Department of Environmental Engineering, Faculty of Engineering, Kocaeli University, 41380, Kocaeli, Turkey.
Environ Sci Pollut Res Int. 2022 Jan;29(4):5240-5255. doi: 10.1007/s11356-021-15833-y. Epub 2021 Aug 21.
In this study, regeneration of spent granular activated carbon (GAC) with reactive dye by hydroxyl and sulfate radical-based advanced oxidation processes (microwave (MW) +persulfate (PS)), (Fe(II)+ PS), and (O + HO) were evaluated. The adsorption of the dye to the GAC surface was characterized by chemisorption and Langmuir isotherm. Regeneration processes have been optimized by the response surface methodology to determine the operating conditions that will provide the highest adsorptive capacity. The optimum conditions of (MW + PS), (Fe (II) + PS), and (O + HO) processes were process PS anion of 45.52 g/L, pH of 11.4, MW power of 126 W, and duration of 14.56 min; Fe (II) of 3.58 g/L, PS anion of 73.5 g/L, duration of 59.8 min, and pH of 10.9; and HO of 2.8 mole/L, flow rate of 8.14 mg ozone/L, duration of 32.8 min, and pH of 5.3, respectively. For (MW + PS), (Fe (II) + PS), and (O + HO) processes, the adsorptive capacity under optimum conditions was found as 4.36, 8.89, and 8.12 mg dye/g GAC, respectively. For (Fe (II) + PS) and (O + HO) processes, these values are approximately equal to the adsorptive capacity of raw GAC (8.01 mg dye/g GAC). The predicted values of the adsorption capacities by the obtained models were in good agreement with the actual experimental results. Preference Ranking Organization Method for Enrichment Evaluation approach was used in the preference of the appropriate regeneration process. The adsorptive capacity of regenerated GAC, operating cost of the regeneration process, change in the adsorptive capacity during the regeneration cycle, and carbon mass loss criteria were taken into account. The order of preference of regeneration processes was determined as (Fe (II) + PS)> (MW + PS)> (O + HO) considering all criteria.
在这项研究中,评估了羟基和硫酸盐自由基基高级氧化工艺(微波 (MW) +过硫酸盐 (PS))、(Fe(II) + PS) 和 (O + HO) 对用过的颗粒状活性炭 (GAC) 进行再生的效果。通过化学吸附和朗格缪尔等温线对染料在 GAC 表面的吸附进行了表征。通过响应面法优化了再生过程,以确定提供最高吸附容量的操作条件。(MW + PS)、(Fe(II) + PS) 和 (O + HO) 工艺的最佳条件分别为:过硫酸盐阴离子 45.52 g/L、pH 值 11.4、MW 功率 126 W、持续时间 14.56 min;Fe(II) 为 3.58 g/L、过硫酸盐阴离子 73.5 g/L、持续时间 59.8 min 和 pH 值 10.9;HO 为 2.8 摩尔/L、臭氧流量 8.14 毫克/升、持续时间 32.8 分钟和 pH 值 5.3。对于 (MW + PS)、(Fe(II) + PS) 和 (O + HO) 工艺,在最佳条件下的吸附容量分别为 4.36、8.89 和 8.12 mg 染料/g GAC。对于 (Fe(II) + PS) 和 (O + HO) 工艺,这些值与原始 GAC 的吸附容量(8.01 mg 染料/g GAC)大致相等。通过获得的模型预测的吸附容量与实际实验结果吻合良好。富集评估方法中的偏好排序组织方法被用于偏好合适的再生过程。考虑到再生 GAC 的吸附容量、再生过程的运行成本、再生循环中吸附容量的变化以及碳质量损失标准,对再生过程进行了偏好排序。综合所有标准,确定再生工艺的优先顺序为 (Fe(II) + PS) > (MW + PS) > (O + HO)。