTION ON SOIL USING SEVERAL SOIL-PH MODIFICATION TECHNIQUES [J].
CLAY, SA ;
KOSKINEN, WC ;
ALLMARAS, RR ;
DOWDY, RH .
JOURNAL OF ENVIRONMENTAL SCIENCE AND HEALTH PART B-PESTICIDES FOOD CONTAMINANTS AND AGRICULTURAL WASTES, 1988, 23 (06) :559-573
[7]   Long-distance transport of gases in plants: a perspective on internal aeration and radial oxygen loss from roots [J].
Colmer, TD .
PLANT CELL AND ENVIRONMENT, 2003, 26 (01) :17-36
[8]  
Comber SDW, 1999, PESTIC SCI, V55, P696, DOI 10.1002/(SICI)1096-9063(199907)55:7&lt
[9]  
696::AID-PS11&gt
[10]  
3.0.CO