Abstract

Neodymium and dysprosium are two rare earth elements (REEs), out of a group of 17 elements. Due to their unique properties, REEs gained increasing importance in many new technologies, like wind turbines, batteries, etc. However, the production of REEs requires high material and energy consumption and is associated with considerable environmental burdens. Due to the strong dependency of European industry on Chinese REE exports, this paper presents a possible European production chain of REEs based on the mineral eudialyte found in Norra Kärr (Sweden). This European production is compared to a Chinese route, as China produces more than 85% of today’s REEs. Bayan Obo as the largest REE deposit in China is considered as the reference system. Using the life cycle assessment method, the environmental impacts of both production lines are assessed. This study presents newly-estimated data of a possible Swedish eudialyte-based production route for Europe. Results for the new eudialyte process route show reduced environmental burdens, although the total REE content in eudialyte is much smaller than in the Bayan Obo deposit. Especially, the results for dysprosium from eudialyte outreach those for Bayan Obo due to the higher content of heavy rare earth elements.

Highlights

  • Today, the production of rare earth elements (REE) mainly takes place in China with approximately85% of the total world mine production of 124,000 t of rare earth oxide (REO) equivalents in 2015 [1].European industries are totally dependent on imports of REEs

  • Resources 2016, 5, 32 share of heavy rare earth elements (HREEs) (up to 50% of total rare earth oxide (TREO))

  • This paper focuses on the comparison of the environmental impacts of a hypothetical European supply chain in Sweden to those of today’s Bayan Obo route in Inner Mongolia

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Summary

Introduction

The production of rare earth elements (REE) mainly takes place in China with approximately. Beside Norra Kärr, eight further deposits (2 in Russia, 3 in Canada, 2 in Greenland, 1 in Malawi) show high potential for future mining of REEs [5,6]. Schüler et al [20] and Binnemans et al [21] widen the scope by comparing primary production to recycling of REEs. This paper focuses on the comparison of the environmental impacts of a hypothetical European supply chain in Sweden to those of today’s Bayan Obo route in Inner Mongolia. European environmental legislation inhibits uncontrolled release into the environment to prevent damages to humans and nature [22,23,24]

Method-Life Cycle Assessment
Goal and Scope Definition
Neodymium and Dysprosium Production
Mining
Beneficiation
Cracking and Separation
RE Metal Production
Process Chain Modelling
Procedure
Life Cycle Impact Assessment
Normalized
Data single process of the process chain is assigned withwith a data
Findings
Interpretation and Conclusion
Full Text
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