Abstract

In the paper, results of drying biofuels from sewage sludge using solar energy are presented. Drying rates of biofuels made from sewage sludge and coal slime (PBS), sewage sludge and meat and bone meal (PBM), and sewage sludge and sawdust (PBT) with 15-mm and 35-mm granule particle size were studied. Tests were performed in a solar greenhouse dryer equipped with a specially designed mixing system. Experiments were aimed at determining the drying time of biofuels under various weather conditions in the southwestern part of Poland. In summer, in order to determine the best conditions for drying, tests were performed using various parameters, i.e., layers of various thickness, such as 5, 10, and 20 cm, and various mixing intensity (no mixing, mixing 3 and 5 times/day). In spring and the fall, 10-cm thick layers combined with 5 times mixing of fuels per day were used. The performed tests demonstrated that it is beneficial to dry fuels in 10-cm thick layer. In spring and the fall, PBS and PBM biofuels laid out in layers with just such thickness showed moisture content reduced to less than 10% after 8 days, while the PBT biofuel reached the same level after 14 days. In summer, the same result may be obtained for all the biofuels after 4 days on average. The presented original method of solar drying of biofuels obtained from sewage sludge and other waste may be used in wastewater treatment plants which process sewage sludge into fuels without incurring any additional costs for supplying heat.

Highlights

  • Sewage sludge management is one of the significant challenges of wastewater management in Poland

  • One of the methods applied to significantly reduce both the mass and volume of sewage sludge involves thermal processes, such as combustion, pyrolysis, or gasification (Fonts et al 2012; Oladejo et al 2019)

  • The method for production of various types of biofuels from sewage sludge, such as sewage sludge with coal slimePBS, sewage sludge with meat and bone meal-PBM, or sewage sludge with sawdust-PBT, makes it possible to choose the type of biofuel to be produced depending on locally available waste

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Summary

Introduction

Sewage sludge management is one of the significant challenges of wastewater management in Poland. Sewage sludge represents a major type of waste produced by wastewater treatment plants and accounts for roughly 1–2% of the total amount volume of wastewater treated. Its disposal can add significant energy demand to the already high requirements of a treatment plant (Capodaglio and Olsson 2020). An amount of sewage sludge cannot be prevented and is disposed in line with the requirements regarding the quality of treated sewage. A total of 3253 municipal wastewater treatment plants were operating in Poland in 2019, which is almost three times as many when compared to 1995, serving more than 28.5 million. The resulting relationship is quite simple—the more sophisticated waste treatment technologies, the more sewage sludge is generated which is harder to dispose of

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