Department of Chemistry, University of Pavia, via Taramelli 12, 27100 Pavia, Italy.
Department of Chemistry, University of Pavia, via Taramelli 12, 27100 Pavia, Italy.
Chemosphere. 2016 May;150:686-693. doi: 10.1016/j.chemosphere.2015.12.127. Epub 2016 Jan 13.
Sepiolite is studied as sorbent for removal of Fluoroquinolone (FQ) contaminants from water. Marbofloxacin (MAR) and Enrofloxacin (ENR) were chosen as model FQs since they are the two most commonly employed veterinary FQs in livestock farming in northern Italy. Adsorption experiments on two sepiolites (SP-1 and SSE16) were carried out in tap water at pH 7.5 to better mimic real conditions. The sorption experimental data were fitted by Freundlich, Langmuir and S-Logistic1 models. The latter better described MAR and ENR adsorptions. Adsorption capacities of SP-1 and SSE16, respectively, were 132 mg g(-1) and 121 mg g(-1) for MAR, and 112 mg g(-1) and 93 mg g(-1) for ENR. X-ray powder diffraction, performed on clay samples enriched with each FQ and on the pristine clays, showed no substantial differences between the two sepiolites and evidenced no significant structural changes after FQs uptake, as also verified by infrared spectroscopy. This indicates that adsorption occurs only on the external surface of the mineral and not in the intracrystalline microporosity, likely due to the interaction between the FQ carboxylic group and the sepiolite surface. For the first time solid-state photodegradation of the adsorbed FQs was investigated for regenerating the sorbent. Results showed that the adsorbed drugs are effectively photodegraded by solar light, thus allowing sepiolite to be reused. The efficiency of this material for remediation of contaminated water was proved on ditch water, collected downstream a swine farm, containing some tens of ng L(-1) of MAR and ENR.
海泡石被研究为吸附剂,用于去除水中的氟喹诺酮(FQ)污染物。马波沙星(MAR)和恩诺沙星(ENR)被选为模型 FQ,因为它们是意大利北部畜牧业中使用最广泛的两种兽医 FQ。在 pH 为 7.5 的自来水中进行了两种海泡石(SP-1 和 SSE16)的吸附实验,以更好地模拟实际情况。吸附实验数据通过 Freundlich、Langmuir 和 S-Logistic1 模型进行拟合。后一种模型更好地描述了 MAR 和 ENR 的吸附。SP-1 和 SSE16 对 MAR 的吸附容量分别为 132 和 121mg g(-1),对 ENR 的吸附容量分别为 112 和 93mg g(-1)。对富含有每个 FQ 的粘土样品和原始粘土进行 X 射线粉末衍射,结果表明两种海泡石之间没有明显差异,并且在 FQ 吸收后没有明显的结构变化,这也通过红外光谱得到了验证。这表明吸附仅发生在矿物的外表面,而不在晶内微孔中,这可能是由于 FQ 羧酸基团与海泡石表面的相互作用所致。首次研究了吸附 FQ 的固态光降解,以再生吸附剂。结果表明,吸附的药物可以被太阳光有效光降解,从而允许海泡石重复使用。该材料对受污染水的修复效果已在猪场下游采集的沟渠水中得到证明,其中含有数十 ng L(-1)的 MAR 和 ENR。