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 prevent accumulation of this highly reactive nitrogen oxide.

4 ty approach and 0.5 ppbv by tagging reactive 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 ffectively scavenges HNO2 and possibly other nitrogen oxides.

16 tes on proteins are susceptible to attack by nitrogen oxides.

17 d norB-lacZ fusions in medium unamended with nitrogen oxides.

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

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

20 soil nutrients and production of detrimental nitrogen oxides.

21 iations with exposure to carbon monoxide and nitrogen oxides.

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

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

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

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

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

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

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

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

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

31 as a trap for membrane-soluble electrophilic nitrogen oxides and other electrophilic mutagens, formin

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

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

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

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

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

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

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

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

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

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

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

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

44 Exposures to 100% oxygen, ozone, nitrogen oxides, and phosgene increase both lung lavage

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

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

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

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

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

50 Nitrogen oxides are essential for the formation of secon

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

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

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

54 Nitrogen oxides are textbook class of molecular compound

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

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

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

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

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

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

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

62 so review potential clinical applications of nitrogen oxide biochemistry.

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

80 global climate and natural and anthropogenic nitrogen oxide emissions.

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

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

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

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

85 Nitrogen oxides emitted from aircraft engines alter the

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

87 5 absorbance, nitrogen dioxide exposure, and nitrogen oxide exposure during the entire pregnancy and

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

105 Nitrogen oxides in the lower troposphere catalyze the ph

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

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

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

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

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

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

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

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

114 was measured by radioimmunoassay, and serum nitrogen oxide levels (NOx = NO2 + NO3) were measured by

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

138 12 knots yielded carbon dioxide (CO(2)) and nitrogen oxides (NO(x)) emissions reductions (in kg/naut

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

154 Nitrogen oxide (NOx) emissions reductions will likely al

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

175 but almost completely inhibited synthesis of nitrogen oxides (NOx) by intact cells.

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

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

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

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

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

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

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

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

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

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

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

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

188 .5 mum (PM2.5), soot (reflectance of PM2.5), nitrogen oxides (NOx), and nitrogen dioxide (NO2).

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

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

209 5% confidence interval (CI): 1.00, 1.17) and nitrogen oxides (OR = 1.18, 95% CI: 1.01, 1.38) per each

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

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

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

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

214 These two nitrogen oxides participate in numerous atmospheric chem

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

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

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

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

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

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

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

222 otolysis could be a substantial tropospheric nitrogen oxide source.

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

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

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

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

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

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

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

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

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

232 ociated with increased formation of reactive nitrogen oxide species.

233 inimizing effects of cytotoxic and genotoxic nitrogen oxide species.

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

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

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

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

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

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

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

241 Denitrifying bacteria metabolize nitrogen oxides through assimilatory and dissimilatory p

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

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

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

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

246 itical to the production of mycobactericidal nitrogen oxides was depressed in malnourished animals in

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

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

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

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

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