污泥预植重金属Cu炭化及炭中重金属的稳定性研究

提出一种污泥预植重金属炭化后固定的概念,并以重金属Cu为代表,以CuCl2的形式植入;研究了在不同Cu预植浓度、不同温度下炭化后污泥本身以及额外添加的重金属在炭中的保留率以及稳定特性,同时采用不同的浸出方法,确定与污泥炭最终处置目标相关的最大可预植量.结果表明,在污泥中Cu的预植量为0.5%(质量分数,以Cu元素计)时,经过热解炭化,90%以上的Cu都保留在污泥炭中,其固定效果与温度有关,400℃以上时,炭化温度越高,Cu越容易浸出.在污泥中预植重金属Cu存在最大容量限制,最大可预植量与污泥炭最终处置目标有关,若选择在卫生填埋场进行填埋,则Cu的预植量不宜超过0.5%.本研究提供了一种污泥包裹其他含重金属的废料共炭化实现无害化的新思路,从而达到用污泥治废的效果.

Carbonization of Heavy Metal Cu Implanted Sewage Sludge and Stability of Heavy Metal in the Resulting Char

In this research, a new method for sewage sludge (SS) disposal was introduced, by which heavy metals were implanted into sewage sludge before pyrolysis. Cu was adopted as the representative of heavy metals to test this process and was implanted in the form of CuCl₂. Effects of Cu implanting concentration and reaction temperature on the residual ratio and immobilization of heavy metals in pyrolysis char were studied. Meanwhile, two leaching methods were employed with the purpose to determine the maximum capacity of heavy metal immobilization in the char. The primary research results showed that when the Cu implanting concentration was 0.5%(mass fraction), more than 90% of Cu remained in the char after carbonization, and the leachability of heavy metals in the char was related to pyrolysis temperature. Cu leaching from the char increased with increasing pyrolysis temperature. There was also a limitation for Cu implanting concentration in the sewage sludge, which was determined by the destination of the pyrolyzed char. If it went to sanitary landfill, the limitation would be 0.5%. The primary results showed that sewage sludge could be kneaded with other wastes containing heavy metals before pyrolysis to achieve co-processing.