State Key Laboratory of Soil and Sustainable Agriculture, Institute of Soil Science, Chinese Academy of Sciences, Nanjing 210008, China.
J Environ Sci (China). 2013 Apr 1;25(4):652-8. doi: 10.1016/s1001-0742(12)60118-1.
The removal efficiency of copper (Cu(II)) from an actual acidic electroplating effluent by biochars generated from canola, rice, soybean and peanut straws was investigated. The biochars simultaneously removed Cu(II) from the effluent, mainly through the mechanisms of adsorption and precipitation, and neutralized its acidity. The removal efficiency of Cu(II) by the biochars followed the order: peanut straw char > soybean straw char > canola straw char > rice straw char >> a commercial activated carbonaceous material, which is consistent with the alkalinity of the biochars. The pH of the effluent was a key factor determining the removal efficiency of Cu(II) by biochars. Raising the initial pH of the effluent enhanced the removal of Cu(II) from it. The optimum pyrolysis temperature was 400 degrees C for producing biochar from crop straws for acidic wastewater treatment, and the optimum reaction time was 8 hr.
利用油菜籽、水稻、大豆和花生秸秆制备的生物炭,研究了其从实际酸性电镀废水中去除铜(Cu(II))的效果。生物炭通过吸附和沉淀等机制同时去除废水中的 Cu(II),并中和其酸性。生物炭对 Cu(II)的去除效率遵循以下顺序:花生秸秆炭>大豆秸秆炭>油菜籽秸秆炭>水稻秸秆炭>>商业活性炭材料,这与生物炭的碱度一致。废水的 pH 值是决定生物炭去除 Cu(II)效率的关键因素。提高废水的初始 pH 值可以增强 Cu(II)的去除效果。对于处理酸性废水而言,作物秸秆制备生物炭的最佳热解温度为 400°C,最佳反应时间为 8 小时。