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Автор: Grafiati
Опубліковано: 6 вересня 2023

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Статті в журналах з теми "Oxide - Nitrogen"

1

Stein, Lisa Y., and Martin G. Klotz. "Nitrifying and denitrifying pathways of methanotrophic bacteria." Biochemical Society Transactions 39, no. 6 (November 21, 2011): 1826–31. http://dx.doi.org/10.1042/bst20110712.

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Nitrous oxide, a potent greenhouse gas and ozone-depleting molecule, continues to accumulate in the atmosphere as a product of anthropogenic activities and land-use change. Nitrogen oxides are intermediates of nitrification and denitrification and are released as terminal products under conditions such as high nitrogen load and low oxygen tension among other factors. The rapid completion and public availability of microbial genome sequences has revealed a high level of enzymatic redundancy in pathways terminating in nitrogen oxide metabolites, with few enzymes involved in returning nitrogen oxides to dinitrogen. The aerobic methanotrophic bacteria are particularly useful for discovering and analysing diverse mechanisms for nitrogen oxide production, as these microbes both nitrify (oxidize ammonia to nitrite) and denitrify (reduce nitrate/nitrite to nitrous oxide via nitric oxide), and yet do not rely on these pathways for growth. The fact that methanotrophs have a rich inventory for nitrogen oxide metabolism is, in part, a consequence of their evolutionary relatedness to ammonia-oxidizing bacteria. Furthermore, the ability of individual methanotrophic taxa to resist toxic intermediates of nitrogen metabolism affects the relative abundance of nitrogen oxides released into the environment, the composition of their community, and the balance between nitrogen and methane cycling.
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2

Duke, Trevor, Mike South, and Alastair Stewart. "Altered activation of the L-arginine nitric oxide pathway during and after cardiopulmonary bypass." Perfusion 12, no. 6 (December 1997): 405–10. http://dx.doi.org/10.1177/026765919701200609.

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The serum concentrations of nitrogen oxides, the stable metabolites of nitric oxide, were measured in 61 children during and after cardiopulmonary bypass (CPB) for surgery of congenital heart disease. Overall, there was a small reduction in serum nitrogen oxide concentrations during CPB, from a median of 27.5 (interquartile range 16.6-55.7) to 26.4 (15.3-40.6) μmol/l, followed by an increase in the following 24 h to 33.1 (21.3-46.7) μmol/l. The largest postoperative increases in nitrogen oxides occurred in children who developed renal impairment, or were treated with nitrovasodilators. There was no relationship between changes in serum nitrogen oxides intraoperatively and early changes in pulmonary vascular resistance, and a weak positive relationship between changes in serum nitrogen oxides and early postoperative changes in cardiac index ( r2 = 0.09, p = 0.04). We found no evidence for increased activation of the L-arginine nitric oxide pathway during CPB; and the reduction in nitric oxide metabolites that occurred during CPB were of doubtful significance to pulmonary or systemic haemodynamic changes in the postoperative period.
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3

VALVINI, E. M., and J. D. YOUNG. "Serum nitrogen oxides during nitric oxide inhalation." British Journal of Anaesthesia 74, no. 3 (March 1995): 338–39. http://dx.doi.org/10.1093/bja/74.3.338.

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4

Ongar, Bulbul, Hristo Beloev, Iliya Iliev, Assem Ibrasheva, and Anara Yegzekova. "Numerical simulation of nitrogen oxide formation in dust furnaces." EUREKA: Physics and Engineering, no. 1 (January 10, 2022): 23–33. http://dx.doi.org/10.21303/2461-4262.2022.002102.

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Even though natural sources of air pollution account for over 50 % of sulphur compounds, 93 % of nitrogen oxide which are the most dangerous artificial anthropogenic sources of air pollution and primarily associated with the combustion of fossil fuel. Coal-fired thermal power plants and industrial fuel-burning plants that emit large quantities of nitrogen oxides (NО and NО2), solids (ash, dust, soot), as well as carbon oxides, aldehydes, organic acids into the atmosphere pollute the environment in majority. In the present work, a mathematical model and a scheme for calculating the formation of nitrogen oxide has been developed. Also, the dependence of the rate of release of fuel nitrogen from coal particles at the initial stage of gasification and content of volatiles has been obtained. The main regularities of the formation of NOx at the initial section of the flame in the ignition zone of the swirl burner flame during the combustion of Ekibastuz coal have been revealed. Modern environmental requirements for the modernization of existing and the creation of new heat and power facilities determine the exceptional relevance of the development of effective methods and constructions to reduce emissions of nitrogen oxides, sulfur oxides and ash to 200, 300, and 100 mg/nm3 at a=1.4. The dust consumption in all experiments was kept constant and amounted to 0.042 g/s, as well as with the results of calculating the thermal decomposition of the Ekibastuz coal dust, the recombination of atomic nitrogen into nitrogen molecules, and the kinetics of the formation of fuel nitric oxide. It was found that despite the presence of oxygen in Ekibastuz coal for gases Odaf=11.8 % in an inert atmosphere, nitrogen oxides are not formed
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5

Ongar, Bulbul, Iliya K. Iliev, Vlastimir Nikolić, and Aleksandar Milašinović. "THE STUDY AND THE MECHANISM OF NITROGEN OXIDES’ FORMATION IN COMBUSTION OF FOSSIL FUELS." Facta Universitatis, Series: Mechanical Engineering 16, no. 2 (August 1, 2018): 273. http://dx.doi.org/10.22190/fume171114026o.

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The burning of all fossil fuels is accompanied by the production of large quantities of nitrogen oxides. Nitrogen oxide from coal combustion is formed from the molecular nitrogen in the air and the nitrogen contained in the fuel. In accordance with the mechanism of formation of nitric oxide from fuel, it is desirable to increase the concentration of coal dust in the flame. The thermal regime of combustion accelerates the release of volatiles, with flames spreading out and the coke residue contributes to the chemical reduction of NOx. In this work we consider the specific issues of the formation mechanism of NOx fuel and ways to reduce their atmospheric emissions. Presented are results from the calculation of the influence of the following on the level of nitric oxides during coal combustion: temperature, oxygen concentration and time of release of fuel nitrogen. It has been established that the influence of nitric oxide fuel on the total nitric oxide emissions is more noticeable at low temperatures of the combustion process.
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6

Kitzler, B., S. Zechmeister-Boltenstern, C. Holtermann, U. Skiba, and K. Butterbach-Bahl. "Nitrogen oxides emission from two beech forests subjected to different nitrogen loads." Biogeosciences Discussions 2, no. 5 (September 9, 2005): 1381–422. http://dx.doi.org/10.5194/bgd-2-1381-2005.

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Abstract. We analysed nitrogen oxides (N2O, NO and NO2) and carbon dioxide (CO2) emissions from two beech forest soils close to Vienna, Austria, which were exposed to different nitrogen input from the atmosphere. The site Schottenwald (SW) received 22.6 kg N y-1 and Klausenleopoldsdorf (KL) 13.5 kg N y-1 through wet and dry deposition. Nitrogen oxide emissions from soil were measured hourly with an automatic dynamic chamber system. Daily N2O measurements were carried out by an automatic gas sampling system. Measurements of nitrous oxide (N2O) and CO2 emissions were conducted over larger areas on a biweekly (SW) or monthly (KL) basis by manually operated chambers. We used an autoregression procedure (time-series analysis) for establishing time-lagged relationships between N-oxide emissions and different climate, soil chemistry and N-deposition data. It was found that changes in soil moisture and soil temperature significantly effected CO2 and N-oxide emissions with a time lag of up to two weeks and could explain up to 95% of the temporal variations of gas emissions. Event emissions after rain or during freezing and thawing cycles contributed significantly (for NO 50%) to overall N-oxides emissions. In the two-year period of analysis the annual gaseous N2O losses at SW ranged from 0.65 to 0.77 kg N ha-1 y-1 and NO losses were 0.18 to 0.67 kg N ha-1 per vegetation period. In KL significantly lower annual N2O emissions (0.52 kg N2O-N kg ha-1 y-1) as well as considerably lower NO-losses were observed. During a three-month measurement campaign NO losses at KL were 0.02 kg, whereas in the same time period significantly more NO was emitted in SW (0.32 kg NO-N ha-1). Higher N-oxide emissions, especially NO emissions from the high N-input site (SW) indicate that atmospheric deposition had a strong impact on losses of gaseous N from our forest soils. At KL there was a strong correlation between N-deposition and N-emission over time, which shows that low N-input sites are especially responsive to increasing N-inputs.
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7

Rudakov, Marat, Ruslan Babkin, and Ekaterina Medova. "Improvement of Working Conditions of Mining Workers by Reducing Nitrogen Oxide Emissions during Blasting Operations." Applied Sciences 11, no. 21 (October 25, 2021): 9969. http://dx.doi.org/10.3390/app11219969.

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The article presents comparison of the values of maximum permissible concentrations, revealed during the analysis of the national standards of Russia and Australia in the field of regulation of nitrogen oxides. The impact of poisoning of the workers of the quarry with nitrogen oxides after blasting operations are presented. A detailed review of studies of methods for reducing nitrogen oxide emissions is given. The way of decreasing emission of nitrogen oxides using highly active catalysts as a part of the profiled tamping is offered. Laboratory studies were carried out using a model explosive and pentaerythritol tetranitrate. The results obtained showed that zinc carbonate (ZnCO3) is the most effective. The reduction in the amount of nitrogen oxide emissions was 40% of that released during experiments without the addition of catalysts.
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8

Davydov, Evgeniy, Georgiy Pariiskii, Iryna Gaponova, Tatyana Pokholok, and Gennady Zaikov. "Polymers in polluted atmosphere. Free radical and ion-radical conversions initiated by nitrogen oxides." Chemistry & Chemical Technology 2, no. 1 (March 15, 2008): 33–45. http://dx.doi.org/10.23939/chcht02.01.033.

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Nitric oxide, nitrogen dioxide, nitrogen trioxide as well as dimers of nitrogen dioxide are reactive initiators of radical transformations of macromolecules and modifying reactants for polymers. Features of the initiation mechanism determining the composition of molecular and radical products in polymers under the action of nitrogen oxides are discussed.
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9

Rotondaro, A. L. Pacheco, R. T. Laaksonen, and S. P. Singh. "Impact of the Nitrogen Concentration of Sub-1.3 nm Gate Oxides on 65 nm Technology Transistor Parameters." Journal of Integrated Circuits and Systems 2, no. 2 (November 17, 2007): 63–66. http://dx.doi.org/10.29292/jics.v2i2.265.

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The nitrogen concentration of ultrathin gate oxides (sub-1.3 nm) was varied in a wide range (from 13 % to 23 %). The threshold voltage and the channel carrier mobility of advanced 65 nm technology CMOSFET transistors fabricated with these oxides were analyzed. It was observed that increasing the nitrogen concentration in the gate oxide results in a negative shift of the threshold voltage for both NMOS and PMOS devices and a degradation of the hole mobility. It was also observed that pchannel transistors are more sensitive to the nitrogen concentration of the gate oxide than n-channel transistors.
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10

Zhang, G., E. I. Papaioannou, and I. S. Metcalfe. "Selective, high-temperature permeation of nitrogen oxides using a supported molten salt membrane." Energy & Environmental Science 8, no. 4 (2015): 1220–23. http://dx.doi.org/10.1039/c4ee02256d.

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Nitrate/ceramic membranes were designed for selective nitrogen oxide permeation. These membranes exhibited selective permeation of nitrogen oxides over carbon dioxide and could be employed in e.g. sensing technologies.
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Дисертації з теми "Oxide - Nitrogen"

1

Li, Sonny X. "Nitrogen doped zinc oxide thin film." Berkeley, Calif. : Oak Ridge, Tenn. : Lawrence Berkeley National Laboratory ; distributed by the Office of Scientific and Technical Information, U.S. Dept. of Energy, 2003. http://www.osti.gov/servlets/purl/821916-VLVAK9/native/.

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Thesis (M.S.); Submitted to the University of California, Berkeley, 210 Hearst Mining Memorial Bldg., Berkeley, CA 94720 (US); 15 Dec 2003.
Published through the Information Bridge: DOE Scientific and Technical Information. "LBNL--54116" Li, Sonny X. USDOE Director. Office of Science. Basic Energy Sciences (US) 12/15/2003. Report is also available in paper and microfiche from NTIS.
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2

Jewmaidang, Jirasak. "Homogeneous sulfur tri-oxide formation in gas reburning for nitrogen oxides control." Ohio : Ohio University, 1999. http://www.ohiolink.edu/etd/view.cgi?ohiou1175801641.

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3

Skinn, Brian Thomas. "Nitrogen oxide delivery systems for biological media." Thesis, Massachusetts Institute of Technology, 2012. http://hdl.handle.net/1721.1/70107.

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Анотація:
Thesis (Ph. D.)--Massachusetts Institute of Technology, Dept. of Chemical Engineering, 2012.
This electronic version was submitted by the student author. The certified thesis is available in the Institute Archives and Special Collections.
Cataloged from student-submitted PDF version of thesis.
Includes bibliographical references (p. 345-363).
Elevated levels of nitric oxide (NO) in vivo are associated with a variety of cellular modifications thought to be mutagenic or carcinogenic. These processes are likely mediated by reactive nitrogen species (RNS) such as nitrogen dioxide (NO2) and peroxynitrite formed from the respective reactions of NO with oxygen and superoxide anion. Controlled delivery of these RNS at levels expected to occur in vivo is desirable in studying these processes and their role in the etiology of various diseases. Two delivery systems were developed that provide novel capabilities for steady, quantitative exposure of biological targets to RNS over periods from hours to days. Quantitative models are presented that accurately describe the behavior of both systems. The first system achieves NO concentrations of 0.6-3.0 [mu]M in a stirred, liquid-filled vessel by diffusion from a gas stream through a porous poly(tetrafluoroethylene) membrane. Oxygen, consumed by reaction with NO or by other processes, is supplied by diffusion from a separate gas stream through a loop of poly(dimethylsiloxane) tubing. The adventitious chemistry observed in a prior device for NO delivery [Wang C. Ann Biomed Eng (2003) 31:65-79] is eliminated in the present design, as evidenced by the close match to model predictions of the accumulation rate of nitrite, the stable end product of NO oxidation. The second system delivers NO2 by direct contacting of a stirred liquid with an NO2- containing gas mixture. Accumulation rates of products in the presence and absence of the NO2-reactive substrate 2,2'-azino-bis(3-ethylbenzothiazoline-6-sulfonate) matched model predictions within 15% for all conditions studied. The predicted steady NO2 concentration in the liquid is on the order of 400 pM, similar to what is expected to be present in extracellular fluids in the presence of 1 [mu]M NO. This system appears to be the first reported with the capability for sustained, quantitative NO2 delivery to suspended cell cultures. Results from initial efforts to test a novel mixing model for bolus delivery of peroxynitrite to agitated solutions imply that the proposed model might accurately describe mixing in bolus delivery experiments with agitation by vortex mixing, but further work is required to validate the model.
by Brian Thomas Skinn.
Ph.D.
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4

Mereb, Jamal Bocher. "Nitrogen oxide abatement by distributed fuel addition." Diss., The University of Arizona, 1991. http://hdl.handle.net/10150/185383.

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Reburning is examined as a means of NOₓ destruction in a 17 kW down-fired pulverized coal combustor. In reburning, a secondary fuel is introduced downstream of the primary flame to produce a reducing zone, favorable to NO destruction, and air is introduced further downstream to complete the combustion. Emphasis is on natural gas reburning and a bituminous coal primary flame. A parametric examination of reburning employing a statistical experimental design, is conducted, complemented by detailed experiments. Mechanisms governing the inter-conversion of nitrogenous species in the fuel rich reburn zone are explored. The effect of reburning on N₂O emissions, the effect of primary flame mode (premixed and diffusion) and the effect of distributing the reburning fuel, are also investigated. The parametric study allowed the effects of significant reburning variables to be identified and examined, but these effects could not be quantified. Detailed experiments identified optimum reburn zone stoichiometry between 0.8 and 0.9, depending on mixing in the reburn zone. Overall NO reductions, as high as 80%, were possible and depended mainly on reburn zone variables, namely, temperature, residence time and stoichiometry. Exhaust N₂O emissions increased after air addition in the final stage of reburning, but were less than 10 ppm. Lower reductions in NO emissions were obtained when the primary flame was of the diffusion type, rather than of the premixed type, but final NO emissions below 250 ppm (dry, 0% O₂) were still possible. Reburning fuel introduction in multiple streams did not enhance NO destruction, relative to single stream injections. Within the reburn zone, reburning mechanisms occurred in two regimes. One regime was in the vicinity of the reburning fuel flame and was distinguished by fast reactions between NO and hydrocarbons that were limited by mixing. The other regime covered the remainder of the reburn zone and was distinguished by slower reactions, without mixing complications. For the latter regime, a simplified model based on detailed gas phase chemical kinetic mechanisms and known rate coefficients was able to predict temporal profiles of NO, HCN and NH₃. Reactions involving hydrocarbons played important roles in both regimes and N₂ fixation by hydrocarbons limited reburning effectiveness at low primary NO values. Appropriate corrections for mixing effects in early time scales of the reburn zone allowed the prediction of nitrogenous species profiles from primary NO values, as well as overall reburning effectiveness.
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5

Estupiñán, Edgar G. "Laboratory studies of potentially important atmospheric processes involving oxides of nitrogen." Diss., Georgia Institute of Technology, 2001. http://hdl.handle.net/1853/25877.

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6

Holmgreen, Erik Michael. "Nitrogen dioxide reduction with methane over palladium-based sulfated zirconia catalysts a componant [i.e. component] of a lean exhaust aftertreatement system /." Columbus, Ohio : Ohio State University, 2006. http://rave.ohiolink.edu/etdc/view?acc%5Fnum=osu1155739813.

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7

Wood, Simon Andrew. "Corrosion studies in liquid nitrogen oxides." Thesis, University of Nottingham, 1996. http://ethos.bl.uk/OrderDetails.do?uin=uk.bl.ethos.262774.

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8

Dunfield, Peter F. "Methane, nitrogen monoxide, and nitrous oxide fluxes in an organic soil." Thesis, National Library of Canada = Bibliothèque nationale du Canada, 1997. http://www.collectionscanada.ca/obj/s4/f2/dsk2/tape16/PQDD_0020/NQ36972.pdf.

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9

Gold, Scott Alan. "Nitrogen incorporation in thin silicon oxide films for passivation of silicon solar cell surfaces." Thesis, Georgia Institute of Technology, 1999. http://hdl.handle.net/1853/11101.

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10

Hannon, Andrew Michael. "Exploring the Reactivity and Decomposition of Ruthenium Nitrosyl Complexes for the Production of Nitrogen Oxides." Diss., The University of Arizona, 2012. http://hdl.handle.net/10150/243113.

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Nitric oxide (NO) has been shown to both suppress and promote tumor growth, depending in part on concentration. Exogenous delivery of NO may lead to tumor suppression. Recent studies have proposed ruthenium nitrosyl complexes as catalytic donors of NO in reductive environments. Catalytic donation can provide a long-term, elevated NO flux compared to single use donors. Site-specific delivery is desirable to reduce systemic side effects, such as lowering of blood pressure. Three new ruthenium nitrosyl complexes were synthesized to impart site-specificity through amide coupling to polymers, silica nanoparticles, iron oxide nanoparticles and antibodies. The catalytic activity of new and existing compounds was then assessed. However, upon one-electron reduction of ruthenium nitrosyl complexes, insignificant amounts of NO were detected, suggesting an alternative mechanism than that proposed in prior reports. The mechanism of [Ru(EDTA)NO]²⁻ decay was more thoroughly analyzed. Spectrophotometric decay of [Ru(EDTA)NO]²⁻ indicates that one or multiple nitrogen oxide species are released. Previous studies have suggested a disproportionation mechanism leading to the generation of more highly reduced species such as N₂ and NH₄⁺. Experiments were designed to analyze possible decomposition products such as [Ru(EDTA)NO]⁻ and [Ru(EDTA)H₂O]²⁻. A disproportionation mechanism was determined likely. Decomposition of [Ru(EDTA)NO]²⁻ was also observable following reductive nitrosylation of [Ru(EDTA)H₂O]⁻ in the presence of HNO. The decomposition product, [Ru(EDTA)H₂O]²⁻, was observed through the binding of pyrazine (pz) or dipyridine (bipy) and formation of [Ru(EDTA)pz]²⁻ or [Ru(EDTA)bipy]³⁻. Formation of [Ru(EDTA)bipy]³⁻ or [Ru(EDTA)pz]²⁻ via reductive nitrosylation of [Ru(EDTA)H₂O]⁻ also provides an indirect method of HNO detection that is selective from NO.
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Книги з теми "Oxide - Nitrogen"

1

1954-, Ozkan Umit S., Agarwal Sanjay K. 1965-, Marcelin George 1948-, American Chemical Society. Division of Petroleum Chemistry., and American Chemical Society Meeting, eds. Reduction of nitrogen oxide emissions. Washington, DC: American Chemical Society, 1995.

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2

Ozkan, Umit S., Sanjay K. Agarwal, and George Marcelin, eds. Reduction of Nitrogen Oxide Emissions. Washington, DC: American Chemical Society, 1995. http://dx.doi.org/10.1021/bk-1995-0587.

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3

Beggs, Thomas W. Nitrogen oxide control for stationary combustion sources. Cincinnati, OH: Office of Research and Development, U.S. Environmental Protection Agency, 1986.

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4

Pels, Jan Remmert. Nitrous oxide in coal combustion. Delft: Eburon, 1995.

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5

E, Galbally I., ed. The Measurement of nitrogen oxide (NO, NO2) exchange over plant/soil surfaces. [Melbourne, Vic.]: Commonwealth Scientific and Industrial Research Organization, 1985.

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6

L, Sloss Leslie, ed. Nitrogen oxides control technology fact book. Park Ridge, N.J., U.S.A: Noyes Data Corp., 1992.

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7

VHB Research and Consulting Inc., SENES Consultants Limited, and Ontario. Fiscal Planning and Economic Analysis Branch., eds. Nitrogen oxide and volatile organic compounds abatement cost study. Ontario: Queen's Printer, 1992.

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8

Martin, Feelisch, and Stamler Jonathan S, eds. Methods in nitric oxide research. Chichester: J. Wiley, 1996.

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9

Kjäldman, Lars. Numerical simulation of combustion and nitrogen pollutants in furnances. Espoo: Technical Research Centre of Finland, 1993.

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10

Hayat, Shamsul. Nitric oxide in plant physiology. Weinheim: Wiley-Blackwell, 2010.

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Частини книг з теми "Oxide - Nitrogen"

1

Pedler, A., F. H. Pollard, George Gibson, and Ilmar Kalnin. "Nitrogen(IV) Oxide." In Inorganic Syntheses, 87–91. Hoboken, NJ, USA: John Wiley & Sons, Inc., 2007. http://dx.doi.org/10.1002/9780470132364.ch24.

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2

Blanchard, Arthur A., C. M. Mason, and Robert L. Barnard. "Nitric Oxide [Nitrogen(II) Oxide]." In Inorganic Syntheses, 126–28. Hoboken, NJ, USA: John Wiley & Sons, Inc., 2007. http://dx.doi.org/10.1002/9780470132333.ch37.

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3

Reay, Dave. "Nitrous Oxide Sources." In Nitrogen and Climate Change, 49–68. London: Palgrave Macmillan UK, 2015. http://dx.doi.org/10.1057/9781137286963_5.

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4

Winkelmann, J. "Diffusion of nitrogen oxide." In Gases in Gases, Liquids and their Mixtures, 144. Berlin, Heidelberg: Springer Berlin Heidelberg, 2007. http://dx.doi.org/10.1007/978-3-540-49718-9_33.

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5

Winkelmann, J. "Diffusion of nitrogen (1); nitrogen oxide (2)." In Gases in Gases, Liquids and their Mixtures, 460. Berlin, Heidelberg: Springer Berlin Heidelberg, 2007. http://dx.doi.org/10.1007/978-3-540-49718-9_233.

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6

Jacyszyn, K., and W. Lesiecki. "Biological Response to Nitrogen Oxide." In Archives of Toxicology, 431. Berlin, Heidelberg: Springer Berlin Heidelberg, 1985. http://dx.doi.org/10.1007/978-3-642-69928-3_96.

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7

Ussiri, David, and Rattan Lal. "Global Nitrogen Cycle." In Soil Emission of Nitrous Oxide and its Mitigation, 29–62. Dordrecht: Springer Netherlands, 2012. http://dx.doi.org/10.1007/978-94-007-5364-8_2.

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8

Meilhoc, Eliane, Alexandre Boscari, Renaud Brouquisse, and Claude Bruand. "Multifaceted Roles of Nitric Oxide in Legume-Rhizobium Symbioses." In Biological Nitrogen Fixation, 637–48. Hoboken, NJ, USA: John Wiley & Sons, Inc, 2015. http://dx.doi.org/10.1002/9781119053095.ch64.

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Gruenhut, N. S., M. Goldfrank, M. L. Cushing, G. V. Caesar, P. D. Caesar, and C. Shoemaker. "Nitrogen(V) Oxide (Nitrogen Pentoxide, Dinitrogen Pentoxide, Nitric Anhydride)." In Inorganic Syntheses, 78–81. Hoboken, NJ, USA: John Wiley & Sons, Inc., 2007. http://dx.doi.org/10.1002/9780470132340.ch20.

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Voßwinkel, R., and H. Bothe. "Production of Nitrous Oxide and Nitric Oxide by Some Nitrate-Respiring Bacteria." In Inorganic Nitrogen in Plants and Microorganisms, 216–21. Berlin, Heidelberg: Springer Berlin Heidelberg, 1990. http://dx.doi.org/10.1007/978-3-642-75812-6_33.

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Тези доповідей конференцій з теми "Oxide - Nitrogen"

1

Yamamura, Karin, Liangchen Zhu, Curtis Irvine, Mandeep Singh, Vipul Bansal, John Scott, Matthew R. Phillips, Cuong Ton-That та Anirudh Jallandhra. "Luminescence signatures of nitrogen in β-Ga2O3 nanowires". У Oxide-based Materials and Devices XIII, редактори Ferechteh H. Teherani та David J. Rogers. SPIE, 2022. http://dx.doi.org/10.1117/12.2621466.

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2

Saruhan-Brings, B., and R. Lontio Fomekong. "P1GS.18 - BaTi-Oxides as High-Temperature Nitrogen Oxide Sensors." In 17th International Meeting on Chemical Sensors - IMCS 2018. AMA Service GmbH, Von-Münchhausen-Str. 49, 31515 Wunstorf, Germany, 2018. http://dx.doi.org/10.5162/imcs2018/p1gs.18.

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3

Dahake, Ashlesh P., Ranjay K. Singh, and Ajay V. Singh. "Nitrogen Oxide Formation Pathways in Gaseous Detonations." In 25th AIAA International Space Planes and Hypersonic Systems and Technologies Conference. Reston, Virginia: American Institute of Aeronautics and Astronautics, 2023. http://dx.doi.org/10.2514/6.2023-3014.

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4

Pukhtinskaya, Marina Gaevna, Vladimir Estrin, and Vladimir Estrin. "Prevention of Sepsis By Inhalation Nitrogen Oxide." In AAP National Conference & Exhibition Meeting Abstracts. American Academy of Pediatrics, 2021. http://dx.doi.org/10.1542/peds.147.3_meetingabstract.723.

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5

Zhang, Guiyin, and Yidong Jin. "Laser photo-acoustic detection of nitrogen oxide." In International Symposium on Photoelectronic Detection and Imaging: Technology and Applications 2007, edited by Liwei Zhou. SPIE, 2007. http://dx.doi.org/10.1117/12.790790.

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6

De Santi, Carlo, Manuel Fregolent, Matteo Buffolo, Masataka Higashiwaki, Gaudenzio Meneghesso, Enrico Zanoni, and Matteo Meneghini. "Deep levels and conduction processes in nitrogen-implanted Ga2O3 Schottky barrier diodes." In Oxide-based Materials and Devices XIII, edited by Ferechteh H. Teherani and David J. Rogers. SPIE, 2022. http://dx.doi.org/10.1117/12.2607613.

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7

Lopez-Estopier, R., M. Aceves-Mijares, Z. Yu, and C. Falcony. "Cathodoluminescence of Silicon Rich Oxide with nitrogen incorporated." In 2007 4th International Conference on Electrical and Electronics Engineering. IEEE, 2007. http://dx.doi.org/10.1109/iceee.2007.4345037.

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Seto, S. P., and T. F. Lyon. "Nitrogen Oxide Emissions Characteristics of Augmented Turbofan Engines." In ASME 1993 International Gas Turbine and Aeroengine Congress and Exposition. American Society of Mechanical Engineers, 1993. http://dx.doi.org/10.1115/93-gt-120.

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Анотація:
The exhaust plumes of modern military engines can be rendered visible at low augmentor power operation by the presence of nitrogen dioxide (NO2). Visible plumes have also been observed from some industrial gas turbines that have duct burners downstream of the power turbines. In 1986, gaseous emissions measurements were taken behind two F101 turbofan engines to determine the effect of reheat level on the degree of conversion of nitric oxide (NO) to nitrogen dioxide and to relate the plume visibility to nitrogen dioxide concentration.
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Zhao, Li, Yi Zhao, Lei Jiang, and Yin-jie Liu. "Removal of nitrogen oxide using nano-TiO2 photocatalyst." In 2011 6th IEEE Conference on Industrial Electronics and Applications (ICIEA). IEEE, 2011. http://dx.doi.org/10.1109/iciea.2011.5976046.

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Zhong, B. J., and P. V. Roslyakov. "NITROGEN DIOXIDE AND NITROUS OXIDE EMISSION IN FLAMES." In Energy and Environment, 1995. Connecticut: Begellhouse, 2023. http://dx.doi.org/10.1615/1-56700-052-5.890.

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Звіти організацій з теми "Oxide - Nitrogen"

1

Li, Sonny Xiao-zhe. Nitrogen doped zinc oxide thin film. Office of Scientific and Technical Information (OSTI), January 2003. http://dx.doi.org/10.2172/821916.

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Elliot R. Bernsteinq. Interactions of Neutral Vanadium Oxide & Titanium Oxide Clusters with Sufur Dioxides, Nitrogen Oxides and Water. Office of Scientific and Technical Information (OSTI), August 2006. http://dx.doi.org/10.2172/890716.

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Wendt, J. O. L., and J. B. Mereb. Nitrogen oxide abatement by distributed fuel addition. Office of Scientific and Technical Information (OSTI), February 1990. http://dx.doi.org/10.2172/5914332.

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Wendt, J. O. L., and J. B. Mereb. Nitrogen oxide abatement by distributed fuel addition. Office of Scientific and Technical Information (OSTI), February 1989. http://dx.doi.org/10.2172/5914370.

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Wendt, J. O. L., and J. Meraab. Nitrogen oxide abatement by distributed fuel addition. Office of Scientific and Technical Information (OSTI), September 1988. http://dx.doi.org/10.2172/5924326.

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Wendt, J. O. L., and J. B. Mereb. Nitrogen oxide abatement by distributed fuel addition. Office of Scientific and Technical Information (OSTI), December 1988. http://dx.doi.org/10.2172/5969378.

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Wendt, J. O. L., and J. Meraab. Nitrogen oxide abatement by distributed fuel addition. Office of Scientific and Technical Information (OSTI), March 1988. http://dx.doi.org/10.2172/5992497.

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Wendt, J., and J. Mereb. Nitrogen oxide abatement by distributed fuel addition. Office of Scientific and Technical Information (OSTI), November 1989. http://dx.doi.org/10.2172/6039249.

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Wendt, J. O. L., and J. B. Mereb. Nitrogen oxide abatement by distributed fuel addition. Office of Scientific and Technical Information (OSTI), August 1989. http://dx.doi.org/10.2172/6083896.

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Wendt, J. O. L., and J. B. Mereb. Nitrogen oxide abatement by distributed fuel addition. Office of Scientific and Technical Information (OSTI), August 1990. http://dx.doi.org/10.2172/6084414.

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