CALL FOR PROPOSALS:

ORGANIZERS

  • Harvey Thorleifson, Chair
    Minnesota Geological Survey
  • Carrie Jennings, Vice Chair
    Minnesota Geological Survey
  • David Bush, Technical Program Chair
    University of West Georgia
  • Jim Miller, Field Trip Chair
    University of Minnesota Duluth
  • Curtis M. Hudak, Sponsorship Chair
    Foth Infrastructure & Environment, LLC

 

Paper No. 17
Presentation Time: 1:00 PM

INITIAL EXAMINATION OF CHEMICAL VARIABILITY WITHIN ATCHAFALAYA BASIN DURING SPRING-SUMMER FLOOD OF 2011


CARLSON, Douglas A., Louisiana Geological Survey, Louisiana State Univ, 3079 Energy Coast & Environment Bldg, Baton Rouge, LA 70803 and HORN, Marty, Louisiana Geological Survey, Louisiana State University, 3079 Energy, Coast, & Env. Bldg, Louisiana State University, Baton Rouge, LA 70803, dcarlson@lsu.edu

The water chemistry in the Atchafalaya Basin (located in south-central Louisiana) is a dynamic variable system. Water quality varies throughout the basin depending on location, distance south from the Morganza spillway, position relative to the basin’s axis, depth from water surface, and time after the start of the flood event starting May 24th, 2011 when gates were opened on the Morganza spillway.

Between May 19th and July 21st several agencies (Louisiana Department of Wildlife and Fisheries, US Geological Survey, and US Fish and Wildlife Service) collected field chemistry measurements (pH, turbidity, dissolved oxygen (DO), Cl-, temperature, and electrical conductivity (EC)) at approximately 45 sites throughout the basin (which is south of 32o 23’ and is 20 km by 80 km, long axis trending at approximately 145o) and collected water samples for later laboratory analysis. Field measurements and sample collection for later laboratory analysis occurred weekly between May 19th and June 23rd and biweekly on July 7th and July 21st. Later laboratory analysis was completed by several agencies/individuals. The staff of the Louisiana Geological Survey determined concentrations of Br-, Fl-, Cl-, NO3-2, PO4-3, and SO4-2 by ion chromatographic analysis; phosphate by colorimeter; and total suspended solids (TSS) by gravimetric analysis.

Generally DO, Fl-, TSS and Turbidity decrease over time, and Cl-, EC, SO4-2, and temperature increases over time. For nutrients of -, NO3-2 and PO4-3 the average concentration appears to be fairly steady during the flood, but the variability depending on location generally increases over time. Some of the variables measured vary depending on location as well as time. Depth of field measurement appears not to influence concentrations of dissolved species such as DO, Cl-, EC, pH, but influences turbidity which increases significantly with depth. Lateral position also influences concentration of some parameters, DO increases from east to west across the basin; turbidity and TSS appear to have higher concentrations near basin’s central axis and decrease towards the edges of the basin; and nutrient concentrations decrease southward and from east to west across the basin.

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