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Evaluation of materials for iodine and technetium immobilization through sorption and redox-driven processes.
Pearce, Carolyn I; Cordova, Elsa A; Garcia, Whitney L; Saslow, Sarah A; Cantrell, Kirk J; Morad, Joseph W; Qafoku, Odeta; Matyás, Josef; Plymale, Andrew E; Chatterjee, Sayandev; Kang, Jaehyuk; Colon, Ferdinan Cintron; Levitskaia, Tatiana G; Rigali, Mark J; Szecsody, Jim E; Heald, Steve M; Balasubramanian, Mahalingam; Wang, Shuao; Sun, Daniel T; Queen, Wendy L; Bontchev, Ranko; Moore, Robert C; Freedman, Vicky L.
Afiliação
  • Pearce CI; Pacific Northwest National Laboratory, Richland, WA, United States of America. Electronic address: carolyn.pearce@pnnl.gov.
  • Cordova EA; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Garcia WL; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Saslow SA; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Cantrell KJ; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Morad JW; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Qafoku O; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Matyás J; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Plymale AE; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Chatterjee S; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Kang J; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Colon FC; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Levitskaia TG; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Rigali MJ; Sandia National Laboratories, Albuquerque, NM, United States of America.
  • Szecsody JE; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Heald SM; Advanced Photon Source, Argonne National Laboratory, Argonne, IL 60439, United States of America.
  • Balasubramanian M; Advanced Photon Source, Argonne National Laboratory, Argonne, IL 60439, United States of America.
  • Wang S; State Key Laboratory of Radiation Medicine and Protection, School for Radiological and interdisciplinary Sciences (RAD-X) and Collaborative Innovation Center of Radiation Medicine of Jiangsu Higher Education Institutions, Soochow University, Suzhou 215123, China.
  • Sun DT; EPFL Valais Wallis, Laboratory for Functional Inorganic Materials, 1951 Sion, Switzerland.
  • Queen WL; EPFL Valais Wallis, Laboratory for Functional Inorganic Materials, 1951 Sion, Switzerland.
  • Bontchev R; Monrovia, CA, United States of America.
  • Moore RC; Pacific Northwest National Laboratory, Richland, WA, United States of America.
  • Freedman VL; Pacific Northwest National Laboratory, Richland, WA, United States of America.
Sci Total Environ ; 716: 136167, 2020 May 10.
Article em En | MEDLINE | ID: mdl-31955840
ABSTRACT
Radioactive iodine-129 (129I) and technetium-99 (99Tc) pose a risk to groundwater due to their long half-lives, toxicity, and high environmental mobility. Based on literature reviewed in Moore et al. (2019) and Pearce et al. (2019), natural and engineered materials, including iron oxides, low-solubility sulfides, tin-based materials, bismuth-based materials, organoclays, and metal organic frameworks, were tested for potential use as a deployed technology for the treatment of 129I and 99Tc to reduce environmental mobility. Materials were evaluated with metrics including capacity for IO3- and TcO4- uptake, selectivity and long-term immobilization potential. Batch testing was used to determine IO3- and TcO4- sorption under aerobic conditions for each material in synthetic groundwater at different solution to solid ratios. Material association with IO3- and TcO4- was spatially resolved using scanning electron microscopy and X-ray microprobe mapping. The potential for redox reactions was assessed using X-ray absorption near edge structure spectroscopy. Of the materials tested, bismuth oxy(hydroxide) and ferrihydrite performed the best for IO3-. The commercial Purolite A530E anion-exchange resin outperformed all materials in its sorption capacity for TcO4-. Tin-based materials had high capacity for TcO4-, but immobilized TcO4- via reductive precipitation. Bismuth-based materials had high capacity for TcO4-, though slightly lower than the tin-based materials, but did not immobilize TcO4- by a redox-drive process, mitigating potential negative re-oxidation effects over longer time periods under oxic conditions. Cationic metal organic frameworks and polymer networks had high Tc removal capacity, with TcO4- trapped within the framework of the sorbent material. Although organoclays did not have the highest capacity for IO3- and TcO4- removal in batch experiments, they are available commercially in large quantities, are relatively low cost and have low environmental impact, so were investigated in column experiments, demonstrating scale-up and removal of IO3- and TcO4- via sorption, and reductive immobilization with iron- and sulfur-based species.
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Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Idioma: En Ano de publicação: 2020 Tipo de documento: Article

Texto completo: 1 Coleções: 01-internacional Base de dados: MEDLINE Idioma: En Ano de publicação: 2020 Tipo de documento: Article