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    硝酸铁改性活性焦脱除二氧化硫及再生性能研究

    Study on Sulfur Dioxide Removal and Regeneration Performance of Ferric Nitrate-Modified Activated Coke

    • 摘要: 二氧化硫(SO2)是燃煤烟气中的主要酸性污染物之一,其高效脱除对实现煤炭清洁利用和区域大气污染防治具有重要意义。针对传统活性焦在低浓度烟气脱硫过程中吸附容量有限、化学活性不足及多次再生后性能衰减明显等问题,采用KOH活化与铁盐浸渍相结合的方法制备了Fe改性活性焦,并系统评价了其在中低温条件下对SO?的脱除性能、循环再生行为及吸附动力学特性,同时结合多种表征手段对其作用机理进行了分析。在120 °C、含O2和水蒸气的模拟烟气条件下,Fe改性活性焦表现出显著优于未改性样品的脱硫性能。未改性活性焦的新鲜样品初始穿透硫容仅为3.22 mg/g,而Fe改性后其初始穿透硫容提升至26.45 mg/g,脱硫能力提高约8倍。经过多次原位热再生后,未改性活性焦的硫容逐渐衰减,第四次再生后降至3.82 mg/g;相比之下,Fe改性活性焦虽在循环过程中硫容呈现下降趋势,但其稳定硫容仍维持在约9 mg/g,显著高于原始活性焦的初始脱硫水平,表明Fe改性有效提升了材料的长期能力。表征结果进一步揭示了Fe改性活性焦的脱硫机理。SEM和FTIR表明,改性后材料表面形成了均匀分布的Fe基活性组分,并在SO2吸附后生成硫酸盐类沉积物。XPS结果显示,吸附后样品表面硫元素主要以高价态硫(S6+)形式存在,同时Fe2+/Fe3+氧化还原对在反应过程中保持动态平衡,说明Fe基活性位点能够催化SO?向热力学稳定的硫酸盐物种转化。综合分析认为,Fe改性活性焦的高脱硫性能主要来源于表面铁物种主导的化学吸附与催化氧化机制,而非单纯依赖物理孔隙吸附。吸附动力学分析表明,未改性活性焦其脱硫过程以物理吸附为主并伴随有限的表面反应。Fe改性活性焦的吸附行为则明显不同,其Bangham模型对实验数据具有更高的拟合优度(R2=0.9982),反映出其表面存在分布不均的高能化学吸附位点,SO2脱除过程由化学吸附与催化反应共同主导。研究结果表明,该改性能够显著提升活性焦的SO2脱除能力和再生稳定性,为SO2的高效、可再生脱除提供了一种具有应用潜力的材料方案。

       

      Abstract: Sulfur dioxide (SO2) is one of the main acidic pollutants in coal-fired flue gas. Its efficient removal is of great significance for achieving clean coal utilization and regional air pollution control. To address the issues of traditional activated coke (AC) such as limited adsorption capacity, insufficient chemical activity, and significant performance degradation after multiple regenerations during low-concentration flue gas desulfurization, Fe-modified activated coke (FeAC) was prepared by combining KOH activation and iron salt impregnation. Its SO2 removal performance, cyclic regeneration behavior, and adsorption kinetic characteristics under medium-low temperature conditions were systematically evaluated, and the underlying mechanism was analyzed using multiple characterization techniques. Under simulated flue gas conditions (120 °C, with O2 and water vapor), FeAC exhibited significantly superior desulfurization performance compared to unmodified AC. The initial breakthrough sulfur capacity of fresh unmodified AC was only 3.22 mg/g, while that of FeAC increased to 26.45 mg/g, representing an approximately 8-fold improvement in desulfurization capacity. After multiple in-situ thermal regenerations, the sulfur capacity of unmodified AC gradually degraded, dropping to 3.82 mg/g after the fourth regeneration. In contrast, although the sulfur capacity of FeAC showed a decreasing trend during cycling, its stable sulfur capacity remained at approximately 9 mg/g, which was significantly higher than the initial desulfurization level of unmodified AC. This indicates that Fe modification effectively enhanced the long-term serviceability of the material. Characterization results further revealed the desulfurization mechanism of FeAC. Scanning Electron Microscopy (SEM) and Fourier Transform Infrared Spectroscopy (FTIR) analyses demonstrated that uniformly distributed Fe-based active components were formed on the surface of modified AC, and sulfate deposits were generated after SO2 adsorption. X-ray Photoelectron Spectroscopy (XPS) results showed that sulfur on the surface of the adsorbed sample mainly existed in the form of high-valent sulfur (S6+), and the Fe2+/Fe3+ redox couple maintained dynamic equilibrium during the reaction. This suggests that Fe-based active sites can catalyze the conversion of SO2 to thermodynamically stable sulfate species. Comprehensive analysis indicates that the high desulfurization performance of FeAC primarily stems from chemisorption and catalytic oxidation mechanisms dominated by surface iron species, rather than relying solely on physical pore adsorption. Adsorption kinetic analysis showed that the SO? adsorption process of unmodified AC indicates that the desulfurization process of unmodified AC is dominated by physical adsorption accompanied by limited surface reactions. In contrast, the adsorption behavior of FeAC was significantly different: the Bangham model showed a higher goodness of fit to the experimental data (R2 = 0.9982), reflecting the presence of unevenly distributed high-energy chemisorption sites on its surface. Thus, the SO2 removal process of FeAC is co-dominated by chemisorption and catalytic reactions. The results of this study demonstrate that this composite modification can significantly enhance the SO2 removal capacity and regeneration stability of activated coke, providing a promising material solution for the efficient and renewable removal of SO2.

       

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