Williams G M, Harrison I, Carlick C A, Crowley O
British Geological Survey, Keyworth, Nottingham, NG12 5GG, UK.
J Contam Hydrol. 2003 Jul;64(3-4):253-67. doi: 10.1016/S0169-7722(02)00206-1.
Natural attenuation of the chiral pesticide mecoprop [2-(2-methyl-4-chlorophenoxy)propionic acid] has been studied by determining changes in its enantiomeric fraction in different redox environments down gradient of a landfill in the Lincolnshire Limestone. Previous studies have shown that mecoprop degrades predominantly aerobically and that differences in the biological behaviour of the two enantiomers will change their relative proportions during biodegradation. Originally deposited as a racemic mixture, there has been no change in the enantiomeric fraction in the most polluted part of the landfill plume where conditions are sulphate reducing/methanogenic. In the nitrate-reducing zone, the proportion of (S)-mecoprop increases, suggesting preferential degradation of (R)-mecoprop; while in the aerobic zone, the proportion of (R)-mecoprop increases, suggesting faster degradation of (S)-mecoprop. Mecoprop persistence in the confined Lincolnshire Limestone further downdip is explained by inhibition of degradation in sulphate-reducing conditions, which develop naturally. Laboratory microcosm experiments using up to 10 mg l(-1) of mecoprop confirm these inferences and show that under aerobic conditions, (S)-mecoprop and (R)-mecoprop degrade with zero-order kinetics at rates of 1.90 and 1.32 mg l(-1) day(-1), respectively. Under nitrate-reducing conditions (S)-mecoprop does not degrade, but (R)-mecoprop degrades with zero-order kinetics at 0.65 mg l(-1) day(-1) to produce a stoichiometric equivalent amount of 4-chloro-2-methylphenol. This metabolite only degrades when the (R)-mecoprop has disappeared. The addition of nitrate to a dormant iron-reducing microcosm devoid of nitrate stimulated anaerobic degradation of (R)-mecoprop after a lag period of 21 days. There was no evidence for enantiomeric inversion. The study demonstrates the sensitivity of changes in enantiomeric fraction for detecting natural attenuation, and reveals subtle differences in mecoprop degradation in different redox environments within the Lincolnshire Limestone aquifer.
通过测定林肯郡石灰岩地区一个垃圾填埋场下游不同氧化还原环境中手性农药甲草胺[2-(2-甲基-4-氯苯氧基)丙酸]对映体分数的变化,对其天然衰减进行了研究。先前的研究表明,甲草胺主要在有氧条件下降解,并且两种对映体在生物降解过程中的生物学行为差异会改变它们的相对比例。最初以消旋混合物形式沉积,在垃圾填埋场羽流中污染最严重的区域(那里的条件是硫酸盐还原/产甲烷),对映体分数没有变化。在硝酸盐还原区,(S)-甲草胺的比例增加,表明(R)-甲草胺优先降解;而在好氧区,(R)-甲草胺的比例增加,表明(S)-甲草胺降解更快。甲草胺在林肯郡石灰岩下游更深处的受限区域中的持久性可以通过自然形成的硫酸盐还原条件下对降解的抑制来解释。使用高达10 mg l(-1)甲草胺的实验室微观实验证实了这些推断,并表明在好氧条件下,(S)-甲草胺和(R)-甲草胺以零级动力学降解,降解速率分别为1.90和1.32 mg l(-1) day(-1)。在硝酸盐还原条件下,(S)-甲草胺不降解,但(R)-甲草胺以零级动力学降解,降解速率为0.65 mg l(-1) day(-1),生成化学计量当量的4-氯-2-甲基苯酚。这种代谢产物只有在(R)-甲草胺消失后才会降解。向缺乏硝酸盐的休眠铁还原微观体系中添加硝酸盐,在21天的滞后期后刺激了(R)-甲草胺的厌氧降解。没有对映体转化的证据。该研究证明了对映体分数变化在检测天然衰减方面的敏感性,并揭示了林肯郡石灰岩含水层中不同氧化还原环境中甲草胺降解的细微差异。