Characterization of heavy metals in fly ash from municipal solid waste incinerators in Shanghai
Introduction
Fly ash is a must by-product of MSW incineration process, which has been classified as a hazardous waste due to its relatively high content of heavy metals all over the world. The presence of heavy metals in municipal solid waste incineration (MSWI) fly ash is of environmental concern due to their leaching potential in landfill environments. Hence, its management is becoming a challenge for incineration of MSW, and therefore attracting world attention. Treatment methods of fly ash include solidification with cement-based materials, chemical stabilization with EDTA, sodium sulfide and thiourea (Zhang et al., 2008), hydrometallurgical extraction by dissolution in acidic or alkaline medium, and sintering or vitrification for reuse as a construction material. Safe management of MSWI fly ash depends on a through understanding of its characterization, especially characterization of heavy metals in it.
Wan et al. (2006) of Tsinghua University China performed a sequential chemical extraction on fly ash samples from a large-scale municipal solid waste incineration plant in East China, to study the leaching behavior of heavy metals such as zinc, lead, cadmium and copper in MSWI fly ash.
Liu et al. (2009) investigated the composition and morphology of raw fly ash and washed fly ash at different sintering temperatures, and examined the newly formed minerals during sintering. Toxicity characteristic leaching procedure (TCLP) tests were carried out to investigate the effect of the washing treatment and sintering process on the leaching performance of heavy metals in fly ash, to study relationship between leaching toxicity of heavy metals and mineral compositions in the thermal treatment process.
Xue et al. (2008) used HCl as extractant to leach Cd, Cr, Cu, Mn, Ni, Pb and Zn from MSWI fly ash under traditional and microwave acid extraction conditions. The redistributions of heavy metals were determined using the sequential extraction procedure before and after extraction. The extraction efficiencies and specification transformation of heavy metals were investigated to study acid extraction efficiencies of heavy metals.
Ye et al. (2007) performed a study on characterization and heavy metals leaching toxicity of fly ash from municipal solid waste incinerators in China. In their study, the characteristics and leaching behavior of heavy metals in fly ash, sampled from 12 MSWI plants in China, were investigated. Component analysis shows that MSWI fly ash in China must be controlled as a hazardous material due to its potential environmental risk. Leaching toxicity of heavy metals, in accordance with TCLP of U.S. EPA and GB 5086.1-1997, was performed, and difference between both standards analyzed.
Lee (2007) studied characterization of bottom and fly ash collected from automobile shredder residue (ASR) incinerator in terms of particle size, compositions, and heavy metal leaching by the standard TCLP method. Two alternative methods were also examined for the treatment of heavy metals in ASR incinerator ash from the aspect of recycling into construction or lightweight aggregate material. It was clearly found in the study that heavy metals could be removed thoroughly or partly from ASR fly ash through acid washing with dilute HCl solution so that the remaining fly ash could be landfilled or used as a construction material.
Based on the above studies, analysis of content and leaching toxicity of heavy metals in MSWI fly ash, as well as their specification distribution and leaching behavior as a function of pH, was performed respectively using ICP, a sequential extraction procedure, XRD and MINTEQA2 modeling. Data derived from these methods may help regulators and plant operators to develop methods for handling MSWI fly ash. These data can also be used as a basis for geo-chemical modeling of long-term ash stabilization, which will aid engineers to explore disposal and recycle methods environmentally benign over the long-term.
Section snippets
Sampling and composition analysis of heavy metals
The ash used in this study came from two biggest municipal solid waste incinerators, Pudong and Jiangqiao MSWI Plant, which handle 1100 tons solid waste per day for the former and 1500 tons per day for the latter. Jiangqiao Plant utilizes German Steinmuller furnace, while Pudong Plant uses French CITY2000 tilted-reversing furnace. Prior to analysis of characteristics of heavy metals, fly ash was dried for 24 h at 105 °C.
Hg detector was used to measure content of Hg, and ICP (IRIS Advantage 5000)
Compositions of heavy metals
In Fig. 1, “Av1” and “Av2” represents respectively the average content of heavy metals from Pudong and Jiangqiao MSWI Plant. It shows that content of heavy metals follows the sequence of Zn > Pb > Cu > Cr > As > Ni > Cd approximately Hg in both plants, and total heavy metals account for around 0.68% by mass of fly ash for Pudong Plant, and approximately 0.71% for Jiangqiao Plant. Content of separate heavy metals in fly ash from Jiangqiao MSWI Plant is generally higher than that from Pudong MSWI Plant,
Conclusions
Content of heavy metals follows the sequence of Zn > Pb > Cu > Cr > As > Ni > Cd approximately Hg in both plants, and total heavy metals account for 1%-minus by mass of fly ash. Leaching toxicity analysis indicates that major hazardous heavy metals are As, Cd, Hg, Pb and Zn.
Soluble Cd mainly exists in the acid, exchangeable and water-soluble phases, soluble Hg mainly in acid and water-soluble phases. In addition, soluble Pb mainly appears in acid soluble, and soluble Zn and As mainly in organically bounded
Acknowledgements
We thank the Leading Academic Discipline Project of Shanghai Municipal Education Commission under the project number J51502. We also thank laboratory technicians of the State Key Laboratory of Pollution Control and Resource Reuse, Tongji University, and of Instrumental Analysis Center, Jiaotong University, for assisting with the experimental work.
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