Abstract
Heavy and light rare earth elements (REEs) are critical to clean energy technologies, and thus the environmental impacts from their production are increasingly scrutinized. Most previous LCAs of REE production focus on sites producing light REEs. This research addresses this gap by collecting primary data from sites producing heavy rare earth oxides (HREOs) from ion-adsorption clays, conducting an LCA, and providing open-source life cycle inventory (LCI) datasets of HREO production for the LCA community. This study conducts a LCA based on acquired primary data from four mining sites in Jiangxi Province, China. The functional unit is 1 kg of mixed HREOs of 90% purity from ion-adsorption clays using the technology of in situ leaching. Previous studies have used the Ecoinvent database, relying mostly on European or global life cycle inventories (LCIs). Here, the Chinese Life Cycle Database provided China-specific reference life cycle inventories (LCIs) for all inputs and processes with the exception of electricity generation LCIs used in a scenario analysis, which were provided by Ecoinvent 3. Twelve impact categories were examined using Impact 2002+, USEtox 2.01, and IPCC methods. Results are provided as a bounded range, reflecting low and high estimates based on collected primary data. Results show 1 kg of mixed HREOs emit 258–408 kg CO2e, and consume 270–443 MJ primary energy. These values fall within the range of previous LCAs that examined both bastnaesite/monazite deposits and ion-adsorption clays using literature values. Other impact categories considered are not similar across studies, however. Differences are due to variability in resource type and quality, technology, and modeling choices, such as reference LCI sources. Mining and extraction contribute most to impacts due to large quantities of chemicals for leaching and precipitation of REOs, and electricity consumption. Among chemicals, ammonium sulfate is the largest contributor to many impact categories. When China’s electricity grid mix change over time is included, environmental impacts for the whole production process can change up to 12%. The primary contributions of this study are the collection and publication of primary data from mining companies in Jiangxi Province, China; the provision of open-source LCI datasets for mixed HREOs from ion-adsorption clays; and a comparison of results between this study and previously published studies. While the scope of this study concludes at the production of mixed HREO, which is a limitation, it provides a foundation for development of LCIs for refined heavy REEs.
Highlights
Clean energy technologies, such as electric vehicles and wind turbines, have increased demand for permanent magnets, and Nd-Fe-B rare earth magnets that are used in electric motors and generators (Alonso et al 2012; Smith Stegen 2015; U.S Department of Energy 2010; Van Gosen et al 2014; Zhou et al 2017)
While the scope of this study concludes at the production of mixed heavy rare earth oxides (HREOs), which is a limitation, it provides a foundation for development of life cycle inventory (LCI) for refined heavy rare earth elements (REEs)
The goals of this research are to (1) collect and publish primary data related to the mining of ion-adsorption clays that produce mixed HREOs; (2) develop a new open-source life cycle inventory (LCI) and conduct a life cycle assessment (LCA) to augment the small but growing body of work characterizing the life cycle impacts of rare earth oxides (REOs) production from ion adsorption clays and production of heavy REOs; and (3) compare results from this LCA to others published in the literature
Summary
Clean energy technologies, such as electric vehicles and wind turbines, have increased demand for permanent magnets, and Nd-Fe-B rare earth magnets that are used in electric motors and generators (Alonso et al 2012; Smith Stegen 2015; U.S Department of Energy 2010; Van Gosen et al 2014; Zhou et al 2017). With the growth in demand for these magnets, the constituent rare earth elements (REEs), such as neodymium and dysprosium, need to be supplied at an increasing rate. Many REEs are critically important to sustainable mobility and energy supply, production of REEs incur significant environmental damages, as their widely dispersed locations and low concentrations make them energy intensive and environmentally taxing to mine, extract, and refine (Eriksson and Olsson 2011; Navarro and Zhao 2014; Schüler et al 2011). China continues to dominate the global REE supply, accounting for nearly 90% of global mine production in 2014 (Gambogi 2016)
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