College of Chemical Sciences, Institute of Chemistry Ceylon, Rajagiriya, CO 10107, Sri Lanka.
Department of Chemistry, Mississippi State University, MS 39762, USA.
Bioresour Technol. 2017 Dec;246:150-159. doi: 10.1016/j.biortech.2017.07.150. Epub 2017 Jul 27.
Utilization of biochar (BC) as a low cost adsorbent for water remediation has gained an immense research interest due to their surface functionality and porosity. Although many reports on the BC based sorptive removal of Sulfonamides (SA) and Tetracyclines (TC) are available in literature, a deep insight into sorption mechanisms is yet to be reviewed. Objective of this review is to fill the research gap of a methodological understanding of sorption mechanisms and characteristics which is essential to develop efficient methods for contaminant removal. The most common adsorption mechanism can be considered as electron donor-acceptor interactions of electron withdrawing moieties with surface arene rings. The strongest adsorption of both antibiotics occurs at mildly acidic pH where the dominant species are zwitterionic or cationic. Smaller SAs exhibit micro pore-filling effects while bulky TCs experience size exclusions. Furthermore, the effect of matrix components and modifications are also been taken into account.
由于生物炭(BC)具有表面官能团和孔隙率,因此将其用作低成本吸附剂来修复水已引起了广泛的研究兴趣。尽管文献中有许多关于基于 BC 的磺胺类(SA)和四环素类(TC)吸附去除的报道,但对吸附机制的深入了解仍有待综述。本综述的目的是填补对吸附机制和特性的方法理解的研究空白,这对于开发有效的污染物去除方法至关重要。最常见的吸附机制可以被认为是具有吸电子部分的电子给体-受体相互作用与表面芳烃环之间的相互作用。在偏酸性 pH 值下,两种抗生素的吸附最强,此时主要的物质为两性离子或阳离子。较小的磺胺类药物表现出微孔填充效应,而较大的四环素类药物则受到尺寸排斥的影响。此外,还考虑了基质成分和修饰的影响。