<?xml version="1.0" encoding="UTF-8"?>
<!DOCTYPE article PUBLIC "-//NLM//DTD Journal Publishing DTD v3.0 20080202//EN" "https://jats.nlm.nih.gov/nlm-dtd/publishing/3.0/journalpublishing3.dtd">
<article xmlns:mml="http://www.w3.org/1998/Math/MathML" xmlns:xlink="http://www.w3.org/1999/xlink" article-type="research-article" dtd-version="3.0" xml:lang="en">
<front>
<journal-meta>
<journal-id journal-id-type="publisher">HESS</journal-id>
<journal-title-group>
<journal-title>Hydrology and Earth System Sciences</journal-title>
<abbrev-journal-title abbrev-type="publisher">HESS</abbrev-journal-title>
<abbrev-journal-title abbrev-type="nlm-ta">Hydrol. Earth Syst. Sci.</abbrev-journal-title>
</journal-title-group>
<issn pub-type="epub">1607-7938</issn>
<publisher><publisher-name>Copernicus Publications</publisher-name>
<publisher-loc>Göttingen, Germany</publisher-loc>
</publisher>
</journal-meta>
<article-meta>
<article-id pub-id-type="doi">10.5194/hess-3-395-1999</article-id>
<title-group>
<article-title>Spatial variability of nitrate concentration in lakes in Snowdonia, North Wales, UK</article-title>
</title-group>
<contrib-group><contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Kernan</surname>
<given-names>M. R.</given-names>
</name>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
</contrib>
<contrib contrib-type="author" xlink:type="simple"><name name-style="western"><surname>Allott</surname>
<given-names>T. E. H.</given-names>
</name>
<xref ref-type="aff" rid="aff2">
<sup>2</sup>
</xref>
<xref ref-type="aff" rid="aff1">
<sup>1</sup>
</xref>
</contrib>
</contrib-group><aff id="aff1">
<label>1</label>
<addr-line>Environmental Change Research Centre, Department of Geography, University College London, 26 Bedford Way, London WC1H 0AP.</addr-line>
</aff>
<aff id="aff2">
<label>2</label>
<addr-line>e-mail address for correspondin author: mkernan@geog.ucl.ac.uk</addr-line>
</aff>
<pub-date pub-type="epub">
<day>30</day>
<month>09</month>
<year>1999</year>
</pub-date>
<volume>3</volume>
<issue>3</issue>
<fpage>395</fpage>
<lpage>408</lpage>
<permissions>
<copyright-statement>Copyright: &#x000a9; 1999 M. R. Kernan</copyright-statement>
<copyright-year>1999</copyright-year>
<license license-type="open-access">
<license-p>This work is licensed under the Creative Commons Attribution-NonCommercial-ShareAlike 2.5 Generic License. To view a copy of this licence, visit <ext-link ext-link-type="uri"  xlink:href="https://creativecommons.org/licenses/by-nc-sa/2.5/">https://creativecommons.org/licenses/by-nc-sa/2.5/</ext-link></license-p>
</license>
</permissions>
<self-uri xlink:href="https://hess.copernicus.org/articles/3/395/1999/hess-3-395-1999.html">This article is available from https://hess.copernicus.org/articles/3/395/1999/hess-3-395-1999.html</self-uri>
<self-uri xlink:href="https://hess.copernicus.org/articles/3/395/1999/hess-3-395-1999.pdf">The full text article is available as a PDF file from https://hess.copernicus.org/articles/3/395/1999/hess-3-395-1999.pdf</self-uri>
<abstract>
<p>At a regional scale, high nitrate (NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt;) 
concentrations in upland surface
waters generally occur in tandem with high nitrogen (N) deposition levels.
However, significant differences in the patterns of surface water NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt;
concentration have been observed within areas of similar N deposition yet
relatively few studies have been undertaken which examine within-region
variation of NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt; concentrations. A study of 
76 lakes in Snowdonia, north Wales,
an area of high deposition and sensitive catchments, was undertaken to assess
variation in surface water NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt; concentration across 
a 20 x 20 km grid square
and to identify catchments vulnerable to NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt; leaching. 
Nitrate concentrations
vary considerably, particularly during winter when values range from 0.7 to 
70 &amp;#956;eq l&lt;sup&gt;-1&lt;/sup&gt;. Although retention by vegetation and soil microbes in summer reduces
the amount of NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt; reaching the lakes, 37 % of sites are 
characterised by NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt;
concentrations greater then 4 &amp;#956;eq l&lt;sup&gt;-1&lt;/sup&gt;. The elevated concentrations occurring in
summer suggests that N breakthrough has occurred. By examining the ratio of NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt;
to total strong acid anions, it is shown that NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt; contributes significantly to
freshwater acidity, particularly during the winter. Redundancy analysis shows
that NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt; leaching is greatest, both in winter and summer, in catchments with
high proportions of bare rock where soil and vegetation cover is limited.
Nitrogen cycling in these catchments, generally at higher altitudes, may no
longer be governed by seasonal biological controls. They are likely to be
saturated with respect to nitrogen (i.e. incapable of further N retention)
as a result of the elevated deposition levels in the area. The contribution of
NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt; to acidity is also greatest at these sites. In winter, significant positive
relationships are also evident between NO&lt;sub&gt;3&lt;/sub&gt;&lt;sup&gt;&amp;#8254;&lt;/sup&gt; concentration and soil pH and
coniferous woodland. The study demonstrates the importance of catchment factors
in modifying the relationship between N deposition and N leaching in upland
catchments.</p>
</abstract>
<counts><page-count count="14"/></counts>
</article-meta>
</front>
<body/>
<back>
</back>
</article>