Uptake and Removal of Uranium by and from Human Teeth
Uranium-238 (238U), a long-lived radiometal, is widespread in the environment because of both naturally occurring processes and anthropogenic processes. The ingestion or inhalation of large amounts of U is a major threat to humans, and its toxicity is considered mostly chemical rather than radiologi...
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Veröffentlicht in: | Chemical research in toxicology 2021-03, Vol.34 (3), p.880-891 |
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creator | Younes, Ali Ali, Jafar Sunga Duda, Artem Alliot, Cyrille Huclier-Markai, Sandrine Wang, Jasmine Kabalan, Fatima Nemirovsky, David Deng, Rebecca Nur, Mohamed Tousif Cao, Minhua Groveman, Samuel Drain, Charles Michael Alexandratos, Spiro D |
description | Uranium-238 (238U), a long-lived radiometal, is widespread in the environment because of both naturally occurring processes and anthropogenic processes. The ingestion or inhalation of large amounts of U is a major threat to humans, and its toxicity is considered mostly chemical rather than radiological. Therefore, a way to remove uranium ingested by humans from uranium-contaminated water or from the air is critically needed. This study investigated the uranium uptake by hydroxyapatite (HAP), a compound found in human bone and teeth. The uptake of U by teeth is a result of U transport as dissolved uranyl (UO2 2+) in contaminated water, and U adsorption has been linked to delays in both tooth eruption and development. In this present work, the influence of pH, contact time, initial U concentration, and buffer solution on the uptake and removal of U in synthetic HAP was investigated and modeled. The influence of pH (pH of human saliva, 6.7–7.4) on the uptake of uranyl was negligible. Furthermore, the kinetics were extremely fast; in one second of exposure, 98% of uranyl was uptaken by HAP. The uptake followed pseudo-second-order kinetics and a Freundlich isotherm model. A 0.2 M sodium carbonate solution removed all the uranyl from HAP after 1 h. Another series of in vitro tests were performed with real teeth as targets. We found that, for a 50 mg/L U in PBS solution adjusted to physiological pH, ∼35% of the uranyl was uptaken by the tooth after 1 h, following pseudo-first-order kinetics. Among several washing solutions tested, a commercially available carbonate, as well as a commercially available fluoride solution, enabled removal of all the uranyl taken up by the teeth. |
doi_str_mv | 10.1021/acs.chemrestox.0c00503 |
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The ingestion or inhalation of large amounts of U is a major threat to humans, and its toxicity is considered mostly chemical rather than radiological. Therefore, a way to remove uranium ingested by humans from uranium-contaminated water or from the air is critically needed. This study investigated the uranium uptake by hydroxyapatite (HAP), a compound found in human bone and teeth. The uptake of U by teeth is a result of U transport as dissolved uranyl (UO2 2+) in contaminated water, and U adsorption has been linked to delays in both tooth eruption and development. In this present work, the influence of pH, contact time, initial U concentration, and buffer solution on the uptake and removal of U in synthetic HAP was investigated and modeled. The influence of pH (pH of human saliva, 6.7–7.4) on the uptake of uranyl was negligible. Furthermore, the kinetics were extremely fast; in one second of exposure, 98% of uranyl was uptaken by HAP. The uptake followed pseudo-second-order kinetics and a Freundlich isotherm model. A 0.2 M sodium carbonate solution removed all the uranyl from HAP after 1 h. Another series of in vitro tests were performed with real teeth as targets. We found that, for a 50 mg/L U in PBS solution adjusted to physiological pH, ∼35% of the uranyl was uptaken by the tooth after 1 h, following pseudo-first-order kinetics. Among several washing solutions tested, a commercially available carbonate, as well as a commercially available fluoride solution, enabled removal of all the uranyl taken up by the teeth.</description><identifier>ISSN: 0893-228X</identifier><identifier>EISSN: 1520-5010</identifier><identifier>DOI: 10.1021/acs.chemrestox.0c00503</identifier><identifier>PMID: 33507734</identifier><language>eng</language><publisher>United States: American Chemical Society</publisher><subject>Chemical Sciences</subject><ispartof>Chemical research in toxicology, 2021-03, Vol.34 (3), p.880-891</ispartof><rights>2021 American Chemical Society</rights><rights>Distributed under a Creative Commons Attribution 4.0 International License</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-a388t-1f3cc5a182c016afe8b7c6057c15f67167cb433bbe4bb7341734f34ac51ecb6a3</citedby><cites>FETCH-LOGICAL-a388t-1f3cc5a182c016afe8b7c6057c15f67167cb433bbe4bb7341734f34ac51ecb6a3</cites><orcidid>0000-0001-7351-2726 ; 0000-0003-1948-6701</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><linktopdf>$$Uhttps://pubs.acs.org/doi/pdf/10.1021/acs.chemrestox.0c00503$$EPDF$$P50$$Gacs$$H</linktopdf><linktohtml>$$Uhttps://pubs.acs.org/doi/10.1021/acs.chemrestox.0c00503$$EHTML$$P50$$Gacs$$H</linktohtml><link.rule.ids>230,314,776,780,881,2751,27055,27903,27904,56716,56766</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/33507734$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink><backlink>$$Uhttps://hal.science/hal-03187713$$DView record in HAL$$Hfree_for_read</backlink></links><search><creatorcontrib>Younes, Ali</creatorcontrib><creatorcontrib>Ali, Jafar Sunga</creatorcontrib><creatorcontrib>Duda, Artem</creatorcontrib><creatorcontrib>Alliot, Cyrille</creatorcontrib><creatorcontrib>Huclier-Markai, Sandrine</creatorcontrib><creatorcontrib>Wang, Jasmine</creatorcontrib><creatorcontrib>Kabalan, Fatima</creatorcontrib><creatorcontrib>Nemirovsky, David</creatorcontrib><creatorcontrib>Deng, Rebecca</creatorcontrib><creatorcontrib>Nur, Mohamed Tousif</creatorcontrib><creatorcontrib>Cao, Minhua</creatorcontrib><creatorcontrib>Groveman, Samuel</creatorcontrib><creatorcontrib>Drain, Charles Michael</creatorcontrib><creatorcontrib>Alexandratos, Spiro D</creatorcontrib><title>Uptake and Removal of Uranium by and from Human Teeth</title><title>Chemical research in toxicology</title><addtitle>Chem. Res. Toxicol</addtitle><description>Uranium-238 (238U), a long-lived radiometal, is widespread in the environment because of both naturally occurring processes and anthropogenic processes. The ingestion or inhalation of large amounts of U is a major threat to humans, and its toxicity is considered mostly chemical rather than radiological. Therefore, a way to remove uranium ingested by humans from uranium-contaminated water or from the air is critically needed. This study investigated the uranium uptake by hydroxyapatite (HAP), a compound found in human bone and teeth. The uptake of U by teeth is a result of U transport as dissolved uranyl (UO2 2+) in contaminated water, and U adsorption has been linked to delays in both tooth eruption and development. In this present work, the influence of pH, contact time, initial U concentration, and buffer solution on the uptake and removal of U in synthetic HAP was investigated and modeled. The influence of pH (pH of human saliva, 6.7–7.4) on the uptake of uranyl was negligible. Furthermore, the kinetics were extremely fast; in one second of exposure, 98% of uranyl was uptaken by HAP. The uptake followed pseudo-second-order kinetics and a Freundlich isotherm model. A 0.2 M sodium carbonate solution removed all the uranyl from HAP after 1 h. Another series of in vitro tests were performed with real teeth as targets. We found that, for a 50 mg/L U in PBS solution adjusted to physiological pH, ∼35% of the uranyl was uptaken by the tooth after 1 h, following pseudo-first-order kinetics. 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Res. Toxicol</addtitle><date>2021-03-15</date><risdate>2021</risdate><volume>34</volume><issue>3</issue><spage>880</spage><epage>891</epage><pages>880-891</pages><issn>0893-228X</issn><eissn>1520-5010</eissn><abstract>Uranium-238 (238U), a long-lived radiometal, is widespread in the environment because of both naturally occurring processes and anthropogenic processes. The ingestion or inhalation of large amounts of U is a major threat to humans, and its toxicity is considered mostly chemical rather than radiological. Therefore, a way to remove uranium ingested by humans from uranium-contaminated water or from the air is critically needed. This study investigated the uranium uptake by hydroxyapatite (HAP), a compound found in human bone and teeth. The uptake of U by teeth is a result of U transport as dissolved uranyl (UO2 2+) in contaminated water, and U adsorption has been linked to delays in both tooth eruption and development. In this present work, the influence of pH, contact time, initial U concentration, and buffer solution on the uptake and removal of U in synthetic HAP was investigated and modeled. The influence of pH (pH of human saliva, 6.7–7.4) on the uptake of uranyl was negligible. Furthermore, the kinetics were extremely fast; in one second of exposure, 98% of uranyl was uptaken by HAP. The uptake followed pseudo-second-order kinetics and a Freundlich isotherm model. A 0.2 M sodium carbonate solution removed all the uranyl from HAP after 1 h. Another series of in vitro tests were performed with real teeth as targets. We found that, for a 50 mg/L U in PBS solution adjusted to physiological pH, ∼35% of the uranyl was uptaken by the tooth after 1 h, following pseudo-first-order kinetics. 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title | Uptake and Removal of Uranium by and from Human Teeth |
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