Abstract

In the present study, stabilization and solidification (S/S) of the waste phosphate sludge (WPS) using Portland cement (PC) and cement kiln dust (CKD) was investigated. In the first place, only PC was used to stabilize 5, 10 and 15% WPS. At a later stage, 10 and 15% CKD were used as PC substitute to stabilize 15%WPS. WPS contained initially 130.2 mg/L Zn and 22.6 mg/L Ni. U.S. Environmental Protection Agency (US-EPA) landfilling limits for Zn and Ni are 4.3 mg/L and 11 mg/L, respectively. Setting times and unconfined compressive strength (UCS) values were measured and permeability of selected samples was determined. TCLP (Toxicity Characteristics Leaching Procedure) and SPLP (Synthetic Precipitation Leaching Procedure) were applied to determine the concentrations of Zn and Ni leached from the mortar samples and leachate pH values were measured. Use of the CKD as a cement substitute delayed setting times, decreased UCS and increased leached heavy metal concentrations. Leached Zn and Ni concentrations of the WPS stabilized with PC and CKD following SPLP were lower than the EPA landfilling limits. However, leached Zn concentrations following TCLP were not compatible with the EPA limit. Leached Ni concentrations remained lower than the EPA limit. It was concluded that relatively low levels of alkalies, CaO and SiO2 content of CKD negatively affected the setting, compressive strength and leaching characteristics.

Highlights

  • Hazardous wastes are generally disposed in landfill after reduction of their toxicity [1]

  • Relationship between leaching and permeability: Relation between leached heavy metal concentrations and permeability results of the waste phosphate sludge (WPS) stabilized with only Portland cement (PC) are shown in Figure 4a (TCLP) and Figure 4b (SPLP)

  • Role of cement kiln dust (CKD) in heavy metal fixation: Fixation of Zn and Ni decreased with using of CKD as a cement substitute. 91% Zn and 94% Ni were fixed in 15% WPS stabilized with only PC

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Summary

Introduction

Hazardous wastes are generally disposed in landfill after reduction of their toxicity [1]. Stabilization and solidification (S/S) process is one of the most common technologies to treat hazardous wastes before landfilling [2]. Portland cement (PC) is widely used as a binding agent for S/S application to reduce toxic characteristics of waste. Alkalinity of the PC make it suitable to fix heavy metals in the form of hydroxides, silicates etc. Compounds which are less soluble forms of the heavy metals [3,4,5]. S/S process allow the using several pozzolanic materials such as cement kiln dust (CKD), fly ash, blast furnace slag, silica fume etc. CKD is a by-product obtained from cement factories and thousands tons of it are disposed annually by cement companies [8]

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