ライフサイエンスコーパス: nitrogen oxide

1 be conservation, rather than consumption, of nitrogen oxide.

2 a low level of oxygen and the presence of a nitrogen oxide.

3 ly been considered to be a permanent sink of nitrogen oxides.

4 mainly from a gas-phase source that consumes nitrogen oxides.

5 at a rate that increases in the presence of nitrogen oxides.

6 gene targets from the inhibitory activity of nitrogen oxides.

7 f isoprene, photolytically generated OH, and nitrogen oxides.

8 concentrations of nitrogen dioxide (NO2) and nitrogen oxides.

9 for a 5th to 95th difference in exposure to nitrogen oxides.

10 to the production of atmospherically active nitrogen oxides.

11 for HNO over other physiologically relevant nitrogen oxides.

12 cal effects of nitric oxide (NO) and related nitrogen oxides.

13 d bioactivities/cytotoxicities of endogenous nitrogen oxides.

14 rachidonic acid mediated by reactive radical nitrogen oxides.

15 ty approach and 0.5 ppbv by tagging reactive nitrogen oxides.

16 nificant role in the inter-transformation of nitrogen oxides.

17 d in locations with the highest emissions of nitrogen oxides.

18 soil nutrients and production of detrimental nitrogen oxides.

19 iations with exposure to carbon monoxide and nitrogen oxides.

20 and, during gestational weeks 1-20, 17% for nitrogen oxides, 10% for particulate matter with an aero

21 owever, there was no effect of L-arginine on nitrogen oxides (19.3+/-7.9 versus 18.6+/-6.7 micromol/L

22 e precursors (volatile organic compounds and nitrogen oxides), air toxics, and particulates.

23 show here a new surface-mediated coupling of nitrogen oxide and halogen activation cycles in which up

24 Elevated emissions of sulfur dioxide, nitrogen oxides and ammonia in China have resulted in hi

25 lters the emission ratios between NMVOCs and nitrogen oxides and hence the ozone chemistry in the eas

26 ion estimates of atmospheric species such as nitrogen oxides and methane.

27 ass-dependent) 17O enrichment to atmospheric nitrogen oxides and nitrate.

28 Atmospheric pollution measurements (nitrogen oxides and particulate matter) were combined wi

29 In the absence of both nitrogen oxides and reactive aqueous seed particles, we

30 OA) and how anthropogenic pollutants such as nitrogen oxides and sulfur affect this process are subje

31 In terms of the chemical species emitted, nitrogen oxides and sulfur dioxide emissions caused the

32 nnual or seasonal reductions in emissions of nitrogen oxides and sulfur dioxide from power plants.

33 t these genes are regulated by physiological nitrogen oxides and that the absence of these bacterial

34 lective catalytic reduction (SCR) of harmful nitrogen oxides and to unveil the SCR mechanism.

35 l addresses with land use regression models (nitrogen oxides) and interpolation from monitoring stati

36 to oxides of nitrogen (nitrogen dioxide and nitrogen oxides) and particulate matter (fine particulat

37 es are several that involve tyrosyl radical, nitrogen oxide, and superoxide ion or their mutual react

38 f levels of arginine, citrulline, ornithine, nitrogen oxides, and IL-10.

39 5), black carbon, sulfates, particle number, nitrogen oxides, and ozone by using fixed monitors, and

40 displaces significantly more sulfur dioxide, nitrogen oxides, and particulate matter than a panel in

41 ns of maternal exposure to nitrogen dioxide, nitrogen oxides, and particulate matter with aerodynamic

42 ion, vascular compliance, plasma and urinary nitrogen oxides, and plasma citrulline formation) were r

43 trations of carbon monoxide, carbon dioxide, nitrogen oxides, and sulfur dioxide are positively assoc

44 onsumption, emissions (i.e., carbon dioxide, nitrogen oxides, and sulfur oxides), and marginal heat r

45 ing active photochemistry in the presence of nitrogen oxides, and therefore with abundant formation o

46 sh burning contributions to carbon monoxide, nitrogen oxides, and volatile organic compounds were fou

47 Nitrogen oxides are essential for the formation of secon

48 ing the background tropospheric abundance of nitrogen oxides are likely responsible for the modeling

49 have established that peroxynitrite-derived nitrogen oxides are present following nNOS turnover.

50 ion to nitrosothiol, nitrite and atmospheric nitrogen oxides are sources of nitrogen oxide that react

51 Nitrogen oxides are textbook class of molecular compound

52 pollutant concentrations, carbon dioxide and nitrogen oxides are the best individual predictors, but

53 ial denitrification, a pathway that produces nitrogen oxides as alternate electron acceptors for anae

54 s responsible for the atmospheric removal of nitrogen oxides as well as the cycling of halogen specie

55 Outdoor concentrations of nitrogen oxides, as a marker of exhaust particles, and p

56 increases in tissue NOS activity and urinary nitrogen oxides, associated with a 2-fold reduction in p

57 diameter of 2.5 mum or less (PM(2).(5)) and nitrogen oxides at baseline (2000) in the Multi-Ethnic S

58 ains the observed levels of nitrous acid and nitrogen oxides at midday under typical marine boundary

59 so review potential clinical applications of nitrogen oxide biochemistry.

60 ease significant amounts of CO2 and reactive nitrogen oxides by abiotic oxidation.

61 ditioned medium collected for measurement of nitrogen oxides by chemiluminescence.

62 ation pathway, we analyzed the metabolism of nitrogen oxides by norB, aniA norB, and nsrR norB mutant

63 oxide (NO) is the only biologically relevant nitrogen oxide capable of activating the enzyme soluble

64 ess than 2.5 microm in aerodynamic diameter, nitrogen oxides, carbon monoxide, sulfur dioxide, and oz

65 no indication of missing OH recycling at low nitrogen oxide concentrations.

66 The presence of nitrogen oxide contaminants (due to the use of dry air a

67 from successful CTPs for sulfur dioxide and nitrogen oxide control.

68 reactive oxygen species to the production of nitrogen oxides could optimize the initial reduction in

69 determine the mechanisms by which different nitrogen oxide derivatives modulate PGHS-1 activity.

70 li's salt may have clinical application as a nitrogen oxide donor for treatment of cardiovascular dis

71 (2), HNO(3), N(2)O(5) and a variety of other nitrogen oxides during transport.

72 activity that can inactivate superoxide and nitrogen oxides (e.g., peroxynitrite and nitrogen dioxid

73 g (kg fuel)(-1), for particle number (EFN), nitrogen oxides (EFNOx), black carbon (EFBC), organics (

74 The primary products of nitrogen oxides electroreduction include nitrous oxide,

75 hich is of relevance as a catalyst in, e.g., nitrogen oxide emission abatement for environmental prot

76 ased marine eutrophication up to 11% through nitrogen oxide emission from storage and nitrate leachin

77 nia, where current underestimates of natural nitrogen oxide emissions bias modelled OH and hence isop

78 n remote oceanic regions with minimal direct nitrogen oxide emissions could increase the formation of

79 lined by over 40%, coincident with trends in nitrogen oxide emissions over the past decade.

80 interaction between anthropogenic sulfur and nitrogen oxide emissions than previously recognized.

81 Variation in nitrification rates and nitrogen oxide emissions tracked variation in forest com

82 ot correlated with climate, productivity, or nitrogen oxide emissions.

83 global climate and natural and anthropogenic nitrogen oxide emissions.

84 el types and NPAH quantities and between the nitrogen oxides emissions from the different fuel types

85 Recent efforts to lower nitrogen oxides emissions have substantially decreased n

86 erates power with reduced greenhouse-gas and nitrogen-oxide emissions, is limited by the availability

87 Nitrogen oxides emitted from aircraft engines alter the

88 y and subsequently to nitric oxide and other nitrogen oxides, enhances ischemia-induced remodeling of

89 5 absorbance, nitrogen dioxide exposure, and nitrogen oxide exposure during the entire pregnancy and

90 The highest quartile of nitrogen oxide exposure was associated with neural tube

91 of chlorinated VOCs as a result of ozone and nitrogen oxide formation.

92 te adjustment, including copollutants, i.e., nitrogen oxides ([Formula: see text]) and particulate ma

93 s both the concentration and distribution of nitrogen oxide free radicals (NO(x)).

94 based catalysts, which are used for removing nitrogen oxides from exhaust fuels, poses a problem for

95 raffic within 50 m and tailpipe emissions of nitrogen oxides from heavy-goods vehicles within 100 m w

96 st that bsNOS functions naturally to produce nitrogen oxides from L-Arg and NHA in a pterin-dependent

97 of arginase increases export of eNOS-derived nitrogen oxides from RBCs under basal conditions.

98 he impact of increased emissions of VOCs and nitrogen oxides from U.S. oil and natural gas (O&NG) sou

99 Simulations show that emissions of nitrogen-oxides from Manaus, a city of ~2 million people

100 major component of sea-salt particles, with nitrogen oxides generate chlorine atom precursors.

101 r with aerodynamic diameter <2.5mum (PM2.5), nitrogen oxides], greenness [Normalized Difference Veget

102 Introduction of the nitrogen-oxide group into the benzene ring decreases the

103 tion' process that recycles nitric acid into nitrogen oxides has been proposed to reconcile observati

104 Nitric acid, a major oxidation product of nitrogen oxides, has traditionally been considered to be

105 was successfully measured in the presence of nitrogen oxides; however, the secondary chemistry must b

106 on-road tailpipe light-duty gasoline vehicle nitrogen oxides, hydrocarbon, carbon monoxide, and carbo

107 ure to fine particulate matter (PM(2.5)) and nitrogen oxides in a cohort of black women living in Los

108 n the physiological pathways of NO and other nitrogen oxides in both enzymatic and nonenzymatic react

109 ission estimates of reactive species such as nitrogen oxides in key emitting countries in the NH that

110 Recycling of nitrogen oxides in remote oceanic regions with minimal d

111 Nitrogen oxides in serum (as an index of endothelial NO

112 recycling of nitric acid to nitrous acid and nitrogen oxides in the clean marine boundary layer via p

113 Nitrogen oxides in the lower troposphere catalyze the ph

114 active hydroxyl radicals as well as volatile nitrogen oxides in the snow.

115 dies predict higher ratios of nitric acid to nitrogen oxides in the troposphere than are observed.

116 In the atmosphere, gas-phase nitrogen oxides including nitric acid react with particl

117 tion between modelled pollutant exposures of nitrogen oxides (including nitrogen dioxide [NO(2)]) and

118 Herein, we investigate the impact of various nitrogen oxides, including nitric oxide, nitrogen dioxid

119 s, NH(4)(+) inhibits chloride transport, and nitrogen oxides inhibit amiloride-sensitive sodium trans

120 product of the production of highly reactive nitrogen oxide intermediates (e.g. peroxynitrite) formed

121 ot require formation of more highly reactive nitrogen oxide intermediates such as peroxynitrite or ni

122 ; P < .001) and enhanced local production of nitrogen oxides (L-arginine 152 +/- 28; saline 78 +/- 12

123 However, there was no change in serum nitrogen oxide levels (42.1 +/- 24.5 vs. 39.1 +/- 16.6 m

124 Serum nitrogen oxide levels increased from 21.6+/-1.7 to 26.7+

125 average nitric oxide, nitrogen dioxide, and nitrogen oxide levels, respectively, over the entire pre

126 ss of PM2.5 filters and nitrogen dioxide and nitrogen oxide levels.

127 nt of the blackness of PM(2.5) filters); and nitrogen oxides levels.

128 ntum vibrational relaxation event, where the nitrogen oxide loses hundreds of kilojoules per mole of

129 previously published computational study of nitrogen oxide metabolism in bacteria, a small number of

130 aris genome also suggests its involvement in nitrogen oxide metabolism.

131 studies suggest a role for these proteins in nitrogen oxide metabolism.

132 Volatile nitrogen oxides (N(2) O, NO, NO(2) , HONO, ...) can nega

133 ter (</= 2.5 mum; PM2.5), black carbon (BC), nitrogen oxides, nitrogen dioxide, ozone (O3), and carbo

134 ered road vehicles are important sources for nitrogen oxide (NO (x)) emissions, and the European pass

135 A 25% reduction in nitrogen oxide (NO + NO2) emissions was predicted to cau

136 ction because ascorbate stimulated both PAEC nitrogen oxide (NO(2)(-) + NO(3)(-)) production and l-ar

137 The overall in-use nitrogen oxide (NO(x)) emission factor was 16.1 +/- 0.1

138 o the net climate forcing from anthropogenic nitrogen oxide (NO(x)) emissions, which increase troposp

139 particulate matter, sulfur dioxide (SO(2)), nitrogen oxide (NO(x)), and ammonia (NH(3)) from stack e

140 A nitrogen oxide (NO(x); x = 1, 2) optical sensor with an

141 Nitrogen oxide (NO) species are markers for oxidative st

142 black carbon (BC), particle number (PN), and nitrogen oxide (NO, NO(2)) concentrations within 24 cens

143 ts to investigate the relative importance of nitrogen oxide (NO/NO2) and hydroperoxyl (HO2) SOA forma

144 Real-world nitrogen oxides (NO (x)) emissions were estimated using

145 r the selective catalytic reduction (SCR) of nitrogen oxides (NO x ) with ammonia (NH3), but the low-

146 Control of nitrogen oxides (NO(x) = NO + NO(2)) emissions has led t

147 emissions of volatile organic compounds and nitrogen oxides (NO(x) = NO + NO(2)) lead to a dramatic

148 ments that in the presence of high levels of nitrogen oxides (NO(x) = NO + NO2) typical of urban atmo

149 ished a number of chemical pathways by which nitrogen oxides (NO(x)) affect atmospheric organic aeros

150 arios consistent with the new regulations on nitrogen oxides (NO(x)) and sulfur dioxide (SO(2)) from

151 fire aerosols and increases in emissions of nitrogen oxides (NO(x)) and volatile organic compounds (

152 ment occurring during multiday smoke events; nitrogen oxides (NO(x)) are not consistently elevated ac

153 asured surface-atmosphere exchange fluxes of nitrogen oxides (NO(x)) at the neighborhood scale at 13

154 ems on 2010 and newer engines reduce emitted nitrogen oxides (NO(x)) by 87 +/- 5% relative to pre-200

155 biodiesel and second generation biofuels on nitrogen oxides (NO(x)) emissions from heavy-duty engine

156 12 knots yielded carbon dioxide (CO(2)) and nitrogen oxides (NO(x)) emissions reductions (in kg/naut

157 ctive strategy for controlling the levels of nitrogen oxides (NO(X)) emitted from a diesel engine, th

158 The removal of nitrogen oxides (NO(x)) has been extensively studied due

159 nitrosopiperazine (MNPZ), a carcinogen, from nitrogen oxides (NO(x)) in flue gas from coal or natural

160 Much of human exposure to nitrogen oxides (NO(x)) of ambient origin occurs indoors

161 o 90% and carbon monoxide up to 98%, whereas nitrogen oxides (NO(X)) remained almost unaffected.

162 missions such as particulate matter (PM) and nitrogen oxides (NO(x)) to comply with stringent emissio

163 ardous to health, sulfur dioxide (SO(2)) and nitrogen oxides (NO(x)), approximately double by 2030 re

164 ehyde, formaldehyde, acetone, nitrous oxide, nitrogen oxides (NO(x)), carbon monoxide (CO), and carbo

165 d biogas ammonia (NH(3)) content and emitted nitrogen oxides (NO(x)), indicating that fuel NO(x) form

166 uantify emissions of carbon dioxide (CO(2)), nitrogen oxides (NO(x)), particle number, and black carb

167 re imposed on life-cycle emissions of SO(2), nitrogen oxides (NO(x)), particulate matter, and greenho

168 Reactive nitrogen oxides (NO(y); NO(y) = NO + NO(2) + HONO) decre

169 Emission ratios of CO/NOx (nitrogen oxides = NO + NO2) and NMHC/NOx decreased by a

170 frequent even as the ozone precursors NO(x) (nitrogen oxides = NO(2) + NO) and VOC (volatile organic

171 nts (particulate matter, black carbon, total nitrogen oxides [NO(X)], and nitrogen dioxide [NO(2)]) w

172 of particulate matter (PM), PM(2.5), PM(10), nitrogen oxides, NO(2), NO(x), ultrafine particles (UFP)

173 Air pollution by nitrogen oxides, NO(x), is a major problem, and new capt

174 rbance, and annual average concentrations of nitrogen oxides (NO2 and NOx), with land use regression

175 d PMcoarse, respectively); PM2.5 absorbance; nitrogen oxides (NO2 and NOx); traffic intensity; and el

176 VOC)-limited conditions associated with high nitrogen oxide (NOX = [NO] + [NO2]) concentrations.

177 Nitrogen oxide (NOx identical with NO + NO2) emissions a

178 that were photochemically aged under varying nitrogen oxide (NOx) concentrations in an oxidation flow

179 n Eagle Ford upstream oil and gas production nitrogen oxide (NOx) emissions caused an estimated local

180 ity demand by 5% over the 2030 Base Case but nitrogen oxide (NOx) emissions decrease by 209 thousand

181 Despite substantial reductions in nitrogen oxide (NOx) emissions in the United States, the

182 Nitrogen oxide (NOx) emissions reductions will likely al

183 at environmentally relevant levels the mono-nitrogen oxide (NOx) fraction of the exhaust gases was a

184 Nitrogen oxide (NOx) pollution is emerging as a primary

185 es that ice-core nitrate reflects changes in nitrogen oxide (NOx) source emissions and that anthropog

186 rmed in the plasma and by the dissolution of nitrogen oxide (NOx) species dominate in the case of air

187 or pellet exhaust components (including high nitrogen oxide (NOx), primary particles, or a combinatio

188 Given its location in a nitrogen oxide (NOx)-limited area, and using the range o

189 have large potential for production of soil nitrogen oxide (NOx=NO+NO2), however these emissions are

190 engines, the poor thermal durability of lean nitrogen oxides (NOx ) aftertreatment systems remains as

191 ity impacts are associated with emissions of nitrogen oxides (NOx = NO + NO2) and volatile organic co

192 HCHO yield decreases as the concentration of nitrogen oxides (NOx identical with NO + NO2) decreases.

193 and poor thermal durability of current lean nitrogen oxides (NOx) aftertreatment catalysts are two o

194 these contaminants make to the formation of nitrogen oxides (NOx) and hence to air pollution and aci

195 g the interaction of sulfur oxides (SOx) and nitrogen oxides (NOx) and investigating the application

196 ch examining the relationship of measures of nitrogen oxides (NOx) and of various measures of traffic

197 d pollutants such as nitrogen dioxide (NO2), nitrogen oxides (NOx) and particulate matter (PM).

198 not only solves the tradeoff problem between nitrogen oxides (NOx) and particulate matter emissions f

199 Wildfires generate substantial emissions of nitrogen oxides (NOx) and volatile organic compounds (VO

200 bon dioxide (CO2), sulfur dioxide (SO2), and nitrogen oxides (NOX) associated with energy use in majo

201 s of traffic-related air pollutants based on nitrogen oxides (NOx) at participants' residential addre

202 3 (PM2.5), PM10, nitrogen dioxide (NO2), and nitrogen oxides (NOx) at the nurses' residences since 19

203 ctors, estimated concentrations of PM2.5 and nitrogen oxides (NOX) between 1999 and 2012.

204 ith a goal of reducing national emissions of nitrogen oxides (NOx) by 10% by 2015 compared with 2010.

205 ol fuels, while total hydrocarbons (THC) and nitrogen oxides (NOx) did not show strong fuel effects.

206 order to estimate the top-down anthropogenic nitrogen oxides (NOx) emission trends.

207 is study, we designed saturation sampling of nitrogen oxides (NOX) for the counties of Los Angeles an

208 (GHG), volatile organic compounds (VOCs) and nitrogen oxides (NOx) for the United States and its Rock

209 Emissions of nitrogen oxides (NOx) in the United States (U.S.) from l

210 However, nitrogen oxides (NOX) of RME and JME exceeded the Euro I

211 o-oxidation is rapid, and in the presence of nitrogen oxides (NOx) produces ozone and degrades air qu

212 Photochemical cycling of nitrogen oxides (NOx) produces tropospheric ozone (O3),

213 d emission rates of carbon monoxide (CO) and nitrogen oxides (NOx) typically increased with increasin

214 ions of particulate matter (PM2.5, PM10) and nitrogen oxides (NOx) with percent emphysema-like lung o

215 gation efficiencies of sulfur dioxide (SO2), nitrogen oxides (NOx), ammonia (NH3), and primary PM are

216 alter the emissions of carbon monoxide (CO), nitrogen oxides (NOx), and hydrocarbon (HC) species, inc

217 .5 mum (PM2.5), soot (reflectance of PM2.5), nitrogen oxides (NOx), and nitrogen dioxide (NO2).

218 oxidants, such as hydroxyl radicals (OH(*)), nitrogen oxides (NOx), and ozone (O(3)).

219 th aerodynamic diameter </= 2.5 mum (PM2.5), nitrogen oxides (NOx), and ozone (O3)] for 30,007 indivi

220 rbons (PB-PAH), particle number count (PNC), nitrogen oxides (NOx), and particulate matter with diame

221 rticulate matter (PM), carbon monoxide (CO), nitrogen oxides (NOx), and total hydrocarbon (THC) decre

222 study, a mobile platform was used to measure nitrogen oxides (NOX), black carbon (BC), and ultrafine

223 Nitrogen oxides (NOx), black carbon (BC), particle numbe

224 ajoules delivered, MJd) for carbon monoxide, nitrogen oxides (NOx), black carbon, methane, total hydr

225 first time, we tag all O3 precursors (i.e., nitrogen oxides (NOx), carbon monoxide (CO), and volatil

226 Vehicle emissions of nitrogen oxides (NOx), carbon monoxide (CO), fine partic

227 cally significant effect on the emissions of nitrogen oxides (NOx), formaldehyde, or acetaldehyde.

228 easurement system (PEMS), duty cycle average nitrogen oxides (NOx), hydrocarbons (HC), carbon monoxid

229 ns of mainly traffic-related air pollutants (nitrogen oxides (NOx), particulate matter (PM) mass or a

230 oncentrations of 17 air pollutants including nitrogen oxides (NOX), particulate matter (PM), and comp

231 iameter of less than 10 microns, ozone (O3), nitrogen oxides (NOx), sulfur dioxide (SO2), and carbon

232 er cent of global anthropogenic emissions of nitrogen oxides (NOx), which are key PM2.5 and ozone pre

233 production rates of nitrous acid (HONO) and nitrogen oxides (NOx).

234 ce causing a sharp peak of HONO, but also of nitrogen oxides (NOx).

235 (FeNO) and exhaled breath condensate pH and nitrogen oxides (NOx).

236 itric oxide (NO), nitrogen dioxide (NO2) and nitrogen oxides (NOx).

237 s, more so at -7 degrees C, contrasting with nitrogen oxides (NOX).

238 ts and emissions of carbon monoxide (CO) and nitrogen oxides (NOx).

239 tion from local road traffic were estimated (nitrogen oxides [NOx] and particulate matter with an aer

240 indicating a negligible long-term impact of nitrogen oxides on the catalytic properties of the model

241 ste recycling strategy is described in which nitrogen oxides or nitric acid are directly employed in

242 5% confidence interval (CI): 1.00, 1.17) and nitrogen oxides (OR = 1.18, 95% CI: 1.01, 1.38) per each

243 M(2).(5), OR = 1.16, 95% CI: 0.94, 1.42; for nitrogen oxides, OR = 1.29, 95% CI: 0.94, 1.76).

244 ith traffic-related exposures such as PM2.5, nitrogen oxides, or noise.

245 y, our findings implicate a greater role for nitrogen oxides (other than peroxynitrite) in beta-cell

246 used by the preferential electroreduction of nitrogen oxides over carbon dioxide.

247 xygen, dry CO2, sulfur-containing compounds, nitrogen oxides, oxygen and steam.

248 ticles due to the presence of sulfur oxides, nitrogen oxides, oxygen, and moisture in flue gases.

249 These two nitrogen oxides participate in numerous atmospheric chem

250 roduction relative to the consumption of its nitrogen oxide precursors.

251 Mass spectrometric analysis of nitrogen oxides produced by cells and purified protein d

252 Released nitrogen oxide reacts with sulfanilamide (SA) and N-(1-n

253 f some aerobic methanotrophs encode putative nitrogen oxide reductases, it is not understood whether

254 on, which donates electrons to carriers, and nitrogen oxides reduction, which receives electrons from

255 From 30 to 50% of the sulfur dioxide and nitrogen oxides released in some of the coal-heavy Rocky

256 is, which was associated with an increase in nitrogen oxides released into the medium.

257 ry and titration of ozone in winter, reduced nitrogen oxides resulted in ozone enhancement in urban a

258 snowpack emissions of molecular bromine and nitrogen oxides, resulting in continued atmospheric merc

259 in [O(3)], reflecting the diminished role of nitrogen oxide sequestration by peroxyacetyl nitrates an

260 Here, we show that nitrogen oxide soil emissions are mediated by microbial

261 otolysis could be a substantial tropospheric nitrogen oxide source.

262 Reactive nitrogen oxide species (RNOx), including peroxynitrite (

263 lian heme proteins are reactive with various nitrogen oxide species and that these reactions may play

264 experimental evidence suggests that reactive nitrogen oxide species can contribute significantly to p

265 ogical mechanisms that control reactivity of nitrogen oxide species formed during autoxidation of nan

266 -derived nitric oxide (NO) vs. intravascular nitrogen oxide species in the regulation of human blood

267 The mechanisms by which reactive nitrogen oxide species may impede protein function throu

268 l as a marker for the generation of reactive nitrogen oxide species with short half-lives such as per

269 , suggesting the involvement of the reactive nitrogen oxide species, N(2)O(3).

270 udy was to evaluate the role of two reactive nitrogen oxide species, nitroxyl (NO(-)) and nitric oxid

271 ociated with increased formation of reactive nitrogen oxide species.

272 inimizing effects of cytotoxic and genotoxic nitrogen oxide species.

273 ese factors might be uniquely susceptible to nitrogen oxide, specifically the nitrite anion (NO(2)(-)

274 These results may lead toward novel nitrogen oxides storing materials.

275 tive oxygen species, such as superoxide, and nitrogen oxides, such as peroxynitrite, are thought to c

276 Burning coal in power plants emits more nitrogen oxides, sulfur dioxide, particulate matter, and

277 enitrifying culture under various carbon and nitrogen oxides supplying conditions.

278 f newly fixed N is the most likely source of nitrogen oxides supporting nitrous oxide cycling within

279 d atmospheric nitrogen oxides are sources of nitrogen oxide that react with the reagents, SA and NNED

280 sts for the inter-conversions of the various nitrogen oxides that are based on such complexes, lookin

281 (for example, nitrates, amines, nitrites and nitrogen oxides) that are typically present in the nitro

282 Denitrifying bacteria metabolize nitrogen oxides through assimilatory and dissimilatory p

283 with consequences for emissions of volatile nitrogen oxides to air.

284 Beewolf wasp eggs release nitrogen oxides to provide protection against fungi and

285 the catalytic converter in conjunction with nitrogen oxide traps.

286 is a source of both particulate chloride and nitrogen oxides, two important precursors for the format

287 often contain numerous contaminants, such as nitrogen oxides, understanding the potential impact of c

288 We demonstrate that the presence of nitrogen oxides (up to 0.83%) in the carbon dioxide feed

289 at is responsive to NO formation from higher nitrogen oxides used as electron acceptors when oxygen i

290 Vs by providing deep reductions in WTW GHGs, nitrogen oxides, volatile organic compounds, and carbon

291 Total nitrogen oxides, volatile organic compounds, and SO2 emi

292 erquartile range (12.4 parts per billion) of nitrogen oxides was 1.14 (95% CI, 1.03-1.25).

293 communities, where reduction of mixtures of nitrogen oxides was monitored, while different carbon so

294 sures to nitric oxide, nitrogen dioxide, and nitrogen oxides were assigned based on birthplace reside

295 Concentrations of gaseous ozone and nitrogen oxides were determined with Fourier-transform i

296 for PM(2.5) were attenuated and the IRRs for nitrogen oxides were essentially unchanged for both outc

297 evels of nitric oxide, nitrogen dioxide, and nitrogen oxides were used to assess the influence of sma

298 r the subtraction of nitrite and atmospheric nitrogen oxides which "contaminate" the nitrosothiol sam

299 zeolite crystals during the deoxygenation of nitrogen oxides with propene.

300 UK has led to reductions in the emissions of nitrogen oxides, with concomitant decreases in N deposit