コーパス検索結果 (１語後でソート)
通し番号をクリックするとPubMedの該当ページを表示します
1 a novel pretreatment strategy based on free nitrous acid (FNA or HNO2) to enhance methane production
3 ter (BTF) through free ammonia (FA) and free nitrous acid (FNA) inhibition on nitrite-oxidizing bacte
4 5-45 mg of N/L) that was established by free nitrous acid (FNA)-based sludge treatment was not higher
6 zing bacteria were not further detected, but nitrous acid (HNO2) was still removed through chemical d
7 in the plasma phase and the solution lead to nitrous acid (HNO2), nitric acid (HNO3), and hydrogen pe
11 labile nighttime radical reservoirs, such as nitrous acid (HONO) and nitryl chloride (ClNO(2)), contr
14 adiated nitrophenols can produce nitrite and nitrous acid (HONO) in bulk aqueous solutions and in vis
20 ve importance of common activities on indoor nitrous acid (HONO) mixing ratios was explored during hi
21 (HA) is thought to promote NO2 conversion to nitrous acid (HONO) on soil surfaces during the day.
22 ion of SO(2) by nitrogen dioxide (NO(2)) and nitrous acid (HONO) takes place, the latter producing ni
27 rising finding is the formation of gas-phase nitrous acid (HONO), a species known to be a major photo
28 HOx production rates from the photolysis of nitrous acid (HONO), hydrogen peroxide (H2O2), ozone (O3
32 ctive nitrogen species involved derives from nitrous acid and is most probably the nitronium cation.
33 lysis mainly sustains the observed levels of nitrous acid and nitrogen oxides at midday under typical
34 idence for rapid recycling of nitric acid to nitrous acid and nitrogen oxides in the clean marine bou
38 or quantification of both enzyme-derived and nitrous acid depolymerization products for structural an
39 e utility of PGC-MS for quantification of HS nitrous acid depolymerization products for structural an
42 of the aniline into an aryl diazonium, using nitrous acid in aqueous conditions, was performed in sit
44 ion events leading to high concentrations of nitrous acid in the atmosphere contributed to an observe
47 ction of 3-amino-5-nitro-1,2,4-triazole with nitrous acid produces the corresponding diazonium salt.
50 The reaction of 6 with in situ generated nitrous acid yielded the primary explosive bis(4-diazo-5
51 gradients of DO, pH, free ammonia, and free nitrous acid, associated with aerated and nonaerated pha
52 yl radicals (OH) in the gas phase to produce nitrous acid, HONO, but essentially nothing is known abo
53 recycling route reproduces levels of gaseous nitrous acid, NO, and NO2 within the model and measureme
55 g microorganisms with the antimicrobial free nitrous acid, which is generated in situ from calcium ni
60 tulated that carbonic anhydrase may act as a nitrous anhydrase in vivo to generate nitric oxide (NO)
61 acetazolamide does not function as either a nitrous anhydrase or a nitrite reductase in the lungs of
62 hysiological role of carbonic anhydrase as a nitrous anhydrase or nitrite reductase as a mechanism fo
68 ffecting the removal ability of strain F2 to nitrous nitrogen (NO(2)(-)N) and nitrate nitrogen (NO(3)
69 thane (CH(4)) and only negligible amounts of nitrous oxide (0.00012 +/- 0.00004 mumol N(2)O gDW(-1) h
70 and solid manure piles were large sources of nitrous oxide (1.5 +/- 0.8 and 1.1 +/- 0.7 kg N2O hd(-1)
71 rted as sources of the potent greenhouse gas nitrous oxide ([Formula: see text]) to the atmosphere ma
72 t of the global budget of the greenhouse gas nitrous oxide ([Formula: see text]O) is limited by poor
79 extent soil release of methane (CH(4) ) and nitrous oxide (N(2) O) may contribute to soil C loss for
80 ltural soils are also an important source of nitrous oxide (N(2) O), a powerful greenhouse gas, and i
81 a methane (CH(4) ) sink and a weak source of nitrous oxide (N(2) O), but studies of wetland forests h
82 itrogen leaching, soil organic carbon (SOC), nitrous oxide (N(2) O), grain yield and nitrogen in grai
86 er laboratory conditions to compare rates of nitrous oxide (N(2)O) and ammonia (NH(3)) emissions when
89 s influencing production of greenhouse gases nitrous oxide (N(2)O) and nitrogen (N(2)) in arable soil
90 15)N/(14)N ratios (delta(15)N(bulk)(N2O)) of nitrous oxide (N(2)O) by quantum cascade laser absorptio
93 ), there were significant differences in the nitrous oxide (N(2)O) emissions between the systems.
94 bal eutrophication are predicted to increase nitrous oxide (N(2)O) emissions from freshwater ecosyste
98 atom transfer reagent for transition metals, nitrous oxide (N(2)O) is a notoriously poor ligand, and
101 , we quantified the magnitude of urine-based nitrous oxide (N(2)O) lost from soil under paired degrad
102 greenhouse gas and an ozone-depleting agent, nitrous oxide (N(2)O) plays a critical role in the globa
103 the incomplete reduction of nitrate and the nitrous oxide (N(2)O) production (between 4 and 20% of n
106 the environmentally critical greenhouse gas nitrous oxide (N(2)O) to dinitrogen (N(2)) as the final
111 est source of CH(4), carbon dioxide (CO(2)), nitrous oxide (N(2)O), and carbon monoxide (CO) emission
112 the inorganic N-N-bond-containing molecules nitrous oxide (N(2)O), dinitrogen (N(2)), and hydrazine
114 activation, such as carbon dioxide (CO(2)), nitrous oxide (N(2)O), tetrahydrofuran (THF), tetrahydro
117 stems can be a source of the greenhouse gas, nitrous oxide (N(2)O); yet in situ measurements of N(2)O
118 tential source of the potent greenhouse gas, nitrous oxide (N2 O) - and denitrification, a major nitr
119 nt effects were quantified by measuring soil nitrous oxide (N2 O) and methane (CH4 ) fluxes and SOC c
120 Carbon dioxide (CO2 ), methane (CH4 ), and nitrous oxide (N2 O) are the three most important greenh
121 the poorly understood formation mechanism of nitrous oxide (N2 O) at higher potentials, which suggest
124 -model ensembles to predict productivity and nitrous oxide (N2 O) emissions for wheat, maize, rice an
126 on carbon dioxide (CO2 ), methane (CH4 ) and nitrous oxide (N2 O) fluxes as well as the underlying me
127 e the responses of carbon dioxide (CO2 ) and nitrous oxide (N2 O) fluxes to (i) temperature, (ii) soi
130 represents the largest contributor to global nitrous oxide (N2 O) production, which is regulated by a
131 sing bacteria (AOB) are thought to emit more nitrous oxide (N2 O) than ammonia oxidising archaea (AOA
132 ly to emissions of the potent greenhouse gas nitrous oxide (N2 O), which is generated during denitrif
135 The PHA turnovers play important roles in nitrous oxide (N2O) accumulation during the denitrifying
136 ymes was developed to improve predictions of nitrous oxide (N2O) accumulations in soil and emissions
139 sessment of manure treatment effects on NH3, nitrous oxide (N2O) and methane (CH4) emissions from man
140 This study investigated the potential for nitrous oxide (N2O) and methane (CH4) generation in diss
141 n of carbon dioxide (CO2), methane (CH4) and nitrous oxide (N2O) and soil biophysical and chemical ch
147 timation of direct and indirect agricultural nitrous oxide (N2O) emissions in developing countries an
149 paddies are a major source of anthropogenic nitrous oxide (N2O) emissions, especially under alternat
152 agricultural emissions of the greenhouse gas nitrous oxide (N2O) have increased by around 20% over th
153 ing carbon dioxide (CO2), methane (CH4), and nitrous oxide (N2O) in a dry-natural air balance at ambi
167 h range is generally recognized to stimulate nitrous oxide (N2O) production by ammonia-oxidizing bact
169 bally prominent N2-producing enzyme, next to nitrous oxide (N2O) reductase from denitrifying microorg
171 th the capacity to reduce the greenhouse gas nitrous oxide (N2O) to harmless dinitrogen gas are recei
172 removed from solution, nitric oxide (NO) and nitrous oxide (N2O) were identified as products confirmi
173 gaseous intermediates nitric oxide (NO) and nitrous oxide (N2O) when oxygen concentrations are limit
175 ss pathways from cropland is the emission of nitrous oxide (N2O), a potent greenhouse gas and ozone d
177 3), water vapor (H2O), carbon dioxide (CO2), nitrous oxide (N2O), and methane (CH4) requires days of
178 le laboratory, ammonia (NH3), methane (CH4), nitrous oxide (N2O), and other trace gas emissions were
179 ses, carbon dioxide (CO2), methane (CH4) and nitrous oxide (N2O), and therefore has an important role
180 substantial amounts of nitric oxide (NO) and nitrous oxide (N2O), both of which contribute to the har
181 n China and quantified the responses of soil nitrous oxide (N2O), carbon dioxide (CO2) and methane (C
186 o nitrite; (2) denitrification of nitrite to nitrous oxide (N2O); and (3) N2O conversion to N2 with e
187 his review article summarizes efforts to use nitrous oxide (N2O, 'laughing gas') as a reagent in synt
188 sted the effects of insulin on production of nitrous oxide (NO)-related substances (nitrites and nitr
189 oom temperature and (ii) reversibly captures nitrous oxide (uptake at room temperature, 1 atm; releas
193 nwind intercepts of CH4, ethane, and tracer (nitrous oxide and acetylene) plumes was performed at 18
194 ed species of nitrogen (i.e., supersaturated nitrous oxide and approximately 1 mmolL(-1) nitrate) and
200 then used in application to the detection of nitrous oxide as an exemplar of the utility of this tech
202 eatment concentrations in children receiving nitrous oxide but not in those receiving general anesthe
205 full remission (HDRS-21 </= 7 points) after nitrous oxide compared with one patient (5%) and none af
206 ntly at 2 hours and 24 hours after receiving nitrous oxide compared with placebo (mean HDRS-21 differ
207 richodesmium colonies are potential sites of nitrous oxide consumption and perhaps earlier steps in t
208 overy in the mid-19th century that ether and nitrous oxide could be used to render patients unconscio
209 likely source of nitrogen oxides supporting nitrous oxide cycling within Trichodesmium colonies.
210 chaea is responsible for global emissions of nitrous oxide directly and indirectly through provision
213 ds to the understanding of the regulation of nitrous oxide emission by denitrifying bacteria in respo
214 ead to increases in nitrate leaching (+30%), nitrous oxide emissions (+30%), nitric oxide (+66%) emis
215 eriments in China, including measurements of nitrous oxide emissions (N2 O), methane emissions (CH4 )
217 tock production, direct energy use, and soil nitrous oxide emissions are currently the largest source
221 , and the resulting increases in methane and nitrous oxide emissions in particular can contribute to
223 capacity of concurrent biogenic methane and nitrous oxide emissions is a factor of about two larger
227 nt losses of N from their systems, either as nitrous oxide emissions or as nitrate leached from the s
229 Although seasonal variations in the measured nitrous oxide emissions were remarkable, the measurement
230 consequences for soil carbon sequestration, nitrous oxide emissions, nitrate pollution, biodiversity
231 tropical field studies of nitrate leaching, nitrous oxide emissions, nitric oxide emissions, and amm
232 that a reduction in agricultural methane and nitrous oxide emissions, particularly in Southern Asia,
236 ults show a distinct, replicable, pattern of nitrous oxide generation and consumption dictated by sub
237 his proof-of-concept trial demonstrated that nitrous oxide has rapid and marked antidepressant effect
238 depletion and its potent greenhouse effect, nitrous oxide has stimulated much research interest rega
241 concomitant carbon accumulation on land and nitrous oxide in the atmosphere suggests millennia of de
242 sorption of two nitric oxide molecules and a nitrous oxide intermediate on Rh1Co3 sites and following
246 dioxide emissions with increased methane and nitrous oxide mitigation efforts and can also guide the
248 ged the denitrifying community and increased nitrous oxide production; and (iii) induced dissimilator
252 intermediate form of the Cu4S active site of nitrous oxide reductase (N2OR) that is observed in singl
253 , they are both dependent on a Cu-containing nitrous oxide reductase (NosZ) for the conversion of N(2
254 OCker using ammonia monooxygenase (amoA) and nitrous oxide reductase (nosZ) genes, mediating oxidatio
255 ate that expression of the gene encoding the nitrous oxide reductase (NosZ), which converts N2O to N2
258 ccupying different energetic niches, express nitrous oxide reductase, potentially acting as a global
259 imics aspects of the Cu(Z) catalytic site of nitrous oxide reductase: activity in the 4Cu(I) :1S redo
260 This coupling creates a metabolic niche for nitrous oxide reduction that completes denitrification b
261 .5% for the nitric oxide and +/-3.9% for the nitrous oxide sensor and can be corrected with exponenti
262 ities were detected for both sensors: by the nitrous oxide sensor to nitric oxide and by the nitric o
264 e called alpha-Fe(ii), which is activated by nitrous oxide to form the reactive intermediate alpha-O;
270 A literature survey of studies reporting nitrous oxide uptake in the soils of natural ecosystems
272 eenhouse gases (carbon dioxide, methane, and nitrous oxide) as well as carbon stable isotope ratios o
274 substrates including dioxygen, nitric oxide, nitrous oxide, 1-azido adamantane, trimethylamine n-oxid
277 4%), bringing tropical agricultural nitrate, nitrous oxide, and ammonia losses in line with temperate
278 eral anesthetics xenon, sulfur hexafluoride, nitrous oxide, and chloroform cause rapid increases of d
279 R. sphaeroides, which can reduce nitrate to nitrous oxide, and their absence from strains such as 2.
280 ite, 4-nitro-2,4-diazabutanal, formaldehyde, nitrous oxide, formate, and ammonia correspond to experi
283 nitrogen conversion processes (nitric oxide, nitrous oxide, nitrogen dioxide, ammonia, hydrazine, hyd
284 thanol, acetaldehyde, formaldehyde, acetone, nitrous oxide, nitrogen oxides (NO(x)), carbon monoxide
285 of nitrogen oxides electroreduction include nitrous oxide, nitrogen, hydroxylamine, and ammonia.
286 ncluding nitric oxide, nitrogen dioxide, and nitrous oxide, on carbon dioxide electroreduction on thr
287 easurements of sulfur hexafluoride (SF6) and nitrous oxide, we calculate the global mean diabatic ove
289 s (8 degrees C) also stimulate production of nitrous oxide, which is consumed by benthic denitrifying
298 andomly assigned to 1-hour inhalation of 50% nitrous oxide/50% oxygen or 50% nitrogen/50% oxygen (pla
299 Mobile source emissions of primary EC and nitrous oxides accounted for 3.396 (95% CI: 2.772, 4.020