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Chitosans as soil amendments for the remediation of metal contaminated soil

机译:壳聚糖作为土壤改良剂用于修复金属污染土壤

摘要

Research was conducted to evaluate the potential of chitosan, a fishery waste-based material, and its derivative cross-linked chitosans, as soil amendments for the remediation of metal contaminated land. This research comprised modification of chitosan followed by a characterisation study, a batch sorption study, two pot experiments and a biodegradation study. Chitosan was modified with three cross-linking reagents, namely glutaraldehyde (GLA), epichlorohydrin (ECH) and ethylene glycol diglycidyl ether (EGDE). The characterisation study used X-ray diffraction (XRD), scanning electron microscopy (SEM), energy dispersive X-ray analysis (EDX) and Fourier transform infrared spectroscopy (FTIR) methods to investigate the effect of cross-linking treatment on the surface and physical properties of chitosan, the effect of metal interaction on the surface properties of chitosan and cross-linked chitosans, and the binding mechanism(s) of metal ions onto the chitosans. Cross-linking treatments on chitosan enhanced its chemical stability in acidic media and increased its BET surface area. Metal interaction reduced the crystallinity and changed the surface morphology of the chitosans. FTIR analysis revealed that the complexation of metal ions was through dative covalent interaction with the amino and hydroxyl groups of the chitosans. The batch sorption study evaluated the ability of chitosan and cross-linked chitosans to bind heavy metals. The effects of contact time, initial metal concentration and background electrolyte on metal binding were assessed. The binding behaviour was described by several kinetic and isotherm models. The maximum binding capacity (Q) values, estimated using the Langmuir isotherm model for the chitosans were comparable with other low-cost sorbents reported in the literature. The sorption-desorption study showed that the chitosans were able to retain metal ions on their surfaces, even at dilution factor of x11. The pot experiments evaluated the effectiveness of chitosan and chitosan-GLA in immobilising heavy metals in the contaminated soil. Their effects on plant growth and metal accumulation in plant tissue were determined using Lolium perenne (perennial ryegrass) and Brassica napus (rapeseed). For perennial ryegrass, the results were dependent on the rate of addition of the chitosans. Low application rates (up to 1% w/w) resulted in an increase in metal uptake, whereas 10% (w/w) addition decreased metal uptake. For rapeseed, metal uptake was decreased at all rates of application of chitosans. The ammonium acetate extractable metals in soil decreased following application of chitosan and plant growth. The biodegradation study measured microbial breakdown of the chitosans in both non-contaminated and contaminated soils. It was estimated that a longer period is required to complete the breakdown of the cross-linked chitosans (up to approximately 100 years) than unmodified chitosan (up to approximately 10 years). The influence of biodegradation on the bioavailable fraction of heavy metals in soil was studied concurrent with the biodegradation trial. It was found that the binding behaviour of chitosan for heavy metals in soils was not affected by the biodegradation process.
机译:进行了研究以评估壳聚糖(一种以渔业废物为基础的材料)及其衍生的交联壳聚糖作为土壤改良剂的潜力,以修复金属污染土地。这项研究包括对壳聚糖的修饰,然后进行表征研究,分批吸附研究,两个锅实验和一个生物降解研究。壳聚糖用三种交联剂改性,即戊二醛(GLA),表氯醇(ECH)和乙二醇二缩水甘油醚(EGDE)。表征研究使用X射线衍射(XRD),扫描电子显微镜(SEM),能量色散X射线分析(EDX)和傅立叶变换红外光谱(FTIR)方法来研究交联处理对表面和表面的影响壳聚糖的物理性质,金属相互作用对壳聚糖和交联壳聚糖的表面性质的影响,以及金属离子与壳聚糖的结合机理。壳聚糖的交联处理提高了其在酸性介质中的化学稳定性,并增加了其BET表面积。金属相互作用降低了结晶度并改变了壳聚糖的表面形态。 FTIR分析表明,金属离子的络合是通过与壳聚糖的氨基和羟基的共价共价相互作用。分批吸附研究评估了壳聚糖和交联壳聚糖结合重金属的能力。评估了接触时间,初始金属浓度和背景电解质对金属结合的影响。通过几种动力学和等温线模型描述了结合行为。使用Langmuir等温线模型估算的壳聚糖的最大结合容量(Q)值可与文献中报道的其他低成本吸附剂相媲美。吸附-解吸研究表明,即使稀释倍数为x11,壳聚糖也能够在其表面上保留金属离子。盆栽实验评估了壳聚糖和壳聚糖-GLA在将重金属固定在受污染土壤中的有效性。使用黑麦草(多年生黑麦草)和甘蓝型油菜(油菜)确定了它们对植物生长和植物组织中金属积累的影响。对于多年生黑麦草,结果取决于壳聚糖的添加速度。低施药量(最高1%w / w)导致金属吸收增加,而10%(w / w)的添加降低金属吸收。对于油菜籽,所有壳聚糖施用量下的金属吸收均降低。施用壳聚糖和植物生长后,土壤中的乙酸铵可萃取金属减少。生物降解研究测量了未污染和污染土壤中壳聚糖的微生物分解。据估计,完成交联脱乙酰壳多糖的分解所需的时间(至多约100年)要比未改性脱乙酰壳多糖(至多约10年)更长。在进行生物降解试验的同时,还研究了生物降解对土壤中重金属生物利用率的影响。发现壳聚糖与土壤中重金属的结合行为不受生物降解过程的影响。

著录项

  • 作者

    Kamari Azlan;

  • 作者单位
  • 年度 2011
  • 总页数
  • 原文格式 PDF
  • 正文语种 English
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