Abstract

Elastic properties of mixtures of illitic clay, thermal power plant fly ash (fluidized fly ash—FFA and pulverized fly ash—PFA), and grog were investigated during the heating and cooling stages of the firing. The grog part in the mixtures was replaced with 10, 20, 30, and 40 mass% of the fly ash, respectively. The temperature dependence of Young’s modulus was derived using the dynamical thermomechanical analysis, in which dimensions and mass determined from thermogravimeric and thermodilatometric results were used. Flexural strength was measured at the room temperature using the three-point bending test. The following results were obtained: (1) Bulk density showed a decreasing trend up to 900 °C and a steep increase above 900 °C. During cooling, the bulk density slightly increased down to the room temperature. (2) Young’s modulus increased significantly during heating up to ~300 °C. Dehydroxylation was almost not reflected in Young’s modulus. At temperatures higher than 800 °C, Young’s modulus began to increase due to sintering. (3) During cooling, down to the glass transformation, Young’s modulus slightly increased and then began to slightly decrease due to microcracking between phases with different thermal expansion coefficients. (4) Around the β→α quartz transition, radial stresses on the quartz grain altered from compressive to tensile, creating microcracks. Below 560 °C, the radial stress remained tensile, and consequently, the microcracking around the quartz grains and a decreasing Young’s modulus continued. (5) With a lower amount of PFA and FFA, a higher Young’s modulus was reached after sintering. The final values of Young’s modulus, measured after firing, show a decreasing trend and depend linearly on the part of fly ash. (6) The flexural strength measured after firing decreased linearly with the amount of the fly ash for both mixtures.

Highlights

  • Industrial and agricultural sectors and cities produce large amounts of waste

  • Fly ash from a fluidized bed combustion boiler operating at 850 ◦ C (FFA), fly ash from a pulverized combustion boiler operating at 1400 ◦ C (PFA)

  • The differential thermal analysis (DTA) shows that the samples with pulverized firing fly ash (PFA) and fluidized fly ash (FFA)

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Summary

Introduction

Industrial and agricultural sectors and cities produce large amounts of waste. Waste is grouped based on the source and effects into four main categories: sewage sludge, ashes, inorganic and organic wastes [1]. As societies strive to develop new ways to recycle and incorporate waste into new products, they must consider the large mass flow and high temperatures required to make such processes viable. One type of waste with a high potential for use in ceramic materials is fly ash, a by-product of coal combustion in thermal power-plants. Fly ash is often stored in landfills, where it is a source of pollution of surrounding areas in the form of dust and toxic substances, such as heavy metals and sulfur compounds.

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