ライフサイエンスコーパス: ultrafine

1 The polymicrogyria was readily detected by ultrafine 1.5-mm coronal slices on three-dimensional, Fo

2 than larger nanocrystalline (60-100 nm) and ultrafine (100-500 nm) grains.

3 Two ultrafine aerosol growth events were observed during oil

4 se state and internal structure of sea spray ultrafine aerosols and other mixed-phase particles under

5 The internal structure of smaller, ultrafine aerosols depends also on the value of the line

6 ir in the presence of 100 to 200 ug.m(-3) of ultrafine aerosols of ammonium sulfate.

7 quid, vitrified, and crystallized water-salt ultrafine aerosols with radii from 2.5 to 9.5 nm and wit

8 Ultrafine aerosols with sizes between 3 and 15 nm have b

9 Earth's troposphere, and iodine oxides form ultrafine aerosols, which may have an impact on climate.

10 By optimizing the Joule heating method, ultrafine Ag nanoparticles ( approximately 40 nm) are ho

11 In experimental settings, ultrafine air pollutants instilled directly into the car

12 ad been identified as an important source of ultrafine air pollutants resulting in elaborated treatme

13 fractions of primary alpha-Al dendrites and ultrafine Al-Si eutectic of lamellar morphology.

14 ethod for direct synthesis of interconnected ultrafine amorphous NiFe-layered double hydroxide (NiFe-

15 In the current study, ultrafine amorphous particles (UAPs) of cyclosporin A (C

16 ts and the subsequent formation of telomeric ultrafine anaphase bridges (UFBs), ultimately leading to

17 lementary strand synthesis in early mitosis, ultrafine anaphase bridges, and G1-specific p53-binding

18 rmation of a new subclass of human ribosomal ultrafine anaphase bridges.

19 ologic, and cardiovascular endpoints between ultrafine and accumulation mode zinc oxide particles.

20 Laboratory number size distributions show ultrafine and accumulation modes at 53 (+/-1) and 276 (+

21 icle size fraction, finding lower values for ultrafine and coarse particles than for submicrometer pa

22 d most of the sulfur was concentrated in the ultrafine and fine modes.

23 While studies show that ultrafine and fine particles can be translocated from th

24 Consumer-level 3D printers emit ultrafine and fine particles, though little is known abo

25 Continuous measurements were made for both ultrafine and fine particulate matter as well as black c

26 roughput synthesis of an extensive series of ultrafine and homogeneous alloy MMNCs, achieved by 1) a

27 r real-time analysis of organic compounds in ultrafine and large aerosol particles.

28 Microstructures in nature are ultrafine and ordered in biological roles, which have at

29 e-resolved particle deposition rates for the ultrafine and submicrometer particles using a nonlinear

30 to improved assessment of human exposure to ultrafine and submicrometer particles.

31 unique reaction type for facile synthesis of ultrafine and well-dispersed Pt nanoparticles supported

32 investigate the microstructural evolution of ultrafine- and nanocrystalline-grained tungsten under co

33 Three particle size modes were seen: ultrafine (below 0.1 mum), fine (0.1 to 1.0 mum), and co

34 as evidenced by the accumulation of anaphase ultrafine bridges and 53BP1 nuclear bodies in G1 phase o

35 cells evade the G2 damage checkpoint to form ultrafine bridges, fragmented centromeres, and uneven ch

36 so a determinant for its localization on the ultrafine bridges.

37 ids (BALf) from male C57BL/6 mice exposed to ultrafine carbon black nanoparticles, a model of chronic

38 duals, well-defined experimental exposure to ultrafine carbon particles (UFP) increases sympathetic n

39 ies is self-assembled from solution to yield ultrafine chitin nanofibers embedded in a silk matrix.

40 is demonstrated by successfully synthesizing ultrafine Co-metal-decorated 3D ordered macroporous tita

41 tigate the mechanism(s) by which exposure to ultrafine concentrated ambient particles (CAPs) adversel

42 lly important fluid separations that require ultrafine differentiation of closely sized molecules.

43 roteins, are localized to the extremities of ultrafine DNA bridges (UFBs), which link sister chromati

44 positive chromatin bridges and DAPI-negative ultrafine DNA bridges (UFBs).

45 g as a marker, we have identified a class of ultrafine DNA bridges in anaphase that are surprisingly

46 target mitotic DNA intertwinements, known as ultrafine DNA bridges, facilitating chromosome segregati

47 ion-mode particles, depicted as low-contrast ultrafine droplets, are observed in TEM images.

48 tudy presented here is dedicated to fine and ultrafine dust characterization and determination in mor

49 t since health hazards arising from fine and ultrafine dust particles have become more evident.

50 Bimodal ultrafine eutectic composites (BUECs) exhibit a good com

51 ing conditions, owing to the formation of an ultrafine eutectoid microstructure that appears as a res

52 characterization of anisotropic responses of ultrafine ferrite grains to stresses using state-of-the-

53 This work describes the development of ultrafine fibers with acai (Euterpe oleracea Mart.) extr

54 potential health effects of exposure to the ultrafine fraction of underground PM warrant further inv

55 rticular focus is placed on particles in the ultrafine fraction.

56 Freshly generated zinc oxide in the fine or ultrafine fractions inhaled by healthy subjects at rest

57 The ultrafine frozen powder exhibits excellent spectral qual

58 elopments include the targeted deposition of ultrafine glucocorticoid particles to treat small airway

59 e to a high density of nano-oxides (NOs) and ultrafine grain sizes.

60 ing between nanoparticles and Al matrix, and ultrafine grain sizes.

61 Low carbon nanograined/ultrafine-grained (NG/UFG) bulk steel was processed usin

62 anoscale spheroidized cementite (Fe3C) in an ultrafine-grained (UFG) ferritic steel.

63 Nanostructured (NS) and ultrafine-grained (UFG) materials have high strength and

64 rittle at 77 K, the uniform elongation of an ultrafine-grained (UFG) microstructure (grain size ~ 2.0

65 induced 9R phase with tens of nm in width in ultrafine-grained aluminium with an average grain size o

66 al damage in single-crystal, coarse-grained, ultrafine-grained and nanograined metals.

67 This is accomplished by generating an ultrafine-grained as-sintered microstructure through hyd

68 Ultrafine-grained die-upset Nd-Fe-B magnets are of impor

69 e use an AlCoCrFeNi(2.1) EHEA to engineer an ultrafine-grained duplex microstructure that deliberatel

70 tructured ferritic alloys are a new class of ultrafine-grained oxide dispersion-strengthened steels t

71 under stress results in faults delineated by ultrafine-grained solid reaction products formed during

72 ulse laser beams for two different grades of ultrafine-grained tungsten.

73 the final pass sample shows a combination of ultrafine grains and micro shear bands.

74 ip, display similar characteristics, in that ultrafine grains approach the nanometre scale, gouge sur

75 or the operation of DRX and the formation of ultrafine grains is significantly reduced.

76 creased biofuel use and mounting evidence on ultrafines' health effects make our result acutely polic

77 the reduced metal elements were gathered to ultrafine HENAs and stabilized by defective carbon suppo

78 Bloom's syndrome protein) helicase decorate ultrafine histone-negative DNA threads that link the seg

79 al Ionization Mass Spectrometer (TDCIMS) and Ultrafine Hygroscopicity Tandem Differential Mobility An

80 measurements of the composition of fine and ultrafine individual particles as demonstrated in initia

81 All hairdryers were found to emit ultrafine iron, carbon, and copper.

82 Impact of ultrafine jet-milling did however not systemically impac

83 nd reduces total PM mass but increases total ultrafine (less than 100 nm in diameter) PM concentratio

84 We exposed C57BL6/J mice to ultrafine (< 100 nm) CAPs using the Harvard University C

85 Human exposure to airborne ultrafine (<<1 mum) particulate pollution may pose subst

86 imes) compared to the fine (0.1-2.5 mum) and ultrafine (<0.1 mum) PM.

87 veness of portable air purifiers in removing ultrafine (<0.10 mum) and submicrometer particles (0.10-

88 characterized by a major single mode in the ultrafine (<0.25 mum) size range and the V(IV) size dist

89 Ultrafine (<100 nm) particle emission rates ranged from

90 composition of single fine (100-300 nm) and ultrafine (<100 nm) particles.

91 tion) analysis on aerosols, particularly for ultrafine (<100 nm) particles.

92 edded inside a matrix of nanocrystalline and ultrafine (<300 nm) grains.

93 high sulfur coal, had the highest amount of ultrafine mass and most of the sulfur was concentrated i

94 Ultrafine mass concentrations were directly related to e

95 ion strategy for preparing highly dispersed, ultrafine metal nanoparticle catalysts on an electroacti

96 es, large surface area, and highly dispersed ultrafine MgO nanocrystallites (ca. 3 nm in size), toget

97 DT and DRX mechanisms, based on which fully ultrafine microstructures having a mean grain size down

98 ial and high energy efficiency, by employing ultrafine Mo(2) C nanoparticles anchored on a carbon nan

99 resulting in a decrease of particles in the ultrafine mode.

100 that combines highly dispersed palladium and ultrafine molybdenum phosphate nanoparticles on silica.

101 n of outbred mice, MF1, can be treated as an ultrafine mosaic of standard inbred strains and accordin

102 hierarchical porous network structure, with ultrafine MOx nanoparticles uniformly distributed in mul

103 nanometer resolutions, which is critical for ultrafine nanocircuit metrology.

104 ging with Gd2O3:Eu(3+) nanorods is that this ultrafine nanorod material exhibits hypersensitive inten

105 The ultrafine nanoseeds achieved by rapid Joule heating rend

106 e is strong support for an important role of ultrafine (nanosized) particles.

107 However, ultra-long metal ultrafine/nanowires are beyond the capability of current

108 Chronic exposure to airborne carbon black ultrafine (nCB) particles generated from incomplete comb

109 Ultrafine organically modified silica-based nanoparticle

110 Ultrafine palladium active phases can be highly disperse

111 he controlled synthesis and stabilization of ultrafine palladium nanoparticles (PdNPs).

112 density (LAD) within the canopy impacts the ultrafine particle (UFP) collection efficiency at the br

113 ng aviation-related contributions to ambient ultrafine particle (UFP) concentrations in complex, mult

114 Sampling strategies in the collection of ultrafine particle (UFP) data to develop land-use regres

115 Ultrafine particle (UFP) emissions and particle number s

116 Long-term ultrafine particle (UFP) exposure estimates at a fine sp

117 filters but their filtration efficiency for ultrafine particle (UFP) is rather low.

118 Ambient ultrafine particle (UFP; 10-100 nm), accumulation mode p

119 ared with the ambient room baseline level of ultrafine particle concentrations (ambient room baseline

120 Fine and ultrafine particle concentrations were 10-50% lower on b

121 Ultrafine particle concentrations were measured within t

122 ze the chemical composition and quantify the ultrafine particle content of the plume generated during

123 s below T(crit) and consequently do not show ultrafine particle emissions above background level.

124 critical brake temperature T(crit), at which ultrafine particle emissions occur, from 140 to 170 degr

125 Ultrafine particle emissions originating from fused depo

126 The majority of the existing ultrafine particle epidemiology studies are based on exp

127 nal care products (PCP) might be a source of ultrafine particle exposure for users owing to the react

128 s obstruction receive an increased dose from ultrafine particle exposure.

129 they may not be significant sources of total ultrafine particle exposure.

130 though an independent analysis suggests that ultrafine particle mass (PM0.1) correlates better with p

131 Samples of ultrafine particle matter mass (PM(0.1)) were collected

132 oad air pollution models for traffic-related ultrafine particle number concentration (PNC).

133 Estimating ultrafine particle number concentrations (PNC) near high

134 le impacts of aviation activities on ambient ultrafine particle number concentrations (PNCs), we anal

135 ulate matter (PM2.5), black carbon (BC), and ultrafine particle number concentrations (UFPN).

136 emission controls showed promise in reducing ultrafine particle number concentrations, although the c

137 nerated two times more particle mass, larger ultrafine particle number distribution modes, and partic

138 s allowed us to build on previous studies of ultrafine particle number I/O ratios to develop predicti

139 ycyclic aromatic hydrocarbons, black carbon, ultrafine particle number, and fine and coarse particula

140 iesel bus emissions to 100 degrees C removed ultrafine particle numbers by 69-82% when a nucleation m

141 cted with 91 PCP to detect the occurrence of ultrafine particle production from exposure to common in

142 position could play a more important role in ultrafine particle removal.

143 cles in the fresh ship engine exhaust are in ultrafine particle size range.

144 mes essential in clean environments in which ultrafine particle sources are present.

145 ions between IHD mortality and both fine and ultrafine particle species and sources.

146 Ultrafine particle-exposed mice exhibited significantly

147 This paper presents ultrafine-particle (UFP) emission factors (EFs) as a fun

148 Ultrafine particles (< 0.1 microm diameter) are believed

149 C57BL/6J mice were exposed to ultrafine particles (< 100 nm in aerodynamic diameter; C

150 they are currently unregulated, atmospheric ultrafine particles (<100 nm) pose health risks because

151 r air pollutants, specifically the number of ultrafine particles (+32%), NO(x) (+9.3%), and the parti

152 uding organic carbon, elemental carbon (EC), ultrafine particles (10-100 nm), inorganic ions, carbohy

153 A high proportion of ultrafine particles (10-30 nm) in RME exhaust could be a

154 Meanwhile, ultrafine particles (20-100 nm) decreased by 35%.

155 ss spectra are normally used to characterize ultrafine particles (defined here as particles smaller t

156 xicology studies indicate that inhalation of ultrafine particles (Dp < 0.1 mum) causes adverse health

157 Fine and ultrafine particles (FP and UFP) were measured continuou

158 llow fiber membrane was used in removing the ultrafine particles (PMs with aerodynamic equivalent dia

159 bons, fine particulate matter (PM(2.5)), and ultrafine particles (reported using particle number conc

160 Ultrafine particles (smaller than about 0.1 microm) are

161 develop land-use regression (LUR) models for ultrafine particles (UFP) and black carbon (BC).

162 Methods to characterize chronic exposure to ultrafine particles (UFP) can help to clarify potential

163 We used two training sets of ultrafine particles (UFP) data (mobile measurements (820

164 Although there is evidence that ultrafine particles (UFP) do affect human health there a

165 Inhalation exposure to ambient ultrafine particles (UFP) has been shown to induce adver

166 Health effects of long-term exposure to ultrafine particles (UFP) have not been investigated in

167 airports, the morphology and composition of ultrafine particles (UFP) in aircraft engine exhaust wer

168 Iodic acid largely explains the growth of ultrafine particles (UFP) in most events.

169 Evidence of short-term effects of ultrafine particles (UFP) on health is still inconsisten

170 Ultrafine particles (UFP) produced by electric heating o

171 miological evidence on the health effects of ultrafine particles (UFP) remains insufficient to infer

172 2.5), PM(10), nitrogen oxides, NO(2), NO(x), ultrafine particles (UFP), and oxidative potential (OP)

173 scientific interest in personal exposure to ultrafine particles (UFP).

174 Human exposure to airborne ultrafine particles (UFP, < 100 nm) has been shown to ha

175 Therefore, the study of ultrafine particles (UFP, <100 nm in diameter) provides

176 Ultrafine particles (UFP, dp < 0.1-0.2 mum) are redox ac

177 Short-term exposure to ultrafine particles (UFP; <100 nm in diameter), which ar

178 dies, controlled exposures to (concentrated) ultrafine particles (UFP; particles with an aerodynamic

179 The epidemiological evidence for ultrafine particles (UFP; particles with diameter <100 n

180 for fleet vehicle-based mobile monitoring of ultrafine particles (UFPs) and black carbon (BC) by comp

181 ar-road air quality based on measurements of ultrafine particles (UFPs) and black carbon (BC) in Toro

182 s, we conducted the current study to compare ultrafine particles (UFPs) and fine particles (PM2.5) in

183 luding traffic-related air pollutants [e.g., ultrafine particles (UFPs) and nitrogen dioxide].

184 sional (3D) printers have been shown to emit ultrafine particles (UFPs) and volatile organic compound

185 Ultrafine particles (UFPs) are airborne particulates of

186 Studies of the health effects of ultrafine particles (UFPs) in large nationwide cohorts a

187 for adverse birth outcomes, but the role of ultrafine particles (UFPs) is not well understood.

188 peroxides and metals are enriched within the ultrafine particles (UFPs) of aged vaping emissions, whi

189 itrogen oxides (NOX), black carbon (BC), and ultrafine particles (UFPs) on diesel-dominated southern

190 logical data exist concerning the impacts of ultrafine particles (UFPs) on the etiology of childhood

191 er of <= 2.5 mum (PM2.5), black carbon (BC), ultrafine particles (UFPs), and accumulated-mode particl

192 ases (>100%) in in-vehicle concentrations of ultrafine particles (UFPs), black carbon, and PM2.5 as w

193 ittle is known about the association between ultrafine particles (UFPs), defined as particles less th

194 Such PAHs are highly bonded to the ultrafine particles (UFPs), the smallest PM size fractio

195 le are frequently exposed to vehicle-derived ultrafine particles (UFPs).

196 diameter</=2.5 mum), black carbon (BC), and ultrafine particles (UFPs, diameter</=100 nm).

197 esktop 3D printers can emit large numbers of ultrafine particles (UFPs, particles less than 100 nm) a

198 tle is known regarding the impact of ambient ultrafine particles (UFPs; <0.1 mum) on childhood asthma

199 rains compared with electric trains were for ultrafine particles 212 000 particles/cm(3) (35-fold), b

200 Exposure to ultrafine particles also resulted in an inhibition of th

201 Epidemiological associations between ultrafine particles and health effects, however, have be

202 Given health concerns related to ultrafine particles and NO(x), our findings call for add

203 ations between long-term exposure to outdoor ultrafine particles and nonaccidental and cause-specific

204 an increase in during-walk exposure to NO2, ultrafine particles and PM2.5, and an increase in PWV an

205 Ultrafine particles are emitted at high rates by jet air

206 Conclusions: As outdoor ultrafine particles are not currently regulated, there i

207 vestigated residential ESP filters to reduce ultrafine particles between 4 to 15 nm and quantified th

208 Fine/ultrafine particles can easily reach the pulmonary acinu

209 However, the fate of ultrafine particles caught in the filters has received l

210 We conclude that ultrafine particles concentrate the proatherogenic effec

211 oc = 100 vs Nloc = 300 the CV in R(2)adj for ultrafine particles decreased from 0.088 to 0.029 and fr

212 The ambient concentration of ultrafine particles during LHR was measured by condensat

213 cal and compositional analyses of individual ultrafine particles in aircraft plumes were performed on

214 thin the Brain Development and Air Pollution Ultrafine Particles in School Children (BREATHE) Project

215 The abundant ultrafine particles in the aviation exhaust with diamete

216 The dosimetry of ultrafine particles in the human lung is poorly characte

217 Evidence of SOA formation (ultrafine particles in the range 10-100 nm) is reported

218 The presence of ultrafine particles indicates that drugs can be aerosoli

219 Thus, ultrafine particles ingestion alters gut microbiota comp

220 stemic effects, recent studies indicate that ultrafine particles may be translocated into the circula

221 condary pollution including formaldehyde and ultrafine particles might be generated, depending on the

222 A majority of the ultrafine particles observed in real-world conditions ar

223 nvironments leads to high levels of fine and ultrafine particles similar to tobacco cigarettes (t-cig

224 These elevations were mostly comprised of ultrafine particles smaller than 40 nm.

225 sure to fully evaluate the health effects of ultrafine particles using epidemiology.

226 tions of black carbon, NO2, PM10, PM2.5, and ultrafine particles were higher on Oxford Street than in

227 Unexpectedly high concentrations of ultrafine particles were observed over a wide range of l

228 ure to PM < 1.0 mum in aerodynamic diameter (ultrafine particles) and PM < 2.5 and < 10 mum in aerody

229 n monoxide, methane, total hydrocarbons, and ultrafine particles) were continuously monitored.

230 ffects of ambient particles of <0.18 microm (ultrafine particles) with particles of <2.5 microm in ge

231 matter (PM2.5), sulfates, black carbon (BC), ultrafine particles, and gaseous pollutants, averaged ov

232 bon, particulate matter (PM) concentrations, ultrafine particles, and nitrogen dioxide (NO2) concentr

233 luded PM2.5 (PM = particulate matter), PM10, ultrafine particles, black carbon, and the elemental com

234 vels of other coemitted pollutants (e.g., EC ultrafine particles, carbonyls, or PAHs, depending on st

235 These animals were exposed to concentrated ultrafine particles, concentrated particles of <2.5 micr

236 OP(DTT) per mass (toxicity) was highest for ultrafine particles, estimated lung deposition was mainl

237 tes with that of the number concentration of ultrafine particles, indicating a potential role of ON i

238 ely utilize the negative ion mass spectra of ultrafine particles, it is important to understand biase

239 Ultrafine particles, often minor contributors to atmosph

240 fire smoke may interact with freshly emitted ultrafine particles, resulting in a decrease of particle

241 PM, especially ultrafine particles, upregulated TH cytokine levels, IgE

242 chemically characterize individual fine and ultrafine particles, with the goal of providing new insi

243 these systems are able to remove almost all ultrafine particles.

244 ype of fuel used--strong sources of fine and ultrafine particles.

245 rticulate emissions DOC especially decreased ultrafine particles.

246 P chemicals and is also activated by ambient ultrafine particles.

247 ht materially influence personal exposure to ultrafine particles.

248 x were associated both with black carbon and ultrafine particles.

249 e in PWV and augmentation index with NO2 and ultrafine particles.

250 onometrics to quantify a key source of urban ultrafine particles.The biofuel ethanol has been introdu

251 red the size, composition, and morphology of ultrafine particulate emissions from a "three-stone" tra

252 of exposure to concentrated ambient fine and ultrafine particulate matter (CAP).

253 to a nanosized subfraction of urban traffic ultrafine particulate matter (nPM, < 200 nm) in vivo, ex

254 nt air pollutants were dominated by fine and ultrafine particulate matter (PM) that was present at hi

255 Exposure to ambient ultrafine particulate matter (UFP) is a well-recognized

256 Ultrafine particulate matter (UFP; diameter <0.1 mum) co

257 t wavelengths, 222 and 254 nm, both produced ultrafine particulate matter.

258 cal stressors, including but not limited to, ultrafine particulate matters.

259 nsation particle counter was used to measure ultrafine particulates (<1 microm).

260 generation by abrasion, absent for fine and ultrafine particulates, which may be derived from high-t

261 cage-supported catalyst with well-dispersed ultrafine Pd nanoparticles (NPs) in a narrow size distri

262 Such ultrafine Pd NPs in Pd@MTC1-1/5, in cooperation with pho

263 emonstrate that the electrical properties of ultrafine platinum nanowires are highly sensitive and se

264 0 mum) was 3-4 times more abundant than fine/ultrafine PM (<2.5 mum).

265 Fine and ultrafine PM (respectively, PM2.5 and PM0.1) by source a

266 llowing 100 mug downwind coarse and downwind ultrafine PM exposures.

267 cyclic aromatic hydrocarbons (PAHs) found in ultrafine PM have been linked to cardiovascular diseases

268 caused greater increases than downwind fine/ultrafine PM in bronchoalveolar lavage neutrophils, eosi

269 les of upwind and downwind coarse, fine, and ultrafine PM were collected using a wind direction-actua

270 t 24 h postexposure compared to the fine and ultrafine PM, and similar toxicity outcomes were observe

271 , little is known about the chemistry of the ultrafine (PM0.1) fraction that may contribute significa

272 hus leading to the formation of the isolated ultrafine polar nanoclusters with varying sizes from 2 t

273 d at 77 K and is subsequently ground into an ultrafine powder.

274 ucture of TiO(2) single crystals coated with ultrafine Pt nanoparticles (NPs, 0.5-2 nm) and exhibit e

275 Homogeneous dispersion of ultrafine Pt nanoparticles on 3D architectures construct

276 are capable of synthesizing surfactant-free, ultrafine PtSn alloyed nanoparticles (NPs) on various ca

277 mall-to-medium size molecules, for which the ultrafine resolution of the bulky, expensive, and high-m

278 osite size fractionated PM (coarse, fine and ultrafine) samples were collected, extracted, chemically

279 confined and controlled local contact at the ultrafine scale in the form of quasi-static nanoindentat

280 Here we report a new class of robust, ultrafine silica core-shell nanoparticles formed from si

281 Herein, this study shows that ultrafine silver (Ag) nanoparticles, which are synthesiz

282 Ultrafine single-chain tadpole polymers (SCTPs), contain

283 red to those with PM2.5, suggesting that the ultrafine size fraction (</= 100 nm) and the fine size f

284 Constructing robust nucleation sites with an ultrafine size in a confined environment is essential to

285 distributions exhibited over 90% of PNCs in ultrafine size range (<100 nm) and a negligible fraction

286 cal agglomerates and gold mirror composed of ultrafine smoothly shaped particles.

287 tion microscopy has enabled visualization of ultrafine spatial organizations of molecular assemblies

288 rconducting magnets have enabled, with their ultrafine spectral resolution, the determination of the

289 Iron-rich, ultrafine, spherical particles, probably combustion-deri

290 onstrate the first photoinduced synthesis of ultrafine (sub-2 nm) Ag2 S quantum dots (QDs) from Ag na

291 otential implications given that NM, such as ultrafine superparamagnetic iron oxide nanoparticles (US

292 e studied the deposition and clearance of an ultrafine technetium-99m-labeled aerosol in 10 patients

293 An ultrafine thermocouple technique was developed to measur

294 he resultant aerogels have highly porous and ultrafine three-dimensional (3D) networks consisting of

295 mpression of plasmonic nanoarrays results in ultrafine tunable line-gaps at sub-10 nm scale by collab

296 (also termed as UTSA-200), is reported with ultrafine tuning of pore size (3.4 A) to effectively blo

297 e studied the effects of chronic exposure to ultrafine (UF) particles.

298 Importantly, ultrafine underground PM shows similar metal-rich concen

299 These results suggest that ultrafine vellum does not necessarily derive from the us

300 , 12 healthy adults inhaled 500 microg/m3 of ultrafine zinc oxide, the same mass of fine zinc oxide,