Determination%20of%20sediment%20phosphorus%20concentrations%20in%20St.%20Albans%20Bay,%20Lake%20Champlain:%20Assessment%20of%20internal%20loading%20and%20seasonal%20variations%20of%20phosphorus%20sediment-water%20column%20cycling - PowerPoint PPT Presentation

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Determination%20of%20sediment%20phosphorus%20concentrations%20in%20St.%20Albans%20Bay,%20Lake%20Champlain:%20Assessment%20of%20internal%20loading%20and%20seasonal%20variations%20of%20phosphorus%20sediment-water%20column%20cycling

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Title: Determination%20of%20sediment%20phosphorus%20concentrations%20in%20St.%20Albans%20Bay,%20Lake%20Champlain:%20Assessment%20of%20internal%20loading%20and%20seasonal%20variations%20of%20phosphorus%20sediment-water%20column%20cycling


1
Determination of sediment phosphorus
concentrations in St. Albans Bay, Lake Champlain
Assessment of internal loading and seasonal
variations of phosphorus sediment-water column
cycling
  • Greg Druschel
  • Department of Geology
  • University of Vermont

2
Acknowledgements
  • Funding for this study through State of Vermont
    Clean Clear Program, administered by the
    Department of Environmental Conservation
  • VT DEC, especially Eric Smeltzer and Pete
    Stengel, for providing logistical support
  • St. Albans Bay Watershed association and town
    administrator Dan Lindley
  • Students at UVM who assisted Aaron Hartmann,
    Rachel Lomonaco, Deb Schulman, and Ken Oldyryd
  • Mary Watzin, Eric Smeltzer, Andrea Lini, Neil
    Kamman for thoughtful and insightful discussions

3
Program Goals
  • Determine the amount of phosphorus currently
    contained in St. Albans Bay sediments
  • Determine how that phosphorus may be mobile
    within the sediments ? what controls P profiles
    and how P may be released from sediments into the
    water column, providing nutrients feeding algal
    blooms

4
Redox Fronts
  • Boundary between oxygen-rich (oxic) and more
    reduced (anoxic) waters
  • Oxygen consumed by microbes which eat organic
    material
  • When Oxygen is gone, there are species of
    microbes that can breathe oxidized forms of
    iron, manganese, and sulfur

5
Methods
  • Gravity Coring
  • Seasonal site ? 10 separate samplings, late May
    through early October
  • Early August collected 43 cores across the bay
    and Stevens Brook Wetland
  • In-situ pore water measurments to determine redox
    front
  • Chemical extractions of iron, manganese, and
    phosphorus in the sediment
  • Inductively-coupled plasma optical emission
    spectroscopy (ICP-OES) to measure iron,
    manganese, and phosphorus from extractant

6
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7
Results Seasonal Work
  • Sediments generally become more reduced as summer
    progresses
  • Redox fronts move up and down in response to
    Temperature, wind, biological activity changes

8
Summer 2004
  • Summer 2004 was, in general, colder than average,
    windy, and rainy ? these factors would drive
    redox fronts higher in the sediment column
  • Sediments at other locations (deeper, in the
    wetland) would be slightly different possibly
    having a lower redox front

9
Seasonal Phosphorus mobility
  • Ascorbic acid extractions of Fe, Mn, and P from
    10 sediment cores collected in summer 2004 show
    strong dependence between P and Mn or Fe
  • Further, profiles show overall enrichment of all
    3 parameters in upper sections of sediment
  • Fe and Mn would be primarily in the form of Fe
    and Mn oxyhydroxide minerals ? transformation of
    these minerals is key to P movement

10
Sediment P mobility and water column
  • Does the P mobilized in the sediment get into the
    water column and does it contribute to algal
    activity/ blooms?
  • From our data, it seems that Fe, Mn mineral
    changes and P mobility in the sediments is linked
    to both P release and algal activity
  • Our study methods were not specifically designed
    for this, but now that we know the processes
    involved, a better study of P transfer from
    sediment and use by algae is possible

11
St. Albans Bay P Load
  • 43 cores subdivided into 7 depth sections each,
    extracted 5 different ways analyzed in
    triplicate
  • 1200 individual samples and 3000 individual
    analyses
  • Results
  • Top 4 cm contains 500 tons of P
  • Top 10 cm of sediment contains 1200 tons of P

12
  • 1992 vs 1982 comparisons suggested P was being
    essentially flushed out of the sediments into the
    main lake

This study finds no evidence to support P
concentrations are substantially decreasing in
time i.e. ? the bay sediments will NOT clean
themselves in the near future
13
Spatial distributions
  • Profiles again reflect a general increase of P,
    Mn, and Fe in top few cm of these cores

14
P Loading and sediment deposition
  • Constantly moving redox fronts affect Fe and Mn
    minerals, mobilize P and turn ideal profile into
    what we actually see

15
Summary of Findings
  • There remains significant P in the sediments of
    St. Albans Bay, and overall rates of P loss from
    the sediments should be much lower than
    previously thought
  • P mobility in the sediments is at least partly
    governed by Iron and Manganese mineralization
    which is strongly affected by redox fronts
  • This mobility has changed the profile of P in the
    sediments by smoothing out any recorded changes
    in P loading.
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