Centre for Environmental Risk Assessment and Remediation, University of South Australia, Mawson Lakes, SA, 5095, Australia,
Rev Environ Contam Toxicol. 2015;233:1-43. doi: 10.1007/978-3-319-10479-9_1.
Chitosan originates from the seafood processing industry and is one of the most abundant of bio-waste materials. Chitosan is a by-product of the alkaline deacetylation process of chitin. Chemically, chitosan is a polysaccharide that is soluble in acidic solution and precipitates at higher pHs. It has great potential for certain environmental applications, such as remediation of organic and inorganic contaminants, including toxic metals and dyes in soil, sediment and water, and development of contaminant sensors. Traditionally, seafood waste has been the primary source of chitin. More recently, alternative sources have emerged such as fungal mycelium, mushroom and krill wastes, and these new sources of chitin and chitosan may overcome seasonal supply limitations that have existed. The production of chitosan from the above-mentioned waste streams not only reduces waste volume, but alleviates pressure on landfills to which the waste would otherwise go. Chitosan production involves four major steps, viz., deproteination, demineralization, bleaching and deacetylation. These four processes require excessive usage of strong alkali at different stages, and drives chitosan's production cost up, potentially making the application of high-grade chitosan for commercial remediation untenable. Alternate chitosan processing techniques, such as microbial or enzymatic processes, may become more cost-effective due to lower energy consumption and waste generation. Chitosan has proved to be versatile for so many environmental applications, because it possesses certain key functional groups, including - OH and -NH2 . However, the efficacy of chitosan is diminished at low pH because of its increased solubility and instability. These deficiencies can be overcome by modifying chitosan's structure via crosslinking. Such modification not only enhances the structural stability of chitosan under low pH conditions, but also improves its physicochemical characteristics, such as porosity, hydraulic conductivity, permeability, surface area and sorption capacity. Crosslinked chitosan is an excellent sorbent for trace metals especially because of the high flexibility of its structural stability. Sorption of trace metals by chitosan is selective and independent of the size and hardness of metal ions, or the physical form of chitosan (e.g., film, powder and solution). Both -OH and -NH2 groups in chitosan provide vital binding sites for complexing metal cations. At low pH, -NH3 + groups attract and coagulate negatively charged contaminants such as metal oxyanions, humic acids and dye molecules. Grafting certain functional molecules into the chitin structure improves sorption capacity and selectivity for remediating specific metal ions. For example, introducing sulfur and nitrogen donor ligands to chitosan alters the sorption preference for metals. Low molecular weight chitosan derivatives have been used to remediate metal contaminated soil and sediments. They have also been applied in permeable reactive barriers to remediate metals in soil and groundwater. Both chitosan and modified chitosan have been used to phytoremediate metals; however, the mechanisms by which they assist in mobilizing metals are not yet well understood. In addition, microbes have been used in combination with chitosan to remediate metals (e.g., Cu and Zn) in contaminated soils. Chitosan has also been used to remediate organic contaminants, such as oil-based wastewater, dyes, tannins, humic acids, phenols, bisphenoi-A, p-benzoquinone, organo-phosphorus insecticides, among others. Chitosan has also been utilized to develop optical and electrochemical sensors for in-situ detection of trace contaminants. In sensor technology, naturally-derived chitosan is used primarily as an immobilizing agent that results from its enzyme compatibility, and stabilizing effect on nanoparticles. Contaminant-sensing agents, such as enzymes, microbes and nanoparticles, have been homogeneously immobilized in chitosan gels by using coagulating (e.g., alginate, phosphate) or crosslinking agents (e.g., GA, ECH). Such immobilization maintains the stability of sensing elements in the chitosan gel phase, and prevents inactivation and loss of the sensing agent. In this review, we have shown that chitosan, an efficient by-product of a waste biomaterial, has great potential for many environmental applications. With certain limitations, chitosan and its derivatives can be used for remediating contaminated soil and wastewater. Notwithstanding, further research is needed to enhance the physicochemical properties of chitosan and mitigate its deficiencies.
壳聚糖来源于海鲜加工行业,是最丰富的生物废料材料之一。壳聚糖是甲壳素碱性脱乙酰过程的副产品。从化学上讲,壳聚糖是一种多糖,可溶于酸性溶液,在较高的 pH 值下沉淀。它在某些环境应用方面具有很大的潜力,例如修复有机和无机污染物,包括土壤、沉积物和水中的有毒金属和染料,以及开发污染物传感器。传统上,海鲜废物是甲壳素的主要来源。最近,出现了替代来源,如真菌菌丝体、蘑菇和磷虾废物,这些新的甲壳素和壳聚糖来源可能克服了存在的季节性供应限制。从上述废物流中生产壳聚糖不仅减少了废物量,而且减轻了废物对垃圾填埋场的压力。壳聚糖的生产涉及四个主要步骤,即脱蛋白、脱矿质、漂白和脱乙酰。这四个过程在不同阶段都需要大量使用强碱,这使得壳聚糖的生产成本上升,可能使高档壳聚糖的商业修复应用变得不可行。替代壳聚糖加工技术,如微生物或酶工艺,由于能耗和废物产生较低,可能变得更具成本效益。壳聚糖已被证明在许多环境应用中具有多功能性,因为它具有某些关键的官能团,包括-OH 和-NH2。然而,由于其溶解度和不稳定性增加,壳聚糖在低 pH 值下的效果会降低。通过交联来改变壳聚糖的结构可以克服这些缺陷。这种修饰不仅增强了壳聚糖在低 pH 条件下的结构稳定性,而且改善了其物理化学特性,如孔隙率、水力传导率、渗透性、表面积和吸附能力。交联壳聚糖是痕量金属的优良吸附剂,特别是因为其结构稳定性的高灵活性。壳聚糖对痕量金属的吸附是选择性的,与金属离子的大小和硬度或壳聚糖的物理形式(例如,薄膜、粉末和溶液)无关。壳聚糖中的-OH 和-NH2 基团为络合金属阳离子提供了重要的结合位点。在低 pH 值下,-NH3+ 基团吸引并凝聚带负电荷的污染物,如金属含氧阴离子、腐殖酸和染料分子。将某些功能分子接枝到甲壳素结构中可以提高对特定金属离子的吸附能力和选择性。例如,向壳聚糖中引入硫和氮供体配体可以改变对金属的吸附偏好。低分子量壳聚糖衍生物已被用于修复受金属污染的土壤和沉积物。它们还被应用于可渗透反应屏障中,以修复土壤和地下水中的金属。壳聚糖和改性壳聚糖都被用于植物修复金属;然而,它们协助金属移动的机制尚不清楚。此外,微生物已与壳聚糖结合用于修复受污染土壤中的金属(如 Cu 和 Zn)。壳聚糖还被用于修复有机污染物,如含油废水、染料、单宁、腐殖酸、酚类、双酚 A、对苯醌、有机磷杀虫剂等。壳聚糖还被用于开发光学和电化学传感器,用于原位检测痕量污染物。在传感器技术中,天然来源的壳聚糖主要用作酶相容性和稳定纳米粒子的固定化剂。污染物传感剂,如酶、微生物和纳米粒子,已通过使用凝结剂(如藻酸盐、磷酸盐)或交联剂(如 GA、ECH)均匀地固定在壳聚糖凝胶中。这种固定化保持了壳聚糖凝胶相中传感元件的稳定性,并防止了传感剂的失活和损失。在本综述中,我们表明壳聚糖,一种有效的废生物质副产品,在许多环境应用中具有巨大的潜力。尽管存在某些限制,但壳聚糖及其衍生物可用于修复受污染的土壤和废水。尽管如此,仍需要进一步研究来增强壳聚糖的物理化学性质并减轻其缺陷。