Paszko Tadeusz, Muszyński Paweł, Materska Małgorzata, Bojanowska Monika, Kostecka Małgorzata, Jackowska Izabella
Department of Chemistry, University of Life Sciences, Lublin, Poland.
Environ Toxicol Chem. 2016 Feb;35(2):271-86. doi: 10.1002/etc.3212. Epub 2016 Jan 8.
The primary aim of the present review on phenoxyalkanoic acid herbicides-2-(2,4-dichlorophenoxy) acetic acid (2,4-D), 2-(4-chloro-2-methylphenoxy) acetic acid (MCPA), (2R)-2-(2,4-dichlorophenoxy) propanoic acid (dichlorprop-P), (2R)-2-(4-chloro-2-methylphenoxy) propanoic acid (mecoprop-P), 4-(2,4-dichlorophenoxy) butanoic acid (2,4-DB), and 4-(4-chloro-2-methylphenoxy) butanoic acid (MCPB)-was to compare the extent of their adsorption in soils and degradation rates to assess their potential for groundwater contamination. The authors found that adsorption decreased in the sequence of 2,4-DB > 2,4-D > MCPA > dichlorprop-P > mecoprop-P. Herbicides are predominantly adsorbed as anions-on organic matter and through a water-bridging mechanism with adsorbed Fe cations-and their neutral forms are adsorbed mainly on organic matter. Adsorption of anions of 2,4-D, MCPA, dichlorprop-P, and mecoprop-P is inversely correlated with their lipophilicity values, and modeling of adsorption of the compounds based on this relationship is possible. The predominant dissipation mechanism of herbicides in soils is bacterial degradation. The contribution of other mechanisms, such as degradation by fungi, photodegradation, or volatilization from soils, is much smaller. The rate of bacterial degradation decreased in the following order: 2,4-D > MCPA > mecoprop-P > dichlorprop-P. It was found that 2,4-D and MCPA have the lowest potential for leaching into groundwater and that mecoprop-P and dichlorprop-P have slightly higher potential. Because of limited data on adsorption and degradation of 2,4-DB and MCPB, estimation of their leaching potential was not possible.
本综述对苯氧基链烷酸类除草剂——2-(2,4-二氯苯氧基)乙酸(2,4-D)、2-(4-氯-2-甲基苯氧基)乙酸(MCPA)、(2R)-2-(2,4-二氯苯氧基)丙酸(二氯丙酸-P)、(2R)-2-(4-氯-2-甲基苯氧基)丙酸(甲羧除草醚-P)、4-(2,4-二氯苯氧基)丁酸(2,4-DB)和4-(4-氯-2-甲基苯氧基)丁酸(MCPB)——的主要目的是比较它们在土壤中的吸附程度和降解速率,以评估它们对地下水污染的可能性。作者发现吸附作用按2,4-DB>2,4-D>MCPA>二氯丙酸-P>甲羧除草醚-P的顺序降低。除草剂主要以阴离子形式吸附在有机物上,并通过与吸附的铁阳离子形成水桥机制进行吸附,其中性形式主要吸附在有机物上。2,4-D、MCPA、二氯丙酸-P和甲羧除草醚-P的阴离子吸附与它们的亲脂性值呈负相关,基于这种关系对化合物的吸附进行建模是可行的。除草剂在土壤中的主要消散机制是细菌降解。其他机制的贡献,如真菌降解、光降解或从土壤中挥发,要小得多。细菌降解速率按以下顺序降低:2,4-D>MCPA>甲羧除草醚-P>二氯丙酸-P。研究发现,2,4-D和MCPA渗入地下水的可能性最低,而甲羧除草醚-P和二氯丙酸-P的可能性略高。由于关于2,4-DB和MCPB吸附和降解的数据有限,无法估计它们的淋溶潜力。