Valorization of polluted biomass waste for the fabrication of Gas Diffusion Electrodes for CO2 electroreduction to formate.
Iker Uriarte-Porres a, Jose Antonio Abarca a, Alvaro Ramirez b, Martin Muñoz-Morales b, Javier Llanos b, Guillermo Díaz-Sainz a, Manuel Alvarez-Guerra a, Angel Irabien a
a Departamento de Ingenierías Química y Biomolecular, Universidad de Cantabria, Avenida de los Castros s/n, 39005 Santander, Spain
b Department of Chemical Engineering, Faculty of Chemical Sciences & Technologies, Ciudad Real, Universidad de Castilla-La Mancha, Ciudad Real 13071, Spain
Materials for Sustainable Development Conference (MATSUS)
Proceedings of MATSUS Fall 2024 Conference (MATSUSFall24)
#PECCO2 - Advances in (Photo)Electrochemical CO2 Conversion to Chemicals and Fuels
Lausanne, Switzerland, 2024 November 12th - 15th
Organizers: Deepak PANT, Adriano Sacco and juqin zeng
Poster, Guillermo Díaz-Sainz, 362
Publication date: 28th August 2024

Climate Change is a phenomenon driven by anthropogenic activities, such as the combustion of fossil fuels, which results in large amount of greenhouse gas emissions. To address this issue, clear objectives must be established. One of the primary goals of the United Nations Conference (COP 28) is to reduce greenhouse gas emissions by 43% by 2030 while limiting the global temperature increase to 1.5°C. Among the various CO2 mitigation strategies, Carbon Capture and Utilization (CCU) to produce useful and renewable chemicals is particularly promising, as it fosters the development of new carbon-neutral techniques using renewable energy sources.

Currently, various approaches have been developed to activate and convert CO2. Among these, the electrochemical reduction of CO2 offers an attractive solution, as it combines the reduction of CO2 emissions with the production of value-added products such as formic acid or formate [1]. The gas diffusion electrode (GDE), the most common and effective configuration for CO2 electrochemical reduction to formic acid and formate, consists of three layers: (i) a carbonaceous support, (ii) a microporous layer, and (iii) a catalytic layer. While the catalytic layer has been extensively studied, the microporous layer plays a crucial role by imparting hydrophobic properties, preventing flooding, and enhancing contact between the CO2 stream and the catalyst [2].

The most common material used for the microporous layer is carbon black, produced through the incomplete combustion of petroleum-derived hydrocarbons. However, these materials have drawbacks that impact both the environment and human health. Therefore, this study focuses on evaluating the performance of GDEs made from biomass materials sourced from phytoremediation processes to create an environmentally friendly microporous layer for the GDEs.

The carbon materials used to fabricate the GDEs were synthesized from three different lignocellulosic species: Phragmites australis, Cladium mariscus and Typha domingensis. These materials were initially subjected to hydrothermal carbonization with a biomass-to-water ratio of 130 g L-1 (200 ºC, 2 h under self-generated pressure). The resulting hydrochar was then further processed through either pyrolysis or chemical activation (with KOH). These materials have demonstrated their effectiveness in generating H2O2 [3] and have the potential to help mitigate climate change by enabling the CO2 electrochemical reduction to formate.

The best results were obtained with a mixture of biomass materials and Vulcan XC-72R (50% wt), achieving a formate concentration of 1.8 g·L−1 at 90 mA·cm−2. The experiment demonstrated a high Faradaic efficiency of nearly 80% and slightly lower energy consumption compared to Vulcan XC-72R alone, based on absolute cell potentials. In conclusion, these new materials combined with Vulcan XC-72R (50% wt) could help reduce soil contamination and mitigate the impact of climate change through CO2 electrochemical reduction to formate, achieving results comparable to those of the microporous layer made with carbon black.

The authors gratefully acknowledge financial support through projects TED2021-129810B-C21, PLEC2022-009398 (MCIN/AEI/10.13039/501100011033 and Unión Europea Next GenerationEU/PRTR), PID2022-138491OB-C31 and PID2022-141265OB-I00 (MICIU/AEI /10.13039/501100011033 and FEDER, UE) and the Complementary Plan in the area of Energy and Renewable Hydrogen” (funded by Autonomous Community of Cantabria, Spain, and the European Union Next GenerationEU/PRTR). The present work is related to CAPTUS Project. This project has received funding from the European Union’s Horizon Europe research and innovation programme under grant agreement No 101118265​. Jose Antonio Abarca gratefully acknowledges the predoctoral research grant (FPI) PRE2021-097200.

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