The Potential for Utilising Disturbed and Contaminated Sites for the Production of Willow Short Rotation Coppice Forestry

Total Page:16

File Type:pdf, Size:1020Kb

The Potential for Utilising Disturbed and Contaminated Sites for the Production of Willow Short Rotation Coppice Forestry Rees, Stephen (2010) The potential for utilising disturbed and contaminated sites for the production of willow short rotation coppice forestry. MSc(R) thesis. http://theses.gla.ac.uk/1888/ Copyright and moral rights for this thesis are retained by the Author A copy can be downloaded for personal non-commercial research or study, without prior permission or charge This thesis cannot be reproduced or quoted extensively from without first obtaining permission in writing from the Author The content must not be changed in any way or sold commercially in any format or medium without the formal permission of the Author When referring to this work, full bibliographic details including the author, title, awarding institution and date of the thesis must be given Glasgow Theses Service http://theses.gla.ac.uk/ [email protected] The Potential for Utilising Disturbed and Contaminated Sites for the Production of Willow Short Rotation Coppice Forestry Stephen Rees MEnvS University of Strathclyde BSc (Hons) University of Wales, Swansea Submitted in fulfilment for the degree of MSc to the Chemistry Department, University of Glasgow, July 2008 © Stephen Rees, July 2008 1 Er cof am Dadcu a Mamgu annwyl Mr William Jones ‘Will Typicca’ & Mrs Lilwen May Jones ‘Mam’ “A garwyd mewn bywyd, a drysorir mewn cof” Also in memory of Mrs Mary Campbell and Ollie 2 3 CONTENTS LIST Page DECLARATION............................................................................................................. 18 ACKNOWLEDGEMENTS ........................................................................................... 19 ABSTRACT..................................................................................................................... 20 CHAPTER 1 - THE RECLAMATION AND RESTORATION OF DISTURBED AND CONTAMINATED INDUSTRIAL SITES......................................................... 22 1.1 Introduction............................................................................................................. 22 1.2 Background History to the Restoration and Reclamation of Disturbed and Contaminated Industrial Sites....................................................................................... 23 1.3 The New Contaminated Land Regime: Part IIA of the Environmental Protection Act 1990........................................................................................................................ 26 1.4 Guidelines Used to Determine Whether Land is to be Classed as Contaminated in the UK........................................................................................................................... 27 1.5 Treatment Technologies Currently Employed for the Restoration and Remediation of Contaminated and Disturbed Industrial Sites ........................................................... 31 1.6 Willow Short Rotation Forestry.............................................................................. 36 1.7 Using Willow Short Rotation Coppice to Phytoremediate Contaminated Sites..... 40 1.8 Additional Opportunities from Growing Willow Short Rotation Coppice on Disturbed and Contaminated Industrial Sites ............................................................... 43 1.8.1 Site Enhancement & Stabilisation .................................................................... 44 1.8.2 Sewage Sludge Disposal................................................................................... 45 1.8.3 Carbon Sequestration........................................................................................ 46 1.8.4 Amenity and Wildlife Havens .......................................................................... 47 1.8.5 Reduced Management Costs............................................................................. 48 1.9 Conditions Required For the Successful Establishment and Growth of Willow Short Rotation Coppice................................................................................................. 48 1.9.1 Site Selection and Preparation .......................................................................... 49 1.9.2 Planting ............................................................................................................. 49 4 1.9.3 Weed control..................................................................................................... 51 1.9.4 Fertilisation and Irrigation ................................................................................ 52 1.9.5 Harvesting......................................................................................................... 53 1.10 An Evaluation of the Potential End-Uses for Willow Short Rotation Coppice.... 54 1.10.1 Introduction..................................................................................................... 54 1.10.2 Existing and Potential End Uses for Willow SRC Biomass........................... 56 1.10.3 Energy Related uses - Bioenergy.................................................................. 57 (i) Direct Combustion ................................................................................................ 58 (ii) Gasification.......................................................................................................... 60 (iii) Pyrolysis.............................................................................................................. 61 (iv) District Heating................................................................................................... 62 (v) Fuel Cells ............................................................................................................. 63 (vi) Non-Thermal Conversion Processes................................................................... 63 (vii) Combined heat and Power (CHP)...................................................................... 64 (viii) Densified Fuels/ Briquetting/ Pellets ................................................................ 65 (ix) Green Electricity ................................................................................................. 66 1.10.4. Non-Energy Related Activities...................................................................... 67 (i) Biomass Refining.................................................................................................. 67 (ii) Feedstock for the Forest Product Industry........................................................... 67 (iii) Other varied and miscellaneous uses.................................................................. 67 (iv) Combined Projects .............................................................................................. 68 1.10.5 Conclusions..................................................................................................... 75 CHAPTER 2 - ESTABLISHMENT OF FIELD TRIAL AND ANALYTICAL METHODS ...................................................................................................................... 77 2.1 Introduction............................................................................................................. 77 2.2 The Field Trial ........................................................................................................ 78 2.2.1 The History of the Hallside Steelworks Site..................................................... 78 2.2.2 The Proposal ..................................................................................................... 80 2.2.3 The Solution...................................................................................................... 81 2.3 The Hallside Field Trial.......................................................................................... 86 5 (i) The effect of weed control treatments upon the SRC yield. ................................................................................................................................... 86 (ii) The use of inorganic fertiliser to promote coppice growth and subsequent yields. ................................................................................................................................... 87 (iii) The implication of stool spacing upon yields. .................................................... 87 (iv) The influence of coppicing upon yield................................................................ 87 2.4 Fertiliser Application .............................................................................................. 98 2.5 Weed Control.......................................................................................................... 98 2.6 Measurements & Harvesting................................................................................. 100 2.7 Additional Clone Testing...................................................................................... 102 2.8 Growing Medium Analysis................................................................................... 107 2.8.1 Sample Collection, Preparation and Analysis................................................. 107 2.9 Heavy Metal Analysis of the Plant Tissue............................................................ 108 2.9.1 Sample Collection, Preparation and Analysis................................................. 108 2.10 Preparation of Calibration Standards.................................................................. 108 CHAPTER 3 - RESULTS ............................................................................................ 111 3.0 Introduction..........................................................................................................
Recommended publications
  • Short Rotation Intensive Culture of Willow, Spent Mushroom Substrate
    plants Article Short Rotation Intensive Culture of Willow, Spent Mushroom Substrate and Ramial Chipped Wood for Bioremediation of a Contaminated Site Used for Land Farming Activities of a Former Petrochemical Plant Maxime Fortin Faubert 1 , Mohamed Hijri 1,2 and Michel Labrecque 1,* 1 Institut de Recherche en biologie végétale, Université de Montréal and Jardin Botanique de Montréal, 4101 Sherbrooke East, Montréal, QC H1X 2B2, Canada; [email protected] (M.F.F.); [email protected] (M.H.) 2 African Genome Center, Mohammed VI Polytechnic University (UM6P), Lot 660, Hay Moulay Rachid, Ben Guerir 43150, Morocco * Correspondence: [email protected]; Tel.: +1-514-978-1862 Abstract: The aim of this study was to investigate the bioremediation impacts of willows grown in short rotation intensive culture (SRIC) and supplemented or not with spent mushroom substrate (SMS) and ramial chipped wood (RCW). Results did not show that SMS significantly improved either biomass production or phytoremediation efficiency. After the three growing seasons, RCW- amended S. miyabeana accumulated significantly more Zn in the shoots, and greater increases of some PAHs were found in the soil of RCW-amended plots than in the soil of the two other ground Citation: Fortin Faubert, M.; Hijri, cover treatments’ plots. Significantly higher Cd concentrations were found in the shoots of cultivar M.; Labrecque, M. Short Rotation ‘SX61’. The results suggest that ‘SX61’ have reduced the natural attenuation of C10-C50 that occurred Intensive Culture of Willow, Spent in the unvegetated control plots. The presence of willows also tended to increase the total soil Mushroom Substrate and Ramial concentrations of PCBs.
    [Show full text]
  • The Use of Vegetation in the Stabilization, Reclamation, and Remediation of Impacted INDOT Soils
    Final Report FHWA/IN/JTRP-2004/17 The Use of Vegetation in the Stabilization, Reclamation, and Remediation of Impacted INDOT Soils by Mark S. McClain Graduate Research Assistant and M. Katherine Banks Professor School of Civil Engineering and A. Paul Schwab Department of Agronomy Purdue University Joint Transportation Research Program Project No. C-36-68T File No. 4-7-20 SPR-2624 Prepared in Cooperation with the Indiana Department of Transportation and the U.S. Department of Transportation Federal Highway Administration The contents of this report reflect the views of the author who is responsible for the facts and the accuracy of the data presented herein. The contents do not necessarily reflect the official views or policies of the Indiana Department of Transportation or the Fedeeral Highway Administration at the time of publication. This report does not constitute a standard, specification, or regulation. Purdue University West Lafayette, Indiana 47907 October 2004 TECHNICAL Summary Technology Transfer and Project Implementation Information INDOT Research TRB Subject Code: 23-8 Ecological Abatement October 2004 Publication No.: FHWA/IN/JTRP-2004/17, SPR-2624 Final Report The Use of Vegetation in the Stabilization, Reclamation, and Remediation of Impacted INDOT Soils Introduction Soils can be severely impacted by transportation- Phytoremediation uses plants to degrade, extract, related activities including highway construction, contain, or immobilize contaminants from soil and renovations, maintenance, and accidental spills. water. Phytoremediation is an innovative, cost- Reclamation or remediation of soils contaminated effective alternative to more conventional treatment by salts, solvents, paints, petroleum, and metals methods used in the remediation of hazardous may be necessary to comply with current waste sites.
    [Show full text]
  • Phytoremediation Potential of Fast-Growing Energy Plants: Challenges and Perspectives – a Review
    Pol. J. Environ. Stud. Vol. 29, No. 1 (2020), 505-516 DOI: 10.15244/pjoes/101621 ONLINE PUBLICATION DATE: 2019-09-10 Review Phytoremediation Potential of Fast-Growing Energy Plants: Challenges and Perspectives – a Review Martin Hauptvogl1*, Marián Kotrla2, Martin Prčík1, Žaneta Pauková3, Marián Kováčik4, Tomáš Lošák5 1Department of Environmental Management, Slovak University of Agriculture in Nitra, Slovakia 2Department of Regional Bioenergetics, Slovak University of Agriculture in Nitra, Slovakia 3Department of Regional Bioenergetics , Slovak University of Agriculture in Nitra, Slovakia 4Department of EU Policies, Slovak University of Agriculture in Nitra, Slovakia 5Department of Environmentalistics and Natural Resources, Mendel University in Brno, Czech Republic Received: 23 July 2018 Accepted: 15 December 2018 Abstract Contamination of soil by toxic elements is a global issue of growing importance due to the increased anthropogenic impact on the natural environment. Conventional methods of soil decontamination possess disadvantages in forms of environmental and financial burdens. This fact leads to the search for alternative approaches of remediation of contaminated sites. One such approach includes phytoremediation. Phytoremediation advantages consist of low costs and small environmental impact. Several fast-growing energy plant species are suitable for phytoremediation purposes. Our article focuses on the phytoremediation potential of energy woody crops of Salix and Populus, and energy grasses Miscanthus and Arundo, which are grown primarily for biomass production. This approach links the environmentally friendly and economically less demanding remediation approach with the production of the local sustainable form of energy that decreases dependency on external energy supplies. Energy plants are able to provide high biomass yields in a short period of time, they are resistant against abiotic stress conditions and have the ability to accumulate toxic substances, thus helping to restore the desirable soil properties.
    [Show full text]
  • Interest Increases in Using Plants for Environmental Remediation
    Specialty Plant Products Interest Increases in Using Plants For Environmental Remediation In an effort to meet environmental regulations of the last three decades, environmental remediation has developed into a multibillion dollar industry. The high cost of many traditional methods is causing many organizations to look to lower cost alternatives. Bioremediation is a commercial remediation technology with a growing market and continuing research. Phytoremediation is another potential low-cost technology that is currently being investigated for many remediation applications. Health and environmental risks of pollution have become Table 14--Soil remediation technologies more apparent throughout the world over the past several Method In situ Ex situ decades. Air, water, and soil contaminants can include nu- merous organic and inorganic substances, such as munici- Physical Soil vapor extraction Landfilling pal waste and sewage, various gaseous emissions, fertiliz- Thermally enhanced Incineration ers, pesticides, chemicals, heavy metals, and radionuclides soil vapor extraction Thermal desorption (radioactive substances). Contaminants can cause land and Containment systems Soil vapor extraction groundwater to be unusable. In addition, animals and in- and barriers sects may come in contact with a contaminant, thus intro- ducing a toxic substance into the food chain. Because of in- Chemical Soil flushing Soil washing creased public awareness and concern, environmental Solidification Solidification regulations have been created to not only prevent
    [Show full text]
  • Phytoremediation of Wood Preservatives FWRC
    Phytoremediation of Wood Preservatives FWRC Soil and waste contaminated with wood for contaminated areas: 1) enhanced microbial preservatives have been found in many former degradation of contaminants within the rhizosphere, and active wood treating plants, resulting from 2) hyperaccumulators where plants uptake and store past practices and accidental spillage. During the harmful contaminants, commonly heavy metals, in spring of 2001, newspaper articles in Florida raised their roots and shoots, 3) rhizofiltration where plant a public alarm over the perception that arsenate roots absorb, concentrate, or precipitate heavy metal from CCA (chromated copper arsenate) treated ions from water and, 4) phytovolatilization where wood—used in playground equipment— was leaching plants uptake volatile organic compounds (VOCs) in into soils and potentially into groundwater reserves. groundwater allowing them to be released into the As a result, CCA treated wood was voluntarily atmosphere via the stomata openings. taken off the market by the industry. Physical Surface waters and shallow aquifers were the removal of contaminated soils followed by treatment first sites where plants were applied as a method of technologies—soil washing, solidification cleanup. Many different plants and trees can and stabilization, chemical remove or degrade toxic pollutants. treatment,vitrification, thermal The primary disadvantage in using desorption, electrokinetics, trees for environmental cleanup and incineration—is not a is the time needed for tree cost effective soil cleanup growth. Faster growing method for heavy metal flora like grasses may be contaminated water. The suited for some situations. most common technologies Although the roots of include: coagulation/ grasses do not penetrate filtration (activated carbon), the soil at the same depths lime softening, chemical as tree roots, they can treatment, reverse osmosis, proliferate within the topsoil.
    [Show full text]
  • Sustainable Use of Plants for Heavy Metal Removal from Water: Phytoremediation
    A.P. Bhat and P.P. Bhat (2016) Int J Appl Sci Biotechnol, Vol 4(2): 150-154 DOI: 10.3126/ijasbt.v4i2.14742 Mini Review SUSTAINABLE USE OF PLANTS FOR HEAVY METAL REMOVAL FROM WATER: PHYTOREMEDIATION Akash P. Bhat1* and Pooja P. Bhat2 1Department of Chemical Engineering, Thadomal Shahani Engineering College, Bandra West, Mumbai 400050, Maharashtra, India, 2Department of Botany, Ramnarain Ruia College, Matunga, Mumbai 400019, Maharashtra, India. *Corresponding Author email: [email protected] Abstract There are various methods for removal of heavy metals from contaminated water and many of them can be costly and also consume a lot of resources. Phytoremediation is the use of plants as a filter for removal of unwanted elements and substances from contaminated water. This process is called rhizofiltration. Phytoremediation has not achieved a lot of importance on large scale level. This review- study shows how several species like Brassica juncea and Chenopodium amaranticolor, Pistia stratiotes, Helianthus annuus L. and Phaseolus vulgaris L. var. vulgaris, Eleocharis acicularis, Lemna minor L., Phragmites australis and Eichhornia Crassipes can be used for effective removal of heavy metals. These species are selected based on a review on various studies on rhizofiltration. Hence rhizofiltration can be an eco-friendly and innovative method of removal of heavy metals and has to be applied for large scale treatment of heavy metals in real time waters. Keywords: Phytoremediation; Rhizofiltration; Plants; Heavy metals; Removal Introduction processes should be at the utmost important place for Heavy metals and pollutants in water and aqueous wastes combating global warming and pollution. are a huge threat currently to the environment.
    [Show full text]
  • THE ABIOTIC STRESS RESPONSE of HYDROPONIC VETIVER GRASS (Chrysopogon Zizanioides L.) to ACID MINE DRAINAGE and ITS POTENTIAL for ENVIRONMENTAL REMEDIATION
    Michigan Technological University Digital Commons @ Michigan Tech Dissertations, Master's Theses and Master's Reports 2018 THE ABIOTIC STRESS RESPONSE OF HYDROPONIC VETIVER GRASS (Chrysopogon zizanioides L.) TO ACID MINE DRAINAGE AND ITS POTENTIAL FOR ENVIRONMENTAL REMEDIATION Jef Kiiskila Michigan Technological University, [email protected] Copyright 2018 Jef Kiiskila Recommended Citation Kiiskila, Jef, "THE ABIOTIC STRESS RESPONSE OF HYDROPONIC VETIVER GRASS (Chrysopogon zizanioides L.) TO ACID MINE DRAINAGE AND ITS POTENTIAL FOR ENVIRONMENTAL REMEDIATION", Open Access Dissertation, Michigan Technological University, 2018. https://doi.org/10.37099/mtu.dc.etdr/763 Follow this and additional works at: https://digitalcommons.mtu.edu/etdr Part of the Biochemistry Commons, Environmental Sciences Commons, and the Plant Biology Commons THE ABIOTIC STRESS RESPONSE OF HYDROPONIC VETIVER GRASS (Chrysopogon zizanioides L.) TO ACID MINE DRAINAGE AND ITS POTENTIAL FOR ENVIRONMENTAL REMEDIATION By Jeffrey D. Kiiskila A DISSERTATION Submitted in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY In Biochemistry and Molecular Biology MICHIGAN TECHNOLOGICAL UNIVERSITY 2018 © 2018 Jeffrey D. Kiiskila This dissertation has been approved in partial fulfillment of the requirements for the Degree of DOCTOR OF PHILOSOPHY in Biochemistry and Molecular Biology. Department of Biological Sciences Dissertation Advisor: Rupali Datta Committee Member: Dibyendu Sarkar Committee Member: Tarun K. Dam Committee Member: Victor Busov Department
    [Show full text]
  • Phytoextraction of Cadmium: the Advantages, Limitations, Cost and Potential Improvements of This Remediation Technique
    Phytoextraction of Cadmium: the advantages, limitations, cost and potential improvements of this remediation technique. Becky Meyerholt Abstract Throughout the United States there are multiple sites where the soil has been contaminated with heavy metals such as zinc, cadmium, lead, and arsenic. Due of the risk that these metals pose to humans and the local ecosystem, these contaminated sites are not fit for food production until the contamination is remediated. Because of the cost and perceived invasiveness of traditional ex-situ remediation techniques, there has been an increase in the number of sites that are remediated using in-situ techniques such as phytoremediation. Phytoremediation uses plants to reduce the concentration of a contaminant and/or reduce the risk of exposure from a contaminant in the environment. Phytoextraction uses plants to remove a soil contaminate by sequestering it in the plant tissues, which are then harvested and removed. As with all remediation techniques, phytoextraction has a limited effectiveness. Its two main limitations are: metal toxicity to plants at high concentrations and the cost to dispose of the plant tissues. Recent studies have proposed different methods to overcome these limitations through the use of genetic engineering and coupling the disposal of harvested biomass with the production of energy, biofuels or as a source for the mining of valuable metals. 1. Introduction: The land area of our planet is finite and as the world population grows, it is important that degraded lands are restored for productive uses such as food and sustainable energy production. Land degradation, or the loss of productive value from a given area of land, can occur due to multiple reasons including chemical contamination from both natural and anthropogenic sources.
    [Show full text]
  • Phytoremediation of Metal Contamination Using Salix (Willows)
    University of Denver Digital Commons @ DU Electronic Theses and Dissertations Graduate Studies 1-1-2015 Phytoremediation of Metal Contamination Using Salix (Willows) Gordon J. Kersten University of Denver Follow this and additional works at: https://digitalcommons.du.edu/etd Part of the Ecology and Evolutionary Biology Commons, and the Other Environmental Sciences Commons Recommended Citation Kersten, Gordon J., "Phytoremediation of Metal Contamination Using Salix (Willows)" (2015). Electronic Theses and Dissertations. 1034. https://digitalcommons.du.edu/etd/1034 This Thesis is brought to you for free and open access by the Graduate Studies at Digital Commons @ DU. It has been accepted for inclusion in Electronic Theses and Dissertations by an authorized administrator of Digital Commons @ DU. For more information, please contact [email protected],[email protected]. Phytoremediation of Metal Contamination using Salix (willows) ______________________ A Thesis Presented to The Faculty of Natural Sciences and Mathematics University of Denver ______________________ In Partial Fulfillment Of the Requirements for the Degree Master of Science ______________________ By Gordon J. Kersten August 2015 Advisor: Martin F. Quigley Author: Gordon J. Kersten Title: Phytoremediation of Metal Contamination using Salix (willows) Advisor: Martin F. Quigley Degree Date: August 2015 ABSTRACT Abandoned hardrock mines and the resulting Acid Mine Drainage (AMD) are a source of vast, environmental degradation that are toxic threats to plants, animals, and humans. Cadmium (Cd) and lead (Pb) are metal contaminants often found in AMD. In my mine outwash water samples, cadmium and lead concentrations were 19 and 160 times greater than concentrations in control waterways, and 300 and 40 times greater than EPA Aquatic Life Use water quality standards, respectively.
    [Show full text]
  • Rhizofiltration for Removal of Inorganic and Organic Pollutants in Groundwater: a Review
    Review Volume 11, Issue 4, 2021, 12326 - 12347 https://doi.org/10.33263/BRIAC114.1232612347 Rhizofiltration for Removal of Inorganic and Organic Pollutants in Groundwater: a Review Risky Ayu Kristanti 1,* , Wei Jie Ngu 2, Adhi Yuniarto 3 , Tony Hadibarata 2 1 Faculty of Military Engineering, Universitas Pertahanan, Bogor, 16810, Indonesia 2 Department of Environmental Engineering, Faculty of Engineering and Science, Curtin University Malaysia, CDT 250, Miri, Malaysia 3 Department of Environmental Engineering, Faculty of Civil, Environmental and Geo-Engineering, Institut Teknologi Sepuluh Nopember, Surabaya, 60111, Indonesia * Correspondence: [email protected]; Scopus Author ID 46861527200 Received: 5.12.2020; Revised: 30.12.2020; Accepted: 2.01.2021; Published: 4.01.2021 Abstract: Groundwater serves as the water recharge of surface water and provides clean water for domestic, industrial, and agricultural usage for human life. However, rapid developments resulted in groundwater contamination by heavy metals, pesticides, waste by-products, cosmetics, pharmaceutics, and biological agents. Groundwater contamination by the percolation of heavy metals (HM) is focused on in this review. Heavy metals known for their persistence, bioaccumulation, and biomagnification properties are hazardous to live organisms. Long-term exposure to heavy metals brings adverse effects on respiratory diseases, cardiovascular disorders, cancer, etc. They are considered toxins, carcinogens, mutagens, and teratogens for humans in low concentrations. Hence, technologies to remediate heavy metals and organic pollutant in groundwater is vital to prevent environmental and health issues. However, current conventional remediation technologies that are expensive, utilize hazardous materials, and produce toxic by-products in effluents are insufficient to alleviate heavy metals' effects in groundwater.
    [Show full text]
  • (PCE) and TRICHLOROETHYLENE (TCE) USING BLACK WILLOW and EASTERN POPLAR by STACEY HEATH BOX (Under the Direction of Dr
    GREENHOUSE TREATABILITY STUDIES ON PHYTOREMEDIATION OF PERCHLOROETHYLENE (PCE) AND TRICHLOROETHYLENE (TCE) USING BLACK WILLOW AND EASTERN POPLAR by STACEY HEATH BOX (Under the direction of Dr. Valentine Asongu Nzengung) ABSTRACT Greenhouse studies were conducted to determine the effectiveness of black willow, eastern poplar, and duckweed to uptake, transform, and degrade perchloroethylene (PCE) and trichloroethylene (TCE). Results indicate that both black willow and eastern poplar are capable of decontaminating solution concentrations of up to 20 mg/L of PCE and 45 mg/L TCE. High concentrations of 45 mg/L PCE were shown to be toxic to the plants. Duckweed did not exhibit the ability to degrade these compounds. The results indicate that black willow and eastern poplar can transform and degrade these recalcitrant compounds and have the potential for application to remediate shallow, contaminated soil and groundwater. INDEX WORDS: Phytoremediation, Perchloroethylene, Trichloroethylene, Groundwater, Contamination, Populus, Salix, Lemnaceae GREENHOUSE TREATABILITY STUDIES ON PHYTOREMEDIATION OF PERCHLOROETHYLENE (PCE) AND TRICHLOROETHYLENE (TCE) USING BLACK WILLOW AND EASTERN POPLAR by STACEY HEATH BOX B.S., Mississippi State University, 1995 A Thesis Submitted to the Graduate Faculty of The University of Georgia in Partial Fulfillment of the Requirements for the Degree MASTER OF SCIENCE ATHENS, GEORGIA 2002 ã 2002 Stacey Heath Box All Rights Reserved GREENHOUSE TREATABILITY STUDIES ON PHYTOREMEDIATION OF PERCHLOROETHYLENE (PCE) AND TRICHLOROETHYLENE (TCE) USING BLACK WILLOW AND EASTERN POPLAR by STACEY HEATH BOX Approved: Major Professor: Valentine Nzengung Committee: Dave Wenner Matt Smith Electronic Version Approved: Gordhan L. Patel Dean of the Graduate School The University of Georgia August 2002 DEDICATION To Heather iv ACKNOWLEDGMENTS First off, I must thank my major advisor, Dr.
    [Show full text]
  • Bioremediation, Its Applications to Contaminated Sites in India
    Phytofi ltration Phytovolatilization Phytoremediation Blastofi ltration Phytoevaporation Phytocontainment Phytohydraulics Phytostimulation Phytoaccumulation Phytodegradation Phytoextraction Phytoconcentration Phytoassimilation Phytotransfer Phytotransformation Phytomining Phytoimmobilization Phytoreduction Phytostabilization Phytooxidation Phytosequestration Rhizosphere Rhizoremediation Transportation Bacterial ACC Nitrilase Desorption Deaminase Bioremediation Adsorption Respiration Cytochromes P450 Nitroreductases Precipitation Acidifi cation Hydrolases Redox reactions Oxidases Leakage Glucosyltransferases Chelation Exudation Peroxidases Complexation Laccase Fungi Bacteria A State-of-the-Art report on For further details, please contact: Bioremediation, its Applications to Dr. G.V. Subrahmanyam Dr. M.N.V. Prasad Advisor Professor Contaminated Sites in India Ministry of Environment & Forests Department of Plant Sciences Dr. M.N.V. Prasad, Dept. of Plant Sciences, University of Hyderabad, Hyderabad Paryavaran Bhawan, CGO Complex University of Hyderabad Lodhi Road, New Delhi - 110003 Prof. C.R. Rao Road, Gachibowli P.O. Central University, Hyderabad 500046 Tel: +91-11-24364594 Fax: +91-11-24364594 Tel +91-40-23134509, 66794509 email: [email protected] Fax +91-40-23010120, 23010145 Mobile: +91 9989144651 E-mail: [email protected] March 2011 Ministry of Environment & Forests tgk¡ gS gfj;kyh A Government of India ogk¡ gS [kq’kgkyh AA Nelumbo nucifera (Indian Lotus), in constructed wetland for water purifi cation A State-of-the-Art report
    [Show full text]