Abstract

It has been shown that precipitated calcium carbonate prepared by surfactant-assisted agglomeration (PCC-SAA) provided higher capacity for the carbon dioxide capture during calcination carbonation cycling as compared to commercially available calcium carbonate. It was also shown previously that the capacity was maintained over multiple cycles while commercially available calcium carbonate significantly lost its capacity. In order to understand the differences in the calcination behaviour of the PCC-SAA sample as compared to the commercially available laboratory-grade calcium carbonate (AC) sample, a non-isothermal topochemical approach was adopted to delineate the various controlling mechanisms for calcination of CaCO3. Activation energies were calculated using iso-conversional methods such as Friedman's method, the KSA method, and the FWO method. In addition, the mechanism was identified at different heating rates by applying the Malek's method and evaluated in some cases using the JMA kinetics. Finally, four mechanisms were used to calculate the pre-exponential (frequency factor). Some key differences such as the initiation temperature, and mechanisms were found between the two samples. Generally, it was found that the differences in the two samples were primarily due to the structural causes. It was observed that the initiation temperature for CaCO3 decomposition, activation energies and mechanisms were a function of the heating rates. D2 or D4 was identified as the controlling mechanisms at lower temperatures for the PCC-SAA sample in contrast to JMA (n > 1) kinetics for the higher heating rates. For the AC sample, 3D diffusion process appears to control the calcination of the AC sample. Keywords: Greenhouse gas, precipitated calcium carbonate, surfactant-assisted agglomeration, calcination kinetics, diffusion, iso-conversional.

Highlights

  • CO2, a greenhouse gas, is produced in a number of industrial applications

  • The activation energy was found to increase with conversion for PCC-SAA sample while it was found to decrease for the available laboratory-grade calcium carbonate (AC) sample

  • Based on the data obtained from this analysis, it was concluded that the initiation temperature for CaCO3 decomposition is a function of the heating rate

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Summary

Introduction

CO2, a greenhouse gas, is produced in a number of industrial applications. To mitigate its effect on climate change, research is under way for its reduction from such industrial effluent streams. For sustained reactivity and uptake, the calcination kinetics and the degree of calcination of the CaCO3 over multiple cycles would be vital for its commercial application. The kinetics and decomposition mechanism were evaluated using a variety of calculation procedures including the FWO iso-conversion method Their results show that the selection of the proper mechanism is vital for the evaluation of the process, and the use of model-independent methods to isolate and estimate some of the parameters followed by mechanism selection is necessary for analysis. No study has been conducted to evaluate the mechanisms of calcination or carbonation of PCC to understand its differences that may elucidate its enhanced performance reported by Gupta and Fan[14] and Dasgupta et al.[11]. Malek’s method was employed to identify possible mechansims and the pre-exponent factor was estimated based on the selected models

Experimental
Random nucleation Deceleratory 1st order
Results and Discussion
Conclusions
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