Abstract

The decrease in the calorific value of refuse-derived fuel (RDF) is an unintended outcome of the progress made toward more sustainable waste management. Plastics and paper separation and recycling leads to the overall decrease in waste’s calorific value, further limiting its applicability for thermal treatment. Pyrolysis has been proposed to densify energy in RDF and generate carbonized solid fuel (CSF). The challenge is that the feedstock composition of RDF is variable and site-specific. Therefore, the optimal pyrolysis conditions have to be established every time, depending on feedstock composition. In this research, we developed a model to predict the higher heating value (HHV) of the RDF composed of eight morphological refuse groups after low-temperature pyrolysis in CO2 (300–500 °C and 60 min) into CSF. The model considers cardboard, fabric, kitchen waste, paper, plastic, rubber, PAP/AL/PE (paper/aluminum/polyethylene) composite packaging pack, and wood, pyrolysis temperature, and residence time. The determination coefficients (R2) and Akaike information criteria were used for selecting the best model among four mathematical functions: (I) linear, (II) second-order polynomial, (III) factorial regression, and (IV) quadratic regression. For each RDF waste component, among these four models, the one best fitted to the experimental data was chosen; then, these models were integrated into the general model that predicts the HHV of CSF from the blends of RDF. The general model was validated experimentally by the application to the RDF blends. The validation revealed that the model explains 70–75% CSF HHV data variability. The results show that the optimal pyrolysis conditions depend on the most abundant waste in the waste mixture. High-quality CSF can be obtained from wastes such as paper, carton, plastic, and rubber when processed at relatively low temperatures (300 °C), whereas wastes such as fabrics and wood require higher temperatures (500 °C). The developed model showed that it is possible to achieve the CSF with the highest HHV value by optimizing the pyrolysis of RDF with the process temperature, residence time, and feedstock blends pretreatment.

Highlights

  • IntroductionThe market for alternative fuels such as RDF/SRF (refuse-derived fuel/solid recovered fuel) is developing dynamically, and optimization processes of waste used in the energy industry are sought to increase the efficiency of the process

  • For the first time, we provide regression models for higher heating value (HHV) prediction for main morphological groups of refuse-derived fuel (RDF) carbonized under low-temperature pyrolysis (300–500 ◦C, up to 60 min), and one general predictive model for the estimation of HHV of a carbonized solid fuel (CSF) derived from RDF

  • The eight regression models for individual main components with the best fitting to experimental data were provided and described. These models can predict an HHV of the carbonized carton, fabric kitchen waste, paper, plastic, rubber, PAP/AL/PE composite packaging pack, and wood, based on pyrolysis temperature and residence time

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Summary

Introduction

The market for alternative fuels such as RDF/SRF (refuse-derived fuel/solid recovered fuel) is developing dynamically, and optimization processes of waste used in the energy industry are sought to increase the efficiency of the process. The RDF is an alternative fuel produced from the combustible fraction of municipal solid waste. In Poland, RDF is co-fired with other conventional fuels in cement kilns, and the annual consumption of alternative fuel is approximately 1.6 mln Mg [1,2]. The calorific value of RDF fuel is one of the key parameters determining the fuel quality and varies in the range of 15–21 MJ·kg−1. The important criteria for the quality of RDF are ash content of ≈3.4–16% and moisture content, which must not exceed 20% [3]

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