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(Oxy)Hydroxide Electrocatalysts for Water Oxidation Bryan R
www.acsami.org Research Article Effect of Selenium Content on Nickel Sulfoselenide-Derived Nickel (Oxy)hydroxide Electrocatalysts for Water Oxidation Bryan R. Wygant, Anna H. Poterek, James N. Burrow, and C. Buddie Mullins* Cite This: ACS Appl. Mater. Interfaces 2020, 12, 20366−20375 Read Online ACCESS Metrics & More Article Recommendations *sı Supporting Information ABSTRACT: An efficient and inexpensive electrocatalyst for the oxygen evolution reaction (OER) must be found in order to improve the viability of hydrogen fuel production via water electrolysis. Recent work has indicated that nickel chalcogenide materials show promise as electrocatalysts for this reaction and that their performance can be further enhanced with the generation of ternary, bimetallic chalcogenides (i.e., Ni1−aMaX2); however, relatively few studies have investigated ternary chalcogenides created through the addition of a second chalcogen (i.e., NiX2−aYa). To address this, we fi studied a series of Se-modi ed Ni3S2 composites for use as OER electrocatalysts in alkaline solution. We found that the addition of Se results in the creation of Ni3S2/NiSe composites composed of cross-doped metal chalcogenides and show that the addition of 10% Se reduces the overpotential required to reach a current density of 10 mA/cm2 by 40 mV versus a pure nickel sulfide material. Chemical analysis of the composites’ surfaces shows a reduction in the amount of nickel oxide species with Se incorporation, which is supported by transmission electron microscopy; this reduction is correlated with a decrease in the OER overpotentials measured for these samples. Together, our results suggest that the incorporation of Se into Ni3S2 creates a more conductive material with a less-oxidized surface that is more electrocatalytically active and resistant to further oxidation. -
Proton Transfer Reaction in Water: Hydronium Ion Formation
Advanced Journal of Chemistry-Section A, 2020, 3(3), 255–258 Available online at : www.ajchem-a.com ISSN Online: 2645-5676 DOI: 10.33945/SAMI/AJCA.2020.3.2 Short Communication Proton Transfer Reaction in Water: Hydronium Ion Formation In Sang Leea, Sitansu Sekhar Nandab,* a Research Division, Divine Lab Limited, Seoul, South Korea b Department of Chemistry, Myongji University, Yongin, South Korea A R T I C L E I N F O A B S T R A C T Received: 28 June 2019 The current ongoing scientific debate deals with accumulation of hydronium Revised: 07 August 2019 ions (H3O+) on water surface. Elevated interfacial concentration measured by Accepted: 31 August 2019 using Raman spectroscopy. A strong surface affinity of H3O+ indicated by Raman Available online: 03 September 2019 spectroscopy under similar conditions. Ion adsorption phenomena, H3O+ formation and its structural activity emphasized in our study. Asymmetric water ion adsorption clearly observed in our research. K E Y W O R D S Raman spectroscopy Hydronium Water Infrared spectroscopy G R A P H I C A L A B S T R A C T * Corresponding author's E-mail address: [email protected] Proton Transfer Reaction in Water: Hydronium… 256 Introduction employed for recording Raman spectra with 2– 10 s acquisition time. A scanning area of 30 μm × In nature, interfacial charge formation is 30 μm was applied to avoid laser damage to known as a ubiquitous phenomenon. water. Fundamental mechanism of interfacial charge formation related with its identification. Results and discussions Researchers have been attracted for charge formation development of appropriate models. -
The Influence of Sodium Hydroxide Concentration on the Phase, Morphology and Agglomeration of Cobalt Oxide Nanoparticles and Application As Fenton Catalyst
Digest Journal of Nanomaterials and Biostructures Vol.14, No.4, October-December 2019, p. 1131-1137 THE INFLUENCE OF SODIUM HYDROXIDE CONCENTRATION ON THE PHASE, MORPHOLOGY AND AGGLOMERATION OF COBALT OXIDE NANOPARTICLES AND APPLICATION AS FENTON CATALYST E. L. VILJOENa,*, P. M. THABEDEa, M. J. MOLOTOa, K. P. MUBIAYIb, B. W. DIKIZAa aDepartment of Chemistry, Vaal University of Technology Private, Bag X021, Vanderbijlpark 1900, South Africa bSchool of Chemistry, University of the Witwatersrand, 1 Jan Smuts Avenue, Braamfontein Johannesburg 2000, South Africa The concentration of NaOH was varied from 0.2 M to 0.7 M during the preparation of the cobalt oxide/cobalt oxide hydroxide nanoparticles by precipitation and air oxidation. Cubic shaped and less well defined Co3O4 nanoparticles formed at 0.2 M NaOH. An increase in the NaOH concentration increased the number of well-defined cubic shaped nanoparticles. Agglomerated CoO(OH) particles with different shapes formed at the highest NaOH concentration. The cubic shaped Co3O4 nanoparticles were subsequently used as catalyst for the Fenton degradation of methylene blue and it was found that the least agglomerated nanoparticles were the most catalytically active. (Received June 25, 2019; Accepted December 6, 2019) Keywords: Cobalt oxide, Nanoparticles, Precipitation, pH, Fenton reaction 1. Introduction Controlling the size and the shape of nanoparticles using simple, inexpensive precipitation methods without sophisticated capping molecules, remains a challenge. Literature has indicated that the concentration of the base (pH) is an important parameter to control the size, shape and phase of metal oxide nanoparticles. Obodo et al.[1] used chemical bath deposition at atmospheric pressure and 70 °C to precipitate Co3O4 crystallites on a glass substrate and they showed that the crystallite sizes were larger at a higher pH of 12 in comparison to when a pH of 10 was used. -
SODIUM HYDROXIDE @Lye, Limewater, Lyewater@
Oregon Department of Human Services Office of Environmental Public Health (503) 731-4030 Emergency 800 NE Oregon Street #604 (971) 673-0405 Portland, OR 97232-2162 (971) 673-0457 FAX (971) 673-0372 TTY-Nonvoice TECHNICAL BULLETIN HEALTH EFFECTS INFORMATION Prepared by: ENVIRONMENTAL TOXICOLOGY SECTION OCTOBER, 1998 SODIUM HYDROXIDE @Lye, limewater, lyewater@ For More Information Contact: Environmental Toxicology Section (971) 673-0440 Drinking Water Section (971) 673-0405 Technical Bulletin - Health Effects Information Sodium Hydroxide Page 2 SYNONYMS: Caustic soda, sodium hydrate, soda lye, lye, natrium hydroxide CHEMICAL AND PHYSICAL PROPERTIES: - Molecular Formula: NaOH - White solid, crystals or powder, will draw moisture from the air and become damp on exposure - Odorless, flat, sweetish flavor - Pure solid material or concentrated solutions are extremely caustic, immediately injurious to skin, eyes and respiratory system WHERE DOES IT COME FROM? Sodium hydroxide is extracted from seawater or other brines by industrial processes. WHAT ARE THE PRINCIPLE USES OF SODIUM HYDROXIDE? Sodium hydroxide is an ingredient of many household products used for cleaning and disinfecting, in many cosmetic products such as mouth washes, tooth paste and lotions, and in food and beverage production for adjustment of pH and as a stabilizer. In its concentrated form (lye) it is used as a household drain cleaner because of its ability to dissolve organic solids. It is also used in many industries including glassmaking, paper manufacturing and mining. It is used widely in medications, for regulation of acidity. Sodium hydroxide may be used to counteract acidity in swimming pool water, or in drinking water. IS SODIUM HYDROXIDE NATURALLY PRESENT IN DRINKING WATER? Yes, because sodium and hydroxide ions are common natural mineral substances, they are present in many natural soils, in groundwater, in plants and in animal tissues. -
A Study of Hydrogen Exchange in Benzene And
A STUDY OF HYDROGEN EXCHANGE IN BENZENE AND SEVERAL ALKYLBENZENES By REX LYNN ELMORE B~chelor of Arts Austin College Sherman, Texas 1960 Submitted to the faculty of the Graduate School of the Oklahpma State University in partial fulfillment of the requirements for the degree of DOCTOR OF PHILOSOPHY August, 1965 J OKLAHOMA Jjf STATE UNIVERSITY .;.;, i' LIBRARY f DEC 6 1965 j' A STUDY OF HYDROGEN EXCHANGE IN BENZE~ AND ,,:.-· ;" . ·..... : SEVERAL ALKYLBENZENES f ~~~~~~~"'~"''""i;·~l'J!'~~ Thesis Approved: 593417 ii .ACKNOWLEDGMENTS Grateful acknowledgment is made to-Dr. E. M. Hodnett, research adviser, for his patience, guidance, and assistance throughout this work; to Dr. O. C. Dermer, head of the Chemistry Department, for his reading of the manuscript prior to its being typed; to Mr. C.R. Williams, formerly in the Chemistry Department, for his assistance in the early phases of the computer programming; to Mr. Preston Gant, Central Research Division of the Continental Oil Company, for helpful suggestions on the tritium assays; and to Mr. Prem S. Juneja for his helpful suggestions concerning experimental details which arose from time to time. Acknowledgment is made of financial assistance in the form of a graduate teaching assistantship in the Chemis.try Department. Also, a research as.sistantship from the Atomic Energy Commission, Contract No. AT(ll-1)-1049, through the Research Foundation is appreciated. Research done during the term of the latter assistantship provided material for this thesis. iii TABLE OF CONTENTS Chapter Page I. INTRODUCTION. 1 II. HISTORICAL, , 3 III. INTRODUCTION TO THE EXPERIMENTAL WORK 14 Objectives and Plan of the Study. -
Carbon Dioxide Capture from Atmospheric Air Using Sodium
Environ. Sci. Technol. 2008, 42, 2728–2735 Carbon Dioxide Capture from Nearly all current research on CCS focuses on capturing CO2 from large, stationary sources such as power plants. Atmospheric Air Using Sodium Such plans usually entail separating CO2 from flue gas, compressing it, and transporting it via pipeline to be Hydroxide Spray sequestered underground. In contrast, the system described in this paper captures CO2 directly from ambient air (“air § capture”). This strategy will be expensive compared to capture JOSHUAH K. STOLAROFF, from point sources, but may nevertheless act as an important DAVID W. KEITH,‡ AND complement, since CO emissions from any sector can be GREGORY V. LOWRY*,† 2 captured, including emissions from diffuse sources such as Chemical and Petroleum Engineering, University of Calgary, aircraft or automobiles, where on-board carbon capture is and Departments of Civil and Environmental Engineering very difficult and the cost of alternatives is high. Additionally, and Engineering and Public Policy, Carnegie Mellon in a future economy with low carbon emissions, air capture University, Pittsburgh, Pennsylvania 15213 might be deployed to generate negative net emissions (1). This ability to reduce atmospheric CO2 concentrations faster Received October 15, 2007. Revised manuscript received than natural cycles allow would be particularly desirable in February 05, 2008. Accepted February 06, 2008. scenarios where climate sensitivity is on the high end of what is expected, resulting in unacceptable shifts in land usability and stress to ecosystems. In contrast to conventional carbon capture systems for Previous research has shown that air capture is theoreti- cally feasible in terms of thermodynamic energy require- power plants and other large point sources, the system described ments, land use (2), and local atmospheric transport of CO2 in this paper captures CO2 directly from ambient air. -
Answer Key Chapter 16: Standard Review Worksheet – + 1
Answer Key Chapter 16: Standard Review Worksheet – + 1. H3PO4(aq) + H2O(l) H2PO4 (aq) + H3O (aq) + + NH4 (aq) + H2O(l) NH3(aq) + H3O (aq) 2. When we say that acetic acid is a weak acid, we can take either of two points of view. Usually we say that acetic acid is a weak acid because it doesn’t ionize very much when dissolved in water. We say that not very many acetic acid molecules dissociate. However, we can describe this situation from another point of view. We could say that the reason acetic acid doesn’t dissociate much when we dissolve it in water is because the acetate ion (the conjugate base of acetic acid) is extremely effective at holding onto protons and specifically is better at holding onto protons than water is in attracting them. + – HC2H3O2 + H2O H3O + C2H3O2 Now what would happen if we had a source of free acetate ions (for example, sodium acetate) and placed them into water? Since acetate ion is better at attracting protons than is water, the acetate ions would pull protons out of water molecules, leaving hydroxide ions. That is, – – C2H3O2 + H2O HC2H3O2 + OH Since an increase in hydroxide ion concentration would take place in the solution, the solution would be basic. Because acetic acid is a weak acid, the acetate ion is a base in aqueous solution. – – 3. Since HCl, HNO3, and HClO4 are all strong acids, we know that their anions (Cl , NO3 , – and ClO4 ) must be very weak bases and that solutions of the sodium salts of these anions would not be basic. -
Exposure to Potassium Hydroxide Can Cause Headache, Eye Contact Dizziness, Nausea and Vomiting
Right to Know Hazardous Substance Fact Sheet Common Name: POTASSIUM HYDROXIDE Synonyms: Caustic Potash; Lye; Potassium Hydrate CAS Number: 1310-58-3 Chemical Name: Potassium Hydroxide (KOH) RTK Substance Number: 1571 Date: May 2001 Revision: January 2010 DOT Number: UN 1813 Description and Use EMERGENCY RESPONDERS >>>> SEE LAST PAGE Potassium Hydroxide is an odorless, white or slightly yellow, Hazard Summary flakey or lumpy solid which is often in a water solution. It is Hazard Rating NJDOH NFPA used in making soap, as an electrolyte in alkaline batteries and HEALTH - 3 in electroplating, lithography, and paint and varnish removers. FLAMMABILITY - 0 Liquid drain cleaners contain 25 to 36% of Potassium REACTIVITY - 1 Hydroxide. CORROSIVE POISONOUS GASES ARE PRODUCED IN FIRE DOES NOT BURN Reasons for Citation Hazard Rating Key: 0=minimal; 1=slight; 2=moderate; 3=serious; f Potassium Hydroxide is on the Right to Know Hazardous 4=severe Substance List because it is cited by ACGIH, DOT, NIOSH, NFPA and EPA. f Potassium Hydroxide can affect you when inhaled and by f This chemical is on the Special Health Hazard Substance passing through the skin. List. f Potassium Hydroxide is a HIGHLY CORROSIVE CHEMICAL and contact can severely irritate and burn the skin and eyes leading to eye damage. f Contact can irritate the nose and throat. f Inhaling Potassium Hydroxide can irritate the lungs. SEE GLOSSARY ON PAGE 5. Higher exposures may cause a build-up of fluid in the lungs (pulmonary edema), a medical emergency. FIRST AID f Exposure to Potassium Hydroxide can cause headache, Eye Contact dizziness, nausea and vomiting. -
Chemistry 20 - Unit 2 - Ph and Poh Notes Name: ______+ - [H3O ] and [OH ]
Chemistry 20 - Unit 2 - pH and pOH Notes Name: _________________________________________ + - [H3O ] and [OH ] + - + - In water both H3O and OH exist H2O + H2O ⇌ H3O + OH + - -14 These concentrations exist in a balanced relationship [H3O ][OH ] = 1.00 x 10 + - This relationship is inversely related ↑ [H3O ] = ↓ [OH ] Example 1: -4 What is the hydroxide ion concentration in a solution with a hydronium ion concentration of 2.59 x 10 M ? + - -14 [H3O ][OH ] = 1.00 x 10 −14 − 1.00×10 [OH ] = + [H3O ] −14 [OH−] = 1.00×10 = 3.86 × 10−11 2.59×10−4 Example 2: If 2.50 g of NaOH was dissolved in water to produce 500mL of solution, what would be the concentration of hydronium and hydroxide ions in solution? + - NaOH ⟶ Na + OH − mol 1 mol 1 [OH ] L = 2.50 g × 40 g × 0.500 L = 0.125 M + - -14 [H3O ][OH ] = 1.00 x 10 −14 −14 [H O+] = 1.00×10 = 1.00×10 = 8.0 × 10−14M 3 [OH−] 1.25 pH Review + pH = − log[H3O ] + −pH [H3O ] = 10 Example 3: What is the pH of a solution of 0.159 M HCl? + - HCl ⟶ H + Cl + pH = − log[H3O ] pH = − log[0.159 M] pH = 0.799 Example 4: What is the hydronium and hydroxide ion concentration of a solution with a pH of 2.42? + −pH −2.42 [H3O ] = 10 = 10 = 0.0038 M + - -14 [H3O ][OH ] = 1.00 x 10 −14 −14 − 1.00×10 1.00×10 −12 [OH ] = + = = 2.63 × 10 M [H3O ] 0.0038 M pOH - Power of OH Since: + - -14 [H3O ][OH ] = 1.00 x 10 Can take the “log” of both sides… pOH = − log[OH−] + - -14 -log([H3O ][OH ]) = -log(1.00 x 10 ) − −pOH [OH ] = 10 + - + - And -log([H3O ][OH ]) = -log[H3O ] + -log[OH ] Therefore… pH + pOH = 14 Example 5: A solution has a pH of 5.750. -
Ionization, Dissociation, and the Investigation of Structure in Small Molecular Models to Develop a Broader Understanding of Gas Phase Ion Chemistry
Ionization, dissociation, and the investigation of structure in small molecular models to develop a broader understanding of gas phase ion chemistry DISSERTATION Presented in Partial Fulfillment of the Requirements for the Degree Doctor of Philosophy in the Graduate School of The Ohio State University By Matthew Bernier Graduate Program in Chemistry The Ohio State University 2014 Dissertation Committee: Professor Vicki Wysocki, Advisor Professor Terry Gustafson Professor Abraham Badu-Tawiah Copyright by Matthew Bernier 2014 Abstract This dissertation focuses on molecular systems in the low-mass range to determine how chemical and structural changes can affect subsequent fragmentation chemistry and protonation site. Each system was investigated using MS analysis and gas-phase ion structural techniques selected from tandem MS (MSMS), hydrogen-deuterium exchange (HDX), ion-mobility (IM), and action infra-red multi-photon dissociation (IRMPD). In Chapter 3, the non-standard amino acid gamma-aminobutyric acid (GABA) was placed into a peptide system to test a mechanism which explained the lack of a3 ions in standard peptide fragmentations. GABA extends the peptide backbone by two methylene units and its insertion into the second position of larger peptides increases the intensity of a3 ion. Using MSMS, it was found that this was a result of blocking common favorable fragmentation pathways. The results demonstrated the use of modified peptides for revealing reasons for how peptides fragment. Chapter 4 focused on a unique set of non-canonical amino acids and their ability to affect the trans/cis nature of adjacent amide bonds in peptide sequences. In solution, 4- R-Flouroproline (R-Flp) is found to favor the trans peptide bond and 4-S-fluoroproline (S- flp) favors the cis bond. -
Drugs and Acid Dissociation Constants Ionisation of Drug Molecules Most Drugs Ionise in Aqueous Solution.1 They Are Weak Acids Or Weak Bases
Drugs and acid dissociation constants Ionisation of drug molecules Most drugs ionise in aqueous solution.1 They are weak acids or weak bases. Those that are weak acids ionise in water to give acidic solutions while those that are weak bases ionise to give basic solutions. Drug molecules that are weak acids Drug molecules that are weak bases where, HA = acid (the drug molecule) where, B = base (the drug molecule) H2O = base H2O = acid A− = conjugate base (the drug anion) OH− = conjugate base (the drug anion) + + H3O = conjugate acid BH = conjugate acid Acid dissociation constant, Ka For a drug molecule that is a weak acid The equilibrium constant for this ionisation is given by the equation + − where [H3O ], [A ], [HA] and [H2O] are the concentrations at equilibrium. In a dilute solution the concentration of water is to all intents and purposes constant. So the equation is simplified to: where Ka is the acid dissociation constant for the weak acid + + Also, H3O is often written simply as H and the equation for Ka is usually written as: Values for Ka are extremely small and, therefore, pKa values are given (similar to the reason pH is used rather than [H+]. The relationship between pKa and pH is given by the Henderson–Hasselbalch equation: or This relationship is important when determining pKa values from pH measurements. Base dissociation constant, Kb For a drug molecule that is a weak base: 1 Ionisation of drug molecules. 1 Following the same logic as for deriving Ka, base dissociation constant, Kb, is given by: and Ionisation of water Water ionises very slightly. -
Protonation and Chloroplast Membrane Structure
PROTONATION AND CHLOROPLAST MEMBRANE STRUCTURE SATORU MURAKAMI and LESTER PACKER From the Department of Physiology-Anatomy, University of California, Berkeley, California 94720 Downloaded from http://rupress.org/jcb/article-pdf/47/2/332/1069424/332.pdf by guest on 29 September 2021 ABSTRACT Light changes the structure of chloroplasts . This effect was investigated by high resolution electron microscopy, photometric methods, and chemical modification . (a) A reversible contraction of chloroplast membrane occurs upon illumination, dark titration with H+, or increasing osmolarity . These gross structural changes arise from a flattening of the thylakoids, with a corresponding decrease in the spacing between membranes . Microdensitometry showed that illumination or dark addition of H+ resulted in a 13-23% decrease in mem- brane thickness. Osmotically contracted chloroplasts do not show this effect . (b) Rapid glutaraldehyde fixation during actual experiments revealed that transmission changes are closely correlated with the spacing changes and therefore reflect an osmotic mechanism, whereas the light scattering changes have kinetics most similar to changes in membrane thickness or conformation . (c) Kinetic analysis of light scattering and transmission changes with the changes in fluorescence of anilinonaphthalene sulfonic acid bound to membranes revealed that fluorescence preceded light scattering or transmission changes. (d) It is concluded that the temporal sequence of events following illumination probably are proto- nation, changes in the environment within the membrane, change in membrane thickness, change in internal osmolarity accompanying ion movements with consequent collapse and flattening of thylakoid, change in the gross morphology of the inner chloroplast membrane system, and change in the gross morphology of whole chloroplasts . INTRODUCTION Ample evidence has been brought forward in changes in chloroplast membranes is still undeter- recent years to demonstrate, both in vitro (1-9) mined .