
NSF Org: |
EAR Division Of Earth Sciences |
Recipient: |
|
Initial Amendment Date: | March 2, 2015 |
Latest Amendment Date: | February 1, 2019 |
Award Number: | 1446724 |
Award Instrument: | Standard Grant |
Program Manager: |
Laura Lautz
llautz@nsf.gov (703)292-7775 EAR Division Of Earth Sciences GEO Directorate for Geosciences |
Start Date: | March 1, 2015 |
End Date: | January 31, 2020 (Estimated) |
Total Intended Award Amount: | $256,672.00 |
Total Awarded Amount to Date: | $289,432.00 |
Funds Obligated to Date: |
FY 2019 = $32,760.00 |
History of Investigator: |
|
Recipient Sponsored Research Office: |
1960 KENNY RD COLUMBUS OH US 43210-1016 (614)688-8735 |
Sponsor Congressional District: |
|
Primary Place of Performance: |
1960 Kenny Road Columbus OH US 43210-1016 |
Primary Place of
Performance Congressional District: |
|
Unique Entity Identifier (UEI): |
|
Parent UEI: |
|
NSF Program(s): |
EnvE-Environmental Engineering, Hydrologic Sciences, Integrat & Collab Ed & Rsearch |
Primary Program Source: |
01001920DB NSF RESEARCH & RELATED ACTIVIT |
Program Reference Code(s): |
|
Program Element Code(s): |
|
Award Agency Code: | 4900 |
Fund Agency Code: | 4900 |
Assistance Listing Number(s): | 47.050 |
ABSTRACT
Humans have dramatically altered the nitrogen cycle through food and energy production activities. Increased nitrogen loading to landscapes often results in nitrogen export to the coast, leading to algal blooms, dead zones, and declines in fisheries. Nitrate removal in riparian aquifers and riverbeds provides an important ecosystem service that mitigates nitrogen loads to coasts. However a vast majority of nitrogen never reaches the coast, rather it is retained within the watershed or transformed by microbes. Riverbanks and bottoms are prime locations for this retention and transformation, providing a valuable ecosystem service. In tidal freshwater zones (TFZs) where tides pump river water in and out of the riverbanks and riverbed, nitrate removal may be particularly effective. This study will determine the nitrogen removal efficiency of TFZs. If TFZs play a disproportionately large role in nitrogen removal within watersheds, management strategies should seek to protect TFZs by maintaining riparian buffer zones and limiting sediment sources that could clog riverbeds, reducing their removal efficiency. The research should improve our ability to manage nitrate in freshwater and better value the ecosystems services of tidal freshwater zones and estuaries. The results will be shared with the public in two ways: (1) Creek Fest, an outreach event that promotes watershed stewardship to over 1000 attendees, the PIs will will discuss implications for TFZ management with local stakeholders; and (2) the PIs will also develop a virtual field trip to educate high school and college students in land-locked classrooms on ecosystem services in tidal environments.
Rarely monitored for discharge or nutrient fluxes, TFZs are dynamic transition zones between rivers and estuaries. In TFZs, semidiurnal stage fluctuations should promote intense bank storage and release. Bank storage zones may be efficient sites of nitrate removal. However, associated water table fluctuations may also aerate shallow groundwater and enhance nitrification, adding nitrate to groundwater. The net effect of these two tidally induced, opposing processes could range from net nitrate production to removal within TFZs. This proposal asks how tidally induced hydrodynamic processes such as bank storage and water table fluctuations control nitrogen transformations within the riparian aquifers of TFZs and how these processes upscale to influence nitrogen fluxes from land to sea. It is hypothesized that: 1) TFZ hydrodynamics promote two hot spots of nitrogen transformation in the riparian aquifer: a nitrification hot spot at the soil-groundwater interface where semidiurnal water table fluctuations oxygenate the shallow groundwater, and a denitrification hot spot near the river-groundwater interface where surface water exchanges through oxygen depleted sediments; 2) as tidal range increases in the downstream direction within the TFZ, nitrate production via nitrification increases more than nitrate removal via denitrification. These hypotheses will be tested using a combination of field observations within a TFZ, laboratory experiments, and numerical models. The field component will characterize fluid and nitrogen fluxes across the river-aquifer interface and identify non-conservative nitrogen transport in the riparian aquifer of a TFZ within the Christina River Basin (Delaware). Sediment cores will be used in laboratory column experiments to explore relationships between water table fluctuations, groundwater redox conditions, and nitrogen transformation. Numerical models will be used to upscale nitrogen fate along the TFZ of the Christina River Basin.
PUBLICATIONS PRODUCED AS A RESULT OF THIS RESEARCH
Note:
When clicking on a Digital Object Identifier (DOI) number, you will be taken to an external
site maintained by the publisher. Some full text articles may not yet be available without a
charge during the embargo (administrative interval).
Some links on this page may take you to non-federal websites. Their policies may differ from
this site.
PROJECT OUTCOMES REPORT
Disclaimer
This Project Outcomes Report for the General Public is displayed verbatim as submitted by the Principal Investigator (PI) for this award. Any opinions, findings, and conclusions or recommendations expressed in this Report are those of the PI and do not necessarily reflect the views of the National Science Foundation; NSF has not approved or endorsed its content.
Human activities related to energy and food production add large amounts of reactive nitrogen to the landscape. Rain and snow wash some of that nitrogen into rivers and eventually to the coast, where it can cause excessive algal growth and lead to fish kills. As nitrogen travels to the coast, microbes in the sediment beneath and near the river process and remove nitrogen, but prior to this study, it was unclear how much nitrogen might be removed within the tidal freshwater zone (TFZ) due to daily tidal fluctuations. We conducted four field campaigns to assess surface water-groundwater exchange rates and biogeochemical dynamics at our primary field site along White Clay Creek. We monitored water levels in the river and aquifer and measured the chemistry of water and sediment. Water and redox levels were measured continuously with sensors. These measurements reveal that along TFZs, there are different zones of nitrogen processing created by variations in the supply of reactants across sediment types and water exchange rates. Zones of nitrate production exist within the stream bank aquifer, but conditions favoring nitrate removal dominate. Based on our measurements, we developed a series of progressively more complex models of reactive transport to assess nitrogen dynamics in TFZs: 1) one-dimensional vertical reactive transport models in the riverbed, 2) box models in the bed and banks, and 3) two-dimensional reactive transport models in the bed and banks. These combined efforts reveal that how the water moves through the subsurface, controlled in large part by aquifer and sediment characteristics, drives reactant availability (oxygen and organic matter) and thus nitrogen cycling within these near coastal regions. We trained 3 graduate students (two PhDs, two Masters theses), supervised 3 undergraduate theses (2 from CC and 1 from OSU), and provided additional field and lab experiences for ten students (mostly undergraduates). We presented our work twice to a broad audience of citizens living near tidal rivers at White Clay Creek Fest, Colorado College students screened their short movie at the Associated Colleges of the Midwest Film Festival (Spring 2018), and we presented our findings at more than 15 scientific conferences and within nine submitted peer reviewed manuscripts.
Last Modified: 05/04/2020
Modified by: Audrey H Sawyer
Please report errors in award information by writing to: awardsearch@nsf.gov.