Comparison of life cycle assessment between hydrogen production from silicon waste and alkaline water electrolysis.

Sci Total Environ

Faculty of Metallurgical and Energy Engineering, Kunming University of Science and Technology, Kunming 650093, PR China; State Key Laboratory of Complex Nonferrous Metal Resources Clean Utilization, Kunming University of Science and Technology, Kunming 650093, PR China; National Engineering Research Center for Vacuum Metallurgy, Kunming 650093, PR China.

Published: April 2024

AI Article Synopsis

  • Global warming is leading to increased scrutiny of environmental issues, particularly in materials like crystalline silicon used in photovoltaics and semiconductors, which produces significant silicon waste during cutting.
  • The article assesses the environmental impacts of hydrogen production using diamond-wire sawing silicon waste (DSSW) compared to alkaline water electrolysis (AEL), with findings showing that the hydrogen production stage in the DSSW method has substantial environmental impacts.
  • While the DACH route (using DSSW) has a higher environmental impact than the AEL route, it's primarily due to raw material use, whereas AEL’s impact stems from electricity consumption; using renewable energy for AEL could greatly lessen its environmental effects.

Article Abstract

With global warming becoming increasingly severe, environmental issues are receiving international attention. Crystalline silicon is an indispensable and important raw material for photovoltaic and semiconductor fields, but the cutting of crystalline silicon materials generates a large amount of silicon wastes. This article evaluates the environmental impact of a hydrogen production process using diamond-wire sawing silicon waste (DSSW) using the life cycle assessment (LCA) methodology. For comparison, it was also analyzed the environmental impact of the alkaline water electrolysis (AEL) hydrogen production route. In the DSSW alkaline catalyzed hydrolysis (DACH) hydrogen production route, the hydrogen production stage accounts for the main contribution of nine environmental impact indexes, including GWP, PED, ADP, AP, EP, ODP, ET, HT-cancer, and HT-non cancer, exceeding 56 %. Whereas for the AEL route, the environmental impacts of the electrolytic cell manufacturing stage can be neglected, and the operating stage contributes almost all the environmental impacts, contributing more than 92 % to the twelve environmental impact indexes. Compared to the AEL route, the DACH route has higher environmental impacts, with GWP index reaching 87.78 kg CO -eq/kg H, PED index reaching 1772.90 MJ/kg H, and IWU index reaching 622.37 kg/kg H which are 2.85, 4.07 and 7.56 times higher than the former, respectively. Although the environmental impact of the DACH route is significant, most of its indirect impacts were caused by the use of raw materials, and the energy consumption and direct environmental impact are both low. The environmental impact of the AEL route is mainly indirect effects generated due to the use of electricity. If clean renewable energy sources (e.g., solar PV, hydropower, geothermal or biofuels), were used for the AEL route, all twelve environmental impact indexes would be significantly reduced.

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Source
http://dx.doi.org/10.1016/j.scitotenv.2024.171065DOI Listing

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