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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:creator>Benjamin S. Linhoff</dc:creator>
  <dc:date>2022</dc:date>
  <dc:description>&lt;p id="sp0045"&gt;&lt;span&gt;Recently, the&amp;nbsp;subsoils&amp;nbsp;of&amp;nbsp;ephemeral stream&amp;nbsp;(arroyos) floodplains in the northern Chihuahuan Desert were discovered to contain large naturally occurring NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;reservoirs (floodplain: ~38,000 kg NO&lt;sub&gt;3&lt;/sub&gt;-N/ha; background: ~60 kg NO&lt;sub&gt;3&lt;/sub&gt;&lt;span&gt;-N/ha). These reservoirs may be mobilized through&amp;nbsp;land use change&amp;nbsp;or natural stream channel migration which makes differentiating between anthropogenic and natural groundwater NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;sources challenging. In this study, the fate and sources of NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;were investigated in an area with multiple NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;sources such as accidental sewer line releases and sewage&amp;nbsp;lagoons&amp;nbsp;as well as natural reservoirs of subsoil NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;. To differentiate sources, this study used a large suite of geochemical tools including δ&lt;sup&gt;15&lt;/sup&gt;N[NO&lt;sub&gt;3&lt;/sub&gt;], δ&lt;sup&gt;18&lt;/sup&gt;O[NO&lt;sub&gt;3&lt;/sub&gt;], δ&lt;sup&gt;15&lt;/sup&gt;N[N&lt;sub&gt;2&lt;/sub&gt;], δ&lt;sup&gt;13&lt;/sup&gt;C[DIC],&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;sup&gt;14&lt;/sup&gt;&lt;span&gt;C,&amp;nbsp;tritium&amp;nbsp;(&lt;/span&gt;&lt;sup&gt;3&lt;/sup&gt;&lt;span&gt;H), dissolved gas concentrations, major ion chemistry, and contaminants of emerging concern (CEC) including artificial&amp;nbsp;sweeteners. NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;at sites with the highest concentrations (25 to 229 mg/L NO&lt;sub&gt;3&lt;/sub&gt;-N) were determined to be largely sourced from naturally occurring subsoil NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;based on δ&lt;sup&gt;15&lt;/sup&gt;N[NO&lt;sub&gt;3&lt;/sub&gt;] (&amp;lt;8 ‰) and mass ratios of Cl&lt;sup&gt;−&lt;/sup&gt;/Br&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;(〈100) and NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;/Cl&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;(&amp;gt;1.5). Anthropogenic NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;was deciphered using mass ratios of Cl&lt;sup&gt;−&lt;/sup&gt;/Br&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;(&amp;gt;120) and NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;/Cl&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;&lt;/span&gt;(&amp;lt;1), δ&lt;sup&gt;15&lt;/sup&gt;N[NO&lt;sub&gt;3&lt;/sub&gt;&lt;span&gt;] (&amp;gt;8 ‰), and CEC detections.&amp;nbsp;Nitrogen isotope&amp;nbsp;analyses indicated that&amp;nbsp;denitrification&amp;nbsp;is fairly limited in the field area. CEC were detected at 67 % of sites including&amp;nbsp;&lt;/span&gt;&lt;sup&gt;3&lt;/sup&gt;H dead sites (&amp;lt;1 pCi/L) with low percent modern carbon-14 (PMC; &amp;lt;30 %). Local supply wells are&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;sup&gt;3&lt;/sup&gt;H dead with low PMC; as&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;sup&gt;3&lt;/sup&gt;H does not re-equilibrate and&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;sup&gt;14&lt;/sup&gt;C is very slow to re-equilibrate during recirculation through infrastructure, sites with low PMC,&lt;span&gt;&amp;nbsp;&lt;/span&gt;&lt;sup&gt;3&lt;/sup&gt;&lt;span&gt;H &amp;lt; 1 pCi/L, and CEC detections were interpreted as locations with substantial anthropogenic&amp;nbsp;groundwater recharge. Neotame was used to identify locations of very recent (&amp;lt;15 years before present) or ongoing wastewater influxes to the aquifer. This work shows the important influence of naturally occurring subsoil NO&lt;/span&gt;&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;−&lt;/sup&gt;&lt;span&gt;&amp;nbsp;reservoirs on groundwater in arid regions and the major contribution of&amp;nbsp;artificial recharge.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1016/j.scitotenv.2022.157345</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Elsevier</dc:publisher>
  <dc:title>Deciphering natural and anthropogenic nitrate and recharge sources in arid region groundwater</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>