 |
Anne Kremer Huth and Roger Bales install scour chains in a gravel bar of the Sab Pedro
|
|
|
|
The major goal of Thrust Area
3 (TA3) is to understand how riparian systems affect
and are affected by changes in water quantity (e.g.,
due to ground-water pumping or conjunctive stream-water
management) or water quality (e.g., nitrogen inputs
from precipitation or agricultural runoff).
Research in TA3 is generally separated
into two foci:
- Water
and carbon exchange in riparian systems.
- Nutrient
cycling in riparian systems.
These two groups are linked through
the common need to understand the dynamics of the water
balance and
movement within the riparian zone, as well as within
the basin.
This need for common knowledge also
necessitates the collaboration of TA3 members with researchers
from TA1, TA2 and TA4 for understanding the possible
long-term effects of climate-change and anthropogenic
stressors on the health of the riparian system. Figure
3.1 illustrates the stratification within TA3, the
links within and across the SAHRA TAs, and the collaboration
with other research groups with which there are strong
active partnerships. Much of the research being performed
is a continuation of the SALSA (Semi-Arid Land Surface
Atmosphere) project, and is heavily leveraged with many
entities in the Upper San Pedro River Valley.
3.1 Water and Carbon Exchange in Riparian Systems
The major goal of this group is to develop a holistic
approach for assessing the effects of ground-water development
and conjunctive surface-water management on riparian
ecosystems. Most of the historic riparian areas in the
southwest have disappeared over the last century. This
is believed to be a direct consequence of groundwater
pumping for agriculture, mining, and municipal needs.
These riparian corridors harbor a large majority of
the regional biodiversity, and provide an aesthetic
value for many humans, and presently, they are facing
great stress. Researchers in this group seek to understand
the effects of changing hydrologic dynamics (ground,
vadose, surface, and plant water movements) on riparian
ecology on the time scales of hours to years.
Individual research efforts include:
The collaborative relationships
both within this subtask and with other projects are
illustrated in left side of Figure 3.1.
These projects are closely related as they are focused
directly on the interplay of the riparian plants with
the movement and availability of water. The sum of these
projects will be new tools to predict ecological succession
with changing hydrologic stress. Since this work is
interested in long-term effects of hydrologic changes
on the riparian ecology, there are connections with
the infiltration/runoff studies in TA1 and the basin-scale,
water-balance studies in TA2. In addition, the micrometeorological
flux measurements will tie into similar measurements
in TA1 and TA2. This data will also be used to calibrate
land-surface models in TA4. Furthermore, the understanding
of what sources of water are used by which plant communities
will be critical information for basin management, and
therefore will tie into TA5.
Activities
and plans for next reporting period
The major activities of the various task areas for the
last year are listed below:
3.2 Nutrient Cycling in Riparian Systems
The central objective of this group is to understand
the role of biogeochemical cycling in the hyporheic
zones of streams as a pathway for removal of natural
and anthropogenic solutes in riparian ecosystems. Riparian
zones can be highly variable, depending on channel type,
perturbations, and local vegetation. The interaction
of nutrients and biota affects redox conditions in shallow
ground water, which influences the movement of anthropogenic
inputs in the system (e.g., metals). The efficiency
of this biogeochemical cycling depends on availability
of nutrients, characteristics of the riparian ecotone,
and hydrologic characteristics of hyporheic flow paths.
In streams of the semi-arid Southwest, the common limiting
nutrient is nitrogen. Large nitrogen inputs from precipitation,
fertilizer applications, and other human activities
thus could potentially contribute to eutrophication
of aquatic ecosystems. In addition, rainfall and nitrogen
inputs from floods exhibit seasonal patterns.
Individual research efforts include:
- Understanding
the links between hydrology, geomorphology and nutrient
cycling within the semi-arid riparian/stream system.
Grimm (ASU), Conklin (UA), Villinski (UA)
- Contribution
of terrestrially produced dissolved organic matter
(DOM) to carbon and nitrogen cycling in semi-arid
riparian ecosystems.
Brooks (UA)
- The
influence of episodic flow events on nutrient and
sediment loads in semi-arid streams.
Conklin, Villinski (UA-HWR)
- Relating
hydrologic flowpaths to nutrient speciation and retention.
Grimm, Schade, Lewis (ASU)
- Spatial
and temporal variability of the sources, sinks and
speciation of nitrogen and carbon in semi-arid rivers.
Villinski, Hogan, Brooks, Conklin (UA-HWR)
All are concerned with nutrient
cycling in the riparian/stream system. Crucial to all
these projects and those of the other focus of TA3 is
the understanding of the flow of water in the various
hydrologic units within the system. Therefore, these
projects will not only share data within TA3, but will
also share data with TA1 and TA2 regarding hydrologic
inputs into the riparian system. The ultimate goal is
to create a "nutrient" model that combined
with the other modeling activities within the San Pedro
River Basin can result in an integrated riparian ecosystem
model.
Relevance
of Thrust Area efforts to SAHRA goals
The results from these research activities will be included
in the integrated modeling effort of TA4, adding the
critical nutrient component that is often overlooked
in hydrologic modeling.
|