Tang Chao, Guan Jiaojiao
Chongqing Water Resources and Electric Engineering College, Chongqing 402160, China.
State Key Laboratory of Petroleum and Pollution Control, Beijing 102206, China.
Int J Anal Chem. 2022 Aug 18;2022:6734039. doi: 10.1155/2022/6734039. eCollection 2022.
The preparation process of synergistic preparation of sludge carbon by oily sludge and walnut shells are divided into two stages: carbonization preparation of a carbon precursor and activation preparation of sludge carbon. The preparation conditions of the carbon precursor are 2.5:1 mass ratio of oily sludge and walnut shells, carbonization temperature is 450°C, and time is 2 h. There are some pores on the surface of the prepared carbon precursor, the heavy metal content of leachate does not exceed the standard, and the use process will not cause heavy metal pollution. Intensive research is carried out on factors affecting the preparation of sludge carbon by activation of the carbon precursor by the orthogonal experiment and single-factor experiment. The optimal activation conditions are determined by using ZnCl as an activator, mass ratio of the carbon precursor to ZnCl is 1:4, activation temperature is 800°C, heating rate is 15°C/min, and activation holding time is 1 h. The surface of sludge carbon is distributed with many pores, several layers of small pores can be seen deeply in the large holes, and pore size distribution is dominated by micropores and mesopores. BET Specific surface area, pore volume, average pore, and iodine value are 1772.69 m/g, 1.98 cm/g, 1.64 nm, and 1011.65 mg/g, respectively, which surpasses commercially available activated carbon comprehensively.
碳前驱体的碳化制备和污泥炭的活化制备。碳前驱体的制备条件为含油污泥与核桃壳的质量比为2.5:1,碳化温度为450℃,时间为2小时。制备的碳前驱体表面存在一些孔隙,渗滤液重金属含量达标,使用过程不会造成重金属污染。通过正交试验和单因素试验对影响碳前驱体活化制备污泥炭的因素进行了深入研究。以ZnCl为活化剂,确定最佳活化条件为:碳前驱体与ZnCl的质量比为1:4,活化温度为800℃,升温速率为15℃/min,活化保温时间为1小时。污泥炭表面分布着许多孔隙,大孔内可见多层小孔,孔径分布以微孔和中孔为主。BET比表面积、孔容、平均孔径和碘值分别为1772.69m²/g、1.98cm³/g、1.64nm和1011.65mg/g,综合超过市售活性炭。