Martins J M, Chevre N, Spack L, Tarradellas J, Mermoud A
Laboratoire d'Hydrologie et Aménagements, IATE, Ecole Polytechnique Fédérale de Lausanne, EPFL, Switzerland.
Chemosphere. 2001 Nov;45(4-5):515-22. doi: 10.1016/s0045-6535(01)00040-6.
The degradation and ecotoxicity of sulfonylurea herbicide rimsulfuron and its major metabolites were examined in batch samples of an alluvial sandy loam and in freshwater. An HPLC-DAD method was adapted to simultaneously identify and quantify rimsulfuron and its metabolites, which was successfully validated by GC-MS analysis. In aqueous solutions, pure rimsulfuron was rapidly hydrolyzed into metabolite 1 (N-(4,6-dimethoxypyrimidin-2-yl)-N-(3-(ethylsulfonyl)-2-pyridinylurea)), which itself was transformed into the more stable metabolite 2 (N-((3-(ethylsulfonyl)-2-pyridinyl)-4,6-dimethoxy-2-pyrimidineamine)), with half-life (t(1/2)) values of 2 and 2.5 days, respectively. Hydrolysis was instantaneous under alkaline conditions (pH = 10). In aqueous suspensions of the alluvial soil (pH = 8), formulated rimsulfuron had a half-life of 7 days, whereas that of metabolite 1 was similar to that in water (about 3.5 days). The degradation of the two major metabolites was also studied in soil suspensions with the pure compounds at concentrations ranging from 1 to 10 mg l(-1). The half-life of metabolite 1 ranged from 3.9 to 5 days, close to the previous values. Metabolite 2 was more persistent and its degradation is strongly dependent on the initial concentration (C0): half-life values ranged from 8.1 to 55 days at 2-10 mg l(-1), respectively. These values are higher than those determined from the kinetics of metabolite 1 transformation into metabolite 2 (t(1/2) = 8-19 days). The ecotoxicity of the three chemicals was evaluated through their effect on Daphnia magna and Vibrio fischeri (Microtox bioassay). No effect was observed on D. magna with 24 and 48 h acute toxicity tests. Similarly, no toxic effect was observed with the Microtox test for the three chemicals in the range of concentrations tested that included the field application dose. Thus, being of low persistence and lacking acute toxicity, these chemicals present a low environmental risk. However, chronic effects should be studied in order to confirm the safety of rimsulfuron and its major metabolites.
在冲积砂壤土和淡水中的批次样品中,研究了磺酰脲类除草剂玉嘧磺隆及其主要代谢产物的降解和生态毒性。采用高效液相色谱 - 二极管阵列检测法(HPLC - DAD)同时鉴定和定量玉嘧磺隆及其代谢产物,并通过气相色谱 - 质谱联用(GC - MS)分析成功验证。在水溶液中,纯玉嘧磺隆迅速水解为代谢产物1(N - (4,6 - 二甲氧基嘧啶 - 2 - 基) - N - (3 - (乙基磺酰基) - 2 - 吡啶基脲)),其自身又转化为更稳定的代谢产物2(N - ((3 - (乙基磺酰基) - 2 - 吡啶基) - 4,6 - 二甲氧基 - 2 - 嘧啶胺)),半衰期(t(1/2))值分别为2天和2.5天。在碱性条件(pH = 10)下水解瞬间发生。在冲积土壤(pH = 8)的水悬浮液中,制剂玉嘧磺隆的半衰期为7天,而代谢产物1的半衰期与在水中相似(约3.5天)。还研究了在浓度范围为1至10 mg l(-1)的纯化合物土壤悬浮液中两种主要代谢产物的降解情况。代谢产物1的半衰期为3.9至5天,接近先前的值。代谢产物2更持久,其降解强烈依赖于初始浓度(C0):在2至10 mg l(-1)时,半衰期值分别为8.1至55天。这些值高于从代谢产物1转化为代谢产物2的动力学测定值(t(1/2) = 8 - 19天)。通过它们对大型溞和费氏弧菌(微毒性生物测定)的影响评估了这三种化学物质的生态毒性。在24小时和48小时急性毒性试验中,未观察到对大型溞有影响。同样,在所测试的包括田间施用剂量的浓度范围内,微毒性试验对这三种化学物质均未观察到毒性作用。因此,由于这些化学物质持久性低且缺乏急性毒性,它们对环境的风险较低。然而,应研究其慢性影响以确认玉嘧磺隆及其主要代谢产物的安全性。