Fe-Zr双金属改性银杏叶生物炭的制备及其去除矿井水中硫酸根的机理

Preparation of Fe-Zr bimetallic modified ginkgo leaf biochar and its mechanism for removing sulfate ions from mine water

  • 摘要: 黄河流域部分矿区矿井水中硫酸根离子(\mathrmSO_4^2- )超标问题突出,但现有的膜处理和稀释混合法存在成本高、效果不确定等问题。为此,采用热解耦合高能球磨方法制备银杏叶生物炭(Zr-Fe@BC),并进行过渡金属(Fe和Zr)改性修饰,开发针对矿井水中\mathrmSO_4^2- 的高效低耗去除技术,探究了制备条件、吸附条件及干扰离子对\mathrmSO_4^2- 去除效率的影响。结果显示,生物炭最佳制备条件:在空气氛围条件下,改性剂与生物炭质量比为0.2,热解时间为6 h,热解温度为700 ℃,球磨时间为2 h。经ZrOCl2·8H2O和FeCl3·6H2O双金属改性修饰后,Zr和Fe均成功负载于银杏叶生物炭表面。高能球磨处理能够显著提升Zr和Fe的暴露活性且使生物炭比表面积显著增大。通过X射线光电子能谱技术(XPS)分析确定,Zr-Fe@BC中Zr和Fe的质量分数分别为1.94%和0.11%。利用MINTEQ软件对\mathrmSO_4^2- 在pH为1~12的形态进行了模拟,并通过试验发现Zr-Fe@BC在pH为2时,对初始质量浓度为500 mg/L的\mathrmSO_4^2- 去除率为74.8%。虽然pH升高伴随的OH质量浓度增加会和\mathrmSO_4^2- 竞争Zr-Fe@BC的活性位点,但即便pH增加到8,溶液中\mathrmSO_4^2- 的质量浓度仅为231 mg/L,满足GB 3838—2002《地表水环境质量Ⅲ类标准》的排放标准(\mathrmSO_4^2- 的质量浓度< 250 mg/L)。通过竞争离子吸附试验发现:\mathrmCO_3^2- 显著影响Zr-Fe@BC对\mathrmSO_4^2- 的吸附,其次为\mathrmPO_4^3- 。相比之下,Cl的存在对Zr-Fe@BC吸附\mathrmSO_4^2- 的影响最小。经吸附热力学和动力学分析,Zr-Fe@BC吸附\mathrmSO_4^2- 更符合Langmuir吸附等温模型和准二级吸附动力学模型,且吸附机理主要靠物理吸附(范德华力)、静电吸引、离子交换(\mathrmSO_4^2- 和Zr—OH及Fe—OH中的—OH)。利用Zr-Fe@BC能够对实际矿井疏干水中的\mathrmSO_4^2- (初始质量浓度436.4 mg/L)在20 min完成达标处理。整体来看,本研究合成的Zr-Fe@BC吸附性能稳定,能够为黄河流域矿井水中\mathrmSO_4^2- 的深度去除提供技术支持和理论依据。

     

    Abstract: The issue of exceeded sulfate ion (\mathrmSO_4^2- ) in mine water in certain regions of Yellow River Basin, poses significant environmental challenges. High operational costs and variable effectiveness hinder traditional remediation methods, such as membrane filtration and dilution. This study focuses on the synthesis of ginkgo leaf biochar via pyrolysis combined with high-energy ball milling (designated as Zr-Fe@BC), followed by transition metal modifications using iron (Fe) and zirconium (Zr) to establish a more efficient and economical sulfate removal technology. The systematically examined the effects of various preparation conditions, adsorption parameters, and the presence of interfering ions on sulfate elimination efficiency were systematically examined. Optimal biochar synthesis parameters were identified: pyrolysis conducted in an inert atmosphere for 6 hours at 700 °C, a modifier-to-biochar mass ratio of 0.2, and a subsequent ball milling duration of 2 h. Post-modification, both Zr and Fe were successfully integrated onto the biochar surface using ZrOCl2·8H2O and FeCl3·6H2O. The high-energy ball milling notably improved the accessibility of these metals and significantly enhanced the surface area of the biochar. Quantitative analysis via X-ray photoelectron spectroscopy (XPS) revealed that the contents of Zr and Fe in the Zr-Fe@BC were 1.94% and 0.11%, respectively. Simulations conducted with MINTEQ software investigated sulfate ion morphology across a pH range of 1 to 12. Experimental results demonstrated that Zr-Fe@BC achieved a sulfate removal efficiency of 74.8% at an initial mass concentration of 500 mg/L and pH 2. Even with a pH increase to 8, where competing hydroxide ions (OH) increase, the active sulfate binding sites on Zr-Fe@BC corresponded to a mass concentration of only 231 mg/L, complying with Class III Environmental Quality Standards for Surface Water (GB 3838—2002), which stipulate a limit of \mathrmSO_4^2- < 250 mg/L. Competitive adsorption studies indicated that carbonate ions (\mathrmCO_3^2- ) exert a significant inhibitory effect on sulfate adsorption, followed by phosphate ions (\mathrmPO_4^3- ). Conversely, the presence of chloride ions (Cl) had minimal impact on sulfate uptake. Kinetic and thermodynamic analyses of the adsorption process demonstrated that sulfate absorption onto Zr-Fe@BC aligns closely with the Langmuir isotherm model and follows pseudo-second-order kinetics. The predominant sulfate sorption mechanisms were identified as physical adsorption (van der Waals forces), electrostatic interactions, and ion exchange processes involving \mathrmSO_4^2- with Zr—OH and Fe—OH groups. Crucially, Zr-Fe@BC could effectively reduce sulfate levels from an initial concentration of 436.4 mg/L in actual mine dewatering effluent to within regulatory limits in under 20 min. In summary, the Zr-Fe@BC synthesized in this study not only demonstrates robust and stable \mathrmSO_4^2- adsorption performance but also offers significant potential for practical applications, thereby contributing valuable insights and technical foundations for the advanced removal of sulfate in mine waters across Yellow River Basin.

     

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