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<oai_dc:dc xmlns:dc="http://purl.org/dc/elements/1.1/" xmlns:oai_dc="http://www.openarchives.org/OAI/2.0/oai_dc/" xmlns:xsi="http://www.w3.org/2001/XMLSchema-instance" xsi:schemaLocation="http://www.openarchives.org/OAI/2.0/oai_dc/ http://www.openarchives.org/OAI/2.0/oai_dc.xsd">
  <dc:contributor>Kristin M. Romanok</dc:contributor>
  <dc:contributor>Kelly Smalling</dc:contributor>
  <dc:contributor>Lee Donahue</dc:contributor>
  <dc:contributor>Mark P. Gaikowski</dc:contributor>
  <dc:contributor>Randy K. Hines</dc:contributor>
  <dc:contributor>Sara E. Breitmeyer</dc:contributor>
  <dc:contributor>Stephanie E. Gordon</dc:contributor>
  <dc:contributor>Keith A. Loftin</dc:contributor>
  <dc:contributor>R. Blaine McCleskey</dc:contributor>
  <dc:contributor>Shannon M. Meppelink</dc:contributor>
  <dc:contributor>Molly L. Schreiner</dc:contributor>
  <dc:creator>Paul M. Bradley</dc:creator>
  <dc:date>2025</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Tapwater (TW) safety and sustainability are priorities in the United States. Per/polyfluoroalkyl substance(s) (PFAS) contamination is a growing public-health concern due to prolific use, widespread TW exposures, and mounting human-health concerns. Historically-rural, actively-urbanizing communities that rely on surficial-aquifer private wells incur elevated risks of unrecognized TW exposures, including PFAS, due to limited private-well monitoring and contaminant-source proliferation in urbanizing landscapes. Here, a broad-analytical-scope TW-assessment was conducted in a hydrologically-vulnerable, Mississippi River alluvial-island community, where PFAS contamination of the shallow-alluvial drinking-water aquifer has been documented, but more comprehensive contaminant characterization to inform decision-making is currently lacking. In 2021, we analyzed 510 organics, 34 inorganics, and 3 microbial groups in 11 residential and community locations to assess (1) TW risks beyond recognized PFAS issues, (2) day-to-day and year-to-year risk variability, and (3) suitability of the underlying sandstone aquifer as an alternative source to mitigate TW-PFAS exposures. Seventy-six organics and 25 inorganics were detected. Potential human-health risks of detected TW exposures were explored based on cumulative benchmark-based toxicity quotients (&lt;/span&gt;&lt;i&gt;∑&lt;/i&gt;&lt;small&gt;&lt;sub&gt;TQ&lt;/sub&gt;&lt;/small&gt;&lt;span&gt;). Elevated risks (&lt;/span&gt;&lt;i&gt;∑&lt;/i&gt;&lt;small&gt;&lt;sub&gt;TQ&lt;/sub&gt;&lt;/small&gt;&lt;span&gt;&amp;nbsp;≥ 1) from organic and inorganic contaminants were observed in all alluvial-aquifer-sourced synoptic samples but not in sandstone-aquifer-sourced samples. Repeated sampling at 3 sites over 52–55 h indicated limited variability in risk over the short-term. Comparable PFAS-specific&amp;nbsp;&lt;/span&gt;&lt;i&gt;∑&lt;/i&gt;&lt;small&gt;&lt;sub&gt;TQ&lt;/sub&gt;&lt;/small&gt;&lt;span&gt;&amp;nbsp;for spatial-synoptic, short-term (3 days) temporal, and long-term (3 years quarterly) temporal samples indicated that synoptic results provided useful insight into the risks of TW-PFAS exposures at French Island over the long-term. No PFAS detections in sandstone-aquifer-sourced samples over a 3 year period indicated no PFAS-associated risk and supported the sandstone aquifer as an alternative drinking-water source to mitigate community TW-PFAS exposures. This study illustrated the importance of expanded contaminant monitoring of private-well TW, beyond known concerns (in this case, PFAS), to reduce the risks of a range of unrecognized contaminant exposures.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1039/D5EM00005J</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Royal Society of Chemistry</dc:publisher>
  <dc:title>Tapwater exposures, residential risk, and mitigation in a PFAS-impacted-groundwater community</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>