ライフサイエンスコーパス: burning

1 sources (19 to 73% contribution from biomass burning).

2 from vehicle emissions and residential fuel burning.

3 as a hydrocarbon flame, indicating soot-free burning.

4 ) emissions are much lower than from biomass burning.

5 nd the PPARalpha-FGF21 axis that reduces fat burning.

6 at-residue burning, leaf litter, and garbage burning.

7 lly in tropical areas with extensive biomass burning.

8 erally adverse effects of smoke from biomass burning.

9 ly enhanced by the nuclear ashes of hydrogen burning.

10 g brown carbon compounds produced by biomass burning.

11 15% (n = 12) of the EC stemmed from biomass burning.

12 ating possible fuel limitations to continued burning.

13 itivity, and one patient exhibited cutaneous burning.

14 ribution yield 57 +/- 21% of EC from biomass burning.

15 riety of sources, often dominated by biomass burning.

16 e gases, and toxic compounds from open waste burning.

17 arboiled rice samples, dried by gas and wood burning.

18 tration of K, an inorganic tracer of biomass burning.

19 oline vehicles, diesel vehicles, and biomass burning.

20 by extensive deforestation and anthropogenic burning.

21 ning contribution comes from natural biomass burning.

22 o the increases in non-N nutrients caused by burning.

23 TSF and the units' difference in time since burning.

24 tion in regions strongly impacted by biomass burning.

25 ate emissions worldwide from industrial coal-burning.

26 nd to a lesser degree from increased biomass burning.

27 le particles present in emissions of biomass burning.

28 pulation-weighted ambient PM2.5 from biofuel burning (11 mug/m(3)) could be almost as large as from f

29 Agra had much higher MSW-burning (39-202 incidents/km2-day; 672-3485 kg/km2-day)

30 The delta(15)N-NOx produced by burning a variety of biomass types ranged from -7 to +12

31 ield method thus captures differences in MSW-burning across cities, neighborhoods, diurnally and seas

32 related uncertainties, and reveal widespread burning across large regions of western North America du

33 rganic carbon aerosol emissions from biomass burning activities are a main cause of the observed decl

34 uring the periods with enhanced open biomass-burning activities in Southeast Asia or Southeast China.

35 easing fraction of absorption as the biomass-burning aerosol aged.

36 HULIS) in particulate matter such as biomass burning aerosol chelate Fe(II), but the effect on ROS fo

37 tudy illustrates that reducing local biomass burning aerosol emissions may be a useful way to mitigat

38 this chloride acid displacement, the biomass-burning aerosol still converted on the order of 10% of r

39 ies, the particulate chloride in the biomass-burning aerosol was rapidly but incompletely displaced,

40 circulation changes, the increase in biomass burning aerosols causes local drying of the atmosphere.

41 We suggest that the brownishness of biomass burning aerosols indicates the amount of BC/BrC as well

42 s larger than approximately 0.8, all biomass burning aerosols look blackish.

43 Biomass burning aerosols mainly consist of black carbon (BC) and

44 The regional characteristics of biomass burning aerosols were found to depend strongly on the mo

45 black carbon and larger than that of biomass burning aerosols.

46 the lowest exciton state, that is, resonant burning allows the protein to access only its conformati

47 that is caused by BC from direct fossil fuel burning and 0.86% of the warming associated with CO2 emi

48 dicted for northern peatlands will stimulate burning and carbon losses as has occurred in their small

49 ic carbon emitted as a result of fossil fuel burning and cement manufacture.

50 strongly associated with pollution from coal burning and further data are needed about other solid fu

51 States, almost 90% of which is from biomass burning and gasoline vehicles.

52 of England, a region with a history of coal burning and heavy industry.

53 of pulmonary disease attributable to biomass burning and infectious diseases among women in low- to m

54 he spatial frequency of the incidence of MSW-burning and presents results in three neighborhoods of v

55 sions and facilitating conversion to cleaner-burning and renewable fuels.

56 OC indicator, and PC represents both biomass burning and secondary aerosol.

57 rgence of Hg emissions from unregulated coal burning and small-scale gold mining.

58 apes through deforestation, agriculture, and burning and thereby might reduce the capacity of landsca

59 vels of atmospheric SO2 emitted from biomass burning and volcanic eruptions.

60 own how ecosystems will respond to increased burning and warming.

61 sures included the reduction of pruritus and burning and/or pain according to a visual analog scale (

62 the ratio of carbon to oxygen during helium burning, and affects subsequent carbon, neon, oxygen, an

63 etter quantify the HCOOH source from biomass burning, and assess whether fire emissions can help clos

64 olatile oxygenated organic aerosols, biomass burning, and hydrocarbon like organic aerosols.

65 are converted into titanium suboxides during burning, and initial biotoxicity screening suggests that

66 exchange, gross primary production, biomass burning, and respiration to these climate anomalies by a

67 In addition, vehicular emissions, biomass burning, and soil sources were associated with all respi

68 Day 1, the residents' wood burning appliance operated as usual with no air cleaner.

69 tions, specifically improved-technology wood-burning appliances or air-filtration devices, would impr

70 gases and particulate matter from open waste burning are more significant on regional scales.

71 Global emissions of CO2 from open waste burning are relatively small compared to total anthropog

72 No association was observed for burning artificial fire-logs [HR=0.98 (95% CI: 0.85, 1.1

73 reasons, informal activities including open burning, backyard recycling, and landfill are still the

74 by carbon monoxide poisoning resulting from burning barbecue charcoal reached epidemic levels in Hon

75 attributed to primary emissions from biomass burning (BB) and fossil fuel burning (FFB).

76 carbon (BrC), from laboratory-based biomass burning (BB) has been studied intensively to understand

77 Particles from smoldering biomass burning (BB) represent a major source of carbonaceous ae

78 IS), which are abundantly emitted in biomass burning (BBOA) and include highly oxidized OA from multi

79 the Indo-Gangetic Plain (IGP) region is from burning biomass fuel used in traditional, open-design co

80 ent of the total carbon that is emitted from burning biomass over the same period.

81 ed trial to compare the effects of a cleaner burning biomass-fuelled cookstove intervention to contin

82 ence that an intervention comprising cleaner burning biomass-fuelled cookstoves reduced the risk of p

83 ence that an intervention comprising cleaner burning biomass-fuelled cookstoves reduced the risk of p

84 sised that replacing open fires with cleaner burning biomass-fuelled cookstoves would reduce pneumoni

85 geochemical processes, including fossil fuel burning, biospheric photosynthesis and respiration, hydr

86 ition that the FOA3 is applicable to engines burning both conventional and alternative fuel blends wi

87 Initially, large biomass burning BrC molecules were rapidly photoenhanced, follow

88 d the total light absorption of aged biomass burning BrC.

89 intrinsic DTT activity, followed by biomass burning (BURN) and heavy-duty diesel vehicles (HDDV) (0.

90 from fossil fuel combustion, especially coal burning but also from diesel traffic, were associated wi

91 osene were also low compared with solid fuel burning but had a relatively high F30 value of approxima

92 In contrast to extensive burning by European settlers, variations in indigenous p

93 This study reveals that open-field biomass burning can be an important source of various semivolati

94 molecular weight BrC compounds from biomass burning can be relatively long-lived components in atmos

95 The exhaust of a burning candle was introduced in the chamber as a typica

96 Burning caused a less than 4 month increase in leaf nitr

97 ust sensing, without electrode corrosion and burning/causing discomfort in subjects.

98 c, heterogeneous combustion process within a burning cigarette was investigated by a miniaturized ext

99 Here we have discovered that burning coal also produces large quantities of otherwise

100 Yet, burning coal produces more global warming CO2 relative t

101 of HB data for both nonresonant and resonant burning conditions.

102 orptive properties of POA depend strongly on burning conditions.

103 ine, diesel, and coal fly ash, while biomass burning contained a combination of Se(0)/Se(-II) and Se(

104 about 2%-3% of total generated MSW; morning-burning contributed >65% of the total.

105 The aqSOA from biomass burning contributes to the "brown" carbon (BrC) budget a

106 a at cruise altitudes are sparse for engines burning conventional fuels, and no data have previously

107 Using two new wood-burning cookstove designs from Lawrence Berkeley Nationa

108 Deployment of improved biomass burning cookstoves is recognized as a black carbon (BC)

109 rimental health and climate effects; cleaner-burning cookstoves may provide "co-benefits".

110 to extend to fires in other regions, biomass burning could produce 14 Tg/a of HCOOH in the tropics or

111 DRF at the top of atmosphere during biomass burning days decreased in negative magnitude by several

112 ient conditions to 3.6 W/m(2) during biomass burning days.

113 Burning declined abruptly before temperatures cooled, in

114 Although global biomass burning decreased in last 150 years, regional large scal

115 We found that PM2.5 from biomass burning, diesel vehicle, gasoline vehicle, and dust sour

116 days of global C emissions from fossil fuel burning each year.

117 nst instabilities triggered by spectral hole burning effects, and the possibility of more versatile m

118 on at midcentury reflects policies promoting burning efficiency and fuel transitions rather than regu

119 research has yet to harness their potential burning efficiency for enhanced combustion.

120 est adult residence at least once a week and burning either wood or natural gas/propane was associate

121 mospheric methane with these revised biomass burning emissions (and assuming no change to the chemica

122 We collected filter samples of biomass-burning emissions at three locations in Canada and the U

123 nocturnal chemistry using authentic biomass-burning emissions in a smog chamber.

124 OA mass formation from processing of biomass-burning emissions in the aqueous phase.

125 Here we show that biomass burning emissions of methane decreased by 3.7 (+/-1.4) T

126 he inversion estimates a decrease in biomass-burning emissions that could explain falling ethane abun

127 rmore, contributions of biogenic and biomass-burning emissions to contemporary OC were estimated to b

128 ynamometer tests, cooking emissions, biomass burning emissions, and a highway traffic tunnel.

129 ds, such as alkaloids resulting from biomass burning emissions, are among HULIS constituents.

130 experiments for fresh and processed biomass-burning emissions.

131 s exposed to air pollution caused by biomass burning emissions.

132 e-stream smoke (the smoke emanating from the burning end of the cigarette), a major component of SHS,

133 roadside measurements under apparent biomass burning event (Delta-C > 1000 ng m(-3)) and nonevent (De

134 investigate the influence of a major biomass burning event on the light absorption properties of atmo

135 t was observed during the night-long biomass burning event.

136 n chest [aPR=1.58 (95% CI: 1.37, 1.81)], and burning eyes [aPR=1.48 (95% CI: 1.35, 1.64).

137 ns from biomass burning (BB) and fossil fuel burning (FFB).

138 since fire and the difference in time since burning for a focal-source pair ranging from 3 to 58 mon

139 dung), wood, kerosene/diesel, or natural gas burning for cooking and heating and all-cause and cause-

140 I show that the hottest pile of burning fuel occurs when the height of the pile is rough

141 sented, including their thoughts on the most burning fundamental and practical questions regarding th

142 ng to source apportionment analysis, biomass burning had the highest contribution (50.3%) to average

143 hese findings establish the concern that the burning-hair plume often present during LHR should be co

144 calculation of resonant and nonresonant hole-burning (HB) spectra of pigment-protein complexes is pre

145 paradoxical, sometimes painful, sensation of burning heat.

146 used by deforestation and associated biomass burning Hg emissions.

147 Increased burning, however, did not persist throughout the MCA.

148 understand the importance of the products of burning in global C cycle dynamics.

149 cles, products of cooking, heating, and wood burning in indoor environments, and, more recently, prod

150 Near Arkhangelsk (White Sea), biomass burning in mid-latitudes, surface transportation, and re

151 ymptoms, with the strongest associations for burning in nose, throat, or lungs (OR = 4.73; 95% CI: 3.

152 ming associated with CO2 emissions from coal burning in power plants.

153 material apparently originating from biomass burning in South America is also present, while a smalle

154 e transport of air pollutants from wildfires burning in southern California.

155 eam and electricity production, biomass open burning in sugarcane fields, and diesel-powered agricult

156 g episodic neuropathic pain characterized by burning in the extremities.

157 the OSRC, with the strongest association for burning in the nose, throat, or lungs [adjusted PR (aPR)

158 This study suggest a larger role for biomass burning in the radiative forcing of climate in the remot

159 related pollutant species from solid biomass burning in traditional cookstoves is a global concern.

160 ollution focus on emissions from fossil fuel burning in urban centers.

161 Daily MSW-burning incidents ranged from 24 to 130/km2-day during w

162 Burning increased exotic plant invasion relative to pref

163 Recurring biomass burning-induced smoke haze is a serious regional air pol

164 s to be favored at sites with strong biomass burning influence or connected to more polluted air mass

165 Biomass burning is a known source of brown carbon aerosol in the

166 Household air pollution from solid fuel burning is a leading contributor to disease burden globa

167 se experiments directly confirm that biomass burning is a potentially significant source of atmospher

168 Biomass burning is a source of both particulate chloride and nit

169 The estimated F- flux from biomass burning is comparable to total fluorine emissions from c

170 Seasonal biomass burning is considered a large pollution source in Africa

171 ed in current inventories because open waste burning is not included, consistent with studies that co

172 hes (OR = 1.81; 95% CI: 1.41, 2.58); watery, burning, itchy eyes (OR = 1.61; 95% CI: 1.20, 2.16); and

173 combustion include paddy- and wheat-residue burning, leaf litter, and garbage burning.

174 ted with oxygenated species (primary biomass burning markers) increased (decreased) with MCE; fresh O

175 resh litter, and the historical frequency of burning may alter C and N retention of both fresh litter

176 glyoxal emissions from agricultural biomass burning may be significantly overestimated.

177 soil nitrogen that result from more frequent burning may in turn decrease the carbon that is sequeste

178 broadening, as observed using spectral hole burning measurements.

179 including fossil fuel, microbial and biomass-burning methane emission sources.

180 nt across years, were found for residual oil burning (nickel, zinc), near-road traffic (copper, iron,

181 e fractional contribution to BC from biomass burning (north of 60 degrees N) vary between 11% and 68%

182 bon-like OA (HOA), cooking OA (COA), biomass burning OA (BBOA), and low volatility and semivolatile o

183 OOA (MO-OOA), cooking OA (COA), and biomass burning OA (BBOA).

184 -like OA is largely water-insoluble, biomass burning OA and cooking OA have the largest range of wate

185 on days while high concentrations of biomass burning OA inhibited particle growth.

186 s spectrometer resolved two types of biomass burning OA, which appeared to have different chemical co

187 Local burning occurred at least three times in the past 4,500

188 Smoke from the burning of biomass fuels has been linked with adverse pr

189 wn to increase during fasting to enhance the burning of fat by activating the beta-oxidation pathway.

190 e growth in global carbon emissions from the burning of fossil fuels and cement production between 20

191 te levels of climate change due to the human burning of fossil fuels.

192 Indoor burning of fuel for heating or cooking releases carcinog

193 in the core are high enough to start nuclear burning of hydrogen.

194 The burning of LPG and alcohol had the lowest PM2.5 mass emi

195 Open-burning of municipal solid waste (MSW) is a major source

196 ith high incidence of lung cancer due to the burning of smoky coal (a bituminous coal, which in healt

197 However, the burning of these resources in ever increasing pace is ac

198 wn-regulation after hepatectomy promotes the burning of TRAS-derived lipids to fuel hypertrophic live

199 for 39 individual SVOCs are determined from burning of various fuel types that are common in tropica

200 The open burning of waste, whether at individual residences, busi

201 The ''in situ burning" of trapped crude oil on the surface of Gulf wat

202 We tested the impacts of burning on different sized herbivores' habitat preferenc

203 ant light absorption contributors of biomass burning organic aerosol (BBOA), suggesting that night ti

204 transport (6-45 h), suggesting that biomass burning organic aerosol concentration and chemical prope

205 ting substantial nighttime emissions of wood burning organic aerosols (OA) from local residential hea

206 formation of reactive compounds capable of 'burning out' the whole photosynthetic unit.

207 an ingredient in spicy peppers that produces burning pain by activating transient receptor potential

208 mplaints of recurrent redness, swelling, and burning pain in his left arm.

209 yndrome characterized by episodes of intense burning pain triggered by warmth, is caused by mutations

210 nts with IEM suffer from episodes of intense burning pain triggered by warmth, the effects of increas

211 Cutaneous porphyria patients suffer from burning pain upon exposure to sunlight and other patient

212 tense acute flares of inflammation, itching, burning pain, vasodilatation, and redness of the extremi

213 Long-term global climate change, caused by burning petroleum and other fossil fuels, has motivated

214 E-DBD does not reach a stable state during a burning phase, whereat the maximum and minimum Talphabet

215 for reducing CO2 emissions from fossil fuel burning plants.

216 ide and formaldehyde in agricultural biomass burning plumes intercepted by the NOAA WP-3D aircraft du

217 the primary PM2.5 sources assessed, biomass burning PM2.5 was most strongly associated with respirat

218 f respiratory disease ED visits with biomass burning PM2.5; associations with diesel and gasoline PM2

219 thoxyphenol, GUA), a lignocellulosic biomass burning pollutant, is addressed in this work.

220 st of electricity generated by a fossil fuel-burning power plant would rise substantially, owing to t

221 ations based on data from 19,941 fossil-fuel burning power plants.

222 pective, but from an understory perspective, burning promoted rich and productive native understories

223 nd a larger sized mode dominating under slow burning pyrolysis (Dva approximately 600 nm).

224 of log wood on glowing embers, that is, slow burning pyrolysis conditions.

225 m explained 17% of the variability in ocular burning (R = 0.41; P < .001), and PTSD score, tear break

226 play a major role in determining the global burning rate.

227 Burning reduced the cover of the dominant grasses by mor

228 complications from the API such as residual burning, reflux or metallic taste sensations to deal wit

229 Near the main biomass burning regions, global and regional modelling indicates

230 H underestimate most prominent over tropical burning regions, suggesting a major missing source of or

231 al biomass burning, we estimate that biomass burning releases 76 Gg F- yr(-1) to the atmosphere, with

232 iated with lowering the water table and peat burning, releasing large amounts of carbon stored in pea

233 e human lung.Solid-state emissions from coal burning remain an environmental concern.

234 These data demonstrate that biomass burning represents a major source of fluorine to the atm

235 uding six major emission indicators: boilers burning residual oil; traffic density; industrial struct

236 issippi River sulfate due to coal mining and burning, respectively.

237 e in Serengeti National Park, as mediated by burning's effects on vegetation height, live : dead biom

238 ering the carbon sink capacity of frequently burning savanna grasslands and broadleaf forests.

239 In the September-October 2007 biomass-burning season in Santa Cruz, Bolivia, we studied light

240 n (P-treatment x time interaction < 0.0005), burning sensation (P-treatment x time interaction < 0.00

241 Other symptoms were dryness, redness, burning sensation and itching.

242 All patients complained of a mild burning sensation upon application of the ointment.

243 However, burning sensation was more pronounced with tacrolimus (P

244 ress as shown by the associations with pain, burning sensation, nausea, and bloating scores.

245 eover, both groups decreased the presence of burning sensation, tearing, foreign body sensation, conj

246 ith skin or is ingested, it causes a painful burning sensation.

247 in foreign body sensation, and reduction in burning sensation.

248 ng pain is followed by a C-related prolonged burning sensation.

249 g (P <0.001), dry mouth (P <0.001), and oral burning sensations (P <0.05) were worse among patients i

250 mpared with the control plots, Rs in the low burning severity plots decreased by 19%, while it decrea

251 y 19%, while it decreased by 28% in the high burning severity plots.

252 e results showed that Rs decreased with fire burning severity.

253 remaining samples (n=15) collected from peat burning, shredded tire combustion, and cook-stove emissi

254 t PAH exposure was up to 6 times higher when burning smoky coal than smokeless coal and varied by up

255 s that due to the emissions from fossil fuel burning, so changes in either will impact future climate

256 exposures from vehicular emissions, biomass burning, soil, and secondary nitrate and sulfate sources

257 he concentrations and composition of biomass burning-, soil bacterial- and plant wax- tracers corresp

258 ool to apportion the contribution of biomass burning sources to the BCeq mass.

259 l combustion exposures, especially from coal-burning sources.

260 subsequent carbon, neon, oxygen, and silicon burning stages.

261 M-dwarf stars--hydrogen-burning stars that are smaller than 60 per cent of the s

262 rate/severe pain, 41.1% vs 24.2%, P = .003), burning/stinging bother (often/always, 38.7% vs 15.7%, P

263 cy end points included additional VAS items (burning/stinging, itching, foreign body sensation, eye d

264 this prospective study, using an indoor wood-burning stove/fireplace in the longest adult residence a

265 Having an indoor wood-burning stove/fireplace in the longest adult residence w

266 mized trial was conducted in homes with wood-burning stoves among children with asthma.

267 icantly higher for Philips wood and charcoal-burning stoves compared to the threestone fire and coalp

268 the impact of indoor air pollution from wood-burning stoves or fireplaces on breast cancer risk.

269 ildren living with asthma in homes with wood-burning stoves.

270 The lack of specific codes for charcoal-burning suicide in the International Classification of D

271 ime trends and regional patterns of charcoal-burning suicide throughout East/Southeast Asia during th

272 In 1995/1996, charcoal-burning suicides accounted for <1% of all suicides in al

273 Charcoal-burning suicides increased markedly in some East/Southea

274 ure and archaeology reveal hermetic sealing, burning sulfur, desiccant dusts, and toxic botanicals as

275 ed 120 y, representing a 260% higher rate of burning than during the period of dendroecological sampl

276 form of steady-state phononic spectral hole burning that produces a wideband transparency window wit

277 During days dominated by biomass burning the absorption of solar energy by aerosols withi

278 sal strategies such as boiling, roasting, or burning to be differentiated.

279 We investigated the ability of biomass burning to produce N2O5(g) and ClNO2(g) through nocturna

280 Acrolein is formed during combustion (e.g., burning tobacco or biomass), during high-temperature coo

281 values of glyoxal relative to other biomass burning trace gases, indicating that glyoxal emissions f

282 rtime atmospheric processing of this biomass burning tracer.

283 iquitous gas in the atmosphere and a biomass burning tracer.

284 ive correlations of O3 with multiple biomass burning tracers in these HOLW structures.

285 radiative forcing and could serve as biomass burning tracers.

286 a were used to assign PMF factors to biomass burning, traffic, and smoking emission sources.

287 highest PAH emissions were found during fast burning under hot air starved combustion conditions, in

288 Doxepin was associated with more stinging or burning, unpleasant taste, and greater drowsiness than t

289 rsion into oil palm plantation with periodic burning was 1400 Mg C ha(-1) over 100 years, which is eq

290 ogical catastrophes.' Landscape-scale severe burning was catastrophic from a tree overstory perspecti

291 Most burning was confined to deforested lands (82%; 133,216 h

292 llen and charcoal data indicate that biomass burning was relatively low during warm/dry steppe-domina

293 when farming communities expanded and forest burning was used for land clearance.

294 ased on recent evaluations of global biomass burning, we estimate that biomass burning releases 76 Gg

295 d 10-year hazard ratios from kerosene/diesel burning were 1.06 (95% confidence interval, 1.02-1.10) a

296 .5) water-soluble fluoride (F-) from biomass burning were evaluated during the fourth Fire Laboratory

297 oncentrations observed during Amazon biomass burning were sufficient to induce severe adverse effects

298 t direct contact with smoke near an actively burning wildland fire.

299 itional stove/fuel combinations, the Philips burning wood or charcoal showed significant fuel and ene

300 Burning wood or plant materials (tobacco stems, corncobs