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Geochemistry, Biochemistry, and
Surface/Groundwater Interactions for As, Cr, Ni, Zn, and Cd with
Applications to Contaminated Waterfronts
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| EPA Agreement Number |
R828771-0-01 |
| Investigators |
Barth F. Smets (UConn); Allison A. MacKay(UConn) |
| Type of Research |
Basic Research (Field and Laboratory) |
| Project Period |
10/1/01 - 9/30/02 |
| Objectives of Research |
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Many
industrial and urban sites with subsurface contamination are
characterized by shallow aquifers that discharge to nearby surface water
bodies. In such cases, pore
water in the stream or pond sediments contain a mixture of surface water
and groundwater and are herein refered to as the groundwater/surface
water interface (GSI). There
is little understanding of the extent to which groundwater contaminants
may be immobilized in the GSI, or discharged to the surface water
column. Studies in Montana
have shown that high pH, oxygenated surface water induces precipitation
of iron and manganese oxides and sorption of heavy metals from
discharging groundwater (e.g., Fuller & Harvey (2000) Environ. Sci
Technol., 34: 1150-1155). Biological
processes may also be important in the GSI due to the greater abundance
of nutrients in stream sediments than in groundwater zones.
Thus, GSI processes may play an important role in attenuating
groundwater contaminant discharges to surface water bodies.
The objectives of this research project are to
identify and assess the relative importance of the complex, and
potentially antagonistic, microbial and chemical processes that govern
the retardation and migration of metals, specifically Cd, Zn, Ni, As,
Cr, from a reduced aquifer zone through the GSI into an adjacent surface
water body. Specific
sub-objectives of this work are: (1) determine the significance of
dissimilatory sulfate and iron reduction in the immobilization of
typical cations and oxyanions; (2) determine the relative significance
of microbial and chemical iron oxidation in the GSI; (3) characterize
solid-phase and dissolved heavy metal species in groundwater as a
function of location with respect to the reduced or GSI zones |
| Project
Summary/Accomplishments |
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The proposed experimental approach consists of field observations and
controlled laboratory experiments.
The progress in each of these two areas is described below: |
Field
Observations:
Field tasks consisted of Geoprobe direct push sampling
of pore water and solids in transects across the shoreline at a
contaminated waterfront site. A
doctoral student (Ping Gan) has primary responsibility for directing
field sampling tasks in consultation with PIs.
The proposed site location in Stratford, CT was chosen because of
the extensive site characterization undertaken by other University of
Connecticut researchers and because of the working relationship between
the site owner and the university.
Upon review of the site characterization report, this site was
deemed to be unsuited for this GSI study because the groundwater plume
depth was to great to feasibly sample with the equipment available to
us. Project tasks were thus
revised to include a “Site Evaluation” stage.
Site evaluation is being conducted with the aid of EPA Region 1 (Mr.
Dick Willey) and CT Dept. of Environmental Protection (Mr. Maurice
Hamel). The goal of the
site selection is to identify potential field sites with differing
groundwater and surface water chemistries and where groundwater
contaminants are known to impact adjacent surface water quality.
In this way, this project can focus on biological and chemical
processes without extensive hydrologic characterization.
Thus, the criteria for site selection include: (1) a review of
existing site data noting observations of groundwater seeps and sediment
pore water concentrations of contaminants; (2) visual inspection and
walk-through; (3) pore water collection and solids collection using
hand-sampling techniques. To date, four potential sites have been identified and
reviewed. Two sites have
been eliminated from consideration for various reasons.
Of the two sites under consideration, one is located in CT and
has been sampled to obtain current groundwater samples and profiles of
pore water chemistry through the GSI.
Chemical parameter analyses are currently being conducted.
A review of existing site data is being conducted of the final
New England site under consideration. It appears to hold greatest
promise as anecdotal reports of iron precipitation at groundwater seeps
in the adjacent river have been correlated with arsenic immobilization
in the solid phase. Sampling of this site will commence in the coming month after
some optimization tests of the push-point pore water samplers are
conducted. |
| Laboratory
Studies:
Laboratory studies of the types of microbial populations present
in solids from the GSI will be undertaken with the specific objectives
of identifying impacts of carbon fluxes on microbial processes.
A Masters student (Jenna Shea) is currently being trained to
conduct microbial assays with 16S rRNA-targeted PCR primers.
Isolation of sufficient quantities of DNA from complex
environmental samples is a challenge being addressed by Ms. Shea before
solid cores are obtained. |
| Publications/Presentations |
N/A |
| Future
Activities |
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| Field Observations:
We will collect solid and groundwater samples from both the
upgradient and GSI zones of the heavy metal contaminated waterfront
site. The tasks will employ
both Geoprobe techniques and low volume push-point samplers.
The low volume push-point samplers are recently available
sampling tools to achieve high resolution (cm) pore water profiles that
are critical for delineating the GSI location and guiding larger sample
collections with traditional techniques. Correlations of pore water and solid phase concentrations of
a variety of chemical parameters, including conductivity, dissolved
oxygen, pH, iron species, heavy metals will be used to support
laboratory investigations of key GSI processes. |
| Laboratory Studies:
Microcosm tests will be used to determine the significance of
dissimilatory sulfate and iron reduction in the direct or indirect
immobilization of typical cations and oxyanions and the mobilization of
bound arsenic species under reducing conditions. Microcosm studies will also be used to determine the relative
significance of microbial and chemical oxidation of iron. |
| Supplemental Keywords |
GSI,
metal transport, arsenic, chromate, bacteria |
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