Abstract

Liquid to solid partitioning as a function of pH leaching Procedure LSP EPA method 1313 was carried out to test the effectiveness , performance and efficiency of the cement-based solidification / stabilization (S/S) of heavy metals contaminated sand samples using Ordinary Portland Cement OPC type A . Two cement based mix designs ( 7 and 25 % ) have been applied to (S/S) sand contaminated samples with different heavy metal ions ( Pb , Cu , Cr , and Cd ) having the following concentrations ( 500 , 1500 and 3000 mg / kg ). Fixed water to cement ratio of 0.45 was maintained for all the experiments. Effective retention levels for the heavy metal ions was achieved using a 25 % OPC mix ratio to (S/S) the contaminated samples even when the extraction solutions were of pH levels as low as 2. Leaching experiments showed that as the pH level of the extraction solution is reduces and as the OPC content in the (S/S) samples is reduced the more heavy metal ions that can leach out. Up to 80 % of chromium, cadmium, lead, and copper ions leachability can be prevented when higher cement content is introduced to the solidification / stabilization process under the same pH extraction. Acidic extraction effects and solubilized the Calcium – Silica – Hydrate (C-S-H) gel that is created by the OPC binder, which holds, and contain the heavy metal ions and thus results in more release of those ions into the extraction solutions. The alkaline environments provided by the cement binder are believed to have participated in the precipitation of several metal ions such as cadmium and lead io, leading to their less detection in the leaching extracts. Alkaline extraction experiments (pH 8-13) showed that the mobility of the metal ions under the same experimental conditions followed the order of pb> Cr > Cu > Cd in samples of various cement contents.

Highlights

  • Disposal of hazardous wastes in landfills is a worldwide environmental problem and the pollutants can leach into the surrounding environments causing a serious threat to life even longer after the source of pollution has been removed [1]

  • This study focuses on the cement based (S/S) process and the leaching characteristics under different pH extractions of five selected heavy metal ions (Cd, Cr, Cu, and Pb)

  • Liquid to solid portioning (LSP) as a function of pH leaching tests was carried after 28 days of curing of the cement-based solidification and stabilization of the heavy metal ions contaminated sand samples using Environmental Protection Agency (EPA) method 1313

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Summary

Introduction

Disposal of hazardous wastes in landfills is a worldwide environmental problem and the pollutants can leach into the surrounding environments causing a serious threat to life even longer after the source of pollution has been removed [1] This is where solidification/ stabilization (S/S) comes as an effective technology of hazardous waste management. The technology works by converting the waste into a solid matrix, which allows for the ultimate disposal of the waste in a safe manner [2] This remediation and treatment method is capable of reducing the mobility of the polluted contaminants so that they do not move through the environment. In cement-based solidification/stabilization, the water-Cement reactions formulate three main products: Hydrated Calcium Silicates (C2SHx, C3S2 Hx) Known by calcium Silicate Hydrate gels (C-S-H), Hydrated Calcium aluminates (C3AHx, C4AHx) and Hydrated Lime Ca(OH) Because of those reactions, the cement particles bind the adjacent grains together and form aharden skeleton matrix. This study focuses on the cement based (S/S) process and the leaching characteristics under different pH extractions of five selected heavy metal ions (Cd, Cr, Cu, and Pb)

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