Tissue-Specific Toxicokinetics of Aqueous Radium-226 in an Estuarine Mussel, Geukensia demissa
Radiological contamination of coastal habitats poses potential risk for native fauna, but the bioavailability of aqueous radium (Ra) and other dissolved metals to marine bivalves remains unclear. This study was the first to examine the tissue-specific disposition of aqueous Ra in a coastal mussel, s...
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Veröffentlicht in: | Environmental science & technology 2023-02, Vol.57 (8), p.3187-3197 |
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creator | Donaher, Sarah E Dunn, Robert P Gonzales, Annelise K Wattier, Bryanna D Powell, Brian A Martinez, Nicole E |
description | Radiological contamination of coastal habitats poses potential risk for native fauna, but the bioavailability of aqueous radium (Ra) and other dissolved metals to marine bivalves remains unclear. This study was the first to examine the tissue-specific disposition of aqueous
Ra in a coastal mussel, specifically the Atlantic ribbed mussel
. Most organ groups reached steady-state concentrations within 7 days during experimental exposure, with an average uptake rate constant of 0.0013 mL g
d
. When moved to Ra-free synthetic seawater, mussels rapidly eliminated aqueous
Ra (average elimination rate constant 1.56 d
). The biological half-life for aqueous
Ra ranged from 8.9 h for the gills and labial palps to 15.4 h for the muscle. Although previous field studies have demonstrated notable
Ra accumulation in the soft tissues of marine mussels and that, for freshwater mussels, tissue-incorporated
Ra derives primarily from the aqueous phase, our tissue-specific bioconcentration factors (BCFs) were on the order of (8.3 ± 1.5) × 10
indicating low accumulation potential of aqueous
Ra in estuarine mussels. This suggests marine and estuarine mussels obtain
Ra from an alternate route, such as particulate-sorbed Ra ingested during filter-feeding or from a contaminated food source. |
doi_str_mv | 10.1021/acs.est.2c09421 |
format | Article |
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Ra in a coastal mussel, specifically the Atlantic ribbed mussel
. Most organ groups reached steady-state concentrations within 7 days during experimental exposure, with an average uptake rate constant of 0.0013 mL g
d
. When moved to Ra-free synthetic seawater, mussels rapidly eliminated aqueous
Ra (average elimination rate constant 1.56 d
). The biological half-life for aqueous
Ra ranged from 8.9 h for the gills and labial palps to 15.4 h for the muscle. Although previous field studies have demonstrated notable
Ra accumulation in the soft tissues of marine mussels and that, for freshwater mussels, tissue-incorporated
Ra derives primarily from the aqueous phase, our tissue-specific bioconcentration factors (BCFs) were on the order of (8.3 ± 1.5) × 10
indicating low accumulation potential of aqueous
Ra in estuarine mussels. This suggests marine and estuarine mussels obtain
Ra from an alternate route, such as particulate-sorbed Ra ingested during filter-feeding or from a contaminated food source.</description><identifier>ISSN: 0013-936X</identifier><identifier>EISSN: 1520-5851</identifier><identifier>DOI: 10.1021/acs.est.2c09421</identifier><identifier>PMID: 36799656</identifier><language>eng</language><publisher>United States: American Chemical Society</publisher><subject>Accumulation ; Animals ; Bioaccumulation ; Bioavailability ; Biological magnification ; Bivalvia ; Coastal ecology ; Food contamination ; Food sources ; Geukensia demissa ; Gills ; Heavy metals ; Labial palps ; Mollusks ; Muscles ; Mussels ; Radioactive pollution ; Radium ; Radium 226 ; Radium isotopes ; Radium radioisotopes ; Seawater ; Shellfish ; Soft tissues ; Tissues ; Toxicokinetics ; Water</subject><ispartof>Environmental science & technology, 2023-02, Vol.57 (8), p.3187-3197</ispartof><rights>Copyright American Chemical Society Feb 28, 2023</rights><lds50>peer_reviewed</lds50><woscitedreferencessubscribed>false</woscitedreferencessubscribed><citedby>FETCH-LOGICAL-c325t-66dbac006ac1bbf26ab15b4a92db44a67b4434c1dcb1cfbee9bdd56ff414147d3</citedby><cites>FETCH-LOGICAL-c325t-66dbac006ac1bbf26ab15b4a92db44a67b4434c1dcb1cfbee9bdd56ff414147d3</cites><orcidid>0000-0002-3691-319X ; 0000-0003-0423-0180</orcidid></display><links><openurl>$$Topenurl_article</openurl><openurlfulltext>$$Topenurlfull_article</openurlfulltext><thumbnail>$$Tsyndetics_thumb_exl</thumbnail><link.rule.ids>314,780,784,2765,27924,27925</link.rule.ids><backlink>$$Uhttps://www.ncbi.nlm.nih.gov/pubmed/36799656$$D View this record in MEDLINE/PubMed$$Hfree_for_read</backlink></links><search><creatorcontrib>Donaher, Sarah E</creatorcontrib><creatorcontrib>Dunn, Robert P</creatorcontrib><creatorcontrib>Gonzales, Annelise K</creatorcontrib><creatorcontrib>Wattier, Bryanna D</creatorcontrib><creatorcontrib>Powell, Brian A</creatorcontrib><creatorcontrib>Martinez, Nicole E</creatorcontrib><title>Tissue-Specific Toxicokinetics of Aqueous Radium-226 in an Estuarine Mussel, Geukensia demissa</title><title>Environmental science & technology</title><addtitle>Environ Sci Technol</addtitle><description>Radiological contamination of coastal habitats poses potential risk for native fauna, but the bioavailability of aqueous radium (Ra) and other dissolved metals to marine bivalves remains unclear. This study was the first to examine the tissue-specific disposition of aqueous
Ra in a coastal mussel, specifically the Atlantic ribbed mussel
. Most organ groups reached steady-state concentrations within 7 days during experimental exposure, with an average uptake rate constant of 0.0013 mL g
d
. When moved to Ra-free synthetic seawater, mussels rapidly eliminated aqueous
Ra (average elimination rate constant 1.56 d
). The biological half-life for aqueous
Ra ranged from 8.9 h for the gills and labial palps to 15.4 h for the muscle. Although previous field studies have demonstrated notable
Ra accumulation in the soft tissues of marine mussels and that, for freshwater mussels, tissue-incorporated
Ra derives primarily from the aqueous phase, our tissue-specific bioconcentration factors (BCFs) were on the order of (8.3 ± 1.5) × 10
indicating low accumulation potential of aqueous
Ra in estuarine mussels. This suggests marine and estuarine mussels obtain
Ra from an alternate route, such as particulate-sorbed Ra ingested during filter-feeding or from a contaminated food source.</description><subject>Accumulation</subject><subject>Animals</subject><subject>Bioaccumulation</subject><subject>Bioavailability</subject><subject>Biological magnification</subject><subject>Bivalvia</subject><subject>Coastal ecology</subject><subject>Food contamination</subject><subject>Food sources</subject><subject>Geukensia demissa</subject><subject>Gills</subject><subject>Heavy metals</subject><subject>Labial palps</subject><subject>Mollusks</subject><subject>Muscles</subject><subject>Mussels</subject><subject>Radioactive pollution</subject><subject>Radium</subject><subject>Radium 226</subject><subject>Radium isotopes</subject><subject>Radium radioisotopes</subject><subject>Seawater</subject><subject>Shellfish</subject><subject>Soft tissues</subject><subject>Tissues</subject><subject>Toxicokinetics</subject><subject>Water</subject><issn>0013-936X</issn><issn>1520-5851</issn><fulltext>true</fulltext><rsrctype>article</rsrctype><creationdate>2023</creationdate><recordtype>article</recordtype><sourceid>EIF</sourceid><recordid>eNpdkEtLAzEUhYMotlbX7iTgxoXT5jHJzCxLqVWoCFrBlUOekHYedTIB_femtrqQC_duvnPu4QBwidEYI4InQvmx8f2YKFSkBB-BIWYEJSxn-BgMEcI0KSh_G4Az79cIIUJRfgoGlGdFwRkfgveV8z6Y5GVrlLNOwVX76VS7cY3pnfKwtXD6EUwbPHwW2oU6IYRD10DRwLnvg-giCR-D96a6hQsTNqbxTkBt6mgszsGJFZU3F4c7Aq9389XsPlk-LR5m02WiKGF9wrmWQiHEhcJSWsKFxEymoiBapqngWdw0VVgriZWVxhRSa8atTXGcTNMRuNn7brs2xvV9Gd8rU1Wi2WUvSZajjDOSs4he_0PXbeiamO6HKjDKGY_UZE-prvW-M7bcdq4W3VeJUbmrvozVlzv1ofqouDr4Blkb_cf_dk2_AXz7gU0</recordid><startdate>20230228</startdate><enddate>20230228</enddate><creator>Donaher, Sarah E</creator><creator>Dunn, Robert P</creator><creator>Gonzales, Annelise K</creator><creator>Wattier, Bryanna D</creator><creator>Powell, Brian A</creator><creator>Martinez, Nicole E</creator><general>American Chemical Society</general><scope>CGR</scope><scope>CUY</scope><scope>CVF</scope><scope>ECM</scope><scope>EIF</scope><scope>NPM</scope><scope>AAYXX</scope><scope>CITATION</scope><scope>7QO</scope><scope>7ST</scope><scope>7T7</scope><scope>7U7</scope><scope>8FD</scope><scope>C1K</scope><scope>FR3</scope><scope>P64</scope><scope>SOI</scope><scope>7X8</scope><orcidid>https://orcid.org/0000-0002-3691-319X</orcidid><orcidid>https://orcid.org/0000-0003-0423-0180</orcidid></search><sort><creationdate>20230228</creationdate><title>Tissue-Specific Toxicokinetics of Aqueous Radium-226 in an Estuarine Mussel, Geukensia demissa</title><author>Donaher, Sarah E ; Dunn, Robert P ; Gonzales, Annelise K ; Wattier, Bryanna D ; Powell, Brian A ; Martinez, Nicole E</author></sort><facets><frbrtype>5</frbrtype><frbrgroupid>cdi_FETCH-LOGICAL-c325t-66dbac006ac1bbf26ab15b4a92db44a67b4434c1dcb1cfbee9bdd56ff414147d3</frbrgroupid><rsrctype>articles</rsrctype><prefilter>articles</prefilter><language>eng</language><creationdate>2023</creationdate><topic>Accumulation</topic><topic>Animals</topic><topic>Bioaccumulation</topic><topic>Bioavailability</topic><topic>Biological magnification</topic><topic>Bivalvia</topic><topic>Coastal ecology</topic><topic>Food contamination</topic><topic>Food sources</topic><topic>Geukensia demissa</topic><topic>Gills</topic><topic>Heavy metals</topic><topic>Labial palps</topic><topic>Mollusks</topic><topic>Muscles</topic><topic>Mussels</topic><topic>Radioactive pollution</topic><topic>Radium</topic><topic>Radium 226</topic><topic>Radium isotopes</topic><topic>Radium radioisotopes</topic><topic>Seawater</topic><topic>Shellfish</topic><topic>Soft tissues</topic><topic>Tissues</topic><topic>Toxicokinetics</topic><topic>Water</topic><toplevel>peer_reviewed</toplevel><toplevel>online_resources</toplevel><creatorcontrib>Donaher, Sarah E</creatorcontrib><creatorcontrib>Dunn, Robert P</creatorcontrib><creatorcontrib>Gonzales, Annelise K</creatorcontrib><creatorcontrib>Wattier, Bryanna D</creatorcontrib><creatorcontrib>Powell, Brian A</creatorcontrib><creatorcontrib>Martinez, Nicole E</creatorcontrib><collection>Medline</collection><collection>MEDLINE</collection><collection>MEDLINE (Ovid)</collection><collection>MEDLINE</collection><collection>MEDLINE</collection><collection>PubMed</collection><collection>CrossRef</collection><collection>Biotechnology Research Abstracts</collection><collection>Environment Abstracts</collection><collection>Industrial and Applied Microbiology Abstracts (Microbiology A)</collection><collection>Toxicology Abstracts</collection><collection>Technology Research Database</collection><collection>Environmental Sciences and Pollution Management</collection><collection>Engineering Research Database</collection><collection>Biotechnology and BioEngineering Abstracts</collection><collection>Environment Abstracts</collection><collection>MEDLINE - Academic</collection><jtitle>Environmental science & technology</jtitle></facets><delivery><delcategory>Remote Search Resource</delcategory><fulltext>fulltext</fulltext></delivery><addata><au>Donaher, Sarah E</au><au>Dunn, Robert P</au><au>Gonzales, Annelise K</au><au>Wattier, Bryanna D</au><au>Powell, Brian A</au><au>Martinez, Nicole E</au><format>journal</format><genre>article</genre><ristype>JOUR</ristype><atitle>Tissue-Specific Toxicokinetics of Aqueous Radium-226 in an Estuarine Mussel, Geukensia demissa</atitle><jtitle>Environmental science & technology</jtitle><addtitle>Environ Sci Technol</addtitle><date>2023-02-28</date><risdate>2023</risdate><volume>57</volume><issue>8</issue><spage>3187</spage><epage>3197</epage><pages>3187-3197</pages><issn>0013-936X</issn><eissn>1520-5851</eissn><abstract>Radiological contamination of coastal habitats poses potential risk for native fauna, but the bioavailability of aqueous radium (Ra) and other dissolved metals to marine bivalves remains unclear. This study was the first to examine the tissue-specific disposition of aqueous
Ra in a coastal mussel, specifically the Atlantic ribbed mussel
. Most organ groups reached steady-state concentrations within 7 days during experimental exposure, with an average uptake rate constant of 0.0013 mL g
d
. When moved to Ra-free synthetic seawater, mussels rapidly eliminated aqueous
Ra (average elimination rate constant 1.56 d
). The biological half-life for aqueous
Ra ranged from 8.9 h for the gills and labial palps to 15.4 h for the muscle. Although previous field studies have demonstrated notable
Ra accumulation in the soft tissues of marine mussels and that, for freshwater mussels, tissue-incorporated
Ra derives primarily from the aqueous phase, our tissue-specific bioconcentration factors (BCFs) were on the order of (8.3 ± 1.5) × 10
indicating low accumulation potential of aqueous
Ra in estuarine mussels. This suggests marine and estuarine mussels obtain
Ra from an alternate route, such as particulate-sorbed Ra ingested during filter-feeding or from a contaminated food source.</abstract><cop>United States</cop><pub>American Chemical Society</pub><pmid>36799656</pmid><doi>10.1021/acs.est.2c09421</doi><tpages>11</tpages><orcidid>https://orcid.org/0000-0002-3691-319X</orcidid><orcidid>https://orcid.org/0000-0003-0423-0180</orcidid></addata></record> |
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subjects | Accumulation Animals Bioaccumulation Bioavailability Biological magnification Bivalvia Coastal ecology Food contamination Food sources Geukensia demissa Gills Heavy metals Labial palps Mollusks Muscles Mussels Radioactive pollution Radium Radium 226 Radium isotopes Radium radioisotopes Seawater Shellfish Soft tissues Tissues Toxicokinetics Water |
title | Tissue-Specific Toxicokinetics of Aqueous Radium-226 in an Estuarine Mussel, Geukensia demissa |
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