He Pin-Jing, Pu Hong-Xia, Shao Li-Ming, Zhang Hua
State Key Laboratory of Pollution Control and Resource Reuse, Tongji University, Shanghai 200092, China; Institute of Waste Treatment and Reclamation, Tongji University, Shanghai 200092, China; Centre for the Technology Research and Training on Household Waste in Small Towns & Rural Area, Ministry of Housing Urban-Rural Development, Shanghai 200092, China.
State Key Laboratory of Pollution Control and Resource Reuse, Tongji University, Shanghai 200092, China; Institute of Waste Treatment and Reclamation, Tongji University, Shanghai 200092, China.
Waste Manag. 2017 Nov;69:232-241. doi: 10.1016/j.wasman.2017.08.021. Epub 2017 Aug 14.
Incineration has become an important municipal solid waste (MSW) treatment strategy, and generates a large amount of bottom ash (BA). Although some BA is reused, much BA and pretreatment residues from BA recycling are disposed in landfill. When BA and MSW are co-landfilled together, acid neutralization capacity and alkaline earth metal dissolution of BA, as well as different components of MSW may change environmental conditions within the landfill, so the degradation of organic matter and the physical and chemical properties of leachate would be affected. In this study, the effect of co-landfilled BA and MSW on the leachate characteristics during the hydrolysis and acidogenesis phase was studied using different BA/MSW ratios and MSW compositions. The results showed that the co-landfill system increased leachate pH, electric conductivity and alkalinity. For MSW with a high content of degradable components, the release and degradation of total organic carbon (TOC) and volatile fatty acids (VFA) from MSW were promoted when the BA ratio by wet weight was less than 50%, and the biodegradability of leachate was improved. When the BA ratio exceeded 50%, the degradation of organic matters was inhibited. For MSW with low content of degradable components, when the proportion of BA was less than 20%, the release and degradation of TOC and VFA from MSW were promoted and alkalinity increased. When the BA ratio exceeded 20%, the degradation of organic matters was inhibited. The 50% BA ratio could improve the bio-treatability of leachate indicated by the leachate pH and C/N ratio. However, BA inhibited the release of nitrogen (TN and NH-N) at all BA ratios and MSW compositions. At the same time, the addition of BA increased the risk of leachate collection system clogging due to the dissolution and re-precipitation of alkaline earth metals contained in BA.
焚烧已成为一种重要的城市固体废物(MSW)处理策略,并产生大量底灰(BA)。尽管部分底灰得到了再利用,但大量的底灰以及底灰回收过程中的预处理残渣仍被填埋处理。当底灰与城市固体废物共同填埋时,底灰的酸中和能力、碱土金属溶解性以及城市固体废物的不同成分可能会改变填埋场内的环境条件,进而影响有机物的降解以及渗滤液的物理和化学性质。在本研究中,采用不同的底灰/城市固体废物比例和城市固体废物组成,研究了底灰与城市固体废物共同填埋对水解和产酸阶段渗滤液特性的影响。结果表明,共同填埋系统提高了渗滤液的pH值、电导率和碱度。对于可降解成分含量高的城市固体废物,当湿重底灰比例小于50%时,城市固体废物中总有机碳(TOC)和挥发性脂肪酸(VFA)的释放与降解得到促进,渗滤液的生物降解性得到改善。当底灰比例超过50%时,有机物的降解受到抑制。对于可降解成分含量低的城市固体废物,当底灰比例小于20%时,城市固体废物中TOC和VFA的释放与降解得到促进,碱度增加。当底灰比例超过20%时,有机物的降解受到抑制。50%的底灰比例可通过渗滤液的pH值和碳氮比提高渗滤液的生物可处理性。然而,在所有底灰比例和城市固体废物组成情况下,底灰均抑制了氮(TN和NH-N)的释放。同时,底灰的添加增加了渗滤液收集系统因底灰中所含碱土金属的溶解和再沉淀而堵塞的风险。