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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>Scott K. Anderholm</dc:creator>
  <dc:date>1997</dc:date>
  <dc:description>This report describes the quality of shallow ground water and the  &#13;
relations between land use and the quality of that shallow ground water &#13;
in an urban area in and adjacent to Albuquerque, New Mexico. Water&#13;
samples were collected from 24 shallow wells. Samples were analyzed for &#13;
selected common constituents, nutrients, trace elements, radionuclides, &#13;
volatile organic compounds, and pesticides. &#13;
&#13;
     The study area, which is in the Albuquerque Basin in central New Mexico, &#13;
was limited to the Rio Grande flood plain; depth to water in this area  &#13;
generally is less than 25 feet. The amount and composition of recharge to &#13;
the shallow ground-water system are important factors that affect shallow &#13;
ground-water composition in this area. Important sources of recharge that &#13;
affect shallow ground-water quality in the area include infiltration of &#13;
surface water, which is used in agricultural land-use areas to irrigate &#13;
crops, and infiltration of septic-system effluent in residential areas. &#13;
Agricultural land use represents about 28 percent of the area, and residential &#13;
land use represents about 35 percent of the total study area. In most of the &#13;
study area, agricultural land use is interspersed with residential land use &#13;
and neither is the dominant land use in the area. Land use in the study area &#13;
historically has been changing from agricultural to urban.  &#13;
&#13;
     The composition of shallow ground water in the study area varies &#13;
considerably. The dissolved solids concentration in shallow ground water in &#13;
the study area ranges from 272 to 1,650 milligrams per liter, although the &#13;
relative percentages of selected cations and anions do not vary substantially. &#13;
Calcium generally is the dominant cation and bicarbonate generally is the &#13;
dominant anion. Concentrations of nutrients generally were less than 1 &#13;
milligram per liter. The concentration of many trace elements in shallow &#13;
ground water was below or slightly above 1 microgram per liter and there was &#13;
little variation in the concentrations. Barium, iron, manganese, molybdenum, &#13;
and uranium were the only trace elements analyzed for that had median &#13;
concentrations greater than 5 micrograms per liter. Volatile organic &#13;
compounds were detected in 5 of 24 samples. Cis-1,2-dichloroethene and  &#13;
1,1-dichloroethane were the most commonly detected volatile organic compounds   &#13;
(detected in two samples each). Pesticides were detected in 8 of 24 samples. &#13;
Prometon was the most commonly detected pesticide (detected in 5 of 24 &#13;
samples). Concentrations of volatile organic compounds and pesticides detected  &#13;
were much smaller than any U.S. Environmental Protection Agency standards &#13;
that have been established. &#13;
&#13;
     Infiltration of surface water and the evaporation or transpiration of &#13;
this water, which partially is the result of past and present agricultural &#13;
land use, seem to affect the concentrations of common constituents in shallow &#13;
ground water in the study area. The small excess chloride in shallow ground &#13;
water relative to surface water that has been affected by evaporation or &#13;
transpiration could be due to mixing of shallow ground water with small &#13;
amounts of precipitation/bulk deposition or septic-system effluent. &#13;
&#13;
     Infiltration of septic-system effluent (residential land use) has &#13;
affected the shallow ground-water composition in parts of the study area on  &#13;
the basis of the small dissolved oxygen concentrations, large dissolved &#13;
organic carbon concentrations, and excess chloride. Despite the loading of &#13;
nitrogen to the shallow ground-water system as the result of infiltration of &#13;
septic-system effluent, the small nitrogen concentrations in shallow ground &#13;
water probably are due to the small dissolved oxygen concentrations and &#13;
relatively large dissolved organic carbon concentrations. &#13;
&#13;
     The small concentrations and lack of variation of most trace elements &#13;
indicate that land use has not substantially affected the concentration</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.3133/wri974067</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 -- Shallow ground-water quality and land use in the Albuquerque area, central New Mexico, 1993</dc:title>
  <dc:type>reports</dc:type>
</oai_dc:dc>