Electron Donor and Acceptor Utilization by Halorespiring Bacteria'
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Detection of a Bacterial Group Within the Phylum Chloroflexi And
Microbes Environ. Vol. 21, No. 3, 154–162, 2006 http://wwwsoc.nii.ac.jp/jsme2/ Detection of a Bacterial Group within the Phylum Chloroflexi and Reductive-Dehalogenase-Homologous Genes in Pentachlorobenzene- Dechlorinating Estuarine Sediment from the Arakawa River, Japan KYOSUKE SANTOH1, ATSUSHI KOUZUMA1, RYOKO ISHIZEKI2, KENICHI IWATA1, MINORU SHIMURA3, TOSHIO HAYAKAWA3, TOSHIHIRO HOAKI4, HIDEAKI NOJIRI1, TOSHIO OMORI2, HISAKAZU YAMANE1 and HIROSHI HABE1*† 1 Biotechnology Research Center, The University of Tokyo, 1–1–1 Yayoi, Bunkyo-ku, Tokyo 113–8657, Japan 2 Department of Industrial Chemistry, Faculty of Engineering, Shibaura Institute of Technology, Minato-ku, Tokyo 108–8548, Japan 3 Environmental Biotechnology Laboratory, Railway Technical Research Institute, 2–8–38 Hikari-cho, Kokubunji-shi, Tokyo 185–8540, Japan 4 Technology Research Center, Taisei Corporation, 344–1 Nase, Totsuka-ku, Yokohama 245–0051, Japan (Received April 21, 2006—Accepted June 12, 2006) We enriched a pentachlorobenzene (pentaCB)-dechlorinating microbial consortium from an estuarine-sedi- ment sample obtained from the mouth of the Arakawa River. The sediment was incubated together with a mix- ture of four electron donors and pentaCB, and after five months of incubation, the microbial community structure was analyzed. Both DGGE and clone library analyses showed that the most expansive phylogenetic group within the consortium was affiliated with the phylum Chloroflexi, which includes Dehalococcoides-like bacteria. PCR using a degenerate primer set targeting conserved regions in reductive-dehalogenase-homologous (rdh) genes from Dehalococcoides species revealed that DNA fragments (approximately 1.5–1.7 kb) of rdh genes were am- plified from genomic DNA of the consortium. The deduced amino acid sequences of the rdh genes shared sever- al characteristics of reductive dehalogenases. -
The Electron Transport Chain in Anaerobically Functioning Eukaryotes
rl BIOCHIMICA ET BIOPHYSICA ACTA II BBt ELSEVIER Biochimica et Biophysica Acta, 1365 (1998) 71-78 The electron transport chain in anaerobically functioning eukaryotes Aloysius G.M. Tielens*, Jaap J. Van Hellemond Laboratory of Veterinary Biochemistry and Institute for Biomembranes, Utrecht University, P.O. Box 80176, 3508 TD Utrecht, The Netherlands Received 27 January 1998; received in revised form 26 February 1998; accepted 2 March 1998 Abstract Many lower eukaryotes can survive anaerobic conditions via a fermentation pathway that involves the use of the reduction of endogenously produced fumarate as electron sink. This fumarate reduction is linked to electron transport in an especially adapted, anaerobically functioning electron-transport chain. An aerobic energy metabolism with Krebs cycle activity is accompanied by electron transfer from succinate to ubiquinone via complex II of the respiratory chain. On the other hand, in an anaerobic metabolism, where fumarate functions as terminal electron acceptor, electrons are transferred from rhodoquinone to fumarate, which is the reversed direction. Ubiquinone cannot replace rhodoquinone in the process of fumarate reduction in vivo, as ubiquinone can only accept electrons from complex II and cannot donate them to fumarate. Rhodoquinone, with its lower redox potential than ubiquinone, is capable of donating electrons to fumarate. Eukaryotic fumarate reductases were shown to interact with rhodoquinone (a benzoquinone), whereas most prokaryotic fumarate reductases interact with the naphtoquinones mena- quinone and demethylmenaquinone. Fumarate reductase, the enzyme essential for the anaerobic functioning of many eukaryotes, is structurally very similar to succinate dehydrogenase, the Krebs cycle enzyme catalysing the reverse reaction. In prokaryotes these enzymes are differentially expressed depending on the external conditions. -
Biol 1020: Photosynthesis
Chapter 10: Photosynthesis Energy and Carbon Sources Electromagnetic Spectrum and Light Chloroplasts Photosynthesis Overview Light Reactions C3 Cycle Photorespiration Supplemental Carbon Fixation: C4 and CAM pathways . • List and differentiate the 4 possible groups of organisms based on how they obtain energy and useful carbon. Classification by Energy and Carbon Sources energy source chemotrophs can only get energy directly from chemical compounds phototrophs can get energy directly from light (these organisms can use chemical compounds as energy sources as well) . Classification by Energy and Carbon Sources carbon source autotrophs can fix carbon dioxide, thus they can use CO2 as a carbon source heterotrophs cannot fix CO2; they use organic molecules from other organisms as a carbon source . Classification by Energy and Carbon Sources combined, these leads to 4 possible groups: photoautotrophs – carry out photosynthesis use light energy to fix CO2 store energy in chemical bonds of organic molecules includes green plants, algae, and some bacteria photoheterotrophs – use light energy but cannot fix CO2; some nonsulfur purple bacteria chemoautotrophs – obtain energy from reduced inorganic molecules and use some of it to fix CO2; some bacteria chemoheterotrophs – use organic molecules as both carbon and energy sources dependent completely on other organisms for energy capture and carbon fixation includes all animals, all fungi, most protists, and most bacteria . • List and differentiate the 4 possible groups of -
A Systems-Level Investigation of the Metabolism of Dehalococcoides Mccartyi and the Associated Microbial Community
A Systems-Level Investigation of the Metabolism of Dehalococcoides mccartyi and the Associated Microbial Community by Mohammad Ahsanul Islam A thesis submitted in conformity with the requirements for the degree of Doctor of Philosophy Department of Chemical Engineering and Applied Chemistry University of Toronto © Copyright by Mohammad Ahsanul Islam 2014 A Systems-Level Investigation of the Metabolism of Dehalococcoides mccartyi and the Associated Microbial Community Mohammad Ahsanul Islam Doctor of Philosophy Department of Chemical Engineering and Applied Chemistry University of Toronto 2014 Abstract Dehalococcoides mccartyi are a group of strictly anaerobic bacteria important for the detoxification of man-made chloro-organic solvents, most of which are ubiquitous, persistent, and often carcinogenic ground water pollutants. These bacteria exclusively conserve energy for growth from a pollutant detoxification reaction through a novel metabolic process termed organohalide respiration. However, this energy harnessing process is not well elucidated at the level of D. mccartyi metabolism. Also, the underlying reasons behind their robust and rapid growth in mixed consortia as compared to their slow and inefficient growth in pure isolates are unknown. To obtain better insight on D. mccartyi physiology and metabolism, a detailed pan- genome-scale constraint-based mathematical model of metabolism was developed. The model highlighted the energy-starved nature of these bacteria, which probably is linked to their slow growth in isolates. The model also provided a useful framework for subsequent analysis and visualization of high-throughput transcriptomic data of D. mccartyi. Apart from confirming expression of the majority genes of these bacteria, this analysis helped review the annotations of ii metabolic genes. -
Chlorinated Solvent Bioremediation: Fundamentals and Practical Application for Remedial Project Managers Presented By: Christopher Marks, Ph.D
Chlorinated Solvent Bioremediation: Fundamentals and Practical Application for Remedial Project Managers Presented by: Christopher Marks, Ph.D. & Carolyn Acheson, Ph.D. US Environmental Protection Agency Office of Research and Development National Risk Management Research Laboratory CLU-IN Webinar Nov. 14, 2018 Source: Accelerated Bioremediation of Chlorinated Solvents, Interstate Technology and Regulatory Council and Remediation and Technology Development Forum, 2003 1 Bioremediation of Chlorinated Solvents Source: Accelerated Bioremediation of Chlorinated Solvents, Interstate Technology and Regulatory Council and Remediation and Technology 2 Development Forum, 2003 Part I: Introduction to Chlorinated Solvent Properties and Anaerobic Reductive Dechlorination 3 Terminology • Anaerobic: Microbial metabolic processes occurring in the absence of oxygen. • Anaerobic Reductive Dechlorination: The biological removal of a chlorine atom from an organic compound and replacement with a hydrogen atom in a reducing environment. • Biodegradation aka biotransformation: Biologically mediated reactions which convert one chemical to another. For example, PCE is converted to TCE when anaerobic reductive reactions remove a chlorine molecule. • Bioremediation: The engineered approaches using microorganisms to biodegrade contaminants. • Biostimulation: The addition of organic electron donors and nutrients to enhance the rate of reductive dechlorination by the native microflora. • Bioaugmentation: The addition of beneficial microorganisms to enhance the capacity -
CENSUS® – Reductive Dechlorination
CENSUS® – Reductive Dechlorination CENSUS Detect and quantify Dehalococcoides and other bacteria capable of reductive dechlorination Under anaerobic conditions, certain bacteria can use chlorinated ethenes Successful reductive dechlorination can be hindered by a few site-specific (PCE, TCE, DCE, and VC) as electron acceptors in a process called reductive factors that cannot be evaluated with chemical and geochemical tests including: dechlorination. The net result is the sequential dechlorination of PCE and • a lack of a key dechlorinating bacteria including Dehalococcoides, the TCE through daughter products DCE and VC to non-toxic ethene, which only known bacteria that completely dechlorinates PCE and TCE to volatilizes or can be further metabolized. non-toxic ethene • reasons for incomplete dechlorination and the accumulation of daughter PCE TCE cis-DCE VC Ethene products (DCE stall) CENSUS® provides the most direct avenue to investigate the potentials and limitations to implementing corrective action plan decisions and to target a variety of organisms involved in the reductive dechlorination pathway. Target Code Contaminants Environmental Relevance / Data Interpretation Dehalococcoides qDHC PCE, TCE, Only known group of bacteria capable of complete dechlorination of PCE and/or TCE to ethene DCE, VC Absence of Dehalococcoides suggests dechlorination of DCE and VC is improbable and accumulation of daughter products is likely The presence of Dehalococcoides even in low copy numbers indicates the potential for complete reductive dechlorination -
Overview of in Situ Bioremediation of Chlorinated Ethene DNAPL Source Zones
INTERSTATE TECHNOLOGY & REGULATORY COUNCIL Warning! This document has not been amended since publication. Some content may be out of date and may no longer apply. INTERSTATE TECHNOLOGY & REGULATORY COUNCIL Technology Overview Overview of In Situ Bioremediation of Chlorinated Ethene DNAPL Source Zones October 2005 Prepared by The Interstate Technology & Regulatory Council Bioremediation of DNAPLs Team ABOUT ITRC Established in 1995, the Interstate Technology & Regulatory Council (ITRC) is a state-led, national coalition of personnel from the environmental regulatory agencies of more than 40 states and the District of Columbia, three federal agencies, tribes, and public and industry stakeholders. The organization is devoted to reducing barriers to and speeding interstate deployment of, better, more cost-effective, innovative environmental techniques. ITRC operates as a committee of the Environmental Research Institute of the States (ERIS), a Section 501(c)(3) public charity that supports the Environmental Council of the States (ECOS) through its educational and research activities aimed at improving the environment in the United States and providing a forum for state environmental policy makers. More information about ITRC and its available products and services can be found on the Internet at www.itrcweb.org. DISCLAIMER This document is designed to help regulators and others develop a consistent approach to their evaluation, regulatory approval, and deployment of specific technologies at specific sites. Although the information in this document is believed to be reliable and accurate, this document and all material set forth herein are provided without warranties of any kind, either express or implied, including but not limited to warranties of the accuracy or completeness of information contained in the document. -
Sulphate-Reducing Bacteria's Response to Extreme Ph Environments and the Effect of Their Activities on Microbial Corrosion
applied sciences Review Sulphate-Reducing Bacteria’s Response to Extreme pH Environments and the Effect of Their Activities on Microbial Corrosion Thi Thuy Tien Tran 1 , Krishnan Kannoorpatti 1,* , Anna Padovan 2 and Suresh Thennadil 1 1 Energy and Resources Institute, College of Engineering, Information Technology and Environment, Charles Darwin University, Darwin, NT 0909, Australia; [email protected] (T.T.T.T.); [email protected] (S.T.) 2 Research Institute for the Environment and Livelihoods, College of Engineering, Information Technology and Environment, Charles Darwin University, Darwin, NT 0909, Australia; [email protected] * Correspondence: [email protected] Abstract: Sulphate-reducing bacteria (SRB) are dominant species causing corrosion of various types of materials. However, they also play a beneficial role in bioremediation due to their tolerance of extreme pH conditions. The application of sulphate-reducing bacteria (SRB) in bioremediation and control methods for microbiologically influenced corrosion (MIC) in extreme pH environments requires an understanding of the microbial activities in these conditions. Recent studies have found that in order to survive and grow in high alkaline/acidic condition, SRB have developed several strategies to combat the environmental challenges. The strategies mainly include maintaining pH homeostasis in the cytoplasm and adjusting metabolic activities leading to changes in environmental pH. The change in pH of the environment and microbial activities in such conditions can have a Citation: Tran, T.T.T.; Kannoorpatti, significant impact on the microbial corrosion of materials. These bacteria strategies to combat extreme K.; Padovan, A.; Thennadil, S. pH environments and their effect on microbial corrosion are presented and discussed. -
Considerations for the Collection and Evaluation of Natural Attenuation Parameters at Sites Contaminated with Chlorinated Solvents
CONSIDERATIONS FOR THE COLLECTION AND EVALUATION OF NATURAL ATTENUATION PARAMETERS AT SITES CONTAMINATED WITH CHLORINATED SOLVENTS Chlorine • Hydrogen • Carbon • Bond "\. ( . I Vinyl Chloride I . ~ I Cis-1,2-Dichloroethene I ITrichloroethene I .,. Source Area Biological Active Area DowngradientI Area Filure 3 Anaerobic Reductive Dechlorination ofa Trichloroethene Plnm.e Prepared by Florida Department of Environmental Protection (FDEP) Division of Waste Management Bureau of Waste Cleanup Hazardous Waste Cleanup Section April 1999 TABLE OF CONTENTS SECTION TITLE PAGE 1.0 IN'TR.ODUCTION ........................................................................................ 1 ~ 2.0 GENERAL OVERVIEW OF CHLORINATED ALIPHATIC HYDROCARBON BIODEGRADATION................................................. 2 2.1 Bacteria 2.2 Electron Acceptor Reactions 2.3 Electron Donor Reactions 2.4 Co-Metabolism 3.0 NATURAL ATTENUATION BY PHYSICAL PROCESSES ................... 4 4.0 METABOLIC BY-PRODUCTS AND REDOX PROCESSES IN GROUNDWATER SYSTEMS ................................................................... 4 S.O EVIDENCE USED TO SUPPORT NATURAL ATTENUATION•••••••••• S 5.1 Direct Evidence S.2 Examine Changes 5.3 Laboratory microcosm studies 6.0 METHODOLOGY USED FOR DATA REVIEW AND SITE EVALUATION........................................................................................... 6 7.0 NATURAL ATTENUATION SAMPLING AND DATA EVALUATION METHODOLOGY..................................................................................... 9 7.1 Monitor Well -
Redox Potential of the Terminal Quinone Electron Acceptor QB in Photosystem II Reveals the Mechanism of Electron Transfer Regulation
Redox potential of the terminal quinone electron acceptor QB in photosystem II reveals the mechanism of electron transfer regulation Yuki Kato1, Ryo Nagao, and Takumi Noguchi1 Division of Material Science, Graduate School of Science, Nagoya University, Nagoya 464-8602, Japan Edited by Pierre A. Joliot, Institut de Biologie Physico-Chimique, Paris, France, and approved December 4, 2015 (received for review October 12, 2015) Photosystem II (PSII) extracts electrons from water at a Mn4CaO5 (Em values). Both forward and backward electron transfers are cluster using light energy and then transfers them to two plas- important; backward electron transfers control charge recombina- toquinones, the primary quinone electron acceptor QA and the tion in PSII, and this serves as photoprotection for PSII proteins secondary quinone electron acceptor QB. This forward electron (5, 14–17). PSII involves specific mechanisms to regulate for- transfer is an essential process in light energy conversion. Mean- ward and backward electron transfer reactions in response to while, backward electron transfer is also significant in photopro- environmental changes. For instance, in strong light, some spe- tection of PSII proteins. Modulation of the redox potential (Em) gap cies of cyanobacteria increase the Em of Pheo to facilitate charge of QA and QB mainly regulates the forward and backward electron recombination. Specifically, they exchange D1 subunits origi- transfers in PSII. However, the full scheme of electron transfer nating from different psbA genes to change the hydrogen bond regulation remains unresolved due to the unknown Em value of interactions of Pheo (16–20). On the other hand, it was found QB. Here, for the first time (to our knowledge), the Em value of QB that impairment of the Mn4CaO5 cluster led to a significant in- reduction was measured directly using spectroelectrochemistry in crease in the Em of QA by ∼150 mV (21–27). -
Synthesis and Photoinduced Electron Transfer of Donor-Sensitizer-Acceptor Systems
Synthesis and Photoinduced Electron Transfer of Donor-Sensitizer-Acceptor Systems Yunhua Xu Stockholm University 2005 1 Synthesis and Photoinduced Electron Transfer of Donor-Sensitizer-Acceptor Systems Akademisk avhandling som för avläggande av filosofie doktorsexamen vid Stockholms Universitet, tillsammans med arbetena I-VII, offentligen kommer att försvaras i Magnélisalen, Kemiska övnings-laboratoriet, Svante Arrhenius väg 16, onsdagen den 20 april 2005, klockan 10.00. Av Yunhua Xu Avhandlingen försvaras på engelska Institutionen för organisk kemi ISBN 91-7155-034-8 pp 1-53 Arrheniuslaboratoriet Stockholm 2005 Stockholms Universitet 106 91 Stockholm Abstract Artificial systems involving water oxidation and solar cells are promising ways for the conversion of solar energy into fuels and electricity. These systems usually consist of a photosensitizer, an electron donor and / or an electron acceptor. This thesis deals with the synthesis and photoinduced electron transfer of several donor-sensitizer- acceptor supramolecular systems. The first part of this thesis describes the synthesis and properties of two novel dinuclear ruthenium complexes as electron donors to mimic the donor side reaction of Photosystem II. These two Ru2 complexes were then covalently linked to ruthenium trisbipyridine and the properties of the resulting trinuclear complexes were studied by cyclic voltammetry and transient absorption spectroscopy. The second part presents the synthesis and photoinduced electron transfer of covalently linked donor-sensitizer supramolecular systems in the presence of TiO2 as electron acceptors. Electron donors are tyrosine, phenol and their derivatives, and dinuclear ruthenium complexes. Intramolecular electron transfer from the donor to the oxidized sensitizer was observed by transient absorption spectroscopy after light 2+ excitation of the Ru(bpy)3 moiety. -
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