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The Environmental Research Group has a significant amount of research
on-going in the area of contaminant fate, transport, and in-situ
remediation methods. Areas of interest of the faculty involved in
this type of research include:
- Movement, monitoring, and biodegradation of petroleum hydrocarbon
contamination in soils, groundwater, and salt marshes.
- Colloidal-facilitated contaminant transport and development
of colloid-based remediation methods
- Innovative well construction methods for assessment of contaminated
sites.
- Transport and fate of groundwater contaminants in the vadose
zone,
- Hydrologic and contaminant attenuation processes in cold regions,
- Groundwater-surface water interactions,
- Natural contaminant attenuation processes
- Bioremediation of contaminated subsurface environments
Below a few current projects are highlighted.
Project
In-Situ Reactive Wall Formation with Colloidal
Materials.
Contact: Dr. Kevin Gardner
These projects are focused on putting reactive barrier walls in
place by colloid deposition. The advantages are that much less material
is required and deep contamination or inaccessible areas are not
a problem as they are with trench and backfill approaches. In addition,
sites with heterogeneous stratigraphy, which may cause significant
variations in groundwater flow fields, may be more effectively treated
with a reactive wall formed by colloid deposition rather than a
single-thickness wall typical of reactive barrier walls. To date
two types of walls have been developed: zero-valent iron walls and
catalyst walls, in which a chemical oxidant would be required to
react with the contaminant and catalyst.
Project
Enhanced Bioremediation of Oil-Contaminated
Salt Marshes
Contact: Dr. Nancy Kinner
Of all the estuarine and coastal environments, salt marshes are
the most ecologically sensitive areas impacted by oil spills. Remediation
of oil-contaminated marshes is difficult with cutting and burning
of marsh grass, sediment removal and replanting, or natural attenuation
being common current practices. Enhanced bioremediation, such as
adding nutrients using a variety of surface application methods,
has been tried for several kinds of shoreline environments, but
has been hampered because much of the nitrogen/phosphate is lost
during tidal flushing. In 1997, we received grants from the Cooperative
Institute for Coastal and Estuarine Environmental Technologies (CICEET)
and the New Hampshire Department of Environmental Services (NHDES)
to evaluate three types of enhanced bioremediation systems (nutrient,
air, and nitrate amendments) in an oil-contaminated salt marsh in
Portland, ME.
Project
Investigation of Mechanisms of Surfactant-Induced
Hydraulic Conductivity Changes in Soil Flushing Operations
Contact: Dr. Kevin Gardner
A major concern with the use of surfactant flushing to mobilize
non-aqueous phase liquids in aquifers is specific mineral-surfactant
interactions which may effect significant permeability changes in
the soil formation. Soils are being investigated for loss of permeability
upon flushing with solution containing a number of nonionic and
anionic surfactants. Surfactant / clay interactions are being further
investigated as the cause of the permeability reductions, both from
transport/rearrangement and swelling.
Project
Bedrock Bioremediation Center
Contact: Dr. Nancy Kinner
The Bedrock Bioremediation Center (BBC) at the University of New
Hampshire specializes in multidisciplinary research on bioremediation
of organically contaminated bedrock aquifers. The Center is comprised
of a consortium of faculty from the University's Environmental Research
Group (ERG), and the UNH Departments of Microbiology, Earth Sciences,
and Natural Resources. The BBC, in conjunction with the U.S. Air
Force's environmental engineering program at the Pease International
Tradeport (Portsmouth, NH), is developing and evaluating technologies
for enhanced bioremediation of the bedrock aquifer at Pease Site
32.
Water flowing through fractures in bedrock aquifers is used for
drinking water in much of the United States. Remediation of these
aquifers, once contaminated, is often deferred because of difficulties
in characterizing the extent of the problem and the lack of appropriate
cleanup technologies. One possible inexpensive and efficient method
for remediating these sites in situ may be bioremediation using
the naturally-occurring microorganisms that live along the fractures
in the bedrock. However, very limited data are available on the
success/implementation of bioremediation in bedrock aquifers. The
overall goal of the BBC is to improve our understanding of this
new technology, develop methods to apply and enhance its use, and
to monitor its effectiveness in situ. For more information on the
BBC, access the Center's website at www.bbc.unh.edu.
Project
Bioventing of No. 2 Fuel Oil Contaminated
Soils: Effects of Acclimation, Temperature, Air Flowrate and Nutrients
Contact: Dr. Nancy Kinner
The New Hampshire Department of Environmental Services (NHDES)
anticipates that there will be an increasing number of sites discovered
throughout the State that are contaminated with No. 2 fuel oil,
particularly associated with leaking storage tanks at private homes.
A significant portion of the contamination at these sites will be
located in the vadose zone. While several techniques exist for remediating
No. 2 fuel contamination in the vadose zone, bioventing is potentially
the best suited for use at sites associated with private homes.
Bioventing is low cost and does not require removal of the basement
floor and excavation of the soil below it.
Project
Development of a Risk Analysis Framework for
Beneficial Use of Secondary Materials
Contact: Dr. Kevin Gardner
This project is being conducted to answer the following questions:
How should States decide whether a secondary material is safe for
use in different types of applications? What are the risks associated
with using a byproduct that may have some elevated levels of contaminants,
and how can this risk be quantified?
The purpose of this project is to develop a risk analysis framework
for beneficial use of secondary materials. The first stage of the
project involves understanding of water movement in the roadway
environment. HYDRUS2D, a variably saturated two-dimensional model
for water flow and solute transport, is being used to simulate water
movement in the roadways. The model is being calibrated and verified
with data from MnROAD, a field facility project of MnDOT. Ultimately,
a rigorous fate, transport, and risk assessment model will be developed
with the focus of realistically estimating leachate concentrations
and risk from a number of typical, high-volume roadway applications.
Based on this model and results for various highway environments,
a simplified risk assessment approach will be developed for use
by State environmental agencies in support of beneficial use determinations.
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