Abstract

In this study, plasma reforming of toluene as a tar model compound from biomass gasification has been carried out using an AC gliding arc discharge reactor. The influence of steam and CO2 addition on the reforming of toluene has been evaluated. The results show that the highest toluene conversion (59.9%) was achieved when adding 3 vol% CO2 at a toluene concentration of 16.1 g/Nm3 and a specific energy input of 0.25 kWh/m3. Further increasing CO2 concentration to 12 vol% decreased the conversion of toluene. The presence of steam in the plasma CO2 reforming of toluene creates oxidative OH radicals which contribute to the enhanced conversion of toluene and energy efficiency of the plasma reforming process through stepwise oxidation of toluene and reaction intermediates. Hydrogen and C2H2 were identified as the major gas products in the plasma reforming of toluene without CO2 or steam, with a yield of 9.7% and 14.5%, respectively, while syngas was the primary products with a maximum yield of 58.3% (27.5% for H2 and 30.8% for CO) in the plasma reforming with the addition of 12 vol% CO2. The plausible reaction pathways and mechanism in the plasma reforming of toluene have been proposed through the combination of the analysis of gas and condensed products and spectroscopic diagnostics.

Highlights

  • One of the major challenges in the gasification of biomass waste is the contamination of producer gas with tar, an undesirable by-product, consisting of mixed condensable aromatics [1]

  • The influence of C­ O2 and steam on the reforming of toluene has been investigated in a gliding arc discharge reactor

  • We find that both C­ O2 and steam significantly affect the conversion of toluene and the production of gas and liquid products

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Summary

Introduction

One of the major challenges in the gasification of biomass waste is the contamination of producer gas with tar, an undesirable by-product, consisting of mixed condensable aromatics [1]. The concentration of tar in producer gas is in the range of 1–100 g/Nm3, depending on the processing conditions and the type of gasifier, while the acceptable level of tar in the downstream facilities should be less than 100 mg/Nm3 [3, 4]. The physical separation process is efficient for the removal of tars with a low concentration and simple structure. This process might not work if the concentration and number of rings of aromatic molecules increase. Rapid deactivation of the catalysts resulted from catalyst agglomeration, poisoning, and coke deposition remains a critical challenge for this process to be used on a commercial scale due to the complex composition of tars and relatively high operation temperatures (over 600 °C) [9]

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