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1 f NH(4)(+) or transformation products (i.e., nitrous oxide).
2 ing a green, mild methodology for removal of nitrous oxide.
3 nitrogen gas over nitrite, nitric oxide, and nitrous oxide.
4 soflurane, nitrous oxide and isoflurane plus nitrous oxide.
5 y two electrons with either mesityl azide or nitrous oxide.
6 itrification pathway that reduces nitrate to nitrous oxide.
7 trations of methane, tropospheric ozone, and nitrous oxide.
8 erric species with concomitant production of nitrous oxide.
9 (O)=NO-] that decomposes to formaldehyde and nitrous oxide.
10 ical anion and NO2, forming benzoate ion and nitrous oxide.
11 tomidate, midazolam, fentanyl, ketamine, and nitrous oxide.
12 ignificant release of intermediates, such as nitrous oxide.
13 ting as a global sink for the greenhouse gas nitrous oxide.
14 source and sink of the potent greenhouse gas nitrous oxide.
15 could possibly justify the continuing use of nitrous oxide?
16 thane (CH(4)) and only negligible amounts of nitrous oxide (0.00012 +/- 0.00004 mumol N(2)O gDW(-1) h
17 and solid manure piles were large sources of nitrous oxide (1.5 +/- 0.8 and 1.1 +/- 0.7 kg N2O hd(-1)
18 substrates including dioxygen, nitric oxide, nitrous oxide, 1-azido adamantane, trimethylamine n-oxid
19 andomly assigned to 1-hour inhalation of 50% nitrous oxide/50% oxygen or 50% nitrogen/50% oxygen (pla
20 Mobile source emissions of primary EC and nitrous oxides accounted for 3.396 (95% CI: 2.772, 4.020
24 nwind intercepts of CH4, ethane, and tracer (nitrous oxide and acetylene) plumes was performed at 18
25 ed species of nitrogen (i.e., supersaturated nitrous oxide and approximately 1 mmolL(-1) nitrate) and
27 cated in oxidation-reduction associated with nitrous oxide and nitrogen metabolism, respectively.
28 cycle that produces both the greenhouse gas nitrous oxide and oxidized forms of nitrogen used by phy
29 non-CO(2) greenhouse gases, such as methane, nitrous oxide and ozone-depleting substances (largely fr
31 some suggest a possible association between nitrous oxide and the postoperative development of tensi
34 4%), bringing tropical agricultural nitrate, nitrous oxide, and ammonia losses in line with temperate
35 eral anesthetics xenon, sulfur hexafluoride, nitrous oxide, and chloroform cause rapid increases of d
37 R. sphaeroides, which can reduce nitrate to nitrous oxide, and their absence from strains such as 2.
38 lothane, isoflurane, sevoflurane, enflurane, nitrous oxide, and xenon, have been demonstrated to trig
42 controversial issues surrounding the use of nitrous oxide as a component of anesthesia in neurosurgi
44 then used in application to the detection of nitrous oxide as an exemplar of the utility of this tech
46 eenhouse gases (carbon dioxide, methane, and nitrous oxide) as well as carbon stable isotope ratios o
47 eatment concentrations in children receiving nitrous oxide but not in those receiving general anesthe
52 l studies in several species have shown that nitrous oxide can be associated with apoptosis in the de
54 full remission (HDRS-21 </= 7 points) after nitrous oxide compared with one patient (5%) and none af
55 ntly at 2 hours and 24 hours after receiving nitrous oxide compared with placebo (mean HDRS-21 differ
56 richodesmium colonies are potential sites of nitrous oxide consumption and perhaps earlier steps in t
57 sions of carbon dioxide (CO(2)), methane and nitrous oxide could be reduced by a maximum of 1.8 Pg CO
58 overy in the mid-19th century that ether and nitrous oxide could be used to render patients unconscio
60 chaea is responsible for global emissions of nitrous oxide directly and indirectly through provision
63 ds to the understanding of the regulation of nitrous oxide emission by denitrifying bacteria in respo
64 ead to increases in nitrate leaching (+30%), nitrous oxide emissions (+30%), nitric oxide (+66%) emis
65 eriments in China, including measurements of nitrous oxide emissions (N2 O), methane emissions (CH4 )
67 tock production, direct energy use, and soil nitrous oxide emissions are currently the largest source
71 , and the resulting increases in methane and nitrous oxide emissions in particular can contribute to
73 capacity of concurrent biogenic methane and nitrous oxide emissions is a factor of about two larger
77 nt losses of N from their systems, either as nitrous oxide emissions or as nitrate leached from the s
79 Although seasonal variations in the measured nitrous oxide emissions were remarkable, the measurement
80 se of predicted increases in fertilizer use, nitrous oxide emissions will be more important than carb
81 consequences for soil carbon sequestration, nitrous oxide emissions, nitrate pollution, biodiversity
82 tropical field studies of nitrate leaching, nitrous oxide emissions, nitric oxide emissions, and amm
83 that a reduction in agricultural methane and nitrous oxide emissions, particularly in Southern Asia,
86 ite, 4-nitro-2,4-diazabutanal, formaldehyde, nitrous oxide, formate, and ammonia correspond to experi
87 rted as sources of the potent greenhouse gas nitrous oxide ([Formula: see text]) to the atmosphere ma
88 t of the global budget of the greenhouse gas nitrous oxide ([Formula: see text]O) is limited by poor
92 ults show a distinct, replicable, pattern of nitrous oxide generation and consumption dictated by sub
95 his proof-of-concept trial demonstrated that nitrous oxide has rapid and marked antidepressant effect
96 depletion and its potent greenhouse effect, nitrous oxide has stimulated much research interest rega
98 g conditions were not hindered by the use of nitrous oxide; however, the number of patients analysed
99 body of evidence that supports avoidance of nitrous oxide in both pediatric and adult patients, but
103 concomitant carbon accumulation on land and nitrous oxide in the atmosphere suggests millennia of de
104 sorption of two nitric oxide molecules and a nitrous oxide intermediate on Rh1Co3 sites and following
112 dioxide emissions with increased methane and nitrous oxide mitigation efforts and can also guide the
120 extent soil release of methane (CH(4) ) and nitrous oxide (N(2) O) may contribute to soil C loss for
121 ltural soils are also an important source of nitrous oxide (N(2) O), a powerful greenhouse gas, and i
122 a methane (CH(4) ) sink and a weak source of nitrous oxide (N(2) O), but studies of wetland forests h
123 itrogen leaching, soil organic carbon (SOC), nitrous oxide (N(2) O), grain yield and nitrogen in grai
127 er laboratory conditions to compare rates of nitrous oxide (N(2)O) and ammonia (NH(3)) emissions when
133 s influencing production of greenhouse gases nitrous oxide (N(2)O) and nitrogen (N(2)) in arable soil
134 omly assigned to receive 1.8% isoflurane/70% nitrous oxide (N(2)O) anesthesia for 4h or no anesthesia
136 15)N/(14)N ratios (delta(15)N(bulk)(N2O)) of nitrous oxide (N(2)O) by quantum cascade laser absorptio
139 ), there were significant differences in the nitrous oxide (N(2)O) emissions between the systems.
140 bal eutrophication are predicted to increase nitrous oxide (N(2)O) emissions from freshwater ecosyste
141 carbon dioxide (CO(2)), methane (CH(4)), and nitrous oxide (N(2)O) emissions from the agricultural fr
145 sly shown that the antinociceptive effect of nitrous oxide (N(2)O) in the rat hot plate test is sensi
146 atom transfer reagent for transition metals, nitrous oxide (N(2)O) is a notoriously poor ligand, and
150 , we quantified the magnitude of urine-based nitrous oxide (N(2)O) lost from soil under paired degrad
151 greenhouse gas and an ozone-depleting agent, nitrous oxide (N(2)O) plays a critical role in the globa
152 the incomplete reduction of nitrate and the nitrous oxide (N(2)O) production (between 4 and 20% of n
155 the environmentally critical greenhouse gas nitrous oxide (N(2)O) to dinitrogen (N(2)) as the final
156 greenhouse gases carbon dioxide (CO(2)) and nitrous oxide (N(2)O) varied strongly on millennial time
158 The ocean is an important global source of nitrous oxide (N(2)O), a greenhouse gas that contributes
162 est source of CH(4), carbon dioxide (CO(2)), nitrous oxide (N(2)O), and carbon monoxide (CO) emission
163 the inorganic N-N-bond-containing molecules nitrous oxide (N(2)O), dinitrogen (N(2)), and hydrazine
165 hylamine, DEA), alkyl nitrates (RONO(2)) and nitrous oxide (N(2)O), non-methane hydrocarbons (NMHC) i
166 activation, such as carbon dioxide (CO(2)), nitrous oxide (N(2)O), tetrahydrofuran (THF), tetrahydro
167 ive coupling of two *NO molecules to release nitrous oxide (N(2)O), when Cu(+) ion and 2 equiv acid a
172 stems can be a source of the greenhouse gas, nitrous oxide (N(2)O); yet in situ measurements of N(2)O
174 tential source of the potent greenhouse gas, nitrous oxide (N2 O) - and denitrification, a major nitr
175 nt effects were quantified by measuring soil nitrous oxide (N2 O) and methane (CH4 ) fluxes and SOC c
176 Carbon dioxide (CO2 ), methane (CH4 ), and nitrous oxide (N2 O) are the three most important greenh
177 the poorly understood formation mechanism of nitrous oxide (N2 O) at higher potentials, which suggest
180 -model ensembles to predict productivity and nitrous oxide (N2 O) emissions for wheat, maize, rice an
182 on carbon dioxide (CO2 ), methane (CH4 ) and nitrous oxide (N2 O) fluxes as well as the underlying me
183 e the responses of carbon dioxide (CO2 ) and nitrous oxide (N2 O) fluxes to (i) temperature, (ii) soi
186 represents the largest contributor to global nitrous oxide (N2 O) production, which is regulated by a
187 sing bacteria (AOB) are thought to emit more nitrous oxide (N2 O) than ammonia oxidising archaea (AOA
188 ly to emissions of the potent greenhouse gas nitrous oxide (N2 O), which is generated during denitrif
191 The PHA turnovers play important roles in nitrous oxide (N2O) accumulation during the denitrifying
192 ymes was developed to improve predictions of nitrous oxide (N2O) accumulations in soil and emissions
195 sessment of manure treatment effects on NH3, nitrous oxide (N2O) and methane (CH4) emissions from man
196 This study investigated the potential for nitrous oxide (N2O) and methane (CH4) generation in diss
197 n of carbon dioxide (CO2), methane (CH4) and nitrous oxide (N2O) and soil biophysical and chemical ch
200 esses on nitrate (NO3-), nitrite (NO2-), and nitrous oxide (N2O) cycling in these systems, the nitrit
204 timation of direct and indirect agricultural nitrous oxide (N2O) emissions in developing countries an
206 paddies are a major source of anthropogenic nitrous oxide (N2O) emissions, especially under alternat
209 agricultural emissions of the greenhouse gas nitrous oxide (N2O) have increased by around 20% over th
210 ing carbon dioxide (CO2), methane (CH4), and nitrous oxide (N2O) in a dry-natural air balance at ambi
225 h range is generally recognized to stimulate nitrous oxide (N2O) production by ammonia-oxidizing bact
227 bally prominent N2-producing enzyme, next to nitrous oxide (N2O) reductase from denitrifying microorg
229 th the capacity to reduce the greenhouse gas nitrous oxide (N2O) to harmless dinitrogen gas are recei
230 removed from solution, nitric oxide (NO) and nitrous oxide (N2O) were identified as products confirmi
231 gaseous intermediates nitric oxide (NO) and nitrous oxide (N2O) when oxygen concentrations are limit
233 ss pathways from cropland is the emission of nitrous oxide (N2O), a potent greenhouse gas and ozone d
235 3), water vapor (H2O), carbon dioxide (CO2), nitrous oxide (N2O), and methane (CH4) requires days of
236 le laboratory, ammonia (NH3), methane (CH4), nitrous oxide (N2O), and other trace gas emissions were
237 ses, carbon dioxide (CO2), methane (CH4) and nitrous oxide (N2O), and therefore has an important role
238 substantial amounts of nitric oxide (NO) and nitrous oxide (N2O), both of which contribute to the har
239 n China and quantified the responses of soil nitrous oxide (N2O), carbon dioxide (CO2) and methane (C
245 o nitrite; (2) denitrification of nitrite to nitrous oxide (N2O); and (3) N2O conversion to N2 with e
246 his review article summarizes efforts to use nitrous oxide (N2O, 'laughing gas') as a reagent in synt
248 nitrogen conversion processes (nitric oxide, nitrous oxide, nitrogen dioxide, ammonia, hydrazine, hyd
249 thanol, acetaldehyde, formaldehyde, acetone, nitrous oxide, nitrogen oxides (NO(x)), carbon monoxide
250 of nitrogen oxides electroreduction include nitrous oxide, nitrogen, hydroxylamine, and ammonia.
251 sted the effects of insulin on production of nitrous oxide (NO)-related substances (nitrites and nitr
253 any long-term adverse effect from the use of nitrous oxide on gross neurologic or cognitive function.
254 inborn errors of metabolism, but effects of nitrous oxide on the developing human brain are unknown.
255 ncluding nitric oxide, nitrogen dioxide, and nitrous oxide, on carbon dioxide electroreduction on thr
256 al, succinylcholine (SCh) and unsupplemented nitrous oxide/oxygen for Caesarean section was first int
257 thin the next few decades, affecting oceanic nitrous oxide production, reducing supplies of oxidized
259 ged the denitrifying community and increased nitrous oxide production; and (iii) induced dissimilator
262 ulfido-tetracopper active site in the enzyme nitrous oxide reductase (N(2)OR) via a process postulate
263 at the CuZ site in Pseudomonas nautica (Pn) nitrous oxide reductase (N2OR) and Achromobacter cyclocl
265 pper, and the native purple Cu(A) centers of nitrous oxide reductase (N2OR) from Paracoccus denitrifi
266 intermediate form of the Cu4S active site of nitrous oxide reductase (N2OR) that is observed in singl
267 , they are both dependent on a Cu-containing nitrous oxide reductase (NosZ) for the conversion of N(2
268 OCker using ammonia monooxygenase (amoA) and nitrous oxide reductase (nosZ) genes, mediating oxidatio
269 ate that expression of the gene encoding the nitrous oxide reductase (NosZ), which converts N2O to N2
272 lytic tetranuclear copper cluster (Cu(Z)) of nitrous oxide reductase, N(2)OR, requires the coexpressi
273 ccupying different energetic niches, express nitrous oxide reductase, potentially acting as a global
274 ved previously in the native Cu(A) center of nitrous oxide reductase, the faster kinetics of copper i
275 imics aspects of the Cu(Z) catalytic site of nitrous oxide reductase: activity in the 4Cu(I) :1S redo
277 This coupling creates a metabolic niche for nitrous oxide reduction that completes denitrification b
278 Here, we present a molecular mechanism of nitrous oxide's selective inhibition of CaV3.2 low-volta
280 .5% for the nitric oxide and +/-3.9% for the nitrous oxide sensor and can be corrected with exponenti
281 ities were detected for both sensors: by the nitrous oxide sensor to nitric oxide and by the nitric o
283 sickle cell disease, but with the promise of nitrous oxide therapy in this disorder, these cytokines
284 e called alpha-Fe(ii), which is activated by nitrous oxide to form the reactive intermediate alpha-O;
291 A literature survey of studies reporting nitrous oxide uptake in the soils of natural ecosystems
292 oom temperature and (ii) reversibly captures nitrous oxide (uptake at room temperature, 1 atm; releas
293 cent adult human trial found that the use of nitrous oxide was associated with increased adverse outc
295 easurements of sulfur hexafluoride (SF6) and nitrous oxide, we calculate the global mean diabatic ove
298 s (8 degrees C) also stimulate production of nitrous oxide, which is consumed by benthic denitrifying
299 ousands of patients who have been exposed to nitrous oxide without apparent complications would sugge