改性稻壳生物炭对水中Cd2+的吸附性能研究

    Adsorption of Cd2+ from Aqueous Solution by Modified Rice Husk-derived Biochars

    • 摘要: 为提高生物炭对水中Cd2+的吸附去除性能,以BC1和BC2 2种稻壳生物炭为基础材料,分别采用NaOH和FeCl3溶液制备得到NBC1和NBC2以及FBC1和FBC2改性稻壳生物炭,并通过吸附动力学和等温吸附实验研究6种生物炭对水中Cd2+的吸附性能。结果表明,对于50 mg·L-1 Cd2+溶液,当生物炭投加量为1 g·L-1时,BC1、BC2对Cd2+的吸附量分别为14.76和13.72 mg·g-1,NBC1、NBC2对Cd2+的吸附量分别为未改性稻壳生物炭的3.26和2.47倍,而FBC1、FBC2对Cd2+的吸附量则仅为未改性稻壳生物炭的1.03和0.74倍,NaOH改性稻壳生物炭能显著提高稻壳生物炭对Cd2+的吸附能力,而FeCl3改性对稻壳生物炭吸附Cd2+的能力影响不大。稻壳生物炭对Cd2+的吸附符合准二级动力学和Langmuir模型,为单分子层吸附过程;NBC1和NBC2对Cd2+的最大吸附量(131.58和98.04 mg·g-1)明显高于FBC1和FBC2(30.30和23.26 mg·g-1)。与FeCl3改性相比,NaOH改性显著增强稻壳生物炭对Cd2+的吸附能力,其主要原因为NaOH使生物炭表面碱性含氧官能团增多,从而增强了生物炭与Cd2+之间的离子交换和沉淀作用。

       

      Abstract: To improve Cd2+ adsorption ability of biochar in aqueous solution, NaOH- and FeCl3-modified biochars (NBC1, NBC2 and FBC1, FBC2) were prepared based on two kinds of original rice husk-derived biochars (BC1, BC2). Moreover, Cd2+ adsorption performances of the six materials were explored by the kinetics and isothermal adsorption experiments. Results show that Cd2+ equilibrium adsorption capacities of BC1 and BC2 were 14.76 and 13.72 mg·g-1 under the condition of Cd2+ concentration 50 mg·L-1 and biochar dosage 1 g·L-1, respectively. NaOH-modification enhanced the Cd2+ adsorption ability of rice husk-derived biochars consistently and significantly, and the equilibrium adsorption capacities of NBC1 and NBC2 were 3.26 and 2.47 times that of BC1 and BC2, respectively. However, FeCl3-modification had little effect on Cd2+ adsorption of the biochars, and the equilibrium adsorption capacities of FBC1 and FBC2 were only 1.03 and 0.74 times that of BC1 and BC2. The process of Cd2+ adsorption onto the original and modified rice husk-derived biochars was more consistent with the pseudo-second-order model and the Langmuir model, and it was assumed that the adsorption mainly occurs in monolayers. The maximum adsorption capacities of NBC1 and NBC2 (131.58 and 98.04 mg·g-1, respectively) were significantly higher than that of FBC1 and FBC2 (30.30 and 23.26 mg·g-1, respectively). The reason for Cd2+ adsorption capacity enhancement of NaOH-modified biochars is that NaOH-modification increased the amount of alkaline oxygen-containing functional groups on the surface of biochars, which enhances biochars' cation exchange and precipitation capacity with Cd2+.

       

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