Award Abstract # 0935625
Quantifying the Role of Mixing Interfaces in Biogeochemical Cycling in a Contaminated Aquifer-Wetland System: Linking Hydrogeological, Microbiological and Geochemical Processes

NSF Org: EAR
Division Of Earth Sciences
Recipient: UNIVERSITY OF ST THOMAS
Initial Amendment Date: March 27, 2009
Latest Amendment Date: August 19, 2009
Award Number: 0935625
Award Instrument: Standard Grant
Program Manager: Enriqueta Barrera
EAR
 Division Of Earth Sciences
GEO
 Directorate for Geosciences
Start Date: September 1, 2008
End Date: September 30, 2010 (Estimated)
Total Intended Award Amount: $0.00
Total Awarded Amount to Date: $236,176.00
Funds Obligated to Date: FY 2005 = $236,176.00
History of Investigator:
  • Jennifer McGuire (Principal Investigator)
    jtmcguire@stthomas.edu
Recipient Sponsored Research Office: University of St. Thomas
2115 SUMMIT AVE
SAINT PAUL
MN  US  55105-1048
(651)962-6038
Sponsor Congressional District: 04
Primary Place of Performance: University of St. Thomas
2115 SUMMIT AVE
SAINT PAUL
MN  US  55105-1048
Primary Place of Performance
Congressional District:
04
Unique Entity Identifier (UEI): MEQUD34ZB1Y6
Parent UEI: MEQUD34ZB1Y6
NSF Program(s): BE: COUPLED BIOGEOCHEMICAL CYC
Primary Program Source: app-0105 
Program Reference Code(s): 1524, 1689, 1692, 4444, 9187, EGCH
Program Element Code(s): 169200
Award Agency Code: 4900
Fund Agency Code: 4900
Assistance Listing Number(s): 47.050

ABSTRACT

0418488
McGuire

Quantifying the coupled hydrogeological, microbiological, and geochemical processes that control redox potential is a fundamental issue in understanding the fate and transport of nutrients and contaminants in subsurface systems and thus in protecting drinking water and ecosystem health. In subsurface systems, changes in redox state are often controlled by shifts in the terminal electron accepting processes (TEAPs) of microorganisms, initi-ated by the delivery of limiting terminal electron acceptors such as oxygen, nitrate, or sul-fate. Thus, mixing interfaces between reduced aqueous systems and more oxic "re-charge" water, are zones of increased TEAP dynamics. Despite the well-recognized im-portance of mixing interfaces, few field investigations have targeted these small-scale, transient zones due to difficulties in obtaining hydrologic, geochemical and microbial measurements at relevant spatial and temporal scales.
This interdisciplinary study seeks to quantify the solute transport, geochemical, kinetic, and microbiological controls on TEAPs at mixing interfaces within a contami-nated aquifer-wetland system. High-resolution numerical models will be developed to integrate observations, test hypotheses regarding the role of interfaces on the overall re-ducing capabilities of the system, understand processes and guide field/laboratory ex-periments, and evaluate the potential effects of changing hydrologic conditions on the fate and transport of nutrients and organic contaminants. To accomplish this and test the central hypothesis that maximum TEAP dynamics, including microbial activity and transformation rates, are observed at interfaces due to the delivery of limiting electron acceptors or donors we will perform the following tasks: 1) map and quantify the distri-bution of TEAPs across significant mixing interfaces during various hydrologic condi-tions; 2) conduct in-situ kinetic studies of electron acceptor utilization rates at induced mixing interfaces; 3) identify in-situ changes in microbial community directly related to changes in water chemistry; and 4) integrate measured controls using numerical models and test hypotheses regarding the impact of mixing-interface zones on biogeochemical cycling during variable hydrologic conditions. Our novel application of existing and re-cently developed tools will make it possible to quantify the complex linkages between small-scale changes in microbial community structure and activity and the corresponding geochemistry. New and fundamental knowledge of the controls on TEAPs at mixing in-terfaces is expected to improve our understanding of the fate and transport of redox-sensitive species including nutrients and anthropogenic contaminants and thereby im-prove our ability to assess risk and protect drinking water and ecosystem function.
The findings of this research are expected to be of great value not only to scien-tists searching for improved ways to measure and interpret complex, coupled earth sys-tem processes but also to industry, regulatory agencies, and the general public. To ensure the broader impacts of this research are widely disseminated we have developed strate-gies to 1) involve students (K-12, undergraduate and graduate) through direct employ-ment, course development, and educator training; 2) attract researchers from other fields through workshops, meetings, and peer reviewed publications; 3) educate the public through widely distributed fact sheets, research site tours and web page design; and 4) increase diversity by encouraging the participation of underrepresented groups.

PUBLICATIONS PRODUCED AS A RESULT OF THIS RESEARCH

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Mantha S. Phanikumar and Jennifer T. McGuire "A multi-species reactive transport model to estimate biogeochemical rates based on single-well, push-pull test data" Computers & Geosciences , v.36 , 2010
Susan E. Baez-Cazull, Jennifer T. McGuire, Isabelle M. Cozzarelli, and Mary A. Voytek "Determination of dominant biogeochemical proceses in a contaminated aquifer-wetland system using multivariate statistical analyses" Journal of Environmental Quality , v.37 , 2008
Susan E> Baze-Cazull, Jennifer T. McGuire, Isabelle M. Cozzarelli, Anne Raymond, and Lisa Welsh "Centimeter-scale characterization of biogeochemical gradients at a wetland-aquifer interface using capillary electrophoresis" Applied Geochemistry , v.22 , 2008 , p.2664
Tara A. Kneeshaw, Susan E. Baez-Cazull, Erik W. Smith and Isabelle M. Cozzarelli "Evaluation of sulfate reduction at experimentally induced mixing interfaces using small-scale push-pull tests in an aquifer-wetland system" Applied Geochemistry , v.22 , 2007 , p.2618

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