Potter Thomas L, Bosch David D, Joo Hyun, Schaffer Bruce, Muñoz-Carpena Rafael
USDA-ARS, Southeast Watershed Research Lab., P.O. Box 748, Tifton, GA 31793, USA.
J Environ Qual. 2007 Jul 17;36(5):1301-9. doi: 10.2134/jeq2006.0526. Print 2007 Sep-Oct.
At Florida's southeastern tip, sweet corn (Zea Mays) is grown commercially during winter months. Most fields are treated with atrazine (6-chloro-N-ethyl-N'-[1-methylethyl]-1,3,5-triazine-2,4-diamine). Hydrogeologic conditions indicate a potential for shallow groundwater contamination. This was investigated by measuring the parent compound and three degradates--DEA (6-chloro-N-[1-methylethyl]-1,3,5-triazine-2,4-diamine), DIA (6-chloro-N-ethyl)-1,3,5-triazine-2,4-diamine, and HA (6-hydroxy-N-[1-methylethyl]-1,3,5-triazine-2,4-diamine)--in water samples collected beneath sweet corn plots treated annually with the herbicide. During the study, a potential mitigation measure (i.e., the use of a cover crop, Sunn Hemp [Crotalaria juncea L.], during summer fallow periods followed by chopping and turning the crop into soil before planting the next crop) was evaluated. Over 3.5 yr and production of four corn crops, groundwater monitoring indicated leaching of atrazine, DIA, and DEA, with DEA accounting for more than half of all residues in most samples. Predominance of DEA, which increased after the second atrazine application, was interpreted as an indication of rapid and extensive atrazine degradation in soil and indicated that an adapted community of atrazine degrading organisms had developed. A companion laboratory study found a sixfold increase in atrazine degradation rate in soil after three applications. Groundwater data also revealed that atrazine and degradates concentrations were significantly lower in samples collected beneath cover crop plots when compared with concentrations below fallow plots. Together, these findings demonstrated a relatively small although potentially significant risk for leaching of atrazine and its dealkylated degradates to groundwater and that the use of a cover crop like Sunn Hemp during summer months may be an effective mitigation measure.
在佛罗里达州的最南端,甜玉米(玉米)在冬季进行商业化种植。大多数田地都使用莠去津(6-氯-N-乙基-N'-[1-甲基乙基]-1,3,5-三嗪-2,4-二胺)进行处理。水文地质条件表明存在浅层地下水污染的可能性。通过测量母体化合物和三种降解产物——DEA(6-氯-N-[1-甲基乙基]-1,3,5-三嗪-2,4-二胺)、DIA(6-氯-N-乙基)-1,3,5-三嗪-2,4-二胺和HA(6-羟基-N-[1-甲基乙基]-1,3,5-三嗪-2,4-二胺)——在每年用除草剂处理的甜玉米地块下方采集的水样中进行了调查。在研究期间,评估了一种潜在的缓解措施(即在夏季休耕期种植覆盖作物印度菽麻[猪屎豆属植物],然后在下一季作物种植前将作物切碎并翻入土壤中)。在超过3.5年的时间里,种植了四茬玉米,地下水监测表明莠去津、DIA和DEA有淋溶现象,在大多数样品中,DEA占所有残留量的一半以上。DEA的优势在第二次施用莠去津后增加,这被解释为土壤中莠去津快速广泛降解的迹象,表明已经形成了适应的莠去津降解生物群落。一项配套的实验室研究发现,三次施用后土壤中莠去津降解率提高了六倍。地下水数据还显示,与休耕地块下方采集的样品相比,覆盖作物地块下方采集的样品中莠去津及其脱烷基降解产物的浓度显著更低。综合来看,这些发现表明莠去津及其脱烷基降解产物向地下水淋溶的风险相对较小但可能很大,并且在夏季使用印度菽麻等覆盖作物可能是一种有效的缓解措施。