Mazanti L, Rice C, Bialek K, Sparling D, Stevenson C, Johnson W E, Kangas P, Rheinstein J
U.S. Department of Agriculture, Natural Resources Conservation Service, Wetland Science Institute, 12311 Beech Forest Rd., Laurel, Maryland 20708, USA.
Arch Environ Contam Toxicol. 2003 Jan;44(1):67-76. doi: 10.1007/s00244-002-1259-3.
Dissipation processes are described for a combination of commonly used pesticides-atrazine (6-chloro-4-ethylamino-6-isopropylamino- s-triazine), metolachlor (2-chloro- N-[2-ethyl-6-methyl-phenyl]- N-[2-methoxy-1-methylethyl] acetamide), and chlorpyrifos ( O-O diethyl O-[3,5,6-trichloro-2-pyridinyl] phosphorothioate)-in a laboratory and outdoor pond systems. Dosing rates and timing were designed to duplicate those common in the mid-Atlantic Coastal Plain, USA. Treatments ranged from 2 and 2.5 mg/L to 0.2 and 0.25 mg/L respectively for atrazine and metolachlor, and chlorpyrifos was added at 1.0 and 0.1 mg/L in the aquaria and at 0.1 mg/L in the outdoor macrocosms. Chlorpyrifos disappearance was rapid in all of the systems and followed a two-phase sequence. Initial half-lives varied from 0.16 day to 0.38 day and showed similar rates in the aquaria and the outdoor systems. The second phase of the chlorpyrifis loss pattern was slower (18-20 days) in all the treatments except for the low herbicide treatment in the outdoor test, where it was 3.4 days. Compared to the outdoor system, herbicide losses were much slower in the aquaria, e.g., 150 days for atrazine and 55 days for metolachlor, and no appreciable loss of herbicide was apparent in the high-treated aquaria. In the outdoor systems, the half-lives for the low herbicide treatment were 27 days and 12 days, respectively, for atrazine and metolachlor, and 48 and 20 days, respectively for the high herbicide-treated pond. Very low levels of CIAT (6-amino-2-chloro-4-iso-propylamino- s-triazine) and CEAT (2-chloro-4-ethylamino-6-ethylamino- s-triazine), degradation products of atrazine, were observed in the outdoor studies.
在实验室和室外池塘系统中,描述了常用农药阿特拉津(6-氯-4-乙氨基-6-异丙氨基-s-三嗪)、异丙甲草胺(2-氯-N-[2-乙基-6-甲基苯基]-N-[2-甲氧基-1-甲基乙基]乙酰胺)和毒死蜱(O,O-二乙基-O-[3,5,6-三氯-2-吡啶基]硫代磷酸酯)组合的消散过程。给药速率和时间设计为与美国中大西洋沿海平原常见的情况相同。阿特拉津和异丙甲草胺的处理浓度分别为2和2.5毫克/升至0.2和0.25毫克/升,毒死蜱在水族箱中的添加浓度为1.0和0.1毫克/升,在室外大型生态系统中的添加浓度为0.1毫克/升。毒死蜱在所有系统中的消失速度都很快,且遵循两阶段过程。初始半衰期从0.16天到0.38天不等,在水族箱和室外系统中的速率相似。除室外试验中的低除草剂处理(其半衰期为3.4天)外,毒死蜱损失模式的第二阶段在所有处理中都较慢(18 - 20天)。与室外系统相比,除草剂在水族箱中的损失要慢得多,例如阿特拉津为150天,异丙甲草胺为55天,在高浓度处理的水族箱中没有明显的除草剂损失。在室外系统中,低除草剂处理的阿特拉津和异丙甲草胺半衰期分别为27天和12天,高除草剂处理池塘的半衰期分别为48天和20天。在室外研究中观察到了阿特拉津的降解产物CIAT(6-氨基-2-氯-4-异丙氨基-s-三嗪)和CEAT(2-氯-4-乙氨基-6-乙氨基-s-三嗪)的极低水平。