<?xml version='1.0' encoding='utf-8'?>
<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>H. E. LeGrand</dc:creator>
  <dc:date>1965</dc:date>
  <dc:description>&lt;p&gt;&lt;span&gt;Ramifications of&amp;nbsp;&lt;/span&gt;contamination&lt;span&gt;&amp;nbsp;are increasingly involved in the majority of&amp;nbsp;&lt;/span&gt;ground‐water&lt;span&gt;&amp;nbsp;problems. The volume of usable&amp;nbsp;&lt;/span&gt;ground&lt;span&gt;&amp;nbsp;&lt;/span&gt;water&lt;span&gt;&amp;nbsp;is shrinking in many places because of dispersion of contaminated&amp;nbsp;&lt;/span&gt;water&lt;span&gt;. Consideration of&amp;nbsp;&lt;/span&gt;ground‐water&lt;span&gt;&amp;nbsp;&lt;/span&gt;contamination&lt;span&gt;&amp;nbsp;as a multitude of independent problems, separately solvable as each problem arises, is outmoded; wise policies, relating&amp;nbsp;&lt;/span&gt;water&lt;span&gt;&amp;nbsp;supply to&amp;nbsp;&lt;/span&gt;contamination&lt;span&gt;&amp;nbsp;potential, are needed to alleviate and to forestall problems. Methodology of managing&amp;nbsp;&lt;/span&gt;contamination&lt;span&gt;&amp;nbsp;problems calls for appropriate classification of the hydrogeologic environment; these classifications include aspects of interdependent factors such as permeability, sorption, hydraulic gradient, position of&amp;nbsp;&lt;/span&gt;water&lt;span&gt;&amp;nbsp;table relative to some base, and distance from source of&amp;nbsp;&lt;/span&gt;contamination&lt;span&gt;. Effective evaluations relate the dynamics of the hydrogeologic environment to contingencies involving&amp;nbsp;&lt;/span&gt;contamination&lt;span&gt;, as man changes his&amp;nbsp;&lt;/span&gt;water&lt;span&gt;‐development and waste‐disposal practices. Ways of&amp;nbsp;&lt;/span&gt;contamination&lt;span&gt;&amp;nbsp;and pertinent parts of the physical environment include: waste‐disposal practices (at or near land surface and in deep formations), artificial recharge (at land surface and in aquifers), accidents, and salt‐&lt;/span&gt;water&lt;span&gt;&amp;nbsp;&lt;/span&gt;contamination&lt;span&gt;&amp;nbsp;of aquifers (shallow depth from salty surface&amp;nbsp;&lt;/span&gt;water&lt;span&gt;&amp;nbsp;and at variable depths from subjacent salty aquifers). Evaluation of waste‐disposal problems calls for appreciation of two opposing tendencies–the tendency of wastes to move with&amp;nbsp;&lt;/span&gt;ground&lt;span&gt;&amp;nbsp;&lt;/span&gt;water&lt;span&gt;&amp;nbsp;and the tendency to be attenuated near disposal sites by decay or inherent decrease in potency, by chemical and physical sorption, and by dilution through dispersion of&amp;nbsp;&lt;/span&gt;ground&lt;span&gt;&amp;nbsp;&lt;/span&gt;water&lt;span&gt;. Mixed wastes of differing attenuation habits represent special complex problems.&lt;/span&gt;&lt;/p&gt;</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.1111/j.1745-6584.1965.tb01204.x</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Wiley Blackwell</dc:publisher>
  <dc:title>Environmental framework of ground‐water contamination</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>