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用改性椰壳生物炭去除碱性稀土工业废水中的 NO-N。

Removal of NO-N in alkaline rare earth industry effluent using modified coconut shell biochar.

机构信息

School of Agricultural Engineering and Food Science, Shandong University of Technology, Zibo, Shandong 255000, China.

School of Resources and Environmental Engineering, Shandong University of Technology, 266 New Village West Road, Zibo, Shandong 255000, China E-mail:

出版信息

Water Sci Technol. 2019 Aug;80(4):784-793. doi: 10.2166/wst.2019.321.

Abstract

Coconut shell biochar (CSB) was selected as raw material to obtain two kinds of modified biochars by pickling and iron modification. The pickling coconut shell biochar (PCSB) and pickling-iron modified coconut shell biochar (PICSB) were used as adsorbents to remove NO-N in alkaline rare earth industry effluent. The results showed that pickling smoothed the surface of CSB, and α-FeOOH was formed on the surface of PCSB because of FeCl solution modification. Suitable adsorbent dosages of PCSB and PICSB were both 2.0 g/L. The NO-N adsorption process by PCSB and PICSB both reached equilibrium at 30 min. The quasi-first-order kinetic model shows good fit to the NO-N adsorption by PCSB. Whereas, the quasi-second-order kinetic model is more suitable for PICSB adsorbing NO-N. The adsorption mechanisms of PICSB for NO-N removal were ligand exchange and electrostatic attraction, and that of PCSB for NO-N removal was electrostatic attraction. The NO-N adsorption amounts of PCSB and PICSB decreased with increasing adsorption temperature and pH. The maximum NO-N adsorption amounts of PCSB and PICSB were 15.14 mg/L and 10.75 mg/L respectively with adsorbent dosage of 2.0 g/L, adsorption time of 30 min, adsorption temperature of 25 ± 1 °C, and initial solution pH of 2.01.

摘要

椰壳生物炭(CSB)被选为原料,通过酸洗和铁改性获得两种改性生物炭。将酸洗椰壳生物炭(PCSB)和酸洗-铁改性椰壳生物炭(PICSB)用作吸附剂,以去除碱性稀土工业废水中的 NO-N。结果表明,酸洗使 CSB 的表面变得光滑,并且由于 FeCl 溶液改性,在 PCSB 的表面形成了α-FeOOH。PCSB 和 PICSB 的适宜吸附剂剂量均为 2.0 g/L。PCSB 和 PICSB 对 NO-N 的吸附过程均在 30 min 时达到平衡。准一级动力学模型很好地拟合了 PCSB 对 NO-N 的吸附。然而,准二级动力学模型更适合 PICSB 吸附 NO-N。PICSB 去除 NO-N 的吸附机制是配体交换和静电吸引,而 PCSB 去除 NO-N 的吸附机制是静电吸引。随着吸附温度和 pH 的升高,PCSB 和 PICSB 的 NO-N 吸附量均降低。在吸附剂用量为 2.0 g/L、吸附时间为 30 min、吸附温度为 25±1°C、初始溶液 pH 值为 2.01 的条件下,PCSB 和 PICSB 的最大 NO-N 吸附量分别为 15.14 mg/L 和 10.75 mg/L。

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