The Impact of Aluminosilicate Additives upon the Chlorine Distribution and Melting Behavior of Poultry Litter Ash
Author:
Maj Izabella1ORCID, Niesporek Kamil1ORCID, Matus Krzysztof2ORCID, Miccio Francesco3ORCID, Mazzocchi Mauro3, Łój Paweł4
Affiliation:
1. Department of Power Engineering and Turbomachinery, Faculty of Energy and Environmental Engineering, Silesian University of Technology, 44-100 Gliwice, Poland 2. Materials Research Laboratory, Faculty of Mechanical Engineering, Silesian University of Technology, 44-100 Gliwice, Poland 3. Institute of Science, Technology and Sustainability for Ceramics, Italian National Research Council, via Granarolo 64, 84018 Faenza, Italy 4. Department of Fundamentals of Machinery Design, Faculty of Mechanical Engineering, Silesian University of Technology, 44-100 Gliwice, Poland
Abstract
The use of poultry litter (PL) as a sustainable fuel is gaining more attention due to its wide availability and carbon neutrality. However, this type of feedstock is rich in ash and typically contains a high concentration of chlorine (Cl) and alkali elements (Na, K). Therefore, it is likely to cause unwanted issues during combustion and co-combustion, such as chlorine-induced corrosion, ash deposition, and bed agglomeration. In this study, for the first time, the influence of aluminosilicate additives on the above problems of poultry litter was investigated. Three aluminosilicate minerals are under consideration: kaolin, halloysite, and bentonite. Their influence on the chemical composition and meting tendencies of two poultry litter ashes are determined. The investigated ashes, PL1 and PL2, are characterized by different chlorine contents of 6.38% and 0.42%, respectively. The results show that in the case of the chlorine-rich PL1 ash, the additives reduced the chlorine content by up to 45%, resulting in a 3.93% of chlorine in the case of halloysite, 3.48% in the case of kaolin, and 4.25% in the case of bentonite. The additives also positively influenced the shrinkage starting temperature and the deformation temperature of the PL1 ash.
Funder
National Science Centre, Poland National Recovery and Resilience Plan
Reference67 articles.
1. (2023, October 04). Bioenergy—IEA. Available online: https://www.iea.org/energy-system/renewables/bioenergy. 2. Understanding Heavy Metal in the Conversion of Biomass Model Component: Migration and Transformation Characteristics of Cu during Hydrothermal Carbonization of Cellulose;Zhao;Energy,2024 3. Yu, S., Yang, X., Zhou, H., Tan, Z., Cong, K., Zhang, Y., and Li, Q. (2021). Thermal and Kinetic Behaviors during Co-Pyrolysis of Microcrystalline Cellulose and Styrene–Butadiene–Styrene Triblock Copolymer. Processes, 9. 4. Yu, S., He, J., Zhang, Z., Sun, Z., Xie, M., Xu, Y., Bie, X., Li, Q., Zhang, Y., and Sevilla, M. (2024). Towards Negative Emissions: Hydrothermal Carbonization of Biomass for Sustainable Carbon Materials. Adv. Mater., e2307412. 5. An Overview of Biomass Solid Fuels: Biomass Sources, Processing Methods, and Morphological and Microstructural Properties;Ibitoye;J. Bioresour. Bioprod.,2023
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