TY - JOUR
T1 - Impacts of natural weathering on the transformation/neoformation processes in landfilled MSWI bottom ash
T2 - A geoenvironmental perspective
AU - Saffarzadeh, Amirhomayoun
AU - Shimaoka, Takayuki
AU - Wei, Yunmei
AU - Gardner, Kevin H.
AU - Musselman, Craig N.
N1 - Funding Information:
This project was financially supported by the Grant-in-Aid for Japan-USA joint research project (approved by Gakushinkyo-2-9 on April 1. 2010) and Research Grant-in-Aid for Sustainable Society and Waste Management funded by the Ministry of Environment ( K22078 ). Special thanks to CMA Engineers, NH, USA for their supports during the field work. The SEM–EDX analysis was conducted in the Center for Advanced Instrumental Analysis, Kyushu University, Ito branch.
PY - 2011/12
Y1 - 2011/12
N2 - Natural weathering processes are significant mechanisms that noticeably affect the fundamental nature of incineration ash residues. To provide a greater understanding of these processes, a MSWI (mono)landfill site in the north east of the US was selected as the target for systematic investigation of the natural weathering of bottom ash residues. Samples of various ages were collected from locations A (1 yr), B (10 yrs), C (13-14 yrs) and D (20 yrs) of the landfill in 2009. We investigated the phase transformation of the collected bottom ash particles, neoformation processes as well as the behavior and distribution of certain heavy metals (Cu, Pb, Zn, Ni, and Cr) in the neoformed phases using optical microscopy, SEM-EDX, and bulk examinations. Key findings: at the preliminary stage, the waste metallic particles (Al, Fe, and Cu) and unstable minerals such as lime, portlandite, ettringite and hydrocalumite convert to oxide and hydroxide (hydrate) phases, calcite, alumina gel and gypsum. At the intermediate stage, the decomposition of melt products including magnetite spinels and metallic inclusions is triggered due to the partial dissolution of the melt glass. At the longer time horizon it is possible to track the breakdown of the glass phase, the extensive formation of calcite and anhydrite, Al-hydrates and more stable Fe-hydrates all through the older ash deposits. Among the dominant secondary phases, we propose the following order based on their direct metal uptake capacity: Fe-hydrates > Al-hydrates > calcite. Calcite was found to be the least effective phase for the direct sorption of heavy metals. Based on overall findings, a model is proposed that demonstrates the general trend of ash weathering in the landfill.
AB - Natural weathering processes are significant mechanisms that noticeably affect the fundamental nature of incineration ash residues. To provide a greater understanding of these processes, a MSWI (mono)landfill site in the north east of the US was selected as the target for systematic investigation of the natural weathering of bottom ash residues. Samples of various ages were collected from locations A (1 yr), B (10 yrs), C (13-14 yrs) and D (20 yrs) of the landfill in 2009. We investigated the phase transformation of the collected bottom ash particles, neoformation processes as well as the behavior and distribution of certain heavy metals (Cu, Pb, Zn, Ni, and Cr) in the neoformed phases using optical microscopy, SEM-EDX, and bulk examinations. Key findings: at the preliminary stage, the waste metallic particles (Al, Fe, and Cu) and unstable minerals such as lime, portlandite, ettringite and hydrocalumite convert to oxide and hydroxide (hydrate) phases, calcite, alumina gel and gypsum. At the intermediate stage, the decomposition of melt products including magnetite spinels and metallic inclusions is triggered due to the partial dissolution of the melt glass. At the longer time horizon it is possible to track the breakdown of the glass phase, the extensive formation of calcite and anhydrite, Al-hydrates and more stable Fe-hydrates all through the older ash deposits. Among the dominant secondary phases, we propose the following order based on their direct metal uptake capacity: Fe-hydrates > Al-hydrates > calcite. Calcite was found to be the least effective phase for the direct sorption of heavy metals. Based on overall findings, a model is proposed that demonstrates the general trend of ash weathering in the landfill.
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U2 - 10.1016/j.wasman.2011.07.017
DO - 10.1016/j.wasman.2011.07.017
M3 - Article
C2 - 21873042
AN - SCOPUS:80054866394
SN - 0956-053X
VL - 31
SP - 2440
EP - 2454
JO - Waste Management
JF - Waste Management
IS - 12
ER -