Phytoremediation

 

Phytoremediation as Green Infrastructure and a Landscape of Experiences
Frank Sleegers, University of Massachusetts, Amherst, MA  

Selenium Enhanced Retirement of Mercury from Aquatic and Terrestrial Ecosystems
Mark P. Elless, Edenspace Systems Corporation, Dulles,VA 
N
icholas V.C. Ralston, University of North Dakota, Grand Forks, ND

Seaweed Bloom Soaks Up PCBs from Superfund Site in New Bedford Harbor, Massachusetts
Donald Cheney, Northeastern University, Boston, MA  
Nina Farley, Boston College, Boston, MA,
Scott Greenwood,
University of New Hampshire, Durham, NH
Deana Aulisio, University of New Hampshire, Durham, NH
Kevin Gardner, University of New Hampshire, Durham, NH 

Pilot Phytoremediation of Lead Contamination at the Former Skeet Range in the Town of Sprague, CT
Julia Kuzovkina, The University of Connecticut, Storrs, CT
Olena Zhivotovsky, The University of Connecticut, Storrs, CT

Isolation and Characterization of Genes Involved in Arsenic and DDE Metabolism in Plants
Om Parkash, University of Massachusetts, Amherst, MA
Bibin Paulose, University of Massachusetts,
Amherst, MA
Sudesh Chikkara, University of Massachusetts,
Amherst, MA
Jason White
, The Connecticut Agricultural Experiment Station, New Haven CT

Use of Short-Lived Positron Emitting Radioisotopes to Study the Effects of Belowground Contaminants on Plant Growth and Function
Richard A. Ferrieri, Brookhaven National Laboratory, Medical Department, Upton, NY

 

Phytoremediation as Green Infrastructure and a Landscape of Experiences

Frank Sleegers, University of Massachusetts, Department of Landscape Architecture and Regional Planning, Amherst, MA 01003, Email: sleegers@larp.umass.edu

The idea of reconciling landscapes through remediation is not new to our discipline. However the potential of using transformative remediation to build urban form as a large-scale landscape network and that makes the process of remediation part of an urban landscape experience is still underdeveloped in theory and practice. This paper examines how a remediation process could be exhibited and become a design element, and how landscapes of cleaning can become part of the urban infrastructure to create new neighborhoods for research, education, working, and living. The paper proposes a general framework for how remediation could become an artistic, aesthetically pleasing intervention with environmental value.

Urban brownfields are a challenging and a common landscape especially in industrial and post-industrial cities. They inhibit economical growth and impair the ecological systems. Their industrial heritage often isolates them from the urban fabric and creates physical barriers. However the sensual, aesthetic quality that goes along with derelict land has been discovered by our profession. While there are successful examples of urban park developments that are remediated landscapes they are still not well integrated into their larger urban context. A systematic and strategic approach to remediation landscapes that are connected from the regional to the local scale and that tie into the urban fabric as a continuous network and as a part of a green infrastructure framework is still underdeveloped.

Another objective of this research is the exploration to reveal phytoremediation as an aesthetic experience. How can plants as the primary medium determine each phase of the cleaning process as a sensual experience and create a unique and meaningful landscape? The proposal is made to understand phytoremediation as a process-oriented tool for an evolving green infrastructure network that defines new landscapes.

The long-term time requirement for phytoremediation can also provide an opportunity: Changing and growing plant communities can be staged, each step of the cleaning process can transform into specific landscape typologies that build up the framework for urban form and green urban infrastructure and that is simultaneously a landscape of experiences.

Thus phytoremediation as an experience and framework calls for:

  • Re-creation of systematic connectivity - from isolation to network in a flexible framework that structures a multi – layered urban infrastructure.
  • Visible transformation of toxics and contaminants as a sensual  experience through the dynamic media of the landscape.
  • Landscapes to support environmental education and interpretation.
  • Remediation as a tool to build new districts and neighborhoods on former brownfields and a chance for economic growth and revitalization.

The example of two adjacent sites on the contaminated Elbe – Island in Hamburg -  Wilhelmsburg, Germany discusses how the purification process of water and soils can be showcased and experienced by the public and how the landscape framework becomes part of the urban infrastructure.

Strategies and visions were developed under my direction in the UMASS Urban Design Laboratory 2007 - 2008. The scientific framework was established in collaboration with Prof. PHD Guy Lanza,  Department of Environmental Sciences, UMASS.

  • Key words: connectivity, experience, education, green infrastructure, green urbanism, landscape urbanism, phytoremediation.

Selenium Enhanced Retirement of Mercury from Aquatic and Terrestrial Ecosystems

Mark P. Elless, Edenspace Systems Corporation, 3810 Concorde Parkway, Suite 100, Dulles, VA, 20151-1131 Tel: 703-961-8700, Fax: 703-961-8939, Email: elless@edenspace.com
Nicholas V.C. Ralston, Energy and Environmental Research Center, University of North Dakota, 15 North 23rd Street, Grand Forks, ND, 58202-9018 Tel. 701-777-5066, Fax 701-777-5181, Email: nralston@eerc.org

Because mercury (Hg) poses significant public health challenges, reducing its levels in air, soil, and water is an international priority. Global redistribution of Hg through the atmosphere makes current methods of addressing Hg contamination, such as excavation and replacement of soil or pump-and-treat techniques for water, too expensive to be practical given the typically large scale of remediation activity required. This research sought to develop an innovative, low cost method of extracting Hg from soil and water using two recently-identified Hg-hyperaccumulating plant species, one terrestrial (Rabbit’s foot grass) and one aquatic (water hyacinth). The Hg stored in the plant leaves, stems, and roots may then be harvested for disposal, or allowed to remain on-site in an extremely refractory (highly stable) chemical form that is biologically unavailable and poses no health risks. This process depends on the presence of selenium (Se), a nutritionally essential trace element that is naturally taken up from soil by plants. Previous studies have shown Hg and Se coaccumulate in a high molecular weight fraction, potentially indicating formation of a mercury selenide (HgSe) complex. Because the solubility of HgSe is extremely low (<10-58), it is expected that Hg in this form becomes permanently retired from biological cycling. Preliminary results have shown high plant uptake of Hg and Se by both plant species, suggesting the potential for in planta HgSe formation. The end result of the project will be to establish the foundation for a low-cost, solar powered method of removing and stabilizing mercury over large areas of soil and large volumes of water.

Seaweed Bloom Soaks Up PCBs from Superfund Site in New Bedford Harbor, Massachusetts

Donald Cheney, Biology Dept. and Marine Science Center, Northeastern University, Boston, MA 02115, Email: d.cheney@neu.edu
Nina Farley, Biology Dept., Boston College, Chestnut Hill, MA 02467, Email: farleyn@bc.edu
Scott Greenwood, Environmental Research Group, University of New Hampshire, Durham, NH Tel:  603-862-4334, Email: scott.greenwood@unh.edu
Deana Aulisio, Environmental Research Group, University of New Hampshire, Durham, NH Tel: 603-862-4334, Email: deana.aulisio@unh.edu
Kevin Gardner, Environmental Research Group, Dept. Civil Engineering, University of New Hampshire, Durham, NH, Tel: 603-862-4334, Email: kevin.gardner@unh.edu

New Bedford Harbor, in southeastern Massachusetts, is unlike any other estuarine-harbor system in the world. Its lower harbor is home to one of the busiest fishing ports found along the US’s eastern seaboard, while its upper harbor is home to one of the worst polluted Superfund sites found in the US.  Its Superfund site is unique both because of the extremely high levels of PCBs reported in its sediments, and because it is home to a remarkable seaweed bloom that takes up and concentrates PCBs to a level not previously known. In the summer of 2007, we discovered that a bloom of the common green alga  Ulva is growing in the Superfund site area, and that it takes up and concentrates PCBs to levels as high as 98 ppm, which is over 1000X the concentration in the seawater. Furthermore, we know from uptake experiments in the field, that it is capable of taking up PCBs at an extremely rapid rate; as much as 4 ppm per day. We estimate that there is at least 50 tons of Ulva growing in the Superfund site. PCB concentrations in Ulva are correlated with distance from the old Aerovox plant, where PCBs were used in the manufacture of electrical transformers and capacitors from ca. 1940 to 1977. While the full environmental impact of the seaweed bloom is still under investigation, we recently discovered that Ulva is a major source of food for the most abundant, intermediate food chain level fish species in the system, Fundulus heteroclitus (mummichog). These findings raise questions about Ulva’s potential role in the transfer of PCBs up the system’s food chain to top predator species that feed on Fundulus like striped bass, blue fish, egrets and blue herons, as well as on humans that consume these fish species caught in New Bedford and near by waters.

Pilot Phytoremediation of Lead Contamination at the Former Skeet Range in the Town of Sprague, CT

Julia Kuzovkina, Ph.D., Department of Plant Science and Landscape Architecture, The University of Connecticut, 1376 Storrs Rd. Unit 4067, Storrs, CT 06269, Tel: 860-486-3438, Fax: 860-486-0682
Olena Zhivotovsky, Department of Plant Science and Landscape Architecture, The University of Connecticut, 1376 Storrs Rd. Unit 4067, Storrs, CT 06269, Tel: 860-486-2174, Fax: 860-486-0682

A pilot phytoremediation project was conducted at the Mukluk site, Town of Sprague, CT in 2008- 2009 by the Plant Science Department of the University of Connecticut.    This study was primarily an exploratory investigation that sought to collect important preliminary data to be used to asses the possibilities of how to remediate the Mukluk site. A total area of 12-14 acres is currently contaminated by lead shot and requires remediation. A series of experiments were conducted to investigate if phytoremediation and specifically phytoextraction or phytostabiilzation  can be implemented at the site to remediate the soil to below regulatory limits. Greenhouse screening of plants for lead resistance and accumulation using field soil was proposed as the initial step prior to the field installation to identify which plants could be used successfully at the Mukluk site. Plant species with known phytoextraction capabilities included Indian mustard, blue fescue grass and willows.  Based on the results of the screening experiments, only willows and Indian mustard, and various soil amendments were selected for the field installation in May 2008. Indian mustard grew poorly in most of the treatments and  lead accumulation by this species was low in all treatments. In contrast, willows showed tolerance to very high lead concentrations present in the soil and were able to survive and uptake and translocate lead into above ground tissues. However, lead content which had accumulated in plant tissues was relatively low and the post harvest soil analyses indicated that no significant difference in lead concentrations had occurred at the site after one season’s planting and harvesting. More field research is required to confirm the phytoextraction abilities of willows over a period of 3-4 years. The combination of biomass production and the phytoremediation of soil with willows should be further explored.

Isolation and Characterization of Genes Involved in Arsenic and DDE Metabolism in Plants

Om Parkash (Dhankher), Bibin Paulose, and Sudesh Chikkara; Dept. of Plant, Soil and Insect Sciences, University of Massachusetts, Amherst, MA-01003, USA, Tel: 413-545-5231, Email: parkash@psis.umass.edu
Jason White
, The Connecticut Agricultural Experiment Station, 123 Huntington St. Box 1106, New Haven CT- 06504, Email: Jason.White@po.state.ct.us 

Environmental pollutants including heavy metals, metalloids and persistent organic pollutants such as DDE are major sources of food chain contamination and thereby endanger human health. Arsenic (As) is an extremely toxic carcinogenic metalloid pollutant that adversely affects the health of millions of people worldwide. Considerable concern exits globally about arsenic contamination in drinking water and soil. Phytoremediation renders an eco-friendly and sustainable method to remediate the As and DDE polluted sites. However, the progress in this regard is seriously hampered by to the lack of proper understanding of the molecular and biochemical mechanisms of uptake and detoxification of these pollutants in plants. Crambe (Crambe abyssinica) - a non-food high biomass crop, is reported to be able to tolerate and accumulate high amount of As. Understanding the molecular mechanism of As tolerance is essential to improve the efficiency of uptake thereby exploiting the plant for commercial phytoremediation. We have isolated As-induced genes from Crambe seedlings by PCR-Select Suppression Subtraction Hybridization approach. After differential screening, 105 positive cDNA clones from the subtracted library were sequenced. The sequences were categorized based on their similarity with reported sequences in the databases. We grouped the cDNA sequences into different families based on the sequence similarity. Most of the substracted cDNA belongs to families of oxidoreductases, peptidases, transferases, transcription factors, metal ion transporters, heat shock proteins and novel unknown genes. Semi-quantitative RT-PCR confirmed their up-regulation in response to arsenic exposure. Selected genes were expressed in arsenic sensitive yeast strains lacking arsenate reductase, ACR2, arsenite transporter, ACR3, and vacuolar transport pump, YCF1, to evaluate their functional role in arsenic uptake and metabolism. The results showed that the ectopic expression of the genes altered the phenotype of the mutant strains in presence of arsenic indicating their potential role in arsenic metabolism. The candidate genes will be functionally characterized in plants using both forward and reverse genetic approaches.

Persistent organic pollutants (POPs) are of great environmental concern because of their toxicity, global distribution, and resistance to remediation. Cucurbita pepo ssp pepo (zucchini, pumpkin) roots have been shown to phytoextract significant amounts of DDT/DDE, chlordane, and PCBs from soil, followed by effective translocation to aboveground tissues. Similar to As strategy, A PCR select suppression subtraction hybridization approach was employed to identify and isolate the differentially expressed genes in DDE treated Zucchini (C. pepo ssp pepo) as compared to DDE treated Squash (C. pepo ssp ovifera). After differential screening, 46 cDNAs clones (40 cDNAs isolated from shoot and 6 cDNAs isolated from roots) were sequenced. Out of 40 shoot cDNA sequences, 34 cDNAs are similar to different parts of Phloem filament protein 1 (PP1) and few novel unknown genes, whereas, in root, out of 6 cDNAs, 2 are similar to Cytochrome P450 like proteins, one as putative senescence associated protein and rest are novel unknown genes. RT-PCR analysis confirmed the up regulation of these genes in response to DDE exposure. These candidate genes will be further characterized by both forward and reverse genetic approach for their role in uptake of DDEs in plants.

Use of Short-Lived Positron Emitting Radioisotopes to Study the Effects of Belowground Contaminants on Plant Growth and Function

Richard A. Ferrieri, Brookhaven National Laboratory, Medical Department, Upton, NY 11772

One of the major challenges facing plant biology at the beginning of the 21st century is to understand plant responses to environmental perturbation and stress. This understanding is needed from the scale of the single cell to that of the entire organism.  Such an understanding requires the measurement of plant responses across these levels of organization on a time scale from minutes to even days.  Unlike many questions of plant response that can be studied using cell culture and/or destructive techniques, the integration of plant stress responses requires an in vivo approach that allows repeated measurements from a single plant.  An approach is needed that not only addresses the integration of physiological processes, but allows visualization and quantification of molecular movement of substrates across the scale of the entire plant.  By using short-lived positron emitting isotopes such as carbon-11 (half-life: 20.4 min) and nitrogen-13 (half-life: 9.97 min) in combination with PET imaging and autoradiography, we can visualize quantitatively the assimilation, transport and disposition of carbon and nitrogen containing substrates in plants exposed to a variety of types of environmental stress under true tracer conditions. Often, we are interested in measuring changes in C/N allocation, as sugars and amino acids, between source-and-sink tissues in response to contaminant exposure. These kinds of measurements can be carried out by administering doses of 11CO2 or 13NH3 gas to intact leaves. Other times we are interested in measuring contaminant uptake and biodistribution. Through complex radiochemistry, it is often possible to incorporate appropriate radioactive tags either into organic contaminants, or even as radiometals that are ionic or chelated, enabling visualization of their uptake by roots and transport to leaves.  An overview of this technology will be presented with highlights on the phytoremediation of chlorocarbon contaminants by Populus.  This research is supported by the U.S. Department of Energy through the Office of Biological and Environmental Sciences.

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