Bioaugmentation and Correlating Anaerobic Digester Microbial Community to Process Function
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Core Sulphate-Reducing Microorganisms in Metal-Removing Semi-Passive Biochemical Reactors and the Co-Occurrence of Methanogens
microorganisms Article Core Sulphate-Reducing Microorganisms in Metal-Removing Semi-Passive Biochemical Reactors and the Co-Occurrence of Methanogens Maryam Rezadehbashi and Susan A. Baldwin * Chemical and Biological Engineering, University of British Columbia, 2360 East Mall, Vancouver, BC V6T 1Z3, Canada; [email protected] * Correspondence: [email protected]; Tel.: +1-604-822-1973 Received: 2 January 2018; Accepted: 17 February 2018; Published: 23 February 2018 Abstract: Biochemical reactors (BCRs) based on the stimulation of sulphate-reducing microorganisms (SRM) are emerging semi-passive remediation technologies for treatment of mine-influenced water. Their successful removal of metals and sulphate has been proven at the pilot-scale, but little is known about the types of SRM that grow in these systems and whether they are diverse or restricted to particular phylogenetic or taxonomic groups. A phylogenetic study of four established pilot-scale BCRs on three different mine sites compared the diversity of SRM growing in them. The mine sites were geographically distant from each other, nevertheless the BCRs selected for similar SRM types. Clostridia SRM related to Desulfosporosinus spp. known to be tolerant to high concentrations of copper were members of the core microbial community. Members of the SRM family Desulfobacteraceae were dominant, particularly those related to Desulfatirhabdium butyrativorans. Methanogens were dominant archaea and possibly were present at higher relative abundances than SRM in some BCRs. Both hydrogenotrophic and acetoclastic types were present. There were no strong negative or positive co-occurrence correlations of methanogen and SRM taxa. Knowing which SRM inhabit successfully operating BCRs allows practitioners to target these phylogenetic groups when selecting inoculum for future operations. -
Bioaugmentation: an Emerging Strategy of Industrial Wastewater Treatment for Reuse and Discharge
International Journal of Environmental Research and Public Health Review Bioaugmentation: An Emerging Strategy of Industrial Wastewater Treatment for Reuse and Discharge Alexis Nzila 1,*, Shaikh Abdur Razzak 2 and Jesse Zhu 3 1 Department of Life Sciences, King Fahd University of Petroleum and Minerals (KFUPM), P.O. Box 468, Dhahran 31261, Saudi Arabia 2 Department of Chemical Engineering, King Fahd University of Petroleum and Minerals (KFUPM), Dhahran 31261, Saudi Arabia; [email protected] 3 Department of Chemical and Biochemical Engineering, University of Western Ontario, London, ON N6A 5B9, Canada; [email protected] * Correspondence: [email protected]; Tel.: +966-13-860-7716; Fax: +966-13-860-4277 Academic Editors: Rao Bhamidiammarri and Kiran Tota-Maharaj Received: 12 May 2016; Accepted: 9 July 2016; Published: 25 August 2016 Abstract: A promising long-term and sustainable solution to the growing scarcity of water worldwide is to recycle and reuse wastewater. In wastewater treatment plants, the biodegradation of contaminants or pollutants by harnessing microorganisms present in activated sludge is one of the most important strategies to remove organic contaminants from wastewater. However, this approach has limitations because many pollutants are not efficiently eliminated. To counterbalance the limitations, bioaugmentation has been developed and consists of adding specific and efficient pollutant-biodegrading microorganisms into a microbial community in an effort to enhance the ability of this microbial community to biodegrade contaminants. This approach has been tested for wastewater cleaning with encouraging results, but failure has also been reported, especially during scale-up. In this review, work on the bioaugmentation in the context of removal of important pollutants from industrial wastewater is summarized, with an emphasis on recalcitrant compounds, and strategies that can be used to improve the efficiency of bioaugmentation are also discussed. -
Bioaugmentation of Chlorinated Solvents
BIOAUGMENTATION FOR REMEDIATION OF CHLORINATED SOLVENTS: TECHNOLOGY DEVELOPMENT, STATUS, AND RESEARCH NEEDS October 2005 GeoSyntec Consultants TABLE OF CONTENTS LIST OF TABLES ...........................................................................................................................................III LIST OF FIGURES .........................................................................................................................................III ACRONYMNS AND ABBREVIATIONS........................................................................................................V FOREWORD...................................................................................................................................................VII EXECUTIVE SUMMARY ............................................................................................................................... IX 1. INTRODUCTION ..........................................................................................................................................1 2. EARLY DEVELOPMENT OF BIOAUGMENTATION.............................................................................5 3. RECENT PROGRESS IN CHLORINATED SOLVENT BIOREMEDIATION .....................................13 4. DEHALORESPIRATION: THE KEY PROCESS UNDERLYING CURRENT BIOAUGMENTATION PRACTICES..............................................................................................................................................................19 4.1 THE UBIQUITY CONCEPT REVISITED -
Biological Methods
Biological Methods Jerry Walsh, Jenna Bishop, Quinn Albertson, Shane Galloway, Carlos Rivera, Tom Devenney, Jeff Green Physical Mechanisms In Situ Methods Permeable Reactive Barriers Biostimulation Bioaugmentation Phytoremediation Permeable Reactive Barriers (Biobarriers) • Semi-permeable reactive media in flow path • Chemically or biologically-mediated reactions transform contaminants into non-toxic or immobile products • Hydrocarbons need to be oxidized • Chlorinated solvents and nitrate need to be reduced • Microorganisms help mediate redox reactions to gain energy and materials for synthesis Reactive Media Reactive Medium Removal Mechanism Contaminants Removed Organic Material Microbial sulfate reduction Acid mine drainage and precipitation Organic Material Microbial nitrate reduction Nitrate Oxygen/Nitrate-Releasing Microbial degradation BTEX Compounds Resting-State Microbial cometabolism Chlorinated aliphatics Microorganisms Oxidative Biodegradation • To respire electrons removed from contaminants, need electron acceptors Aerobic: • Aerobic methods Molecular Oxygen Anaerobic: • Anaerobic methods Nutrients (nitrate, sulfates, CO2, ferric iron, metal oxides, etc) • Aerobic methods are generally preferred to provide more energy to the microbes • Biochemical oxygen demands (BOD’s) often exceed available oxygen, so adding oxygen to the system can stimulate oxidative biodegradation Reductive Biodegradation • Electron donors are required, which anaerobic environments more abundantly produce • Organic matter is a well-suited electron donor for this process • This method works well for TCE, hexavalent chromium, sulfate, and nitrate contamination • Heterotrophic denitrification to remove nitrate Biostimulation • Modification of environment to stimulate existing bacteria capable of bioremediation. • Only works if correct bacteria are present. • Often done through use of phosphorous, nitrogen, carbon, and oxygen. • Chemicals usually added through injection wells. • EPA approved method. Advantages • Low Costs • Can be tailored to the specific site conditions. -
Selecting Bacteria Candidates for the Bioaugmentation of Activated Sludge to Improve the Aerobic Treatment of Landfill Leachate
water Article Selecting Bacteria Candidates for the Bioaugmentation of Activated Sludge to Improve the Aerobic Treatment of Landfill Leachate Justyna Michalska *, Artur Pi ´nski , Joanna Zur˙ and Agnieszka Mrozik Institute of Biology, Biotechnology and Environmental Protection, Faculty of Natural Sciences, University of Silesia, Jagiello´nska28, 40-032 Katowice, Poland; [email protected] (A.P.); [email protected] (J.Z.);˙ [email protected] (A.M.) * Correspondence: [email protected] Received: 6 November 2019; Accepted: 27 December 2019; Published: 1 January 2020 Abstract: In this study, a multifaceted approach for selecting the suitable candidates for bioaugmentation of activated sludge (AS) that supports leachate treatment was used. To determine the exploitation of 10 bacterial strains isolated from the various matrices for inoculating the AS contaminated with the Kalina pond leachate (KPL), their degradative potential was analyzed along with their aptitude to synthesize compounds improving remediation of pollutants in wastewater and ability to incorporate into the AS flocs. Based on their capability to degrade aromatic compounds (primarily catechol, phenol, and cresols) at a concentration of 1 mg/mL and survive in 12.5% of the KPL, Pseudomonas putida OR45a and P. putida KB3 can be considered to be the best candidates for bioaugmentation of the AS among all of the bacteria tested. Genomic analyses of these two strains revealed the presence of the genes encoding enzymes related to the metabolism of aromatic compounds. Additionally, both microorganisms exhibited a high hydrophobic propensity (above 50%) and an ability to produce biosurfactants as well as high resistance to ammonium (above 600 µg/mL) and heavy metals (especially chromium). -
Bioremediation of Groundwater: an Overview
International Journal of Applied Engineering Research ISSN 0973-4562 Volume 13, Number 24 (2018) pp. 16825-16832 © Research India Publications. http://www.ripublication.com Bioremediation of Groundwater: An Overview Shivam Mani Tripathi 1, Shri Ram2 1 ,2 Civil Engineering Department, MMMUT Gorakhpur, India Abstract can be treated on site, thus reducing exposure risks for clean- In past, we have large open area and abundant land resources up personnel, or potentially wider exposure as a result of and groundwater. But after the industrialization the use of transportation accidents. Methodology of this process is not hazardous chemicals increased due to unmanageable technically difficult, considerable experience and knowledge conditions. The chemical disposed on the ground surface & may require implementing this process, by thoroughly many other anthropogenic activities by humans like use of investigating the site and to know required condition to pesticides and oil spillage contaminated the soil and achieve. groundwater. The different type of contaminant by percolation The usual technique of remediation is to plow up through the ground reach to the aquifer and get affected which contaminated soil and take away to the site, or to cover or cap causes serious problem. We spend lot of money and use many the contaminated area. There are some drawbacks. The first technologies to extract and remediate the contamination. In method simply transport the contaminated materials which spite of different methods, bioremediation is a technology create major risks is excavation, handling, and transport of which is cost efficient and effective by using natural microbes hazardous material. It is very difficult to find the new landfill and degrades the contaminants the conditions and different sites for disposal. -
Advances in Anaerobic Benzene Bioremediation: Microbes, Mechanisms, and Biotechnologies
Advances in Anaerobic Benzene Bioremediation: Microbes, Mechanisms, and Biotechnologies Sandra Dworatzek, Phil Dennis and Jeff Roberts RemTech, Virtual October 15, 2020 Introduction and Acknowledgements • Sandra Dworatzek, Jennifer Webb (SiREM, Guelph, ON) • Elizabeth Edwards, Nancy Bawa, Shen Guo and Courtney Toth (University of Toronto, Toronto, ON) • Kris Bradshaw and Rachel Peters (Federated Co-operatives Ltd., Saskatoon, SK) • Krista Stevenson (Imperial Oil, Sarnia, ON) The Landscape of Hydrocarbon Bioremediation: A Lot Has Changed… Microbial bioremediation is currently the most common technology used to remediate petroleum hydrocarbons Microbial Remediation Phytoremediation Chemical Treatment Contain and Excavate Pump and Treat Other Near Cold Lake, Alberta Adapted from Elekwachi et al., 2014 (J Bioremed Biodeg 5) What Sites are Currently Being Targeted for Hydrocarbon Bioremediation? 4 Shallow Soils and Groundwater 1 2 (aerobic) Offshore Spills Ex situ Bioreactors (mostly aerobic) (mostly aerobic) 3 Tailings Ponds 5 Deeper Groundwater (aerobic and anaerobic) (intrinsically anaerobic) Groundwater Bioremediation Technologies Focusing on Anaerobic Microbial Processes Natural Attenuation Biostimulation Bioaugmentation unsaturated zone aquifer 3- PO4 sugars Plume source - 2- NO3 SO4 VFAs GW flow aquitard Bioaugmentation for anaerobic sites works! Dehalococcoides (Dhc) bioaugmentation is widely accepted to improve reductive dehalogenation of chlorinated ethenes 1 Month Post KB-1® Bioaugmentation Dhc TCE Bioaugmentation for anaerobic -
Microbial Community Changes in Methyl Tert-Butyl Ether (MTBE)- Contaminated Soils
University of Tennessee, Knoxville TRACE: Tennessee Research and Creative Exchange Masters Theses Graduate School 8-2004 Microbial Community Changes in Methyl tert-Butyl Ether (MTBE)- Contaminated Soils Bo Yang University of Tennessee - Knoxville Follow this and additional works at: https://trace.tennessee.edu/utk_gradthes Part of the Civil and Environmental Engineering Commons Recommended Citation Yang, Bo, "Microbial Community Changes in Methyl tert-Butyl Ether (MTBE)-Contaminated Soils. " Master's Thesis, University of Tennessee, 2004. https://trace.tennessee.edu/utk_gradthes/2223 This Thesis is brought to you for free and open access by the Graduate School at TRACE: Tennessee Research and Creative Exchange. It has been accepted for inclusion in Masters Theses by an authorized administrator of TRACE: Tennessee Research and Creative Exchange. For more information, please contact [email protected]. To the Graduate Council: I am submitting herewith a thesis written by Bo Yang entitled "Microbial Community Changes in Methyl tert-Butyl Ether (MTBE)-Contaminated Soils." I have examined the final electronic copy of this thesis for form and content and recommend that it be accepted in partial fulfillment of the requirements for the degree of Master of Science, with a major in Environmental Engineering. Kung-Hui Chu, Major Professor We have read this thesis and recommend its acceptance: Chris D. Cox, Paul D. Frymier Accepted for the Council: Carolyn R. Hodges Vice Provost and Dean of the Graduate School (Original signatures are on file with official studentecor r ds.) To the Graduate Council: I am submitting herewith a thesis written by Bo Yang entitled “Microbial Community Changes in Methyl tert-Butyl Ether (MTBE)-Contaminated Soils.” I have examined the final electronic copy of this thesis for form and content and recommend that it be accepted in partial fulfillment of the requirements for the degree of Master of Science, with a major in Environmental Engineering. -
Syntrophism Among Prokaryotes Bernhard Schink1
Syntrophism Among Prokaryotes Bernhard Schink1 . Alfons J. M. Stams2 1Department of Biology, University of Konstanz, Constance, Germany 2Laboratory of Microbiology, Wageningen University, Wageningen, The Netherlands Introduction: Concepts of Cooperation in Microbial Introduction: Concepts of Cooperation in Communities, Terminology . 471 Microbial Communities, Terminology Electron Flow in Methanogenic and Sulfate-Dependent The study of pure cultures in the laboratory has provided an Degradation . 472 amazingly diverse diorama of metabolic capacities among microorganisms and has established the basis for our under Energetic Aspects . 473 standing of key transformation processes in nature. Pure culture studies are also prerequisites for research in microbial biochem Degradation of Amino Acids . 474 istry and molecular biology. However, desire to understand how Influence of Methanogens . 475 microorganisms act in natural systems requires the realization Obligately Syntrophic Amino Acid Deamination . 475 that microorganisms do not usually occur as pure cultures out Syntrophic Arginine, Threonine, and Lysine there but that every single cell has to cooperate or compete with Fermentation . 475 other micro or macroorganisms. The pure culture is, with some Facultatively Syntrophic Growth with Amino Acids . 476 exceptions such as certain microbes in direct cooperation with Stickland Reaction Versus Methanogenesis . 477 higher organisms, a laboratory artifact. Information gained from the study of pure cultures can be transferred only with Syntrophic Degradation of Fermentation great caution to an understanding of the behavior of microbes in Intermediates . 477 natural communities. Rather, a detailed analysis of the abiotic Syntrophic Ethanol Oxidation . 477 and biotic life conditions at the microscale is needed for a correct Syntrophic Butyrate Oxidation . 478 assessment of the metabolic activities and requirements of Syntrophic Propionate Oxidation . -
Strategies for Remediation of Polycyclic Aromatic Hydrocarbons from Contaminated Soil-An Overview
Innovare Journal of Critical Reviews Academic Sciences ISSN- 2394-5125 Vol 2, Issue 1, 2015 Review Article STRATEGIES FOR REMEDIATION OF POLYCYCLIC AROMATIC HYDROCARBONS FROM CONTAMINATED SOIL-AN OVERVIEW NILANJANA DAS*, DEVLINA DAS Bioremediation Laboratory, SBST, VIT University, Vellore 632014, Tamil Nadu, India. Email: [email protected] Received: 05 Oct 2014 Revised and Accepted: 23 Dec 2014 ABSTRACT Polycyclic aromatic hydrocarbons (PAHs) are one of the most prevalent contaminants having toxicity, mutagenecity and carcinogenicity. Pollution caused by PAHs is a serious problem throughout the world. To solve the problem, substantial research efforts have been directed worldwide to adopt sustainable technologies for the treatment of PAHs containing soil. PAH compounds are transferred, degraded and sequestered in soils. They are relocated in the environment through volatilization, adsorption, leaching and erosion without alteration in their structure. Degradation causes alteration of PAHs structures from their original form though biological and chemical processes and sequestration occurs when PAHs are removed from bioavailable pools and stored for a long period of time. The conventional techniques for PAH removal involve excavation of contaminated soil and its incineration which are quite expensive and in many cases pollutants are transferred from one phase to another. The commonly employed biological methods for PAHs remediation in soil are landfarming, composting, bioaugmentation, biostimulation, phytoremediation etc. and chemical -
'Candidatus Desulfonatronobulbus Propionicus': a First Haloalkaliphilic
Delft University of Technology ‘Candidatus Desulfonatronobulbus propionicus’ a first haloalkaliphilic member of the order Syntrophobacterales from soda lakes Sorokin, D. Y.; Chernyh, N. A. DOI 10.1007/s00792-016-0881-3 Publication date 2016 Document Version Accepted author manuscript Published in Extremophiles: life under extreme conditions Citation (APA) Sorokin, D. Y., & Chernyh, N. A. (2016). ‘Candidatus Desulfonatronobulbus propionicus’: a first haloalkaliphilic member of the order Syntrophobacterales from soda lakes. Extremophiles: life under extreme conditions, 20(6), 895-901. https://doi.org/10.1007/s00792-016-0881-3 Important note To cite this publication, please use the final published version (if applicable). Please check the document version above. Copyright Other than for strictly personal use, it is not permitted to download, forward or distribute the text or part of it, without the consent of the author(s) and/or copyright holder(s), unless the work is under an open content license such as Creative Commons. Takedown policy Please contact us and provide details if you believe this document breaches copyrights. We will remove access to the work immediately and investigate your claim. This work is downloaded from Delft University of Technology. For technical reasons the number of authors shown on this cover page is limited to a maximum of 10. Extremophiles DOI 10.1007/s00792-016-0881-3 ORIGINAL PAPER ‘Candidatus Desulfonatronobulbus propionicus’: a first haloalkaliphilic member of the order Syntrophobacterales from soda lakes D. Y. Sorokin1,2 · N. A. Chernyh1 Received: 23 August 2016 / Accepted: 4 October 2016 © Springer Japan 2016 Abstract Propionate can be directly oxidized anaerobi- from its members at the genus level. -
Bioremediation and Phytoremediation Systems for Breaking Down Total
University of Connecticut OpenCommons@UConn Master's Theses University of Connecticut Graduate School 12-14-2014 Bioremediation and Phytoremediation Systems for Breaking Down Total Petroleum Hydrocarbons (TPH) in Contaminated Sandy Soil Patrick McIntosh University of Connecticut - Storrs, [email protected] Recommended Citation McIntosh, Patrick, "Bioremediation and Phytoremediation Systems for Breaking Down Total Petroleum Hydrocarbons (TPH) in Contaminated Sandy Soil" (2014). Master's Theses. 705. https://opencommons.uconn.edu/gs_theses/705 This work is brought to you for free and open access by the University of Connecticut Graduate School at OpenCommons@UConn. It has been accepted for inclusion in Master's Theses by an authorized administrator of OpenCommons@UConn. For more information, please contact [email protected]. Bioremediation and Phytoremediation Systems for Breaking Down Total Petroleum Hydrocarbons (TPH) in Contaminated Sandy Soil Patrick M. McIntosh, B.S., B.S. University of Connecticut 2008 A Thesis Presented in Partial Fulfillment for the Requirements for the Degree Masters of Science in the Graduate School of the University of Connecticut 2014 APPROVAL PAGE MASTERS OF SCIENCE THESIS Bioremediation and Phytoremediation Systems for Breaking Down Total Petroleum Hydrocarbons (TPH) in Contaminated Sandy Soil Presented by Patrick M. McIntosh B.S., B.S. Major Advisor ____________________________________________ Julia Kuzovkina Associate Advisor _____________________________________________ Karl Guillard Associate Advisor _____________________________________________ Cristian P. Schulthess The University of Connecticut 2014 II ACKNOWLEDGEMENTS I would like to thank the following individuals whose help make all of this possible: • Dr. Julia Kuzovkina, who gave me the opportunity to pursue this application of higher education. Her constant, support, and concern with these projects was greatly appreciated, especially through the tedious editing process I put her through with all of my corrections.