<?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:contributor>S. K. Anderholm</dc:contributor>
  <dc:creator>L. M. Bexfield</dc:creator>
  <dc:date>1997</dc:date>
  <dc:description>From March to May of 1995, water samples were collected from &#13;
30 wells located in the flood plain of the Rio Grande between &#13;
Cochiti Lake, New Mexico, and El Paso, Texas. These samples were &#13;
analyzed for a broad host of constituents, including field &#13;
parameters, major constituents, nutrients, dissolved organic &#13;
carbon, trace elements, radiochemicals, pesticides, and volatile &#13;
organic compounds. The main purpose of this study was to observe &#13;
the quality of ground water in this part of the Rio Grande Valley &#13;
study unit of the U.S. Geological Survey National Water-Quality &#13;
Assessment program. The sampling effort was limited to the basin-&#13;
fill aquifer beneath the above-defined reach of the Rio Grande &#13;
flood plain because of the relative homogeneity of the &#13;
hydrogeology, the large amount of ground-water use for public &#13;
supply, and the potential for land-use activities to affect the &#13;
quality of ground water. Most of the wells sampled for the study &#13;
are used for domestic purposes, including drinking water. Depths &#13;
to the tops of the sampling intervals in the 30 wells ranged from &#13;
10 to 345 feet below land surface, and the median was 161.5 feet; &#13;
the sampling intervals in most of the wells spanned about 10 feet &#13;
or less. Quality-control data were collected at three of the &#13;
wells.&#13;
&#13;
     A significant amount of variation was found in the chemical &#13;
composition of ground water sampled throughout the study area, &#13;
but the water generally was found to be of suitable chemical &#13;
quality for use as drinking water, according to current &#13;
enforceable standards established by the U.S. Environmental &#13;
Protection Agency (EPA). Nutrients generally were measured at &#13;
concentrations near or below their method reporting limits. The &#13;
most dominant nutrient species was nitrite plus nitrate, at a &#13;
maximum concentration of 1.9 milligrams per liter (as N). Only &#13;
eight of the trace elements analyzed for had median &#13;
concentrations greater than their respective minimum reporting &#13;
levels. Water from one well exceeded the lifetime health advisory &#13;
established by the EPA for molybdenum; water from a different well &#13;
exceeded the proposed EPA maximum contaminant level for uranium. &#13;
Gross alpha and gross beta particle activities generally appeared &#13;
to strongly correlate with quantities of uranium and potassium, &#13;
respectively, detected in ground water. However, water from one &#13;
well exceeded the EPA maximum contaminant level for gross alpha &#13;
particle activity and may exceed the EPA maximum contaminant &#13;
level for beta particle and photon activity, although current &#13;
data on gross beta particle activities are not conclusive on this &#13;
point. Radon concentrations did not appear to directly correlate &#13;
with uranium concentrations. The herbicide prometon was the only &#13;
synthetic organic compound detected in ground water in the study &#13;
area, and was detected in only one well, at a concentration of &#13;
0.038 microgram per liter. This well is shallow and is not used &#13;
for drinking water. With the exception of the one detection of &#13;
prometon, no strong evidence was found of effects on ground-water &#13;
quality from human activities. Therefore, most of the water &#13;
sampled probably recharged at the margins of the alluvial basins &#13;
or recharged through the flood plain before human development &#13;
began.&#13;
&#13;
     With respect to major constituents, the concentrations of &#13;
dissolved solids ranged from 209 to 3,380 milligrams per liter, &#13;
and the median concentration was 409.5 milligrams per liter. &#13;
There is evidence that the overall chemical composition of ground &#13;
water in the study area may be affected by several processes, &#13;
including cation exchange, feldspar weathering, calcite &#13;
dissolution and precipitation, dissolution of volcanic glass, and &#13;
microbial activity. Several chemical constituents in ground water &#13;
showed relatively distinct spatial patterns that appear to be &#13;
related to one or more of these processes.</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.3133/wri964249</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>U.S. Geological Survey</dc:publisher>
  <dc:title>Water-quality assessment of the Rio Grande Valley, Colorado, New Mexico and Texas: Ground-water quality in the Rio Grande flood plain, Cochiti Lake, New Mexico, to El Paso, Texas, 1995</dc:title>
  <dc:type>reports</dc:type>
</oai_dc:dc>