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authorJohannes Ranke <jranke@uni-bremen.de>2024-08-26 17:11:43 +0200
committerJohannes Ranke <jranke@uni-bremen.de>2024-08-26 17:11:43 +0200
commit913c383880da2a5f4bdb71c8a82107afbad6ef13 (patch)
tree1c5a988748fc49fde4c279a96650deb26039b711 /docs/reference/GUS.html
parent9e62ed638e530a5cebebf491de055caca49a56ef (diff)
parent396ba6c42252426a132be56b9f417786a1f276e3 (diff)
Merge branch 'main' into crop_group
Diffstat (limited to 'docs/reference/GUS.html')
-rw-r--r--docs/reference/GUS.html87
1 files changed, 39 insertions, 48 deletions
diff --git a/docs/reference/GUS.html b/docs/reference/GUS.html
index 7638dcd..a613d98 100644
--- a/docs/reference/GUS.html
+++ b/docs/reference/GUS.html
@@ -1,47 +1,38 @@
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+$$GUS = \log_{10} DT50_{soil} (4 - \log_{10} K_{oc})$$"><meta property="og:description" content="The groundwater ubiquity score GUS is calculated according to
the following equation
-$$GUS = \log_{10} DT50_{soil} (4 - \log_{10} K_{oc})$$"><!-- mathjax --><script src="https://cdnjs.cloudflare.com/ajax/libs/mathjax/2.7.5/MathJax.js" integrity="sha256-nvJJv9wWKEm88qvoQl9ekL2J+k/RWIsaSScxxlsrv8k=" crossorigin="anonymous"></script><script src="https://cdnjs.cloudflare.com/ajax/libs/mathjax/2.7.5/config/TeX-AMS-MML_HTMLorMML.js" integrity="sha256-84DKXVJXs0/F8OTMzX4UR909+jtl4G7SPypPavF+GfA=" crossorigin="anonymous"></script><!--[if lt IE 9]>
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-<![endif]--></head><body>
+$$GUS = \log_{10} DT50_{soil} (4 - \log_{10} K_{oc})$$"></head><body>
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- <img src="" class="logo" alt=""><h1>Groundwater ubiquity score based on Gustafson (1989)</h1>
+
+ <h1>Groundwater ubiquity score based on Gustafson (1989)</h1>
<small class="dont-index">Source: <a href="https://github.com/jranke/pfm/blob/HEAD/R/GUS.R" class="external-link"><code>R/GUS.R</code></a></small>
<div class="d-none name"><code>GUS.Rd</code></div>
</div>
@@ -56,10 +47,10 @@ $$GUS = \log_{10} DT50_{soil} (4 - \log_{10} K_{oc})$$</p>
<h2 id="ref-usage">Usage<a class="anchor" aria-label="anchor" href="#ref-usage"></a></h2>
<div class="sourceCode"><pre class="sourceCode r"><code><span><span class="fu">GUS</span><span class="op">(</span><span class="va">...</span><span class="op">)</span></span>
<span></span>
-<span><span class="co"># S3 method for numeric</span></span>
+<span><span class="co"># S3 method for class 'numeric'</span></span>
<span><span class="fu">GUS</span><span class="op">(</span><span class="va">DT50</span>, <span class="va">Koc</span>, <span class="va">...</span><span class="op">)</span></span>
<span></span>
-<span><span class="co"># S3 method for chent</span></span>
+<span><span class="co"># S3 method for class 'chent'</span></span>
<span><span class="fu">GUS</span><span class="op">(</span></span>
<span> <span class="va">chent</span>,</span>
<span> degradation_value <span class="op">=</span> <span class="st">"DT50ref"</span>,</span>
@@ -71,18 +62,20 @@ $$GUS = \log_{10} DT50_{soil} (4 - \log_{10} K_{oc})$$</p>
<span> <span class="va">...</span></span>
<span><span class="op">)</span></span>
<span></span>
-<span><span class="co"># S3 method for GUS_result</span></span>
+<span><span class="co"># S3 method for class 'GUS_result'</span></span>
<span><span class="fu"><a href="https://rdrr.io/r/base/print.html" class="external-link">print</a></span><span class="op">(</span><span class="va">x</span>, <span class="va">...</span>, digits <span class="op">=</span> <span class="fl">1</span><span class="op">)</span></span></code></pre></div>
</div>
<div class="section level2">
<h2 id="arguments">Arguments<a class="anchor" aria-label="anchor" href="#arguments"></a></h2>
- <dl><dt>...</dt>
+
+
+<dl><dt id="arg--">...<a class="anchor" aria-label="anchor" href="#arg--"></a></dt>
<dd><p>Included in the generic to allow for further arguments later. Therefore
this also had to be added to the specific methods.</p></dd>
-<dt>DT50</dt>
+<dt id="arg-dt-">DT50<a class="anchor" aria-label="anchor" href="#arg-dt-"></a></dt>
<dd><p>Half-life of the chemical in soil. Should be a field
half-life according to Gustafson (1989). However, leaching to the sub-soil
can not completely be excluded in field dissipation experiments and Gustafson
@@ -90,7 +83,7 @@ did not refer to any normalisation procedure, but says the field study should
be conducted under use conditions.</p></dd>
-<dt>Koc</dt>
+<dt id="arg-koc">Koc<a class="anchor" aria-label="anchor" href="#arg-koc"></a></dt>
<dd><p>The sorption constant normalised to organic carbon. Gustafson
does not mention the nonlinearity of the sorption constant commonly
found and usually described by Freundlich sorption, therefore it is
@@ -98,17 +91,17 @@ unclear at which reference concentration the Koc should be observed
(and if the reference concentration would be in soil or in porewater).</p></dd>
-<dt>chent</dt>
+<dt id="arg-chent">chent<a class="anchor" aria-label="anchor" href="#arg-chent"></a></dt>
<dd><p>If a chent is given with appropriate information present in its
chyaml field, this information is used, with defaults specified below.</p></dd>
-<dt>degradation_value</dt>
+<dt id="arg-degradation-value">degradation_value<a class="anchor" aria-label="anchor" href="#arg-degradation-value"></a></dt>
<dd><p>Which of the available degradation values should
be used?</p></dd>
-<dt>lab_field</dt>
+<dt id="arg-lab-field">lab_field<a class="anchor" aria-label="anchor" href="#arg-lab-field"></a></dt>
<dd><p>Should laboratory or field half-lives be used? This
defaults to lab in this implementation, in order to avoid
double-accounting for mobility. If comparability with the original GUS
@@ -116,11 +109,11 @@ values given by Gustafson (1989) is desired, non-normalised first-order
field half-lives obtained under actual use conditions should be used.</p></dd>
-<dt>redox</dt>
+<dt id="arg-redox">redox<a class="anchor" aria-label="anchor" href="#arg-redox"></a></dt>
<dd><p>Aerobic or anaerobic degradation data</p></dd>
-<dt>sorption_value</dt>
+<dt id="arg-sorption-value">sorption_value<a class="anchor" aria-label="anchor" href="#arg-sorption-value"></a></dt>
<dd><p>Which of the available sorption values should be used?
Defaults to Kfoc as this is what is generally available from the European
pesticide peer review process. These values generally use a reference
@@ -128,27 +121,25 @@ concentration of 1 mg/L in porewater, that means they would be expected to
be Koc values at a concentration of 1 mg/L in the water phase.</p></dd>
-<dt>degradation_aggregator</dt>
+<dt id="arg-degradation-aggregator">degradation_aggregator<a class="anchor" aria-label="anchor" href="#arg-degradation-aggregator"></a></dt>
<dd><p>Function for aggregating half-lives</p></dd>
-<dt>sorption_aggregator</dt>
+<dt id="arg-sorption-aggregator">sorption_aggregator<a class="anchor" aria-label="anchor" href="#arg-sorption-aggregator"></a></dt>
<dd><p>Function for aggregation Koc values</p></dd>
-<dt>x</dt>
+<dt id="arg-x">x<a class="anchor" aria-label="anchor" href="#arg-x"></a></dt>
<dd><p>An object of class GUS_result to be printed</p></dd>
-<dt>digits</dt>
+<dt id="arg-digits">digits<a class="anchor" aria-label="anchor" href="#arg-digits"></a></dt>
<dd><p>The number of digits used in the print method</p></dd>
</dl></div>
<div class="section level2">
<h2 id="value">Value<a class="anchor" aria-label="anchor" href="#value"></a></h2>
-
-
-<p>A list with the DT50 and Koc used as well as the resulting score
+ <p>A list with the DT50 and Koc used as well as the resulting score
of class GUS_result</p>
</div>
<div class="section level2">
@@ -162,23 +153,23 @@ toxicology and chemistry</em> <b>8</b>(4) 339–57.</p>
<p>Johannes Ranke</p>
</div>
- </main><aside class="col-md-3"><nav id="toc"><h2>On this page</h2>
+ </main><aside class="col-md-3"><nav id="toc" aria-label="Table of contents"><h2>On this page</h2>
</nav></aside></div>
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- <p></p><p>Developed by Johannes Ranke.</p>
+ <p>Developed by Johannes Ranke.</p>
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