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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>Dana W. Kolpin</dc:contributor>
  <dc:contributor>Darrin A. Thompson</dc:contributor>
  <dc:contributor>Kristin M. Romanok</dc:contributor>
  <dc:contributor>Kelly L. Smalling</dc:contributor>
  <dc:contributor>Sara E. Breitmeyer</dc:contributor>
  <dc:contributor>Mary C. Cardon</dc:contributor>
  <dc:contributor>David M. Cwiertny</dc:contributor>
  <dc:contributor>Nicola Evans</dc:contributor>
  <dc:contributor>R. William Field</dc:contributor>
  <dc:contributor>Michael J. Focazio</dc:contributor>
  <dc:contributor>Laura E. Beane Freeman</dc:contributor>
  <dc:contributor>Carrie E. Givens</dc:contributor>
  <dc:contributor>James L. Gray</dc:contributor>
  <dc:contributor>Gordon L. Hager</dc:contributor>
  <dc:contributor>Michelle L. Hladik</dc:contributor>
  <dc:contributor>Jonathan N. Hoffman</dc:contributor>
  <dc:contributor>Rena R. Jones</dc:contributor>
  <dc:contributor>Leslie K. Kanagy</dc:contributor>
  <dc:contributor>Rachael F. Lane</dc:contributor>
  <dc:contributor>R. Blaine McCleskey</dc:contributor>
  <dc:contributor>Danielle Medgyesi</dc:contributor>
  <dc:contributor>Elizabeth Medlock-Kakaley</dc:contributor>
  <dc:contributor>Shannon M. Meppelink</dc:contributor>
  <dc:contributor>Michael T. Meyer</dc:contributor>
  <dc:contributor>Diana A. Stavreva</dc:contributor>
  <dc:contributor>Mary H. Ward</dc:contributor>
  <dc:creator>Paul M. Bradley</dc:creator>
  <dc:date>2023</dc:date>
  <dc:description>&lt;div id="ab0005" class="abstract author" lang="en"&gt;&lt;div id="as0005"&gt;&lt;p id="sp0030"&gt;In the United States and globally, contaminant exposure in unregulated private-well point-of-use tapwater (TW) is a recognized public-health data gap and an obstacle to both risk-management and homeowner decision making. To help address the lack of data on broad contaminant exposures in private-well TW from hydrologically-vulnerable (alluvial, karst) aquifers in agriculturally-intensive landscapes, samples were collected in 2018–2019 from 47 northeast Iowa farms and analyzed for 35 inorganics, 437 unique organics, 5 in vitro bioassays, and 11 microbial assays. Twenty-six inorganics and 51 organics, dominated by pesticides and related transformation products (35 herbicide-, 5 insecticide-, and 2 fungicide-related), were observed in TW. Heterotrophic bacteria detections were near ubiquitous (94 % of the samples), with detection of total coliform bacteria in 28 % of the samples and growth on at least one putative-pathogen selective media across all TW samples. Health-based hazard index screening levels were exceeded frequently in private-well TW and attributed primarily to inorganics (nitrate, uranium). Results support incorporation of residential treatment systems to protect against contaminant exposure and the need for increased monitoring of rural private-well homes. Continued assessment of unmonitored and unregulated private-supply TW is needed to model contaminant exposures and human-health risks.&lt;/p&gt;&lt;/div&gt;&lt;/div&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.scitotenv.2023.161672</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>Juxtaposition of intensive agriculture, vulnerable aquifers, and mixed chemical/microbial exposures in private-well tapwater in northeast Iowa</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>