2003 RESEARCH
PROJECTS
Community Dynamics and Microbial Ecology
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PROJECT: |
Ecological
interactions between metals and microbes that impact bioremediation |
PRINCIPAL
INVESTIGATOR: |
Allan
Konopka |
Community
Dynamics and Microbial Ecology |
This project’s focus is to understand the structure and function
of microbial communities present in subsurface soils contaminated with
metals. Although these metals are toxic to many living organisms, some
microbes contain genetic traits that make them resistant to these metals.
Furthermore, microbes have mechanisms whereby these resistance genes
can be transferred to unrelated bacteria. We are specifically interested
in chromium, an important pollutant at DOE sites; neither the biochemical
basis nor the genetics of Cr resistance is well understood. Our objectives
are (1) to determine the effects of environmental factors on community
responses to Cr(VI) contamination. These effects may be mediated by
physiological responses, species selection, or gene transfer. (2) Determine
the role of mobile genetic elements that confer Cr resistance. Microbes
with these elements might function as either “bioprotectants” through
their physiological activity, or reservoirs of transferable resistance
genes. (3) Identify novel physiological and genetic bases for high-level
bacterial resistance to Cr(VI). In addition, metals often are unevenly
distributed in soils, which can lead to local differences in microbial
activity and diversity. We will also determine the distribution of
bacterial diversity and metal-resistance genes at these small local
scales. The research entails a combination of field-oriented analyses
and laboratory simulations of field conditions in microcosms. Both
biochemical and molecular techniques are used to determine the dynamics
of microbial community structure and function under these conditions,
with the long-term objective of identifying microbes and environmental
conditions that can are optimal for bioremediation of contaminated
sites.
PROJECT: |
Subsurface
Bacterial Community Dynamics in the Presence of Plutonium and Uranium |
PRINCIPAL
INVESTIGATOR: |
Cheryl
R. Kuske |
Community
Dynamics and Microbial Ecology |
The goals of this project are to determine the effects of Pu(VI)
on natural bacterial communities in anaerobic subsurface sediments,
and to compare bacterial community dynamics in the presence of Pu(VI)
or U(VI). Using subsurface sediments from DOE sites, we will conduct
laboratory time course experiments where native bacteria are exposed
to Pu(VI) or U(VI). We will use a combination of methods to specifically
analyze Fe(III)- and sulfate-reducing bacterial groups known to reduce
U(VI), and to conduct a broader survey of potentially important soil
species that are active in the presence of Pu or U. We will measure
bacterial abundance of target bacterial groups using real-time quantitative
PCR assays, followed by analysis of species composition in those groups
found to be active and/or correlated with actinide reduction. In parallel,
we will use terminal restriction fragment profiling to determine broad
changes in the total bacterial community as affected by actinide presence.
To insure that potentially important species that are not members of
our quantitative PCR groups are not missed, we will also assess total
bacterial diversity and composition by 16S clone/sequence libraries
conducted at certain points in our time course experiments. This study
will contribute to the NABIR program by providing information on the
dynamics of natural sediment communities in the presence of Pu(VI)
and U(VI) and by identifying groups of indigenous bacteria from subsurface
sediments that are active in the presence of Pu(VI) or U(VI).
PROJECT: |
Molecular
Analysis of Rates of Metal Reduction and Metabolic State of Geobacter
Species
During In Situ Uranium Bioremediation |
PRINCIPAL
INVESTIGATOR: |
Derek
Lovley |
Community
Dynamics and Microbial Ecology |
Our previously funded NABIR Biotransformations research
conclusively demonstrated that microbial U(VI) reduction in uranium-contaminated
aquifers can be stimulated with the simple addition of acetate and
that stimulating this process can effectively remove uranium from contaminated
groundwater. A field experiment confirmed the results of the laboratory
sediment incubations, but also revealed that long-term injection of
acetate may deplete Fe(III) oxides from the site of acetate injection
and promote the growth of acetate-oxidizing sulfate reducers, which
appeared to be less effective than Geobacter species in reducing U(VI).
These results from the field experiment demonstrate a need for further
study of subsurface biotransformations in order to optimize the long-term
in situ uranium bioremediation process. Therefore, the objective of
this research is to evaluate previously unconsidered aspects of the
competition for electron donors near injection wells during in situ
bioremediation, the implications of this for U(VI) reduction, and strategies
for manipulating biotransformations to promote long-term U(VI) reduction.
Studies in which sediments and groundwater from uranium-contaminated
sites will be incubated in flow-through columns, as well as field studies,
will examine the effect of providing different organic electron donors
at various concentrations on long-term U(VI) reduction. It is hypothesized
that addition of acetate in concentrations sufficient to consume all
of the sulfate near the point of injection will provide enough acetate
to maintain an active, downgradient population of Geobacter species,
which will continue to remove U(VI) from the groundwater. One alternative
strategy is to diminish the competitiveness of sulfate reducers near
the point of injection by increasing Fe(III) concentrations in the
sediments. Another strategy is to add lactate, instead of acetate,
because lactate may stimulate the growth of lactate-oxidizing sulfate-reducing
microorganisms which can effectively reduce U(VI) as well as provide
acetate for Geobacter species. The potential for dissimilatory metal-reducing
microorganisms to reduce U(VI) adsorbed onto sediments will also be
examined as this is significant pool of U(VI) at many subsurface sites.
Furthermore, the kinetics of U(IV) oxidation with nitrate and oxygen
once addition of electron donor is terminated will be evaluated. These
studies are expected to expand the basic understanding of biotransformation
processes in uranium-contaminated subsurface sediments and help identify
successful strategies for long-term in situ bioremediation.
PROJECT: |
Importance
of mobile genetic elements and conjugal gene transfer for subsurface
microbial community adaptation to biotransformation of metals |
PRINCIPAL
INVESTIGATOR: |
Soren
Sorensen |
Community
Dynamics and Microbial Ecology |
Based on the results of past NABIR projects we will expand our studies
on the role of horizontal gene transfer (HGT) in adaptation to metal
stress by using culture independent techniques. Thus, for the first
time examination of HGT will encompass the huge diversity of uncultured
bacteria in the subsurface environment. The overall goal of the project
is to reveal the importance of mobile genetic elements and conjugal
gene transfer for subsurface microbial community adaptation to mercury
and chromium stress and to biotransformation. Our studies will examine
the interaction between the fate of these metals in the subsurface
and the microbial community structure and activity. Specifically, we
will seek to answer whether intrinsic processes in subsurface communities
can be harnessed and stimulated to drive metal biotransformation and
immobilization. To maximize the relevance of our findings, we will
employ DOE-site derived materials to identify and study relevant metal-biotransforming
characters (strains and plasmids), examine the incidence of lateral
gene transfer events, and perform lab-scale microcosms studies to biostimulate
in situ metal transformation rates. Our ultimate goal is to provide
a science-based approach to stimulate in situ Hg and Cr reduction kinetics
via a minimally intrusive stimulation and control of subsurface microbial
communities. Ultimately, our findings will promote development of effective
and mechanistically validated bioremediation technologies for subsurface
contaminated with Hg and Cr. These technologies will be of direct value
to DOE, but also to other federal agencies and industries that may
be confronted with subsurface metal contamination.
To accomplish these goals we will:
- Isolate and characterize hitherto uncultured subsurface bacteria
(and their plasmids) of relevance for biotransformation of metals
(Hg(II) and Cr(VI)).
- Qualitatively and quantitatively study horizontal gene transfer
among uncultured subsurface bacteria.
- Study the effect of environmental stress on horizontal gene transfer
in subsurface microbial communities.
- Investigate the significance of mobile genetic elements for microbial
adaptation to metal stress
- Attempt to use horizontal gene transfer as a tool to enhance
the reduction of Hg(II) and Cr(VI) by indigenous subsurface
soil bacteria.
PROJECT: |
Towards
Understanding Population Dynamics of Metal and Radionuclide Reducers
at Field Remediation Sites |
PRINCIPAL
INVESTIGATOR: |
Jim
Tiedje |
Community
Dynamics and Microbial Ecology |
Uranium, chromium and technetium, are important mobile pollutants
in soils and groundwaters at DOE facilities. They potentially can be
reduced to non-mobile forms by microbes in nature and thereby arrest
the further spread of these metals. Successful remediation by immobilization
requires stimulating effective metal and radionuclide reducing microbial
populations in a reliable way over large areas, and maintaining these
elements in immobilized form. To reliably achieve this remediation
process, one needs to establish cause and effect relationships between
the treatment, active populations and the metal reduction in the field.
This project is aimed at defining which microbial groups actually carryout
the metal reductions in the field so that one can better define the
necessary conditions for the most effective populations, and to produce
a set of field-ready methods that can be used to determine which populations
respond in the field at remediation sites. This will be done under
the following objectives: (1) Determine the competitive fitness of
known metal reducers under conditions that simulate field site(s),
(2) determine the microbial populations important for the reduction
of U, Cr and Tc at the NABIR-Field Research Center (FRC) using metagenomics-based
approaches, and (3) apply the developed molecular technologies for
quantifying which microbial populations grew during field implementation
of remediation. To achieve these objectives, we will evaluate the competitiveness
of the four best known metal reducing genera, Geobacter, Shewanella,
Geothrix and Desulfitobacterium, against the FRC native community in
column microcosms, and compare these results to the outcome of the
field implemented remediation at the FRC. We will evaluate the competitiveness
of the populations using multiple primer set real-time (Q)-PCR, RNA-based
stable isotope probing using 13C-labeled substrates that would be practical
for biostimulation and several types of DNA microarrays, including
community genome arrays (CGAs), functional gene arrays (FGAs) and arrays
newly developed using metagenomic approaches, to characterize the unculturable
metal reducers. In the last year, based on the microcosm and field
experience, we will select and optimize a subset of these methods that
are deployable for support of DOE remediation objectives. This research
is being conducted as a collaborative project by scientists at Michigan
State University (MSU) and Oak Ridge National Laboratory (ORNL)
PROJECT: |
Development
and Use of Integrated Microarray-based Genomic Technologies for
Assessing Microbial Community Composition and Dynamics |
PRINCIPAL
INVESTIGATOR: |
Jizhong
Zhou |
Community
Dynamics and Microbial Ecology |
Rapid,
parallel, and cost-effective detection tools that can be operated
in real time and in heterogeneous field-scale environments are needed
for assessing microbial community dynamics. The overall goal of this
project is to develop a rapid, parallel, and cost-effective, integrated
microarray-based genomic technologies for assessing the structure
and dynamics of microbial populations impacted by radioactive and
metal contaminants. Towards this goal, the following objectives will
be pursued: (1) To further develop and evaluate the 50mer functional
gene arrays and SSU rRNA gene-based oligonucleotide microarrays for
assessing microbial community composition and dynamics in the NABIR
Field Research Center; (2) To develop and optimize novel methods
for uniform, sensitive and quantitative amplification of microbial
communities; (3) To determine how radioactive and mixed waste contaminants
affect the structure, dynamics, and responses of microbial communities
using the developed oligonucleotide arrays; and (4) To develop bioinformatics
tools for designing oligonucleotide probes for microbial community
analysis. We will first focus on developing various microarray-based
experimental and computational genomic technologies. Then we will
utilize these technologies to understand the dynamics of the microbial
communities at NABIR FRC using the samples from different field research
projects. In addition, we will integrate our information on microbial
community dynamics with existing site geochemistry data to understand
how contaminants and remediation treatments affect microbial community
diversity, structure, activities and dynamics. Finally we will construct
a database to manage the massive microarray data
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