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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>Michael J. Friedel</dc:contributor>
  <dc:creator>James A. Tindall</dc:creator>
  <dc:date>2016</dc:date>
  <dc:description>The objectives of this research were to determine the role of preferential flow paths in the transport of atrazine (2-chloro-4-(ethylamino)-6-(isopropylamino)-s-triazine)  and  dicamba  (3-6-dichloro-2-methoxybenzoic  acid)  through  silt and loam soils overlying the  High Plains aquifer in Nebraska. In  a previous study, 3 of 6 study areas  demonstrated high percentages  of  macropores;  those  three  areas  were  used  in  this  study  for  analysis  of  chemical  transport.  As  a subsequent  part  of  the  study,  12  intact soil cores (30-cm  diameter  by 40-cm  height),  were  excavated sequentially,  two from each of the following depths: 0-40cm and 40-80cm. These cores were used to study preferential flow characteristics using  dye  staining  and  to  determine  hydraulic  properties.  Two  undisturbed  experimental  field  plots,  each with  a  3-m2 &#13;
surface  area,  were  installed  in  three  study  areas  in  Nebraska.  Each  was  instrumented  with  suction  lysimeters  and tensiometers at  depths of 10cm to 80cm in 10-cm  increments. Additionally, each plot was planted with corn (Zea mays). &#13;
&#13;
A neutron probe access tube was installed in each plot to determine soil w ater content at 15-cm intervals.  All plots were enclosed w ith a raised frame  (of  8-cm height) to prevent surface  runoff.  All  suction  lysimeters were purged monthly  for three  months  and  were  sampled  immediately  prior  to  pre-plant  herbicide  application  to  obtain  background  chemical &#13;
concentrations.  Atrazine  and  dicamba  moved  rapidly  through  the  soil,  but  only  after  a  heavy  rainfall  event,  probably owing  to  the  presence  of  preferential  flow  paths  and  lack  of  microbial  degradation  in  these  soil  areas.  Staining  of laboratory  cores  showed  a  positive  correlation  between  the  percent  area  stained  by  depth  and  the  subsequent &#13;
breakthrough  of  Br-  in  the  laboratory  and  leaching  of  field-applied  herbicides  owing  to  large  rainfall  events.  Suction lysimeter  samples  in  the  field  showed  increases  in  concentrations  of  herbicides  at  depths  where  laboratory  data indicated  greater  percentages of  what  appeared to be preferential  flow  paths. Concentrations of  atrazine  and  dicamba &#13;
exceeding  0.30  and  0.05µg  m1-1  were observed  at  depths  of 10-30cm  and  50-70cm  after two  months following  heavy rainfall events. It appears from the laboratory experiment that preferential flow paths were a significant factor in transport of atrazine and dicamba.</dc:description>
  <dc:format>application/pdf</dc:format>
  <dc:identifier>10.15377/2409-5710.2016.03.01.3</dc:identifier>
  <dc:language>en</dc:language>
  <dc:publisher>Avanti </dc:publisher>
  <dc:title>Transport of atrazine and dicamba through silt and loam soils</dc:title>
  <dc:type>article</dc:type>
</oai_dc:dc>