4.8 Article

LCA of Disposal Practices for Arsenic-Bearing Iron Oxides Reveals the Need for Advanced Arsenic Recovery

Journal

ENVIRONMENTAL SCIENCE & TECHNOLOGY
Volume 56, Issue 19, Pages 14109-14119

Publisher

AMER CHEMICAL SOC
DOI: 10.1021/acs.est.2c0541714109

Keywords

life cycle assessment; landfill disposal; waste management; water treatment residuals; arsenic contamination; circular economy

Funding

  1. Geocenter Danmark start-up grant
  2. Independent Research Fund Denmark (IRFD) [1127-00207B]
  3. U.S. Department of Energy [DE-AC02-05CH11231]
  4. LBNL

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This study compared the toxicity impacts of four common arsenic disposal strategies and found that landfilling had the lowest toxicity impacts but still posed a storage toxicity problem. Other disposal strategies had significantly higher human toxicity and ecotoxicity impacts compared to landfilling. The findings highlight the urgent need for new arsenic recovery technologies to decrease toxicity and emissions.
Iron (Fe)-based groundwater treatment removes carcinogenic arsenic (As) effectively but generates toxic As-rich Fe oxide water treatment residuals (As WTRs) that must be managed appropriately to prevent environmental contamination. In this study, we apply life cycle assessment (LCA) to compare the toxicity impacts of four common As WTR disposal strategies that have different infrastructure requirements and waste control: (i) landfilling, (ii) brick stabilization, (iii) mixture with organic waste, and (iv) open disposal. The As disposal toxicity impacts (functional unit = 1.0 kg As) are compared and benchmarked against impacts of current methods to produce marketable As compounds via As mining and concentrate processing. Landfilling had the lowest non-carcinogen toxicity (2.0 x 10-3 CTUh), carcinogen toxicity (3.8 x 10-5 CTUh), and ecotoxicity (4.6 x 103 CTUe) impacts of the four disposal strategies, with the largest toxicity source being As emission via sewer discharge of treated landfill leachate. Although landfilling had the lowest toxicity impacts, the stored toxicity of this strategy was substantial (ratio of stored toxicity/emitted As = 13), suggesting that landfill disposal simply converts direct As emissions to an impending As toxicity problem for future generations. The remaining disposal strategies, which are frequently practiced in low-income rural As-affected areas, performed poorly. These strategies yielded similar to 3-10 times greater human toxicity and ecotoxicity impacts than landfilling. The significant drawbacks of each disposal strategy indicated by the LCA highlight the urgent need for new methods to recover As from WTRs and convert it into valuable As compounds. Such advanced As recovery technologies, which have not been documented previously, would decrease the stored As toxicity and As emissions from both WTR disposal and from mining As ore.

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