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首页> 外文期刊>Pest Management Science >Photolytic versus microbial degradation of clomazone in a flooded California rice field soil
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Photolytic versus microbial degradation of clomazone in a flooded California rice field soil

机译:淹水的加利福尼亚稻田土壤中的广灭灵的光解与微生物降解

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摘要

BACKGROUND: Clomazone is a popular herbicide used on California rice fields and exhibits rapid anaerobic microbial degradation (t_(1/2) = 7.9 days). To test the potential of direct and indirect photolytic degradation as a cofactor in the overall degradation rate, sacrificial time-series microcosms were amended with water, non-sterilized soil + water and sterilized soil + water. Clomazone was added to each microcosm, which was then exposed to natural and artificial sunlight over 35 days. Water and acetonitrile extracts were analyzed for clomazone and metabolites via LC/MS/MS. RESULTS: The calculated pseudo-first-order degradation rate constants (k) were k_(water) = 0-0.005 ±0.003 day-1, k_(sterile )= 0-0.005 ± 0.003 day~(-1) and k_(non-sterile) = 0.010 ± 0.002-0.044 ± 0.007 day~(-1), depending on light type. The formation of ring-open clomazone, a microbial metabolite, correlated with clomazone degradation. Trace amounts of 5-hydroxyclomazone (m/z = 256 →125), aromatic hydroxyclomazone (m/z = 256 →141) and an unknown product [m/z = 268 -?- 125) were observed. CONCLUSIONS: The photolytic degradation rate depends on both light type and the quality of the chromophores that induce indirect photolysis. Microbial degradation was found to be sensitive to temperature fluctuations. Overall, microbes are shown to be more detrimental to the environmental fate of clomazone than photolysis.
机译:背景:广灭灵是加利福尼亚稻田上流行的除草剂,并表现出快速的厌氧微生物降解(t_(1/2)= 7.9天)。为了测试直接和间接光解降解作为总降解速率中辅助因子的潜力,对牺牲时间序列缩影进行了修正,分别使用水,未灭菌的土壤+水和灭菌的土壤+水。将广灭灵添加到每个缩影中,然后在35天之内暴露于自然和人造阳光下。通过LC / MS / MS分析水和乙腈提取物的广灭灵和代谢物。结果:计算的拟一阶降解速率常数(k)为k_(水)= 0-0.005±0.003 day-1,k_(无菌)= 0-0.005±0.003 day〜(-1)和k_(非-无菌)= 0.010±0.002-0.044±0.007天〜(-1),具体取决于光源类型。开环的广灭灵(一种微生物代谢产物)的形成与广灭灵的降解有关。观察到痕量的5-羟基clomazone(m / z = 256→125),芳香族羟基clomazone(m / z = 256→141)和未知产物[m / z = 268-?-125]。结论:光解降解速率取决于光类型和诱导间接光解的生色团的质量。发现微生物降解对温度波动敏感。总体而言,与光解相比,微生物显示出对广灭灵的环境危害更大。

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