Wang Cuiping, Ding Yunjie, Teppen Brian J, Boyd Stephen A, Song Cunyi, Li Hui
Department of Crop and Soil Sciences, Michigan State University, East Lansing, Michigan 48824, USA.
Environ Sci Technol. 2009 Aug 15;43(16):6171-6. doi: 10.1021/es900760m.
Lincomycin, an antibiotic widely administered as a veterinary medicine, is frequently detected in water. Little is known about the soil-water distribution of lincomycin despite the fact that this is a major determinant of its environmental fate and potential for exposure. Cation exchange was found to be the primary mechanism responsible for lincomycin sorption by soil clay minerals. This was evidenced by pH-dependent sorption, and competition with inorganic cations for sorptive sites. As solution pH increased, lincomycin sorption decreased. The extent of reduction was consistent with the decrease in cationic lincomycin species in solution. The presence of Ca2+ in solution diminished lincomycin sorption. Clay interlayer hydration status strongly influenced lincomycin adsorption. Smectites with the charge deficit from isomorphic substitution in tetrahedral layers (i.e., saponite) manifest a less hydrated interlayer environment resulting in greater sorption than that by octahedrally substituted clays (i.e., montmorillonite). Strongly hydrated exchangeable cations resulted in a more hydrated clay interlayer environment reducing sorption in the order of Ca- < K- < Cs-smectite. X-ray diffraction revealed that lincomycin was intercalated in smectite clay interlayers. Sorption capacity was limited by clay surface area rather than by cation exchange capacity. Smectite interlayer hydration was shown to be a major, yet previously unrecognized, factor influencing the cation exchange process of lincomycin on aluminosilicate mineral surfaces.
林可霉素是一种广泛用作兽药的抗生素,在水中经常被检测到。尽管林可霉素在土壤-水之间的分布是其环境归宿和潜在暴露风险的主要决定因素,但对此了解甚少。研究发现阳离子交换是土壤粘土矿物吸附林可霉素的主要机制。这通过pH依赖吸附以及与无机阳离子竞争吸附位点得到证明。随着溶液pH值升高,林可霉素的吸附量降低。降低程度与溶液中阳离子型林可霉素种类的减少一致。溶液中Ca2+的存在会减少林可霉素的吸附。粘土层间水化状态强烈影响林可霉素的吸附。四面体层因同晶置换而带负电荷的蒙脱石(即皂石)表现出层间水化环境较弱,导致其吸附量大于八面体取代的粘土(即蒙脱石)。强水化的可交换阳离子导致粘土层间水化环境更强,吸附量按Ca-蒙脱石 < K-蒙脱石 < Cs-蒙脱石的顺序降低。X射线衍射显示林可霉素插层进入蒙脱石粘土层间。吸附容量受粘土表面积限制,而非阳离子交换容量。蒙脱石层间水化被证明是影响林可霉素在铝硅酸盐矿物表面阳离子交换过程的一个主要但此前未被认识到的因素。