Abstract

Photovoltaic panels were included in EU Directive as WEEE (Wastes of Electric and Electronic Equipment) requiring the implementation of dedicated collection schemes and end-of-life treatment ensuring targets in terms of recycling rate (80%) and recovery rate (85%). Photovoltaic panels are mainly made up of high-quality solar glass (70–90%), but also metals are present in the frames (Al), the cell (Si), and metallic contacts (Cu and Ag). According to the panel composition, about $72 per 100 kg of panels can be recovered by entirely recycling the panel metal content. The PhotoLife process for the treatment of end-of-life photovoltaic panels was demonstrated at pilot scale to recycle high value glass, Al and Cu scraps. A process upgrade is here reported allowing for polymer separation and Ag and Si recycling. By this advanced PhotoLife process, 82% recycling rate, 94% recovery rate, and 75% recoverable value were attained. Simulations demonstrated the economic feasibility of the process at processing capacity of 30,000 metric ton/y of end-of-life photovoltaic panels.

Highlights

  • One of the major challenges that humanity is facing is to promote the transition from traditional fossil fuels to long-term sustainable energies [1]

  • The main objective of this work is assessing the technical and economic feasibility of an upgraded recycling process including the refining of the polymeric-cell mixture. This process, hereafter referred to as ‘advanced PhotoLife process’, was simulated based on preliminary data derived by lab scale research activities

  • The coarse fraction is further treated by organic solvents, resulting in high quality glass (>3 mm), metallic filaments made of copper, and a polymeric residue containing the photovoltaic panels (PVPs) back sheet, and the EVA encapsulant still glued to the Si cell fragments (Figure 4)

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Summary

Introduction

One of the major challenges that humanity is facing is to promote the transition from traditional fossil fuels to long-term sustainable energies [1]. Photovoltaic (PV) technology has become a competitive technological alternative allowing to reach appreciable power production by conversion of solar energy into electricity [2]. Si-crystalline photovoltaic panels (PVPs) currently represent the dominating technology [3]. The application of alternative PV technologies, such as the thin-film Cd-Te and CIGS panels, is limited by the application of toxic metals (Cd in Cd-Te) and rare elements (In and Ga in CIGS) [5], which contributes to consolidate the dominating market position of the Si based panels [3]. Taking into consideration the PVPs market growth recorded over the past decades [6], a progressively increasing annual flux of the end-of-life (EOL) PVPs is foreseen. It is predicted that about 8 and 78 million EOL-PVPs tons could be generated within 2030 and 2050, respectively [7]

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