Hung-Lung C, Chen T C, Tsai M C, Chen Y L
Department of Environmental Engineering, Fooyin Institute of Technology, Kaoshsiung Hsien, 831, Chinese Taiwan.
Water Sci Technol. 2003;47(1):83-7.
This study selected biosolids from a petrochemical wastewater treatment plant as the raw material. The sludge was immersed in 0 to 5 mol l(-1) of ZnCl2 solutions and pyrolyzed at different temperatures. When the sludge was pyrolyzed for 30 min at temperatures of 400, 500, 600, and 700 degrees C, the corresponding surface area of the biosolid adsorbent was 46, 401, 921, and 727 m2/g, respectively. Pore size analysis indicated that the mesopore (20 to 500 A) contributed more than the macropore and micropore in the sludge pyrolytic residue. When the benzene influent concentration was 800 ppmv, the adsorption capacity ranged from 59 to 164 mg/g for different biosolid adsorbents. A larger BET surface area and smaller average pore diameter yielded a larger benzene adsorption capacity.
本研究选取某石化污水处理厂的生物固体作为原材料。将污泥浸泡在0至5 mol l(-1)的ZnCl2溶液中,并在不同温度下进行热解。当污泥在400、500、600和700摄氏度下热解30分钟时,生物固体吸附剂的相应表面积分别为46、401、921和727 m2/g。孔径分析表明,中孔(20至500 Å)在污泥热解残渣中所占比例大于大孔和微孔。当苯进水浓度为800 ppmv时,不同生物固体吸附剂的吸附容量在59至164 mg/g之间。更大的BET表面积和更小的平均孔径产生更大的苯吸附容量。