Research
Accomplishments and Significant findings (** indicates
projects done completely through the University of Washington) Uptake,
Metabolism, Environmental Impacts and Applications of Phytoremediation of Chlorinated
Solvents Laboratory
While
previous work done as part of the University of Washington research team revealed
three metabolites of trichloroethylene expected from mammalian degradation pathways,
these compounds do not accumulate. We have been working to determine other metabolites
of TCE in plants outside the expected mammalian metabolites. We have shown that
monochloroacetic acid is produced in plants following TCE exposure, but not after
exposure to related compounds perchloroethylene or carbon tetrachloride. We also
confirmed the degradation of carbon tetrachloride to trichloroacetic acid. The
use of hybrid technologies such as pump-and-irrigate, increases the effectiveness
of phytoremediation on sites with physical limitations. However, this system can
lead to exposure to TCE of organism that would normally be protected by the soil
column. Also, insects feeding on plants used for remediation purposes could also
have increased exposure risk. We have done studies on this subject and found that
insect feeding on plants exposed to 50ppm of TCE showed no signs of toxicity,
and that soil organisms were protected by the enhanced uptake and degradation
in planted soils. (student: Sandy Benson)
The
use of genetically engineered plants or microbes for remediation purposes can
lead to discussions about the escape of genes or organisms from the
selected areas. One way to deal with these issues is the use of bacterial strains
that exist almost exclusively as endophytes within the plant vascular tissue.
Researcher at Brookhaven National Laboratory have created a strain of bacteria
transformed with the plasmid that degrades both aromatic solvents and TCE and
related compounds. We are starting studies with them to look at changes in the
metabolite profile and transpiration rates of TCE in colonized plants. (student:
Lucas Odom) **While
plant metabolites of TCE seem to follow mammalian degradation pathways, not much
is known about the plant genes involved. When at the University of Washington,
work was done as part of the team that put mammalian genes known to be involved
in TCE degradation into plants. This resulted in an increase in certain metabolites
within the plants to levels over 600 time higher than that seen in non-transformed
plants. At
USC, we have worked to find plant genes involved in TCE degradation. This could
lead to the development of engineered plants with much greater social acceptance
than the use of mammalian genes. Also, knowledge of those plant genes involved
in TCE metabolism could lead to the development of screening tools to help select
plants suitable to clean-up applications. We have identified four genes with strong
protein sequence homology to the conserved amino acids in the active pocket of
CYP2E1, and at least one of these has shown to be involved in TCE metabolism via
insertional mutations in A. thaliana. We have also transformed these genes into
tobacco with strong constitutive promoters and are screening them for changes
in metabolic profiles. (student: Sarah) We
are working on a study to look at ways to change the levels of enzymes within
plant systems without using genetically engineered plants or bacteria. Certain
agricultural chemicals are known to increase the levels of various enzymes in
plants, and we are looking at how the application of these supposedly inert
compounds could decrease plant toxicity and increase metabolism of solvents within
the plants. (student: Brian Hann) Greenhouse **Hybid
poplars are used on most groundwater phytoremediation sites, but there has been
speculation as to which clonal lines are best suited for remediation of solvents,
or if there is a difference. At study done at the University of Washington has
shown that the major difference between the clonal lines is in the amount of water
take up by the plants. All clonal lines tested had similar toxicity to trichloroethylene,
and all were capable of degrading TCE. Those lines that had the best remediation
potential were those that had the fastest growth rates and took up the highest
levels of water, which in the field would lead to the greatest level of contaminant
uptake. (student: Marietta Sharp) While
the use of such standard plants such as hybrid poplar or willow have been used
on the majority of groundwater remediation projects, there has been an increasing
interest in the use of native vegetation for remediation work. This
would allow for the combined remediation and restoration of impacted sites. This
can be critically important in areas where there are limitations on the introduction
of non-native species, as well as on large scale projects such as the restoration
of decommissioned military bases. While at UW, work was done with the plant Leuceana
leucocephala to remediate ethylene dibromide in Hawaii. More recently work has
been done to look at native and naturalized plants of the Southeast. A study of
deciduous trees has shown that sweetgum and sycamore have excellent potential
for remediation purposes. In a study of conifers, southern Long Leaf Pine, itself
considered vital to revegatation efforts, is capable to uptake and degradation
of TCE. (student: Sarah) In
two related studies, we have looked at grasses that grow either in freshwater
riparian systems, Arundinaria gigantica ssp. Tecta, swithcane, or in brackish
water systems, Arundo donax. Both plants are capable to taking up trichloroethylene
and metabolizing it within the plant. Switchcane is a prime candidate plant for
restoration purposes in impacted riparian zones. Arundo is not native, but has
been proposed as a bioenergy crop. (students: Neshia Mohammed and Gillian Connolly) While
it would be nice to assume that contaminated sites contained one chemical and
we could study how the plants respond to that chemical, in truth, most sites contain
a variety of chemicals. At the Savannah River Site, chlorinated groundwater plumes
can run into areas where there is heavy metal or radionuclide contamination. We
have done a study to determine what happens within the plant systems when a TCE
plume moves into an area already contaminated by nickel. The study looked at changes
in TCE metabolism brought on by nickel uptake by the plants and saw that changes
in nickel levels within the plant altered the levels of TCE metabolites in the
plants. We are currently looking at how the migration of TCE into the area might
affect nickel uptake by the plants by either changing bioavailabilty or root porosity.
(technician: Tom Ciravolo) Before
a remediation action can start, it is critical to know the extent of the contamination
on the site. Typically, this is done by drilling multiple wells on the site until
the plume can be accurately modeled. This is both time consuming and costly. NASA
has proposed using hyperspectral imaging of pre-existing vegetation to determine
if this method can be used to determine the size and boundaries of the plume.
We are doing greenhouse studies to determine if this type of imaging can distinguish
between exposed and unexposed plants, and to learn if this distinction can be
seen at TCE levels low enough to make this a viable tool to use for site characterization.
(technician: Tom Ciravolo) Working
with NASA again with hyperspectral imaging, we are collaborating with the USFS
to determine if this technology can also lead to the development of a tool that
can help to map root systems underground, and to track changes in root development
over time. By screening root/soil systems, we are working with the NASA group
for the development of software that can reduce the operator time for monitoring
root development, fungal interactions and the presence of root foraging soil organism.
(technician: Tom Ciravolo) Field When
phytoremediation of groundwater was first being proposed, most stakeholders were
reluctant to gamble on the new technology. Occidental Chemical, which funded much
of the early research, built a one-of-a-kind test treatment facility outside Fife,
WA where we could test a variety of trees and chemical in contained, simulated
aquifer systems. Over the years, we looked at three different groundwater contaminants,
and ten varieties of trees to determine their relative toxicity, uptake rates,
metabolism, transpiration and impact on soil pore space contamination. Phytoremediation
of groundwater remediation projects have been install around the country, but
there is still reluctance by state regulators to accept a technology that they
themselves have not worked with. At the Southern Sector A&M area site on the
Savannah River Site, we installed a two acre demonstration plot, with one acre
being naturalized plants within a pine plantation, and one acre of planted hybrid
poplar. Extensive monitoring was done monthly on TCE concentrations in the irrigation
water, the air, the trees and the soil pore water. It was found that the site
could treat approximately 1.5 million gallons of contaminated water per growing
season without breakthrough beyond the root zone of the plants. (technician:
Robert Kim) With
the extensive work we have done showing that most plants have some levels of ability
to degrade solvents like TCE, selection of plants for a given site becomes more
an issue of which trees will grow well in a given area. While hybrid poplar is
still the most common tree used, most clonal lines were created either in the
Pacific northwest, or the upper Midwest regions of the country. Thus, determining
which lines have the best suitability for the southeast region can be critical.
With the USFS, we did a study looking at survival, growth, resistance to disease
and insects. We found that there were several lines that did significantly better
than others, and that these would probably be the best clonal lines to use for
remediation projects in the southeast. While
install tree plantations is highly effective in dealing with contaminated groundwaters,
many site managers and owners are now looking more at monitored natural attenuation
or MNA as an even more cost effective way to deal with contamination. However,
there is still debate among the regulatory community as to what conditions have
the potential to lead to a successful MNA treatment site. We did a study at the
Chemical, Metal and Pesticide disposal area on the Savannah River Site to determine
if MNA was taking place on the site, and if so, what the temporal and regional
conditions were that lead to MNA taking place. (student: Neshia Mohammed) Site
Application **In 1997, we worked with the Oregon Department of Environmental
Quality to install the first pump and irrigate system for the treatment
of groundwater contamination. The site was an orphan site outside Medford, OR,
where an accident had spilled a tanker truck of 1,1,1-trichloroethane. After laboratory
study to show that plants could take up the compound, a 7/8-acre test plot was
installed. After three years of growth, it was found that the plot of trees could
take up over one million gallons of contaminated water per growing season without
breakthrough beyond the root zone. In
1998, the Undersea Naval Warfare Center at Keyport decided to install a phytoremediation
system on top of a landfill to control leachate containing TCE and other chemicals
that was threatening a protected wetland. Community involvement was very high,
and the ceremonial Earth Day planting in 1999 included community members, the
base commander and the base chaplin who blessed the trees as we planted. Monitoring
on the site is ongoing to determine the extent of the impact of the trees. We
have deployed some of the most up-to-date groundwater and plant metabolic instrumentation
on the site to deal with problems such as tidal influences on the groundwater.
(student: Marietta Sharp)
Production
of Plant Crops for Biomass and Biodiesel in the Southeast using Biosolids Field The
foreign oil situation is only going to get worse, and the development of renewable
bio-based fuels will need to be one of the ways that the country deals with this
problem. Biomass can be utilized in three major ways for energy production: burning
the mass for electricity or steam production, chemical transformation of the biomass
for ethanol production, and modification of seed oil for biodiesel. In many instances,
these types of energy are economical only if produced locally. We are working
on a project using biosolids as a fertilizer regime to grow plants suitable for
production level growth in the Southeast such as sunflower, caster bean and soy
bean, for both seed oil production, as well as high biomass for ethanol or steam
production. This allows the use of waste product to produce two forms of energy
from the same crop. (student: Brad Temple)
Conditions
Enhancing Carbon Sequestration in Soil Fungal Biomass Field Research
into carbon sequestration is increasing as the need develops to find a way to
reduce the levels of this greenhouse gas in the atmosphere. A lot of work has
gone into developing ways to utilize the plants ability to conduct photosynthesis
and utilize carbon dioxide, but this is considered short term storage. However,
soil fungal biomass has the ability to produce extremely recalcitrant compounds
such as glomalin, which will tie up the carbon for much longer periods of time.
We are working with the US Forest Service on their short-rotation woody crop plantations
to work out which growing regimes will produce the most below ground fungal biomass
and also induce the highest level of glomalin production. We are also doing greenhouse
studies to determine which plant species will best foster fungal growth and glomalin
production under more controlled conditions. (students: Rebecca Maska and Jaclin
Durant)
Phyto
and Photodegradation of Energetics Laboratory Nitroamine
Hexahydro-1,3,5-trinitro-1,3,5-triazine, or Royal Demolition Explosive (RDX) is
widely used by the military as an explosive, rocket propellant, and as a key ingredient
in C-4, a plastic explosive. When test firing shells during practice maneuvers,
incomplete detonation results in widespread areas of varying concentration of
RDX. Due to the fact that these ranges must remain open, a remediation option
that is low maintenance and still allows use is imperative to find. Our lab is
working on using plants with variations in pigmentation to enhance photodegradation
of RDX, as well as diverse secondary metabolic pathways that may enhance the degradation
within the plant tissue. (student: Carrie Beth Hadden)
Phyto
and Enhanced Microbial Degradation of Petroleum Additives and PAHs Laboratory The
US Environmental Protection Agency mandated the addition of methyl-t-butyl ether
to gasoline to reduce air pollution and to boost octane ratings. However, when
MTBE leaks from underground storage tanks, its high water solubility results in
plumes that can be over a mile long and often have no defined source. Greenhouse
work has shown that plant can effectively take up MTBE, but metabolism by plants
has long been debated. Work in our lab has shown that hydroponic cultures of Arabidopsis
are capable of metabolizing MTBE to its primary metabolite, t-butyl ether. Greenhouse The
dredging of waterways results in large volumes of sediments that are often too
contaminated to be placed in open water systems. Thus, much of the sediment in
placed in confined placement facilities, while the Navy and Corps of Engineers
try to decide how to treat them. We looked using various wetland and wet tolerant
plants to determine those that were able to most efficiently dewater the sediments,
as well as promote the increase in microbial communities able to degrade contaminants
such as PAHs. We found that swamp pea, annual rye, and barnyard grass are
all capable of increasing the numbers of pyrene degraders in the sediments. (student:
Paul Biery) **Based
on laboratory studies of plant uptake of MTBE, we did a study at the Port Hueneme
Naval Facility, and looked at the effect of trees on the site of reducing MTBE
concentrations in groundwater. We found the a single mature tree on the base were
able to reduce concentrations of MTBE by 50% after passage through the root zone.
Heavy
Metal and Mercury Sequestration, Availability and Processing in the Environment Laboratory Due
to the proposed plan in build over one hundred new coal burning power plants,
there is a real need to have increased knowledge about the fate of mercury in
the environment. While the use of higher grade coal and scrubbers will reduce
the mercury emission, it will not eliminate them. Much work has been done with
brackish and salt water system, but there is much less knowledge about freshwater
systems. Our work looked at the effectiveness of bench scale processes to predict
what was happening in a field scale application. (student: Michele Harmon)
**There
is still a strong debate as to who plants handle toxic metals at a cellular level;
with various theories being put forward, and then being altered or dropped as
new information becomes available. We proposed to bypass the natural plant systems,
and to utilize the work of Dr. Loeb in selected mutagenesis experiments to design
peptide systems that would require minimal cellular energy yet bind high levels
of heavy metals. cDNA libraries were constructed, inserted in E.coli or yeast
and screened for the ability of to impart resistance to metal toxicity. Promising
candidate genes could then be transformed into plants for both decreased sensitivity
and enhanced remediation activities. Field Construction
of artificial wetlands to deal with environmental contaminants is becoming more
common, but proper design of the systems can be problematic. Minimizing one contaminant
while increasing bioavailability of another is not uncommon. At the Savannah River
Site, the construction of a wetland to reduce copper levels was successful, however,
the conditions in the wetland favored methyl mercury production. We looked at
alternative ways to design these types of systems to reduce metal contamination
to below regulatory levels while not producing other more harmful contaminants.
(student: Michele Harmon) The
water flow in the Winyah Bay area has been hypothesized to limit water movement
in certain areas of the bay, and thus potentially lead to retention of contaminants
in the system. In our study, we looked area plants and sediments both upgradient
and downstream of Georgetown Steel Corporation to determine if plant activities
were increasing metal concentrations in the bay. Sediments were sampled both from
the surface and down to three feet, to determine if historical contamination was
still present. What we found was that our highest levels of contamination were
not near the metal plant, but in our supposed control area, immediately down stream
from a bridge. High levels of lead and zinc were found in all sediments in that
area, as well as higher levels of zinc in the plants. On
the Savannah River Site, the use of coal for energy production has resulted in
both nuclear and coal impacts on the site. At the D-area ash basins, the dumping
of high sulfur coal has resulted in an area with pH typically less than 1, leaching
of toxic heavy metals from the ash, and limited revegetation. We worked on two
projects on the ash basin, the first was using different types of surface and
subsurface amendments to increase survival of plants placed on the site, and to
document those plants that were started to colonize the site, determine their
uptake of heavy metals, and determine conditions in the ash that allowed them
to survive. (student: Jaclin Durrant)
Uptake,
Degradation and Stabilization of Pesticides. Preservatives and Agricultural Chemicals Greenhouse Dichloropropane
was used as an agricultural pesticide for many years until the toxicity to humans
was determined. Storage of the chemical on many agricultural chemical depot sites
resulted in high levels of localized contamination. We did a study that determined
that DCP could be taken up by hybrid poplars and broken down into metabolites
similar to those found in humans. (student: Mary Loftfield) **Pentachlorophenol
was long used as a wood preservative, especially in aquatic environments. We did
a study to determine if a wetland plants would be capable of either taking up
PCP and metabolizing it within the plant tissue, or of enhancing the microbial
breakdown of the PCP within the soil. The eventual application of this information
was the construction of a bioswale to handle contaminated surface water run-off. Site
Applications The Saginaw Mill site in Aberdeen, WA, was the site
of a saw mill that produced cedar shingles. In an attempt to preserve the shingles
and make them more fire-resistant, the company preserved the shingles with formaldehyde,
which was sprayed on in the open. Years of operation resulted in contaminated
groundwaters, which are moving toward the Chehalis River, which is a spawning
salmon route. Poplars were first determined in laboratory studies to be able to
take up the formaldehyde. A site application plan was developed and 5 acres of
hybrid poplars planted on the site. Site monitoring is continuing to determine
the efficiency of the trees in stopping the movement of the contaminated plume.
Decades
of agricultural support activities in eastern Oregon town of Vale lead to the
contamination of ground water with leaked ammonium nitrate, and soil contamination
with various pesticides. When the nitrate levels reach a point where it was above
regulatory limits for the town, the agricultural firm on site elected to do a
clean-up using hybrid poplars. The soil levels of ammonia so high it was toxic
to plants, and it required respirators when working with the soil in the greenhouse.
Extensive amendments needed to be added to the site to deal with this as well
as herbicide contamination in the soils. However, the poplars were established
on the site, and are continuing to grow and are monitored for affects on groundwater
concentrations. (student: Mary Loftfield) **The
use of compounds such as ethylene dibromide for the control of soil nematodes
was widespread. In Hawaii, the Delmonte Corporation had an tanker truck spill,
resulting in contamination of the groundwater supplying drinking water for the
workers. Preliminary greenhouse studies showed that naturalize plants were able
to take up the EDB, and between plant uptake and enhancement of soil microbial
activity, a treatment system was designed to pump up the contaminated water and
run it through a contained plant system. Delmonte installed the system and proved
that the system could remove contaminants to below detection limits. |