ライフサイエンスコーパス: emission

1 on upconversion quantum yield (UCQY) and UV emission.

2 ith some traces of defect-induced trap state emission.

3 biosphere in mitigating anthropogenic CO(2) emissions.

4 ganese industry, a source of airborne metals emissions.

5 has strong, increasing effects on Arctic VOC emissions.

6 or 0.44 and 0.74% (95% CI) of annual global emissions.

7 challenge for determining vent-specific gas emissions.

8 uboptimal solutions in terms of regional GHG emissions.

9 meterization previously used for fossil fuel emissions.

10 the biochemical processes that control N(2)O emissions.

11 oviding advective fingerprints of city CO(2) emissions.

12 were also observed for both CH(4) and NH(3) emissions.

13 rogen loss, conservation, and greenhouse gas emissions.

14 her characterization of these nontraditional emissions.

15 h the potential to reduce net greenhouse gas emissions.

16 t peatlands has resulted in ecosystem carbon emissions.

17 s is dominating the increase in global CH(4) emissions.

18 catalytic membrane significantly reduces NO emissions.

19 their important contribution to global CH(4) emissions.

20 ur dioxide and/or organic precursors in ship emissions.

21 izer use efficiency and mitigation of N(2) O emissions.

22 ke of the ocean in response to anthropogenic emissions.

23 to enrich energy supplies and mitigate CO(2) emissions.

24 2) eq per kg milk because of land use change emissions.

25 undant and reactive VOCs associated with VCP emissions.

26 arming-induced rise in soil CH(4) and N(2) O emissions (1.84 Pg CO(2) -equivalent/year) could reduce

27 Kerr effect(1,2), spontaneous helical light emission(3,4) from ferromagnetic (FM) monolayers and ele

28 cost(3) and selective manipulation of their emission(4).

29 r addition fluorescence (excitation 325 nm / emission 410 nm) as indicator of tyrosine oxidation and

30 o be a suitable approach to decrease methane emissions, a relevant cleaner effect that may contribute

31 ed at the early stages of implementing NH(3) emission abatement.

32 enomenon, supracence only measures molecular emission above its excitation energy due to entanglement

33 o elucidate the breakdown of embodied carbon emissions across products' value chains, how this breakd

34 r chemistry due to their aggregation-induced emission (AIE) properties.

35 mission by air traffic, aviation particulate emission also deserves attention.

36 Anthropogenic emissions alter secondary organic aerosol (SOA) formatio

37 timulation also contributes to the afterglow emission and its contribution can be dominant when ambie

38 g the orbit) and they show both thermal dust emission and line emission from ionized gas(6-10).

39 ts from other models, mitochondrial H(2)O(2) emission and oxidative damage were greater in Taz(KD) th

40 Time-resolved emission and transient absorption experiments revealed t

41 ced bathochromic shifts in both fluorescence emission and UV/Vis absorption spectra of a two-fold int

42 ponsible for the largest anthropogenic CO(2) emissions and are key to effective emission reduction st

43 unt for over half of annual methane (CH(4) ) emissions and can offset summer photosynthetic carbon di

44 s of drought- mortality on second-entry burn emissions and compared emissions for the first- and seco

45 of ships are a considerable source of CO(2) emissions and contribute to climate change.

46 ral species that have different fluorescence emissions and different abilities to diffuse across cell

47 % of the estimated increase in global CFC-11 emissions and is consistent with the emission increases

48 Toxin emissions and legacies are major global issues affecting

49 ectives on managing drivers to reduce carbon emissions and make dentistry more environmentally sustai

50 o accurately estimate facility-scale methane emissions and perform source attribution at subfacility

51 o reach 76.41% in 2050, both reducing carbon emissions and promoting eco-friendly development.

52 ecause of limited knowledge of the precursor emissions and the chemical environment of smoke plumes.

53 by the pervasive human influence on ammonia emissions and the nitrogen cycle in the Anthropocene.

54 d frequency, potentially intensifying carbon emissions and transitioning the region from a globally s

55 to understand how soil greenhouse gas (GHG) emissions and uptake will respond to ongoing climate cha

56 under a high-intensity greenhouse gas (GHG) emissions and urban development pathway.

57 Elevated levels of nitrous oxide (N(2)O) emissions are a matter of concern in agricultural soils

58 Currently, CH(4) emissions are a missing component of VCE C budgets.

59 st, we find that engineered waterways, whose emissions are currently not reported in inventories, may

60 rought risks will be lower if greenhouse gas emissions are cut aggressively.

61 Such direct anthropogenic emissions are gaining importance, as those from furnishi

62 generally overestimated if associated N(2) O emissions are not considered but, with the exception of

63 For the year 2014, the added O&NG emissions are predicted to affect surface ozone across a

64 These emissions are responsible for an increased number of day

65 food systems by examining the greenhouse gas emissions associated with food transport.

66 economy-wide energy requirements and carbon emissions associated with future household consumption,

67 Since the greenhouse gas (GHG) emissions associated with landfilling waste can occur ov

68 le Stokes shift of 15 000 cm(-1) to generate emission at 633 nm.

69 wer sector could cut half of its 2015 carbon emissions at a cost about 6% lower compared to business-

70 que excitation independent photoluminescence emission, attributed to their single-emission fluorescen

71 ind that lower-bound reported annual methane emissions averaged 22.1 Gg (-16.9, +19.5) between 2014 a

72 ric, time horizon, climate threshold, global emissions budget calculation method, and effort-sharing

73 uch-publicized environmental impact of CO(2) emission by air traffic, aviation particulate emission a

74 a comprehensive assessment of greenhouse gas emission by aquatic ecosystems.

75 Moreover, prediction of methane emission by VFA indicators could be useful for increasin

76 , but it reduced energy use by 19.2% and GHG emissions by 15.2%.

77 New York City (NYC) committed to reduce GHG emissions by 80% by 2050 (80 x 50).

78 Remarkably, a broad emission can be demonstrated with quick formation of 3 p

79 In especially affluent suburbs, these emissions can be 15 times higher than nearby neighborhoo

80 al variations in global [Formula: see text]O emissions can be traced to seasonal upwelling in the tro

81 sinks of the biosphere, but methane (CH(4)) emissions can offset their climate cooling effect.

82 o a wide range of biomass ashes in a closed 'emission-capture' process 'loop'.

83 are limited in their capability to estimate emissions changes at scales that capture the grid-scale

84 t fluorescence in the green, cyan, or yellow emission channels, allowing the transgene to be used wit

85 temperatures, particularly for Euro 4 and 5 emission classes.

86 Dopamine transporter single-photon emission computed tomography can improve the accuracy of

87 wever, on typical air pollution events, fire emissions contributed as high as 50-75% (80-120 mug/m(3)

88 ic emissions from meteorological changes and emission control policies on this PM(2.5) concentration

89 ars; they are considered part of an abnormal emission control strategy.

90 Furthermore, the spectral emission could be continuously tuned from blue through g

91 Our results show that garbage burning emissions could increase PM(2.5) concentrations by nearl

92 n the potential of BECCS to achieve negative emissions could result in delayed reductions in gross CO

93 ery close to an interface and its near-field emission couples to the higher refractive index medium (

94 hreshold of ~0.6 muW and a large spontaneous emission coupling efficiency up to 18% under continuous-

95 rials reported possess broad-band absorption/emission covering the whole mid-infrared wavelength(11-1

96 ly disaggregated fossil fuel CO(2) (FFCO(2)) emission data products.

97 Combining study emission data with 2017 GHGRP activity data, the study i

98 carbon emissions using an original sectoral emissions dataset.

99 iques, including super-resolution stimulated emission depletion (STED), photoactivated localization m

100 ive-cell fluorescence imaging and stimulated emission depletion super-resolution microscopy were perf

101 l for long-term, high-resolution (stimulated emission depletion) STED nanoscopy.

102 We correlate stimulated-emission-depletion microscopy of proteins and synchrotro

103 ive indirect proxy for reliably assessing Pb emissions directly linked to human activities.

104 zing non-contact camera sensing of Cherenkov emission during the radiation therapy treatment.

105 Notably, however, the room-temperature emission efficiency and the fluorescence lifetime of the

106 donor shows significant aggregation induced emission enhancement (AIEE) after assembling with SC4AD.

107 Comparing this to previously reported CFC-11 emissions estimated for earlier years, we estimate CFC-1

108 = 0.84) was found between total VOC (C4-C12) emissions estimated using SUMMA canisters and data repor

109 combine direct energy consumption and carbon emission estimates with life cycle assessment to calcula

110 on data from in-field studies assessing AMLD emissions estimates.

111 nce-driven building and street-scale FFCO(2) emissions estimation through the atmospheric CO(2) inver

112 To assess whether the EU ETS reduced carbon emissions even as permits were cheap, we estimate counte

113 The region- and crop-specific emission factors (EFs) of N fertilizer for NH(3) are poo

114 LD emission rate estimates and correct these emissions factors based on data from in-field studies as

115 We derive emissions factors from AMLD emission rate estimates and

116 mobile phones with multipass excitation and emission filters on the flash and camera to image the si

117 escence emission, attributed to their single-emission fluorescence centre.

118 ition, size, and lanthanide doping-dependent emission, focusing on upconversion quantum yield (UCQY)

119 We measured daily soil CO(2) emission for the first two weeks and every other day in

120 on second-entry burn emissions and compared emissions for the first- and second-entry burns.

121 hich contributed to higher second-entry burn emissions for two of the three burn treatments when comp

122 The detection of emission from carbon monoxide in the galaxy yields a mol

123 In BC, the total GHG emission from gas SCVF is estimated to reach about 75,00

124 be used as an effective way to reduce N(2)O emission from hypoxic soil in agricultural production sy

125 hey show both thermal dust emission and line emission from ionized gas(6-10).

126 imated for earlier years, we estimate CFC-11 emissions from (eastern) China to have increased by 7 +/

127 We find that annual methane emissions from abandoned wells are underestimated by 150

128 therefore the global estimate of soil NH(3) emissions from agricultural N fertilizer application is

129 on, and plant community composition on CH(4) emissions from an estuarine tidal wetland.

130 requirements for production, process-related emissions from clinker formation, and raw materials dema

131 hlights the importance of ground-level NH(3) emissions from composting nitrogen-rich organic waste or

132 72% of synthetic N fertilizer-induced NH(3) emissions from croplands in the world and 70% in China.

133 the synchronous increase in biomass burning emissions from deforestation in the Northern Hemisphere.

134 y reducing "business as usual" air pollutant emissions from economic activities.

135 wever, there is little information on N(2) O emissions from forest streams although they constitute a

136 data resulted in the detection of unexpected emissions from FPIs, demonstrating the value of these da

137 characterization of material-specific NH(3) emissions from landfills and land-application of digesta

138 , we found that reductions in sulfur-dioxide emissions from large point sources and nitrates and EC e

139 7.9% (95% CI) of combined total national GHG emissions from Malaysia and Indonesia or 0.44 and 0.74%

140 the influence of reductions in anthropogenic emissions from meteorological changes and emission contr

141 from large point sources and nitrates and EC emissions from mobile sources contributed the largest re

142 ern California homes to (1) quantify methane emissions from natural gas leaks and incomplete combusti

143 Methane (CH(4)) emissions from oil and gas activities are large and poor

144 Emissions from ships in and surrounding ports are a majo

145 ry program designed to reduce greenhouse gas emissions from the electric power sector within the Nort

146 ure and storage (CCS) scenarios with process emissions from the U.S. industrial sector by analyzing t

147 e tested the hypothesis that exposure to the emissions from the volcano is associated with thyroid ca

148 tated to a great degree by the trajectory of emissions from urban areas.

149 since 2008, has been attributed to increased emissions from wetlands and cattle, as well as from shal

150 ns and to project changes under severe, high emissions future (2081-2100) climate projections (RCP8.5

151 Herein, we designed aggregation-induced emission gold clustoluminogens (AIE-Au) to achieve effic

152 The emission has a long photoluminescence (PL) lifetime of 5

153 tain suitable water quality, with associated emissions, has however been seen as challenging from a g

154 Increasing iodine emissions have implications for ozone radiative forcing

155 Instead, atmospheric observations show that emissions have increased and in 2018 were higher than at

156 cial costs of carbon and other air pollutant emissions highlights the importance of ground-level NH(3

157 m and anthraquinone adducts show red-shifted emission in the solid state, attributable to the charge-

158 ut 29% and 5% of total agricultural soil GHG emissions in China and the world, respectively.

159 is the main source of anthropogenic particle emissions in large areas of the globe, influencing clima

160 unts for roughly 20% of greenhouse gas (GHG) emissions in the United States.

161 yr at a 90% capture efficiency or 75% of the emissions in this sector, with missed opportunities equa

162 This would lead to overestimation of emissions in warm biomes, underestimation in cold biomes

163 al risk of dental procedural generated spray emissions (including aerosols and splatters), for severe

164 AGNPs exhibit a series of tunable afterglow emissions, including blue, yellow, green, and white.

165 CFC-11 emissions and is consistent with the emission increases attributed to this region in an earli

166 Greenhouse gas emission intensities for ethanol vehicles ranged from 20

167 Average feedstock production emissions intensities were similar between sorghum and c

168 sed milk yields by 44%-51%, FoCo reduced GHG emission intensity from 2.4 +/- 0.1 to 1.6 +/- 0.1 kg CO

169 Isoprene has the highest emission into Earth's atmosphere of any nonmethane hydro

170 ant sources of mantle carbon dioxide (CO(2)) emission into Earth's atmosphere(1-3).

171 ly strong transverse magnetic (TM) polarized emission is recorded, which is ~4 times stronger than th

172 , either involving propagating or near-field emission, is widely being used in spectroscopy, sensing,

173 t effects of fire, in addition to the direct emissions, is an overlooked mechanism for explaining dec

174 h back the timeline to reduce greenhouse gas emissions, largely undermining the Paris goals.

175 The combination of these emissions led to near-perfect white emission with a phot

176 nalysis of trans-parinaric acid fluorescence emission lifetimes, we could determine that cholesterol

177 ns) of a small spectral side band, the broad emission line shape is constant to 100 ns.

178 borated by DFT calculations reveal a complex emission mechanism involving contributions of both therm

179 of meteorological influences, the effective emission mitigation measures achieved an average decreas

180 Specifically, nitric oxide emissions (NO) lead to increased smog, acid rain, climat

181 sks similarly decreased the outward particle emission of a coughing superemitter, who for unclear rea

182 superfluid which we propose arises from the emission of a flux of surface excitations from the chann

183 ureus enzyme micrococcal nuclease results in emission of a readily detectable fluorescence signal.

184 nt with the estimate from the ionized carbon emission of about 72 billion solar masses.

185 ave adapted to by reducing or mitigating the emission of anthropogenic noise into the environment.

186 report that red-shifting of the fluorescence emission of Au nanoclusters (AuNCs) into NIR-II region w

187 Interestingly, the emission of GO-AuNPs becomes "turn-on" after the additio

188 displacement sensor based on the directional emission of Huygens dipoles excited in an individual dip

189 seagrass loss likely resulted in cumulative emissions of 0.06-0.14 Tg CO(2-eq) over the last 40 year

190 Gulf of Mexico our inventory estimates total emissions of 0.53 Tg CH(4)/yr [0.40-0.71 Tg CH(4)/yr, 95

191 study indicated statistically lower national emissions of 1290 [1246-1342] Gg methane per year or 66%

192 l and gas well inventory yields well average emissions of 55.6 Gg CH(4).

193 Recent reports of unexpected emissions of CFC-11 raise the need to better quantify re

194 ction in India's future power sector related emissions of CO(2).

195 Human emissions of fluorescent aerosol particles (FAPs) can in

196 demonstrate the influence the SML exerts on emissions of iodine and potentially other volatile speci

197 period, we estimated reductions in pollutant emissions of more than a third in comparison with the co

198 observation strongly suggests that changing emissions of other (isotopically-lighter) CH(4) source t

199 pletion in the Antarctic stratosphere due to emissions of ozone-depleting substances(9-11).

200 ne, recent studies have shown that growth in emissions of the less abundant chlorocarbons could pose

201 , and HCFC-22, indicating co-location of the emissions of these compounds.

202 ometric luminescent thermometer based on the emissions of two lanthanide ions.

203 rships for utilities, accounting for scope 3 emissions of utilities, and being open to extend utiliti

204 suring the environmental integrity of carbon emission offsets.

205 Enhancement of optical emission on plasmonic nanostructures is intrinsically li

206 tructures to amplify, direct, and tune their emission or as hosts for isolated, coherent spin states

207 t kiln to improve efficiency and lower CO(2) emissions, or the output gases may be used for other val

208 vations of fires, shows that biomass-burning emissions over the northwest IGP play a crucial role dur

209 a follows the current legislation (baseline) emission pathway.

210 ply the framework to assess final energy and emission pathways for meeting three essential and energy

211 Having emission peaks from 670 nm to 720 nm, the next generatio

212 roughly studied the chemistry involving dual-emission persistent luminescence nanoparticles (D-PLNPs)

213 The kinetics of the first emission phase was mainly correlated with the hydrophobi

214 This work evaluates the emission pricing and technology costs required to conver

215 monstrated attractive broad-band white-light emission properties, they pose a serious long-term envir

216 We derive emissions factors from AMLD emission rate estimates and correct these emissions fact

217 The average NO(x) emission rate increases with engine load and decreasing

218 Monthly emission rates differ by >12x, and 3-hourly rates vary b

219 This study derives methane emission rates from 92 airborne observations collected o

220 ination of their chemical constituents, high emission rates, and global distribution.

221 are controlled mainly by the Dy(3+)-centered emission rather than by the ligand-centered bands, imply

222 The overall thermal emission recorded during drying was significantly differ

223 nic CO(2) emissions and are key to effective emission reduction strategies.

224 nput-output (GMRIO) model to develop scope 3 emission reduction targets for individual economic secto

225 varies by industry, and whether the reported emission reductions vary with the granularity of the PCF

226 d be considered in meeting its commitment to emission reductions.

227 Their area, distribution and emissions respond to interannual and longer-term climate

228 e NiO(x) membrane are observed by both field-emission scanning electron microscope (FE-SEM) and high-

229 Field-emission scanning electron microscopy elucidated the mor

230 the interface was characterised using field emission-scanning electron microscopy (FE-SEM) and cycli

231 spread in its future projection under a high emission scenario.

232 opical coastlines within 30 years under high-emissions scenarios.

233 da(s) ) were found to be lowest under higher emissions scenarios.

234 In a nationwide epidemiological study of emission sector contribution to PM2.5-related mortality,

235 bits two-photon absorption and near-infrared emission simultaneously.

236 The evolutions for both emission spectra and hardness of molten zone were resear

237 Emission spectral features reveal that molecular formati

238 atography-inductively coupled plasma-optical emission spectrometry (HPLC-ICP-OES) in addition to dete

239 ng femtosecond Fe K(alpha) and K(beta) X-ray emission spectroscopy (XES) with Fe K-edge X-ray absorpt

240 site-occupation is determined through X-ray emission spectroscopy (XES).

241 ve femtosecond Fe K(alpha) and K(beta) X-ray emission spectroscopy at an X-ray free-electron laser (F

242 The emission spectrum from the QDs was optimized to match th

243 However, for blue perovskite LEDs, the emission spectrum line width is broadened to over 25 nm

244 the very strong spectral overlap between the emission spectrum of benzimidazole (energy donor) and th

245 and food production sectors to reduce carbon emissions, strengthen adaptive capacity, and increase fo

246 nce of anthropogenic carbon dioxide (CO(2) ) emissions, strongly impacts marine ecosystems.

247 These GHG emissions suggest that conversion of Southeast Asian pea

248 V charging produces ~70% more and ~20% fewer emissions than daytime charging.

249 forest gain, leading to a net greenhouse gas emission that exacerbates global climate change.

250 For crop-specific emissions, the NH(3) EFs averaged 11.13%-13.95% for the

251 sent, but, without mitigating greenhouse gas emissions, this can decrease to 3.5 years by 2100.

252 tored as well as resulting changes in N(2) O emissions to better estimate the climate benefits of the

253 tes the feasibility of using radio-frequency emissions to detect 0.003 to 1,600 MQNs, depending on B(

254 n to constrain the contribution of shale gas emissions to observed atmospheric increases in the globa

255 ortance of both external transport and local emissions to PM(2.5) pollution in Delhi.

256 ensities by using [(18)F]flumazenil positron emission tomography ([(18)F]FMZ-PET) and GABA concentrat

257 ecially that of an important cancer positron emission tomography (PET) agent [(18)F]5-fluorouracil ([

258 one measured with [(11)C]-LY2795050 positron emission tomography (PET) as a predictor of response to

259 Towards this end, positron emission tomography (PET) imaging has emerged as one of

260 arfentanil, a selective MOR agonist positron emission tomography (PET) radioligand, to investigate en

261 All subjects underwent positron emission tomography (PET) scans with two different radio

262 F-florbetapir or (18)F-florbetaben) positron emission tomography (PET), (18)F-flortaucipir PET, and a

263 Using positron emission tomography (PET), we identified the dorsal stri

264 n the basis of promising results of positron emission tomography (PET)-directed treatment approaches,

265 r-infrared spectroscopy (NIRS), and positron-emission tomography (PET).

266 (18)F-Fluorodeoxyglucose (FDG) positron emission tomography (PET)/computed tomography (CT) is cu

267 measures of AT(N) (amyloid and tau positron emission tomography [PET]) structural magnetic resonance

268 rk) study group cohort with amyloid positron emission tomography and behavioral data.

269 nuclear imaging techniques such as positron emission tomography and white blood cell scintigraphy ha

270 brain imaging with high-resolution positron emission tomography brain imaging.

271 Positron-emission tomography can quantify these processes in vivo

272 toacoustic, magnetic resonance, and positron emission tomography modalities.

273 n volume (TSPO V(T)), measured with positron emission tomography, mainly reflects gliosis in neuropsy

274 y of fluorine-18-fluorodeoxyglucose positron emission tomography-computed tomography (18F-FDG-PET/CT)

275 aluate the activity of FAP via FAPI-positron emission tomography-computed tomography scans in human h

276 es and measured brain activity with positron emission tomography.

277 (18)F-fluorodeoxyglucose positron emission tomography/computed tomography ((18)F-FDG PET/C

278 1000 islets) could be visualized by positron emission tomography/computed tomography imaging.

279 tients underwent a 3-month post-CRT positron emission tomography/computed tomography scan and were th

280 imultaneously acquired (11) C-PBR28 positron emission tomography/magnetic resonance imaging data of 1

281 e basin, consistent with the accumulation of emissions underneath inversions.

282 easurements could be used to constrain urban emissions using an inverse modeling framework and (2) qu

283 ere cheap, we estimate counterfactual carbon emissions using an original sectoral emissions dataset.

284 ple is labeled with a different signature of emission wavelengths and mixed with other samples just m

285 RNA interference (RNAi) to suppress isoprene emission, we show that this trait, which is thought to b

286 Global N(2)O emissions were 17.0 (minimum-maximum estimates: 12.2-23.

287 The cumulative N(2)O emissions were between 60 and 600 g N(2)O-N ha(-1), smal

288 CO(2) emissions were consistent across ecosystem types and cli

289 e, (i) 10 times as many potential industrial emissions were detected as compared to the WWTP receivin

290 d and particulate organic carbon, suggesting emissions were primarily fuelled by contemporary carbon

291 irst, NZ's production- and consumption-based emissions were quantified using multiregional input-outp

292 The indirect effects of warming on VOC emissions were significant but smaller than the direct e

293 e sites are primarily due to sustained local emissions, while the low concentrations measured at Mt.

294 Global fossil fuel carbon dioxide (FFCO(2)) emissions will be dictated to a great degree by the traj

295 Finally, amplified spontaneous emission with a low threshold 4.16 uJ cm(-2) is achieved

296 of these emissions led to near-perfect white emission with a photoluminescence quantum efficiency of

297 es can be monitored by measuring the thermal emission with thermal imaging.

298 result in delayed reductions in gross CO(2) emissions, with consequent high risk of overshooting glo

299 nocubes, these new nanocrystals with intense emission would certainly provide a new avenue for contin

300 peratures of continually increasing isoprene emissions yet reported (50 degrees C).