Abstract

The combustion of municipal sewage sludge allows for the recovery of renewable energy. However, it simultaneously causes the formation of ash which is not neutral for the environment. The study presents the research on the possibility of using sewage sludge ash as a raw material for the synthesis of zeolites. The synthesis of zeolites was performed with the use of an indirect fusion method and a direct hydrothermal method. The research on sewage sludge ash after zeolitization included the identification of crystalized phases, the observation of changes of ash particles surface and the measurement of cation exchange capacity (CEC). The research results proved that optimal conditions for the formation of zeolite Y were the synthesis with the indirect fusion method at the sewage sludge ash to hydroxy sodalite ratio of 1:1.8, the activation temperature of 60°C and the crystallization temperature of 90°C. Hydroxy sodalite was found in samples from both methods of zeolitization. However, in the case of direct hydrothermal method, particles of hydroxy sodalite structure were less numerous indicating a small conversion of sewage sludge ash to crystalline zeolite. CEC values comparable to commercial zeolites resulted from zeolitization with the indirect fusion method.

Highlights

  • Municipal sewage sludge, an unavoidable by-product of wastewater treatment plants, is classified as biomass [1]

  • The results show that synthesis products of better properties can be obtained with the use of the indirect fusion method rather than the direct hydrothermal method

  • From a practical point of view, the optimal conditions for the synthesis of zeolite Y are provided by the indirect fusion method at the sewage sludge ash to sodium hydroxide ratio of 1:1.8, the activation temperature of 60oC and the crystallization temperature of 90oC

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Summary

Introduction

An unavoidable by-product of wastewater treatment plants, is classified as biomass [1]. Sewage sludge contains 40-85% of organic matter which is the source of renewable energy [2]. The recovery of energy from sewage sludge may be realized by mono-combustion and co-combustion. There are known methods of using sewage sludge ash in the production of building materials [4,5], the stabilization of soils [6] and the recovery of phosphorus [7]. The dominant method of sewage sludge ash disposal is a landfilling [8]. The landfilling of sewage sludge ash poses a threat to the natural environment [9]

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