Potential for leaching of heavy metals in open-burning bottom ash and soil from a non-engineered solid waste landfill.

Bottom ash from open-burning of municipal waste practised in developing countries poses a risk of heavy metal leaching into groundwater. Compared to incineration ash, there is limited information on heavy metal leaching from open-burning ash and soil from non-engineered landfills. Batch and column experiments were conducted to address three specific objectives; (1) to determine aqua regia extractable concentrations of heavy metals in fresh ash, old ash and soil from beneath the landfill, (2) to determine the relationship between heavy metal leaching, initial and final pH of leaching solution, and aqua regia extractable concentrations, and (3) to determine the breakthrough curves of heavy metals in ashes and soil. Aqua regia extractable concentrations of Cd, Zn, Mn, Cu, Ni and Pb were significantly higher (p < 0.05) in fresh and old ashes than soil beneath landfill and uncontaminated soil (control). Increasing initial solution pH from 5 and 7 to 9 significantly reduced the mobility of Pb, Zn and Cu but not Cd whose mobility peaked at pH 7 and 9. Concentrations of desorbed heavy metals were not correlated with aqua regia extractable concentrations. Final pH of leachate rebounded to close to original pH of the material, suggesting a putative high buffering capacity for all materials. Both batch and column leaching showed that concentrations of leached heavy metals were disproportionately lower (<5%) than aqua regia extractable concentrations in most cases. The retardation of heavy metals was further evidenced by sigmoidal breakthrough curves. Heavy metal retention was attributed to precipitation, pH-dependent adsorption and formation of insoluble organo-metallic complexes at near-neutral to alkaline pH. Overall, the risk of heavy metal leaching from ash and soil from the waste dump into groundwater was low. The high pH and the presence of Zn, Fe, Mn and Cu make ash an ideal low-cost liming material and source of micronutrients particularly on acidic soils prevalent in sub-Saharan Africa.

[1]  Weihua Zhang,et al.  Relative distribution of Pb2+ sorption mechanisms by sludge-derived biochar. , 2012, Water research.

[2]  G. Gee,et al.  Particle-size Analysis , 2018, SSSA Book Series.

[3]  C. Visvanathan,et al.  Influence of tropical seasonal variations on landfill leachate characteristics--results from lysimeter studies. , 2005, Waste management.

[4]  B. J. Alloway,et al.  Heavy metals in soils , 1990 .

[5]  C. Vandecasteele,et al.  Leaching mechanisms of oxyanionic metalloid and metal species in alkaline solid wastes: A review , 2008 .

[6]  Brett H Robinson,et al.  E-waste: an assessment of global production and environmental impacts. , 2009, The Science of the total environment.

[7]  Gan Zhang,et al.  Heavy metal contamination in soils and vegetables near an e-waste processing site, South China. , 2011, Journal of hazardous materials.

[8]  Bing Li,et al.  Immobilization of Zn, Cu, and Pb in contaminated soils using phosphate rock and phosphoric acid. , 2009, Journal of hazardous materials.

[9]  D. J. Hagerty,et al.  Solid Waste Management , 2020, Concise Handbook of Waste Treatment Technologies.

[10]  B. Alloway,et al.  Leaching of cadmium, nickel, and zinc down the profile of sewage sludge-treated soil , 2002 .

[11]  Michael Kersten,et al.  Leaching behaviour and solubility — Controlling solid phases of heavy metals in municipal solid waste incinerator ash , 1996 .

[12]  B. J. Alloway,et al.  Soil mobility of sewage sludge-derived dissolved organic matter, copper, nickel and zinc. , 2004, Environmental pollution.

[13]  D. J. Walker,et al.  Contrasting effects of manure and compost on soil pH, heavy metal availability and growth of Chenopodium album L. in a soil contaminated by pyritic mine waste. , 2004, Chemosphere.

[14]  G. E. Rayment,et al.  Australian laboratory handbook of soil and water chemical methods. , 1992 .

[15]  Masato Yamada,et al.  Heavy metal leaching from aerobic and anaerobic landfill bioreactors of co-disposed municipal solid waste incineration bottom ash and shredded low-organic residues. , 2007, Journal of hazardous materials.

[16]  A. Kabata-Pendias Trace elements in soils and plants , 1984 .

[17]  L. Beesley,et al.  A review of biochars' potential role in the remediation, revegetation and restoration of contaminated soils. , 2011, Environmental pollution.

[18]  J. A. Ryan,et al.  Formation of chloropyromorphite in a lead-contaminated soil amended with hydroxyapatite. , 2001, Environmental science & technology.

[19]  A. Aydilek,et al.  Leaching of Metals from Fly Ash-Amended Permeable Reactive Barriers , 2012 .

[20]  M. Takaoka,et al.  EXAFS speciation and phytoavailability of Pb in a contaminated soil amended with compost and gypsum. , 2011, The Science of the total environment.

[21]  Leaching behavior of heavy metals from municipal solid waste incineration bottom ash and its geochemical modeling , 2008 .

[22]  G. Heron,et al.  Biogeochemistry of landfill leachate plumes , 2001 .

[23]  Sandra Cointreau,et al.  Occupational and environmental health issues of solid waste management : special emphasis on middle and lower-income countries , 2006 .

[24]  Charles D. Shackelford,et al.  Laboratory diffusion testing for waste disposal — A review , 1991 .

[25]  Abhishek Asthana,et al.  THERMODYNAMIC STUDY OF HEAVY METALS BEHAVIOUR DURING MUNICIPAL WASTE INCINERATION , 2006 .