Converting Between the Oxides of Nitrogen Using Metal–
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Chapter 7.1 Nitrogen Dioxide
Chapter 7.1 Nitrogen dioxide General description Many chemical species of nitrogen oxides (NOx) exist, but the air pollutant species of most interest from the point of view of human health is nitrogen dioxide (NO2). Nitrogen dioxide is soluble in water, reddish-brown in colour, and a strong oxidant. Nitrogen dioxide is an important atmospheric trace gas, not only because of its health effects but also because (a) it absorbs visible solar radiation and contributes to impaired atmospheric visibility; (b) as an absorber of visible radiation it could have a potential direct role in global climate change if its concentrations were to become high enough; (c) it is, along with nitric oxide (NO), a chief regulator of the oxidizing capacity of the free troposphere by controlling the build-up and fate of radical species, including hydroxyl radicals; and (d) it plays a critical role in determining ozone (O3) concentrations in the troposphere because the photolysis of nitrogen dioxide is the only key initiator of the photochemical formation of ozone, whether in polluted or unpolluted atmospheres (1, 2). Sources On a global scale, emissions of nitrogen oxides from natural sources far outweigh those generated by human activities. Natural sources include intrusion of stratospheric nitrogen oxides, bacterial and volcanic action, and lightning. Because natural emissions are distributed over the entire surface of the earth, however, the resulting background atmospheric concentrations are very small. The major source of anthropogenic emissions of nitrogen oxides into the atmosphere is the combustion of fossil fuels in stationary sources (heating, power generation) and in motor vehicles (internal combustion engines). -
The Formation, Effects and Control of Oxides of Nitrogen in Diesel Engines
International Journal of Applied Engineering Research ISSN 0973-4562 Volume 13, Number 6 (2018) pp. 3200-3209 © Research India Publications. http://www.ripublication.com The Formation, Effects and Control of Oxides of Nitrogen in Diesel Engines Maroa Semakula1and Prof Freddie Inambao2 1,2University of Kwazulu-Natal Durban South-Africa. Abstract HPL High Pressure Loop EGR The transport service industry is a heavy user of diesel IDICI Indirect Injection Compression Ignition propelled engines as prime movers of goods and services. The diesel propelled engine is praised due to its high fuel efficiency, L Length or Piston Stroke reliability and durability. However, the nitrogen emissions as a result of diesel fuel combustion characteristics raise major LPL Low Pressure Loop EGR concerns for the manufacturing industry, environmentalists and health care researchers. The manner in which diesel engines M Organic Residue combust their fuel is the main cause of the nitrogen oxide NG Natural Gas emission proportion. Although there are other sources of nitrogen oxide emission, this work will cover the sources of NO Nitrogen Oxide nitrogen oxides and their formation within the diesel engine, their routes of formation, identify the mechanisms under which NOX Oxides of Nitrogen Excluding Nitrogen Trioxide the formations occur, identify their types and interactions, look Up at the various effects of the oxides of nitrogen on human health and the overall damage to the natural environment, and look OH Water or Hydroxide Radical critically at control systems. -
Nitrogen Oxide - Wikipedia, the Free Encyclopedia Page 1 of 3
Nitrogen oxide - Wikipedia, the free encyclopedia Page 1 of 3 Nitrogen oxide From Wikipedia, the free encyclopedia Nitrogen oxide can refer to a binary compound of oxygen and nitrogen, or a mixture of such compounds: Contents ■ Nitric oxide (NO), nitrogen(II) oxide ■ Nitrogen dioxide (NO2), nitrogen(IV) oxide ■ 1 NOx ■ Nitrous oxide (N2O), nitrogen(I) oxide ■ 2 Derivatives ■ Nitrate radical (NO3), nitrogen(VI) oxide ■ 3 See also ■ Dinitrogen trioxide (N2O3), nitrogen(II,IV) oxide ■ 4 References ■ Dinitrogen tetroxide (N2O4), nitrogen(IV) oxide ■ Dinitrogen pentoxide (N2O5), nitrogen(V) oxide In atmospheric chemistry and air pollution and related fields, nitrogen oxides refers specifically to NOx [1][2] (NO and NO2). Only the first three of these compounds can be isolated at room temperature. N2O3, N2O4, and N2O5 all decompose rapidly at room temperature. Nitrate radical is very reactive. N2O is stable and rather unreactive at room temperature, while NO and NO2 are quite reactive but nevertheless quite stable when isolated. Dinitrogen trioxide, Nitric oxide, NO Nitrogen dioxide, NO2 Nitrous oxide, N2O N2O3 Dinitrogen tetroxide, Dinitrogen pentoxide, N2O4 N2O5 http://en.wikipedia.org/wiki/Nitrogen_oxide 11/2/2010 Nitrogen oxide - Wikipedia, the free encyclopedia Page 2 of 3 NOx Main article: NOx NOx (often written NOx) refers to NO and NO2. They are produced during combustion, especially at high temperature. These two chemicals are important trace species in Earth's atmosphere. In the troposphere, during daylight, NO reacts with partly oxidized organic species (or the peroxy radical) to form NO2, which is then photolyzed by sunlight to reform NO: NO + CH3O2 → NO2 + CH3O NO2 + sunlight → NO + O The oxygen atom formed in the second reaction then goes on to form ozone; this series of reactions is the main source of tropospheric ozone. -
Nitrogen Oxides
Pollution Prevention and Abatement Handbook WORLD BANK GROUP Effective July 1998 Nitrogen Oxides Nitrogen oxides (NOx) in the ambient air consist 1994). The United States generates about 20 mil- primarily of nitric oxide (NO) and nitrogen di- lion metric tons of nitrogen oxides per year, about oxide (NO2). These two forms of gaseous nitro- 40% of which is emitted from mobile sources. Of gen oxides are significant pollutants of the lower the 11 million to 12 million metric tons of nitrogen atmosphere. Another form, nitrous oxide (N2O), oxides that originate from stationary sources, is a greenhouse gas. At the point of discharge about 30% is the result of fuel combustion in large from man-made sources, nitric oxide, a colorless, industrial furnaces and 70% is from electric utility tasteless gas, is the predominant form of nitro- furnaces (Cooper and Alley 1986). gen oxide. Nitric oxide is readily converted to the much more harmful nitrogen dioxide by Occurrence in Air and Routes of Exposure chemical reaction with ozone present in the at- mosphere. Nitrogen dioxide is a yellowish-or- Annual mean concentrations of nitrogen dioxide ange to reddish-brown gas with a pungent, in urban areas throughout the world are in the irritating odor, and it is a strong oxidant. A por- range of 20–90 micrograms per cubic meter (µg/ tion of nitrogen dioxide in the atmosphere is con- m3). Maximum half-hour values and maximum 24- verted to nitric acid (HNO3) and ammonium hour values of nitrogen dioxide can approach 850 salts. Nitrate aerosol (acid aerosol) is removed µg/m3 and 400 µg/m3, respectively. -
Aqueous Catalytic Disproportionation and Oxidation of Nitric Oxide
Environ. Sci. Technol. 1998, 32, 876-881 Noncatalytic oxidation/reduction and absorption tech- Aqueous Catalytic niques (chemical scrubbing) have the advantage of being able to eliminate both NOx and SOx simultaneously (5, 6). Disproportionation and Oxidation of The primary impediment to their industrial application has Nitric Oxide been the low solubility of NO in aqueous solution. Because nitric oxide is 90-95% of the NOx present in typical flue gas streams (7), it has been necessary to preoxidize NO to NO2 JOSEPH H. MACNEIL, before the scrubber. Direct oxidation with O occurs slowly POLLY A. BERSETH, 2 at the low NO concentrations present in exhaust streams. GLENN WESTWOOD, AND The additional complexity and expense of using alternative WILLIAM C. TROGLER* - oxidants, such as OCl and H2O2, have prevented widespread Department of Chemistry and Biochemistry, University of use of this method. Other approaches to treating NO in California at San Diego, La Jolla, California 92093-0358 aqueous scrubbers have included the addition of heavy metal chelators to sequester nitric oxide for subsequent removal (8) and even the addition of yellow phosphorus emulsions Nitric oxide, a byproduct of combustion exhaust, is a key and O2 to oxidize nitric oxide to a combination of nitrite and nitrate salts (9). species that leads to urban photochemical smog. Nitric oxide exhibits low aqueous solubility, and it has proved In this paper we report a novel catalytic approach for difficult to remove NO from gas streams by aqueous scrubbing removing NO in aqueous solution with supported palladium or platinum metal. The catalysts display activity at ambient methods. -
Oxidation State Slides.Key
Oxidation States Dr. Sobers’ Lecture Slides The Oxidation State Also known as the oxidation number The oxidation state is used to determine whether an element has been oxidized or reduced. The oxidation state is not always a real, quantitative, physical constant. The oxidation state can be the charge on an atom: 2+ - MgCl2 Mg Cl Oxidation State: +2 -1 2 The Oxidation State For covalently bonded substances, it is not as simple as an ionic charge. A covalent bond is a sharing of electrons. The electrons are associated with more than one atomic nuclei. This holds the nuclei together. The electrons may not be equally shared. This creates a polar bond. The electronegativity of a covalently bonded atom is its ability to attract electrons towards itself. 3 Example: Chlorine Sodium chloride is an ionic compound. In sodium chloride, the chloride ion has a charge and an oxidation state of -1. The oxidation state of sodium is +1. 4 Example: Chlorine In a chlorine molecule, the chlorine atoms are covalently bonded. The two atoms share electrons equally and the oxidation state is 0. 5 Example: Chlorine The two atoms of a hydrogen chloride molecule are covalently bonded. The electrons are not shared equally because chlorine is more electronegative than hydrogen. There are no ions but the oxidation state of chlorine in HCl is -1 and the oxidation state of hydrogen is +1. 6 7 Assigning Oxidation States See the handout for the list of rules. Rule 1: Free Elements Free elements have an oxidation state of zero Example Oxidation State O2(g) 0 Fe(s) 0 O3(g) 0 C(graphite) 0 C(diamond) 0 9 Rule 2: Monatomic Ions The oxidation state of monatomic ions is the charge of the ion Example Oxidation State O2- -2 Fe3+ +3 Na+ +1 I- -1 V4+ +4 10 Rule 3: Fluorine in Compounds Fluorine in a compound always has an oxidation state of -1 Example Comments and Oxidation States NaF These are monatomic ions. -
Chapter 10 Acronyms.Pdf
10. Acronyms °C Degrees Celsius (Centigrade) µm Micrometer (micron) 1D One dimensional 3D Three dimensional 3GAHHS Third-generation advanced high-strength steels A Ampere A/C Air conditioning ABR Advanced Battery Research AC Alternating current ACE Advanced Combustion Engines (VTO program) ACEC Advanced Combustion and Emissions Control ACI Advanced compression ignition ADAS Advanced Driver Assistance Systems ADP Advanced drying process AEC Advanced engine combustion AEC Automotive Electronics Council AEV All-electric vehicle AFDC Alternative Fuels Data Center AFV Alternative fuel vehicle Ag Silver Ah Ampere-hour AHHS Advanced high-strength steels AIM Accelerated insertion of materials AKI Anti-knock index Al Aluminum ALD Atomic layer deposition AlF3 Aluminum fluoride AlNiCo Aluminum-nickel-cobalt AMR Annual Merit Review AMT Air maintenance technology AMT Automated manual transmission ANL Argonne National Laboratory APEEM Advanced Power Electronics and Electric Motors API American Petroleum Institute API Application programming interface APS Advanced photon source APTA American Public Transportation Association ARA Automotive Recyclers Association ARC Affordable Rankine cycle ARK Abuse reaction kinetics ARL Army Research Laboratory Acronyms 10-1 2016 ANNUAL MERIT REVIEW, VEHICLE TECHNOLOGIES OFFICE ARPA-E Advanced Research Projects Agency - Energy ASCR Advanced scientific computing research ASI Area specific impedance ASSERT Analysis of Sustainability, Scale, Economics, Risk, and Trade ASTM American Society for Testing and Materials ATF -
Kinetics of Nitrogen Oxide Reduction by Means of Ammonia on a Polish Carbon Sorbent
Polish Journal of Environmental Studies Vol. 11, No. 6 (2002), 689-693 Kinetics of Nitrogen Oxide Reduction by Means of Ammonia on a Polish Carbon Sorbent K. Jastrz¹b*, J. Szarawara aculty of Chemistry, Silesian University of Technology, 44-100 Gliwice, B. Krzywoustego Str. 6, Poland, Received: 16 January, 2002 Accepted: 13 May, 2002 Abstract This paper studies nitrogen oxide reduction by means of ammonia in a flow reactor with a fixed bed of the Polish carbon sorbent AKP-5. The kinetic curves â(t), showing the dependence of the degree of reduction of nitrogen oxide on time have been determined for four inlet NO concentrations. On the basis of the degree of NO reduction determined for the steady state conditions, a simplified model of the kinetic equation has been developed and verified. The results obtained are very important for environmental protection. Keywords: nitrogen oxides, carbon sorbent, selective catalytic reduction, kinetics of reaction Introduction of reactants), the physical adsorption and chemisorption of the substrates on the surface, and a series of catalytic surface The process based on the use of specially prepared reactions. Moreover, the process occurs according to carbon sorbents (so-called active cokes) is an interesting a complex chemical mechanism [7]. In the case of the SCR modification of the selective catalytic reduction (SCR) process, the reduction of NO by ammonia is most often x method. In this process the sorbent plays a double role: described by the following overall equation: it is both an adsorbent of nitrogen oxides and a classical catalyst of NO reduction. An advantage of this method is 4 NO + 4 NH + O = 4 N + 6 H O (1) x 3 2 2 2 the low temperature of the process (100 ÷ 170°C). -
Nitrogen Oxide Emissions from Air Traffic
TECHNOLOGIE 369 CHIMIA 44 (1990) Nr. II (November) Chimia 44 (1990) 369-371 ~'1Schwei=. Chemiker-Verband; ISSN 0009-4293 Nitrogen Oxide Emissions from Air Traffic Robert A. Egli* Rober! A. Eg/i: Born 1926 in Rheineck, Switzer- land. After completing his chemistry education at the HTL Winterthur (1948), he worked for 10years as a group leader in an organic synthesis laboratory for Ci/og AG in Schaffhausen, later as head of the Ahstract. About 153 million metric tons of aviation fuel were consumed in 1987, which analytical development laboratory, and in addition was ca. ]3% of the world's consumption of transportation fuel. Burning this fuel to this job. for 13 years quality control director of Ci/ag AG. From 1985 to 1989, he was responsible produced ca. 2.75 million tons of nitrogen oxides, calculated as N0 , using an average 2 for patents, library, and literature searches. He emission index £1 of 18 g N02 per kg fuel. 0.92 million tons of N02 was exhausted published 17 papers, mainly in the field of organic between 9 and 13 km, which is an especially endangered altitude range, estimated with an analytical chemistry. Since January 1990, Egli is £f of 15 g N02 per kg fuel. Air traffic is the main NO, source between 9 and 13 km. Since working as an independent consultant. For many the NO, background concentration at this altitude is low and the possible lifetime of an years, his special interests have been air pollution problems and climatology. admixture two orders of magnitude larger compared to the ground, these NO .•emissions can lead to an important increase of tropospheric ozone, which contributes to the g]obal greenhouse warming. -
Structure-Property Relationships of Layered Oxypnictides
AN ABSTRACT OF THE DISSERTATION OF Sean W. Muir for the degree of Doctor of Philosophy in Chemistry presented on April 17, 2012. Title: Structure-property Relationships of Layered Oxypnictides Abstract approved:______________________________________________________ M. A. Subramanian Investigating the structure-property relationships of solid state materials can help improve many of the materials we use each day in life. It can also lead to the discovery of materials with interesting and unforeseen properties. In this work the structure property relationships of newly discovered layered oxypnictide phases are presented and discussed. There has generally been worldwide interest in layered oxypnictide materials following the discovery of superconductivity up to 55 K for iron arsenides such as LnFeAsO1-xFx (where Ln = Lanthanoid). This work presents efforts to understand the structure and physical property changes which occur to LnFeAsO materials when Fe is replaced with Rh or Ir and when As is replaced with Sb. As part of this work the solid solution between LaFeAsO and LaRhAsO was examined and superconductivity is observed for low Rh content with a maximum critical temperature of 16 K. LnRhAsO and LnIrAsO compositions are found to be metallic; however Ce based compositions display a resistivity temperature dependence which is typical of Kondo lattice materials. At low temperatures a sudden drop in resistivity occurs for both CeRhAsO and CeIrAsO compositions and this drop coincides with an antiferromagnetic transition. The Kondo scattering temperatures and magnetic transition temperatures observed for these materials can be rationalized by considering the expected difference in N(EF)J parameters between them, where N(EF) is the density of states at the Fermi level and J represents the exchange interaction between the Ce 4f1 electrons and the conduction electrons. -
Enrichment of Denitrifying Bacterial Community Using Nitrite As an Electron Acceptor for Nitrogen Removal from Wastewater
water Article Enrichment of Denitrifying Bacterial Community Using Nitrite as an Electron Acceptor for Nitrogen Removal from Wastewater Renda Yao, Quan Yuan and Kaijun Wang * State Key Joint Laboratory of Environment Simulation and Pollution Control, School of Environment, Tsinghua University, Beijing 100084, China; [email protected] (R.Y.); [email protected] (Q.Y.) * Correspondence: [email protected]; Tel.: +86-10-6278-9411 Received: 31 October 2019; Accepted: 17 December 2019; Published: 20 December 2019 Abstract: This work aimed to enrich a denitrifying bacterial community for economical denitrification via nitrite to provide the basic objects for enhancing nitrogen removal from wastewater. A sequencing batch reactor (SBR) with continuous nitrite and acetate feeding was operated by reasonably adjusting the supply rate based on the reaction rate, and at a temperature of 20 2 C, pH of 7.5 0.2, ± ◦ ± and dissolved oxygen (DO) of 0 mg/L. The results revealed that the expected nitrite concentration can be achieved during the whole anoxic reaction period. The nitrite denitrification rate of nitrogen removal from synthetic wastewater gradually increased from approximately 10 mg/(L h) to 275.35 mg/(L h) over 12 days (the specific rate increased from 3.83 mg/(g h) to 51.80 mg/(g h)). Correspondingly, the chemical oxygen demand/nitrogen (COD/N) ratio of reaction decreased from 7.9 to 2.7. Both nitrite and nitrate can be used as electron acceptors for denitrification. The mechanism of this operational mode was determined via material balance analysis of substrates in a typical cycle. High-throughput sequencing showed that the main bacterial community was related to denitrification, which accounted for 84.26% in the cultivated sludge, and was significantly higher than the 2.16% in the seed sludge. -
Plutonium Is a Physicist's Dream but an Engineer's Nightmare. with Little
Plutonium An element at odds with itself lutonium is a physicist’s dream but an engineer’s nightmare. With little provocation, the metal changes its density by as much as 25 percent. It can Pbe as brittle as glass or as malleable as aluminum; it expands when it solidi- fies—much like water freezing to ice; and its shiny, silvery, freshly machined surface will tarnish in minutes. It is highly reactive in air and strongly reducing in solution, forming multiple compounds and complexes in the environment and dur- ing chemical processing. It transmutes by radioactive decay, causing damage to its crystalline lattice and leaving behind helium, americium, uranium, neptunium, and other impurities. Plutonium damages materials on contact and is therefore difficult to handle, store, or transport. Only physicists would ever dream of making and using such a material. And they did make it—in order to take advantage of the extraordinary nuclear properties of plutonium-239. Plutonium, the Most Complex Metal Plutonium, the sixth member of the actinide series, is a metal, and like other metals, it conducts electricity (albeit quite poorly), is electropositive, and dissolves in mineral acids. It is extremely dense—more than twice as dense as iron—and as it is heated, it begins to show its incredible sensitivity to temperature, undergoing dramatic length changes equivalent to density changes of more than 20 percent. Six Distinct Solid-State Phases of Plutonium Body-centered orthorhombic, 8 atoms per unit cell Face-centered cubic, 4 atoms per unit cell Body-centered monoclinic, Body-centered cubic, 8 34 atoms per unit cell 2 atoms per unit cell δ δ′ ε Contraction on melting 6 γ L L 4 β Monoclinic, 16 atoms per unit cell Anomalous Thermal Expansion and Phase Instability of Plutonium Length change (%) 2 Pure Pu Pure Al α 0 200 400 600 800 Temperature (°C) 16 Los Alamos Science Number 26 2000 Plutonium Overview Table I.