Department of Environmental Engineering, China Jiliang University, Hangzhou, Zhejiang 310018, China; Key Laboratory of Environment Remediation and Ecological Health (Zhejiang University), Ministry of Education, Hangzhou, Zhejiang 310058, China.
Department of Environmental Engineering, China Jiliang University, Hangzhou, Zhejiang 310018, China.
Water Res. 2020 Nov 1;186:116303. doi: 10.1016/j.watres.2020.116303. Epub 2020 Aug 14.
Removal of nitrogen (N) and phosphorus (P) from water through the use of various sorbents is often considered an economically viable way for supplementing conventional methods. Biochar has been widely studied for its potential adsorption capabilities for soluble N and P, but the performance of different types of biochars can vary widely. In this review, we summarized the adsorption capacities of biochars in removing N (NH-N and NO-N) and P (PO-P) based on the reported data, and discussed the possible mechanisms and influencing factors. In general, the NH-N adsorption capacity of unmodified biochars is relatively low, at levels of less than 20 mg/g. This adsorption is mainly via ion exchange and/or interactions with oxygen-containing functional groups on biochar surfaces. The affinity is even lower for NO-N, because of electrostatic repulsion by negatively charged biochar surfaces. Precipitation of PO-P by metals/metal oxides in biochar is the primary mechanism for PO-P removal. Biochars modified by metals have a significantly higher capacity to remove NH-N, NO-N, and PO-P than unmodified biochar, due to the change in surface charge and the increase in metal oxides on the biochar surface. Ambient conditions in the aqueous phase, including temperature, pH, and co-existing ions, can significantly alter the adsorption of N and P by biochars, indicating the importance of optimal processing parameters for N and P removal. However, the release of endogenous N and P from biochar to water can impede its performance, and the presence of competing ions in water poses practical challenges for the use of biochar for nutrient removal. This review demonstrates that progress is needed to improve the performance of biochars and overcome challenges before the widespread field application of biochar for N and P removal is realized.
通过使用各种吸附剂从水中去除氮(N)和磷(P)通常被认为是补充传统方法的一种经济可行的方法。生物炭因其对可溶性 N 和 P 的潜在吸附能力而被广泛研究,但不同类型的生物炭的性能可能差异很大。在这篇综述中,我们根据报道的数据总结了生物炭去除 N(NH-N 和 NO-N)和 P(PO-P)的吸附能力,并讨论了可能的机制和影响因素。一般来说,未改性生物炭的 NH-N 吸附容量相对较低,低于 20mg/g。这种吸附主要是通过离子交换和/或与生物炭表面含氧官能团相互作用实现的。由于带负电荷的生物炭表面的静电排斥,NO-N 的亲和力更低。生物炭中金属/金属氧化物对 PO-P 的沉淀是去除 PO-P 的主要机制。与未改性生物炭相比,经过金属改性的生物炭去除 NH-N、NO-N 和 PO-P 的能力显著提高,这是由于表面电荷的变化和生物炭表面金属氧化物的增加。水相中的环境条件,包括温度、pH 值和共存离子,会显著改变 N 和 P 被生物炭吸附的情况,这表明优化 N 和 P 去除的处理参数非常重要。然而,生物炭向水中释放内源 N 和 P 会阻碍其性能,而且水中竞争离子的存在对生物炭用于养分去除提出了实际挑战。本综述表明,在广泛应用生物炭去除 N 和 P 之前,需要在提高生物炭性能和克服挑战方面取得进展。