Leaching behavior of aluminum, copper, iron and zinc from cement activated fly ash and slag stabilized soils

Copyright © 2019 Elsevier Ltd. All rights reserved.

Bibliographische Detailangaben
Veröffentlicht in:Waste management (New York, N.Y.). - 1999. - 95(2019) vom: 15. Juli, Seite 334-355
1. Verfasser: Mahedi, Masrur (VerfasserIn)
Weitere Verfasser: Cetin, Bora, Dayioglu, Asli Y
Format: Online-Aufsatz
Sprache:English
Veröffentlicht: 2019
Zugriff auf das übergeordnete Werk:Waste management (New York, N.Y.)
Schlagworte:Journal Article Fly ash Geochemical modeling Leaching Metals Slag pH-dependent Coal Ash Metals, Heavy Soil mehr... Carbon 7440-44-0 Copper 789U1901C5 Aluminum CPD4NFA903 Iron E1UOL152H7 Zinc J41CSQ7QDS
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520 |a The use of industrial by-products such as fly ash and slag have become very prevalent in soil stabilization owing to its suitable physical and mechanical properties, and economical advantages. However, fly ash and slag have been identified as the potential source of toxic substances, and may pose environmental risk by leaching heavy and trace metals into soil, surface and groundwater. Toxicity characteristic leaching procedure (TCLP) tests were conducted to investigate the environmental hazards associated with the leaching of aluminum (Al), copper (Cu), iron (Fe) and zinc (Zn) from fly ashes, slag, type I/II cement and cement activated fly ash and slag stabilized soils. Sulfate (SO4), dissolved inorganic carbon (DIC) and dissolved organic carbon (DOC) concentrations were also quantified to evaluate their influence on metal leaching. To understand the effect of pH on the leaching behavior, pH-dependent leach tests were conducted at the pH ranges of 2-14. Results indicated that an increase in fly ash or slag content may not necessarily increase the effluent metal concentrations. Al, Cu, Zn and DOC followed an amphoteric leaching pattern where concentrations increased in both acidic and basic conditions. In contrast, maximum DIC concentrations occurred at neutral or near neutral pH values. Fe and SO4 showed cationic leaching behavior where concentrations decreased with an increase in effluent pH. Additionally, the leaching controlling mechanisms of the metals were identified by implementing geochemical modeling program Visual MINTEQ. The geochemical analyses indicated that the solubility of Al3+ and Fe3+ were controlled by precipitation/dissolution reactions of oxide/hydroxide minerals at all pH values. Leaching of Cu2+ was only solubility controlled at pH higher than 7, whereas Zn2+ leaching was solubility controlled in the pH range of 8-12 
650 4 |a Journal Article 
650 4 |a Fly ash 
650 4 |a Geochemical modeling 
650 4 |a Leaching 
650 4 |a Metals 
650 4 |a Slag 
650 4 |a pH-dependent 
650 7 |a Coal Ash  |2 NLM 
650 7 |a Metals, Heavy  |2 NLM 
650 7 |a Soil  |2 NLM 
650 7 |a Carbon  |2 NLM 
650 7 |a 7440-44-0  |2 NLM 
650 7 |a Copper  |2 NLM 
650 7 |a 789U1901C5  |2 NLM 
650 7 |a Aluminum  |2 NLM 
650 7 |a CPD4NFA903  |2 NLM 
650 7 |a Iron  |2 NLM 
650 7 |a E1UOL152H7  |2 NLM 
650 7 |a Zinc  |2 NLM 
650 7 |a J41CSQ7QDS  |2 NLM 
700 1 |a Cetin, Bora  |e verfasserin  |4 aut 
700 1 |a Dayioglu, Asli Y  |e verfasserin  |4 aut 
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773 1 8 |g volume:95  |g year:2019  |g day:15  |g month:07  |g pages:334-355 
856 4 0 |u http://dx.doi.org/10.1016/j.wasman.2019.06.018  |3 Volltext 
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