Hydrogen Peroxide Detoxification Is a Key Mechanism for Growth of Ammonia-Oxidizing Archaea
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Consistent Responses of Soil Microbial Communities to Elevated Nutrient Inputs in Grasslands Across the Globe
Consistent responses of soil microbial communities to elevated nutrient inputs in grasslands across the globe Jonathan W. Leffa,b, Stuart E. Jonesc, Suzanne M. Proberd, Albert Barberána, Elizabeth T. Borere, Jennifer L. Firnf, W. Stanley Harpoleg,h,i, Sarah E. Hobbiee, Kirsten S. Hofmockelj, Johannes M. H. Knopsk, Rebecca L. McCulleyl, Kimberly La Pierrem, Anita C. Rischn, Eric W. Seabloomo, Martin Schützn, Christopher Steenbockb, Carly J. Stevensp, and Noah Fierera,b,1 aCooperative Institute for Research in Environmental Sciences, University of Colorado, Boulder, CO 80309; bDepartment of Ecology and Evolutionary Biology, University of Colorado, Boulder, CO 80309; cDepartment of Biological Sciences, University of Notre Dame, Notre Dame, IN 46556; dCommonwealth Scientific and Industrial Research Organisation Land and Water Flagship, Wembley, WA 6913, Australia; eDepartment of Ecology, Evolution and Behavior, University of Minnesota, St. Paul, MN 55108; fSchool of Earth, Environmental and Biological Sciences, Queensland University of Technology, Brisbane, QLD 4001, Australia; gDepartment of Physiological Diversity, Helmholtz Center for Environmental Research UFZ, 04318 Leipzig, Germany; hGerman Centre for Integrative Biodiversity Research Halle-Jena-Leipzig, D-04103 Leipzig, Germany; iInstitute of Biology, Martin Luther University Halle-Wittenberg, 06108 Halle (Saale), Germany; jEcology, Evolution, and Organismal Biology Department, Iowa State University, Ames, IA 50011; kSchool of Biological Sciences, University of Nebraska, Lincoln, NE 68588; lDepartment of Plant and Soil Sciences, University of Kentucky, Lexington, KY 40546; mDepartment of Integrative Biology, University of California, Berkeley, CA 94720; nCommunity Ecology, Swiss Federal Institute for Forest, Snow and Landscape Research, 8903 Birmensdorf, Switzerland; oDepartment of Ecology, Evolution, and Behavior, University of Minnesota, St. Paul, MN 55108; and pLancaster Environment Centre, Lancaster University, Lancaster, LA1 4YQ, United Kingdom Edited by Peter M. -
Introduction to the Preparation and Properties of Hydiogen Peroxide
CHAPTER 1 Introduction to the Preparation and Properties of Hydiogen Peroxide 1 Introduction The following chapter will discuss the preparation of hydrogen peroxide, historically, the present day and future vistas for its in situ preparation. A brief introduction to the physical properties of hydrogen peroxide will also be made for the sake of completeness. Finally, the chapter will conclude with a practical approach to the safe handling of peroxygen species, destruction of residual peroxygens, and the toxicological and occupational health considerations required when handling hydrogen peroxide. 2 Industrial Manufacture of Hydrogen Peroxide The industrial manufacture of hydrogen peroxide can be traced back to its isolation in 18 18 by L. J. Thenard. Thenard reacted barium peroxide with nitric acid to produce a low concentration of aqueous hydrogen peroxide; the process can, however, be significantly improved by the use of hydrochloric acid. The hydrogen peroxide is formed in conjunction with barium chloride, both of which are soluble in water. The barium chloride is subsequently removed by precipitation with sulfuric acid (Figure 1.1). Hence, Thenard gave birth to the first commercial manufacture of aqueous hydrogen peroxide, although it took over sixty years before Thenard’s wet chemical process was employed in a commercial capacity.2 The industrial production of hydrogen peroxide using the above route was still operating until the middle of the 20th century. At the turn of the 19th century, approximately 10000 metric tonnes per annurn of barium peroxide were converted to about 2000 metric tonnes of hydrogen peroxide. Thenard’s process has, however, some major drawbacks which quenched the expectant explosion of its use in an aqueous form. -
The Decomposition Kinetics of Peracetic Acid and Hydrogen Peroxide in Municipal Wastewaters
Disinfection Forum No 10, October 2015 The Decomposition Kinetics of Peracetic Acid and Hydrogen Peroxide in Municipal Wastewaters INTRODUCTION Efficient control of microbial populations in municipal wastewater using peracetic acid (PAA) requires an understanding of the PAA decomposition kinetics. This knowledge is critical to ensure the proper dosing of PAA needed to achieve an adequate concentration within the contact time of the disinfection chamber. In addition, the impact of PAA on the environment, post-discharge into the receiving water body, also is dependent upon the longevity of the PAA in the environment, before decomposing to acetic acid, oxygen and water. As a result, the decomposition kinetics of PAA may have a significant impact on aquatic and environmental toxicity. PAA is not manufactured as a pure compound. The solution exists as an equilibrium mixture of PAA, hydrogen peroxide, acetic acid, and water: ↔ + + Acetic Acid Hydrogen Peroxide Peracetic Acid Water PeroxyChem’s VigorOx® WWT II Wastewater Disinfection Technology contains 15% peracetic acid by weight and 23% hydrogen peroxide as delivered. Although hydrogen peroxide is present in the formulation, peracetic acid is considered to be the active component for disinfection1 in wastewater. There have been several published studies investigating the decomposition kinetics of PAA in different water matrices, including municipal wastewater2-7. Yuan7 states that PAA may be consumed in the following three competitive reactions: 1. Spontaneous decomposition 2 CH3CO3H à 2 CH3CO2H + O2 Eq (1) 2. Hydrolysis CH3CO3H + H2O à CH3CO2H + H2O2 Eq (2) 3. Transition metal catalyzed decomposition + CH3CO3H + M à CH3CO2H + O2 + other products Eq (3) At neutral pH’s, both peracetic acid and hydrogen peroxide can be rapidly consumed by these reactions7 (hydrogen peroxide will decompose to water and oxygen via 2H2O2 à 2H2O + O2). -
Preparing to Manufacture Hydrogen Peroxide
PREPARING TO MANUFACTURE HYDROGEN PEROXIDE Part of the Hydrogen Peroxide Propulsion Guide The early laboratory preparation of hydrogen peroxide was based on the technique that Thenard used during the initial preparation of hydrogen peroxide. In this technique, barium nitrate, purified by recrystallization, was decomposed by heating in air in a porcelain retort. The resulting oxide was further oxidized by heating in a stream of oxygen to a dull red heat. The barium peroxide which formed was then dampened, ground, and dissolved in hydrochloric acid (nitric acid was used in Thenard’s initial experiments). A slight excess of sulfuric acid was then added to precipitate barium sulfate and regenerate hydrochloric acid. The procedure of barium peroxide solution and sulfate precipitation was repeated several times in the same solution to increase the peroxide concentration (concentrations of up to 33 percent by weight hydrogen peroxide could be achieved in this manner). The concentrated solution containing water, hydrogen peroxide, and hydrochloric acid, along with accumulated impurities, was cooled with ice and saturated with barium peroxide; iron and manganese impurities in the solution were then precipitated out as phosphates. The hydrochloric acid was removed by the addition of silver sulfate and the sulfate ion was removed by the subsequent addition of barium oxide. Further concentration was accomplished by vacuum distillation until “no further density increase occurs.” Thenard reported that 100 w/o hydrogen peroxide (on the basis of density data and the measurement of the volume of oxygen released) could be obtained by this technique. The first record of commercial production of hydrogen peroxide appeared in the 1865 to 1875 period. -
University of Groningen Discovery of a Eugenol Oxidase From
University of Groningen Discovery of a eugenol oxidase from Rhodococcus sp strain RHA1 Jin, J.F.; Mazon, H.; van den Heuvel, R.H.H.; Janssen, D.B.; Fraaije, M.W. Published in: Febs Journal DOI: 10.1111/j.1742-4658.2007.05767.x IMPORTANT NOTE: You are advised to consult the publisher's version (publisher's PDF) if you wish to cite from it. Please check the document version below. Document Version Publisher's PDF, also known as Version of record Publication date: 2007 Link to publication in University of Groningen/UMCG research database Citation for published version (APA): Jin, J. F., Mazon, H., van den Heuvel, R. H. H., Janssen, D. B., & Fraaije, M. W. (2007). Discovery of a eugenol oxidase from Rhodococcus sp strain RHA1. Febs Journal, 274(9), 2311 - 2321. https://doi.org/10.1111/j.1742-4658.2007.05767.x Copyright Other than for strictly personal use, it is not permitted to download or to forward/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 (like Creative Commons). Take-down policy If you believe that this document breaches copyright please contact us providing details, and we will remove access to the work immediately and investigate your claim. Downloaded from the University of Groningen/UMCG research database (Pure): http://www.rug.nl/research/portal. For technical reasons the number of authors shown on this cover page is limited to 10 maximum. Download date: 23-09-2021 Discovery of a eugenol oxidase from Rhodococcus sp. -
The Trophic-Dynamic Aspect of Ecology Author(S): Raymond L
The Trophic-Dynamic Aspect of Ecology Author(s): Raymond L. Lindeman Reviewed work(s): Source: Ecology, Vol. 23, No. 4 (Oct., 1942), pp. 399-417 Published by: Ecological Society of America Stable URL: http://www.jstor.org/stable/1930126 . Accessed: 30/01/2012 10:50 Your use of the JSTOR archive indicates your acceptance of the Terms & Conditions of Use, available at . http://www.jstor.org/page/info/about/policies/terms.jsp JSTOR is a not-for-profit service that helps scholars, researchers, and students discover, use, and build upon a wide range of content in a trusted digital archive. We use information technology and tools to increase productivity and facilitate new forms of scholarship. For more information about JSTOR, please contact [email protected]. Ecological Society of America is collaborating with JSTOR to digitize, preserve and extend access to Ecology. http://www.jstor.org THE TROPHIC-DYNAMIC ASPECT OF ECOLOGY RAYMOND L. LINDEMAN OsbornZoological Laboratory,Yale University Recent progressin the studyof aquatic community. A more "bio-ecological" food-cycle relationships invites a re- species-distributionalapproach would appraisal of certain ecological tenets. recognize both the plants and animals Quantitative productivitydata provide as co-constituentsof restricted"biotic" a basis for enunciating certain trophic communities,such as "plankton com- principles, which, when applied to a munities," "benthic communities,"etc., series of successional stages, shed new in which membersof the living commu- light on the dynamics of ecological nity "co-act" with each other and "re- succession. act" with the non-livingenvironment (Clementsand Shelford,'39; Carpenter, "COMMUNITY" CONCEPTS '39, '40; T. Park, '41). -
Algorithmic Analysis of Chemical Dynamics of the Autoignition of NH3–H2O2/Air Mixtures
energies Article Algorithmic Analysis of Chemical Dynamics of the Autoignition of NH3–H2O2/Air Mixtures Ahmed T. Khalil 1,2, Dimitris M. Manias 3, Efstathios-Al. Tingas 4, Dimitrios C. Kyritsis 1,2,* and Dimitris A. Goussis 1,2 1 Department of Mechanical Engineering, Khalifa University of Science and Technology, Abu Dhabi 127788, UAE; [email protected] (A.T.K.); [email protected] (D.A.G.) 2 Research and Innovation Center on CO2 and H2 (RICH), Khalifa University of Science and Technology, P.O. Box 127788, Abu Dhabi, UAE 3 Department of Mechanics, School of Applied Mathematics and Physical Sciences, National Technical University of Athens, 157 73 Athens, Greece; [email protected] 4 Perth College, University of the Highlands and Islands, (UHI), Perth PH1 2NX, UK; [email protected] * Correspondence: [email protected] Received: 8 September 2019; Accepted: 7 October 2019; Published: 21 November 2019 Abstract: The dynamics of a homogeneous adiabatic autoignition of an ammonia/air mixture at constant volume was studied, using the algorithmic tools of Computational Singular Perturbation. Since ammonia combustion is characterized by both unrealistically long ignition delays and elevated NOx emissions, the time frame of action of the modes that are responsible for ignition was analyzed by calculating the developing time scales throughout the process and by studying their possible relation to NOx emissions. The reactions that support or oppose the explosive time scale were identified, along with the variables that are related the most to the dynamics that drive the system to an explosion. -
Interaction of Ozone and Hydrogen Peroxide in Water Implications For
UC Irvine Faculty Publications Title Interaction of ozone and hydrogen peroxide in water: Implications for analysis of H 2 O 2 in air Permalink https://escholarship.org/uc/item/7j7454z7 Journal Geophysical Research Letters, 9(3) ISSN 00948276 Authors Zika, R. G Saltzman, E. S Publication Date 1982-03-01 DOI 10.1029/GL009i003p00231 License https://creativecommons.org/licenses/by/4.0/ 4.0 Peer reviewed eScholarship.org Powered by the California Digital Library University of California GEOPHYSICLARESEARCH LETTERS, VOL. 9, NO. 3, PAGES231-234 , MARCH1982 INTERACTION OF OZONE AND HYDROGEN PEROXIDE IN WATER: IMPLICATIONSFORANALYSIS oFH20 2 IN AIR R.G. Zika and E.S. Saltzman Division of Marine and Atmospheric Chemistry, University of Miami, Miami, Florida 331#9 Abstract. We have attempted to measure gaseous Analytical Methods H202 in air usingan aqueoustrapping method. With continuousbubbling, H 20 2 levels in the traps reacheda a. Hydrogen Peroxide. Hydrogen peroxide in aqueous plateau, indicating that a state of dynamic equilibrium solution was measured using a modified fluorescence involving H202 destrbction was established. We decay technique [Perschke and Broda, 1976; Zika and attribute this behavior to the interaction of ozone and its Zelmer, 1982]. The method involved the addition of a decompositionproducts (OH, O[) withH 20 2 inacld:•ous known amot•at of scopoletin (6-methyl-7-hydroxyl-i,2- solution. This hypothesis was investigated by replacing benzopyrone)to a pH 7.0 phosphatebuffered. sample. the air stream with a mixture of N2, 02 and 0 3. The The sample was prepared bY diluting an aliquot of the results Of this experiment show that H O was both reaction solution to 20 mls with low contaminant producedand destroyedin the traps. -
(Antarctica) Glacial, Basal, and Accretion Ice
CHARACTERIZATION OF ORGANISMS IN VOSTOK (ANTARCTICA) GLACIAL, BASAL, AND ACCRETION ICE Colby J. Gura A Thesis Submitted to the Graduate College of Bowling Green State University in partial fulfillment of the requirements for the degree of MASTER OF SCIENCE December 2019 Committee: Scott O. Rogers, Advisor Helen Michaels Paul Morris © 2019 Colby Gura All Rights Reserved iii ABSTRACT Scott O. Rogers, Advisor Chapter 1: Lake Vostok is named for the nearby Vostok Station located at 78°28’S, 106°48’E and at an elevation of 3,488 m. The lake is covered by a glacier that is approximately 4 km thick and comprised of 4 different types of ice: meteoric, basal, type 1 accretion ice, and type 2 accretion ice. Six samples were derived from the glacial, basal, and accretion ice of the 5G ice core (depths of 2,149 m; 3,501 m; 3,520 m; 3,540 m; 3,569 m; and 3,585 m) and prepared through several processes. The RNA and DNA were extracted from ultracentrifugally concentrated meltwater samples. From the extracted RNA, cDNA was synthesized so the samples could be further manipulated. Both the cDNA and the DNA were amplified through polymerase chain reaction. Ion Torrent primers were attached to the DNA and cDNA and then prepared to be sequenced. Following sequencing the sequences were analyzed using BLAST. Python and Biopython were then used to collect more data and organize the data for manual curation and analysis. Chapter 2: As a result of the glacier and its geographic location, Lake Vostok is an extreme and unique environment that is often compared to Jupiter’s ice-covered moon, Europa. -
Spatial Ecology of Territorial Populations
Spatial ecology of territorial populations Benjamin G. Weinera, Anna Posfaib, and Ned S. Wingreenc,1 aDepartment of Physics, Princeton University, Princeton, NJ 08544; bSimons Center for Quantitative Biology, Cold Spring Harbor Laboratory, Cold Spring Harbor, NY 11724; and cLewis–Sigler Institute for Integrative Genomics, Princeton University, Princeton, NJ 08544 Edited by Nigel Goldenfeld, University of Illinois at Urbana–Champaign, Urbana, IL, and approved July 30, 2019 (received for review July 9, 2019) Many ecosystems, from vegetation to biofilms, are composed of and penalize niche overlap (25), but did not otherwise struc- territorial populations that compete for both nutrients and phys- ture the spatial interactions. All these models allow coexistence ical space. What are the implications of such spatial organization when the combination of spatial segregation and local interac- for biodiversity? To address this question, we developed and ana- tions weakens interspecific competition relative to intraspecifc lyzed a model of territorial resource competition. In the model, competition. However, it remains unclear how such interactions all species obey trade-offs inspired by biophysical constraints on relate to concrete biophysical processes. metabolism; the species occupy nonoverlapping territories, while Here, we study biodiversity in a model where species interact nutrients diffuse in space. We find that the nutrient diffusion through spatial resource competition. We specifically consider time is an important control parameter for both biodiversity and surface-associated populations which exclude each other as they the timescale of population dynamics. Interestingly, fast nutri- compete for territory. This is an appropriate description for ent diffusion allows the populations of some species to fluctuate biofilms, vegetation, and marine ecosystems like mussels (28) or to zero, leading to extinctions. -
Hydrogen Peroxide Cas #7722-84-1
HYDROGEN PEROXIDE CAS #7722-84-1 Division of Toxicology ToxFAQsTM April 2002 This fact sheet answers the most frequently asked health questions (FAQs) about hydrogen peroxicde. For more information, call the ATSDR Information Center at 1-888-422-8737. This fact sheet is one in a series of summaries about hazardous substances and their health effects. It is important you understand this information because this substance may harm you. The effects of exposure to any hazardous substance depend on the dose, the duration, how you are exposed, personal traits and habits, and whether other chemicals are present. HIGHLIGHTS: Hydrogen peroxide is a manufactured chemical, although small amounts of hydrogen peroxide gas may occur naturally in the air. Low exposure may occur from use at home; higher exposures may occur from industrial use. Exposure to hydrogen peroxide can cause irritation of the eyes, throat, respiratory airway, and skin. Drinking concentrated liquid can cause mild to severe gastrointestinal effects. This substance has been found in at least 18 of the 1,585 National Priorities List sites identified by the Environmental Protection Agency (EPA). What is hydrogen peroxide? ‘ If released to soil, hydrogen peroxide will be broken down Hydrogen peroxide is a colorless liquid at room temperature by reacting with other compounds. with a bitter taste. Small amounts of gaseous hydrogen peroxide occur naturally in the air. Hydrogen peroxide is ‘ Hydrogen peroxide does not accumulate in the food chain. unstable, decomposing readily to oxygen and water with release of heat. Although nonflammable, it is a powerful How might I be exposed to hydrogen peroxide? oxidizing agent that can cause spontaneous combustion when it comes in contact with organic material. -
Sulfur Dioxide in Workplace Atmospheres (Bubbler)
Withdrawn Provided For Historical Reference Only SULFUR DIOXIDE IN WORKPLACE ATMOSPHERES (BUBBLER) ♦ Method Number: ID-104 Matrix: Air OSHA PEL Sulfur Dioxide (Final Rule Limit): 2 ppm (Time Weighted Limit) 5 ppm (Short-Term Exposure Limit) Sulfur Dioxide (Transitional Limit): 5 ppm (Time Weighted Limit) Collection Device: A calibrated personal sampling pump is used to draw a known volume of air through a midget-fritted glass bubbler containing 10 to 15 mL of 0.3 N hydrogen peroxide. Recommended Air Volume: 15 to 60 L Recommended Sampling Rate: 1 L/min Analytical Procedure: Samples are directly analyzed with no sample preparation by ion chromatography as total sulfate. Detection Limit Qualitative: 0.0041 ppm (60-L air volume) Quantitative: 0.010 ppm (60-L air volume) Precision and Accuracy Validation Level: 2.5 to 10.0 ppm (60-L air volume) CVT 0.012 Bias -0.046 Overall Error ±7% Method Classification: Validated Method Chemist: Ted Wilczek, Edward Zimowski Date (Date Revised): 1981 (December, 1989) Commercial manufacturers and products mentioned in this method are for descriptive use only and do not constitute endorsements by USDOL-OSHA. Similar products from other sources can be substituted. Branch of Inorganic Methods Development OSHA Technical Center Salt Lake City, Utah 1 of 9 Note: OSHA no longer uses or supports this method (November 2019). Withdrawn Provided For Historical Reference Only 1. Introduction This method describes the collection and analysis of airborne sulfur dioxide (SO2) using midget-fritted glass bubblers (MFGBs) in the workplace. It is applicable for both short-term (STEL) and time weighted average (TWA) exposure evaluations.