Key Laboratory of Eco-environments in Three Gorges Reservoir Region, Ministry of Education, Chongqing Key Laboratory of Agricultural Resources and Environment, College of Resources and Environment, Department of Environmental Science and Engineering, Southwest University, Chongqing 400716, China.
Key Laboratory of Eco-environments in Three Gorges Reservoir Region, Ministry of Education, Chongqing Key Laboratory of Agricultural Resources and Environment, College of Resources and Environment, Department of Environmental Science and Engineering, Southwest University, Chongqing 400716, China; Department of Forest Ecology and Management, Swedish University of Agricultural Sciences, Umeå SE-90183, Sweden.
J Environ Sci (China). 2016 Apr;42:152-162. doi: 10.1016/j.jes.2015.08.008. Epub 2015 Oct 28.
Iron oxide (FeO) coated by natural organic matter (NOM) is ubiquitous. The associations of minerals with organic matter (OM) significantly changes their surface properties and reactivity, and thus affect the environmental fate of pollutants, including nutrients (e.g., phosphorus (P)). In this study, ferrihydrite/goethite-humic acid (FH/GE-HA) complexes were prepared and their adsorption characteristics on P at various pH and ionic strength were investigated. The results indicated that the FeO-OM complexes showed a decreased P adsorption capacity in comparison with bare FeO. The maximum adsorption capacity (Qmax) decreased in the order of FH (22.17 mg/g)>FH-HA (5.43 mg/g)>GE (4.67 mg/g)>GE-HA (3.27 mg/g). After coating with HA, the amorphous FH-HA complex still showed higher P adsorption than the crystalline GE-HA complex. The decreased P adsorption observed might be attributed to changes of the FeO surface charges caused by OM association. The dependence of P adsorption on the specific surface area of adsorbents suggests that the FeO component in the complexes is still the main contributor for the adsorption surfaces. The P adsorptions on FeO-HA complexes decreased with increasing initial pH or decreasing initial ionic strength. A strong dependence of P adsorption on ionic strength and pH may demonstrate that outer-sphere complexes between the OM component on the surface and P possibly coexist with inner-sphere surface complexes between the FeO component and P. Therefore, previous over-emphasis on the contributions of original minerals to P immobilization possibly over-estimates the P loading capacity of soils, especially in humic-rich areas.
氧化铁(FeO)被天然有机物(NOM)包裹的情况非常普遍。矿物质与有机物(OM)的结合显著改变了它们的表面性质和反应性,从而影响了污染物的环境归宿,包括营养物质(例如磷(P))。在这项研究中,制备了水铁矿/针铁矿-腐殖酸(FH/GE-HA)复合物,并研究了它们在不同 pH 和离子强度下对 P 的吸附特性。结果表明,与裸露的 FeO 相比,FeO-OM 复合物的 P 吸附容量降低。最大吸附容量(Qmax)的顺序为 FH(22.17 mg/g)>FH-HA(5.43 mg/g)>GE(4.67 mg/g)>GE-HA(3.27 mg/g)。HA 涂层后,无定形 FH-HA 复合物的 P 吸附量仍高于结晶态 GE-HA 复合物。观察到的 P 吸附减少可能归因于 OM 结合引起的 FeO 表面电荷变化。吸附剂比表面积对 P 吸附的依赖性表明,复合物中的 FeO 组分仍然是吸附表面的主要贡献者。FeO-HA 复合物上的 P 吸附随初始 pH 值的升高或初始离子强度的降低而降低。P 吸附对离子强度和 pH 值的强烈依赖性表明,OM 成分表面与 P 之间可能存在外配位络合物,同时也存在 FeO 成分与 P 之间的内配位表面络合物。因此,先前对原始矿物质对 P 固定化的贡献的过分强调可能高估了土壤的 P 负载能力,尤其是在富腐殖质地区。