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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:contributor>J.E. Putnam</dc:contributor>
  <dc:creator>L. M. Pope</dc:creator>
  <dc:date>1997</dc:date>
  <dc:description>A study of urban-related water-qulity effects in the Kansas River,  Shunganunga Creek Basin, and Soldier Creek in Topeka, Kansas, was  conducted from October 1993 through September 1995.  The purpose of this  report is to assess the effects of urbanization on instream  concentrations of selected physical and chemical constituents within the  city of Topeka.  A network of seven sampling sites was established in the  study area.  Samples principally were collected at monthly intervals from  the Kansas River and from the Shunganunga Creek Basin, and at quarterly  intervals from Soldier Creek.  The effects of urbanization werestatistically evaluated from differences in constituent concentrations  between sites on the same stream.  No significant differences in median concentrations of dissolved  solids, nutrients, or metals and trace elements, or median densities offecal bacteria were documented between sampling sites upstream and  downstream from the major urbanized length of the Kansas River in Topeka.Discharge from the city's primary wastewater- treatment plant is the  largest potential source of contamination to the Kansas River.  This  discharge increased concentrations of dissolved ammonia, totalphosphorus, and densities of fecal bacteria.Calculated dissolved  ammonia as nitrogen concentrations in water from the Kansas River ranged  from 0.03 to 1.1 milligrams per liter after receiving treatment-plant  discharge.  However, most of the calculated concentrations wereconsiderably less than 50 percent of Kansas Department of Health and  Environment water- quality criteria, with a median value of 20 percent.Generally, treatment-plant discharge increased calculated total  phosphorus concentrations in water from the Kansas River by 0.01 to 0.04  milligrams per liter, with a median percentage increase of 7.6 percent.   The calculated median densities of fecal coliform and fecal Streptococci  bacteria in water from the Kansas River increased from 120 and 150colonies per 100 milliliters of water, respectively, before  treatment-plant discharge to a calculated 4,900 and 4,700 colonies per  100 milliliters of water, respectively, after discharge.  Median concentrations of dissolved solids were not significantly different between three sampling sites in the Shunganunga Creek Basin.   Median concentrations of dissolved nitrate as nitrogen, total phosphorus,  and dissolved orthophosphate were significantly larger in water from the  upstream- most Shunganunga Creek sampling site than in water from either  of the other sampling sites in the Shunganunga Creek Basin probably  because of the site's proximity to a wastewater-treatment plant.Median  concentrations of dissolved nitrate as nitrogen and total phosphorus  during 1993-95 at upstream sampling sites were either significantlylarger than during 1979-81 in response to increase of  wastewater-treatment plant discharge or smaller because of the  elimination of wastewater-treatment plant discharge.  Median  concentrations of dissolved ammonia as nitrogen were significantly less  during 1993-95 than during 1979-81.  Median concentrations of total aluminum, iron, maganese, and  molybdenum were significantly larger in water from the downstream-mostShunganunga Creek sampling site than in water from the upstream-most  sampling site.  This probably reflects their widespread use in the urbanenvironment between the upstream and downstream Shunganunga Creek  sampling sites.  Little water-quality effect from the urbanization was indicated by  results from the Soldier Creek sampling site. Median concentrations of  most water-quality constituents in water from this sampling site were the  smallest in water from any sampling site in the study area.  Herbicides were detected in water from all sampling sites.  Some of  the more frequently detected herbicides included acetochlor, alachlor,atrazine, cyanazine, EPTC, metolachlor, prometon, simazine, and  tebuthiuron.  Detected insecticides including chlordane,</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.3133/wri974045</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>U.S. Geological Survey ;&#13;
Information Services [distributor],</dc:publisher>
  <dc:title>Effects of urbanization on water quality in the Kansas River, Shunganunga Creek Basin, and Soldier Creek, Topeka, Kansas, October 1993 through September 1995</dc:title>
  <dc:type>reports</dc:type>
</oai_dc:dc>