The immobilization of potentially toxic elements due to incineration and weathering of bottom ash fines

被引:35
作者
Alam, Qadeer [1 ]
Schollbach, Katrin [1 ,2 ]
Rijnders, Marco [2 ]
van Hoek, Corrie [2 ]
van der Laan, Sieger [1 ,2 ]
Brouwers, H. J. H. [1 ]
机构
[1] Eindhoven Univ Technol, Dept Built Environm, POB 513, NL-5600 MB Eindhoven, Netherlands
[2] Tata Steel, R&D, MSC, POB 10-000, NL-1970 CA Ijmuiden, Netherlands
关键词
MSWI; Bottom ash; Weathering; Leaching; Potentially toxic elements; PYROLYSIS/MELTING TREATMENT; LEACHING BEHAVIOR; ANTIMONY; EVOLUTION; PHASES; COPPER; SLAG;
D O I
10.1016/j.jhazmat.2019.120798
中图分类号
X [环境科学、安全科学];
学科分类号
08 ; 0830 ;
摘要
Incineration bottom ash fines (<= 125 mu m) are known to contain potentially toxic elements (PTEs) and inorganic salts. The most abundant PTEs in the fines were Zn (0.5%), Cu (0.25%), Pb (0.12%), Mn (0.08%) and Cr (0.03%). The systematic quantification of the mineral phases and PTEs associated with them was performed with a multimethod approach using quantitative XRD, phase mapping with PhAse Recognition and Characterization (PARC) software and microprobe analysis. The mineral phases in the fines can be categorized as follows: 1) residual phases (e.g., quartz), 2) incineration phases (e.g., melilitic slag and iron oxides) and 3) quenching/weathering phases (e.g., calcite, ettringite, gypsum, hydrous Fe- and Al-oxides). Among the incineration phases, the melilitic slag was observed to contain Cr, Cu and Zn with 0.02%, 0.13% and 0.19%, respectively. In order of predominance, the weathering phases containing the most PTEs were: calcite < ettringite < hydrous Al-oxides < hydrous Fe-oxides. More than 70% of the phases in the BA fines were formed during incineration and weathering processes that explain the enrichment of PTEs in the smaller particles. During the one-batch leaching test, dissolution of weathering phases, especially ettringite, was observed (total mass loss: 7.2%).
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页数:9
相关论文
共 53 条
[1]   In-depth mineralogical quantification of MSWI bottom ash phases and their association with potentially toxic elements [J].
Alam, Qadeer ;
Schollbach, Katrin ;
van Hoek, Corrie ;
van der Laan, Sieger ;
de Wolf, Tom ;
Brouwers, H. J. H. .
WASTE MANAGEMENT, 2019, 87 :1-12
[2]   Novel low temperature synthesis of sodium silicate and ordered mesoporous silica from incineration bottom ash [J].
Alam, Qadeer ;
Hendrix, Yuri ;
Thijs, Luuk ;
Lazaro, Alberto ;
Schollbach, Katrin ;
Brouwers, H. J. H. .
JOURNAL OF CLEANER PRODUCTION, 2019, 211 :874-883
[3]   A two-stage treatment for Municipal Solid Waste Incineration (MSWI) bottom ash to remove agglomerated fine particles and leachable contaminants [J].
Alam, Qadeer ;
Florea, M. V. A. ;
Schollbach, K. ;
Brouwers, H. J. H. .
WASTE MANAGEMENT, 2017, 67 :181-192
[4]  
[Anonymous], 4 INT C SUST SOL WAS
[5]  
[Anonymous], 2007, SOIL QUAL DECR REG B
[6]  
Anthony JW, 2003, HDB MINERALOGY
[7]   Simultaneous application of dissolution/precipitation and surface complexation/surface precipitation modeling to contaminant leaching [J].
Apul, DS ;
Gardner, KH ;
Eighmy, TT ;
Fällman, AM ;
Comans, RNJ .
ENVIRONMENTAL SCIENCE & TECHNOLOGY, 2005, 39 (15) :5736-5741
[8]   Understanding the chemical and mineralogical properties of the inorganic portion of MSWI bottom ash [J].
Bayuseno, A. P. ;
Schmahl, W. W. .
WASTE MANAGEMENT, 2010, 30 (8-9) :1509-1520
[9]   The dissolution kinetics of major elements in municipal solid waste incineration bottom ash particles [J].
Bendz, David ;
Tuechsen, Peter L. ;
Christensen, Thomas H. .
JOURNAL OF CONTAMINANT HYDROLOGY, 2007, 94 (3-4) :178-194
[10]  
Bhada-Tata PerinazDaniel A. Hoornweg., 2012, What a Waste?: A Global Review of Solid Waste Management