ライフサイエンスコーパス: dust

1 rse are obscured by large columns of gas and dust.

2 twice, compared to the background household dust.

3 tudies could detect peanut allergen in house dust.

4 to high temperatures and increased airborne dust.

5 furniture would have higher levels of FRs in dust.

6 indicated atmospheric input of platinum-rich dust.

7 are frequently found in and re-emitted from dust.

8 ctly from contaminated food, water, air, and dust.

9 y, including salts, plays in water uptake by dust.

10 reFAAs were higher than for PFAAs in air and dust.

11 e of serum PBDE levels than vacuum-collected dust.

12 on surfaces of soot and non-tailpipe traffic dust.

13 vestigate the direct transfer from source to dust.

14 soluble inorganic phosphate (delta(18)OP) in dust.

15 mospherically important component of mineral dust.

16 Der p 1 weight/weight concentration in house dust.

17 o ambient dust, suggesting mixing with local dust.

18 described the water uptake properties of the dusts.

19 es can determine the hygroscopicity of playa dusts.

20 For H(+) < 10(-4) mol/g of dust, 1-10% of the total P is dissolved, largely as a re

21 s showed the highest median concentration in dust (1200 ng/g), followed by EFRs (730 ng/g) and HBCDDs

22 apatite-P (Ap-P), the major mineral phase in dust (79-96%), occurs whether calcium carbonate (calcite

23 ely the major influences on European glacial dust activity and propose that European dust emissions w

24 we project that climate change will increase dust activity in the southern Great Plains from spring t

25 This study found that changes of dust activity in the U.S. in the recent decade are large

26 However, whether dust activity in U.S. will increase in the future is not

27 Mineral dust aerosol is one of the major types of aerosol presen

28 Mineral dust aerosols are responsible for some of the largest so

29 impact in one of largest sources of mineral dust aerosols of the U.S., the Owens Lake area in Califo

30 basin that might limit the impact of mineral dust aerosols on climate.

31 tes of OHCs, ingestion of OHCs (i) via house dust and (ii) via cat food.

32 FRs can migrate out of products into dust and are linked to cancer, neurological impairment,

33 Deposited mineral dust and black carbon are known to reduce the albedo of

34 ldren (n = 17), PBDEs were measured in house dust and child handwipes sampled during a home visit.

35 Mean annual dust and dissolved boron atmospheric depositions are com

36 ons and isotopic compositions of atmospheric dust and dissolved depositions were monitored over a two

37 results imply that the bulk of the obscuring dust and gas is located within a few to tens of parsecs

38 DNA from mattress dust and nasal samples of 86 school age children was ana

39 rtant because it regulates the efficiency of dust and planetesimal coagulation, and the formation of

40 ited alkalinity from the carbonate buffer in dust and seasalt can provide the only likely set of cond

41 y air and personal ambient air), dust (floor dust and surface dust), and hand wipes were sampled from

42 n index [aOR = 0.41 (0.21-0.83)] in mattress dust and to a lower extent in nasal samples [richness aO

43 rt measurements of CCN activation from playa dusts and parameterize these results in terms of both ka

44 , leaf grades (whole leaf, broken, fannings, dust) and manufacturing techniques (orthodox, "crush, te

45 l ambient air), dust (floor dust and surface dust), and hand wipes were sampled from 61 participants

46 Paired samples of cat serum, house dust, and cat food were analyzed for brominated flame re

47 engths because of absorption by interstellar dust, and distances are very large and hard to measure.

48 ether occupational exposures to vapors, gas, dust, and fumes (VGDF) are associated with high-attenuat

49 asses of gas and 2.5 billion solar masses of dust, and is more massive than any other known object at

50 sunlight reflected from local interplanetary dust, and large discrepancies in the inferred brightness

51 peanut proteins have been detected in house dust, and their levels correlate with peanut allergy pre

52 hermetic sealing, burning sulfur, desiccant dusts, and toxic botanicals as early control methods.

53 AAs) that have been widely detected in house dust, aquatic biota, surface water, and wastewater envir

54 asthma with bacterial diversity in mattress dust as compared to nasal samples suggests microbial inv

55 Instead of focusing on dust as the major iron source and emphasizing iron's tig

56 esistance genes (ARGs) compared with ambient dust, asserting that the origin of these genes is local

57 es was also compared to that of Arizona Test Dust (ATD) particles.

58 sent a comparative study on the diversity of dust-borne bacterial communities in dust storms from thr

59 e primarily to the initiation of substantive dust-borne iron fertilization of the Southern Ocean duri

60 Characterizing the dust-borne microbiome in dust storms of different origin

61 on of binary asteroids and to the release of dust, both directly and, in some cases, through uncoveri

62 nosity, which arises from the sublimation of dust; by the gravitational potential of the black hole;

63 ental exposure to aeroallergens in household dust can be a risk factor for the development of allergi

64 though the annual deposition flux of mineral dust can be up to 20 times higher than that of BC, we fi

65 Our results demonstrate that exogenic dust can drive the evolution of nutrient budgets in mont

66 fine mode, whereas total metals and mineral dust cations were highest at the road-side site and in t

67 We report a change in dust chemistry from an Asian affinity to a Central-South

68 Dust classification was the most prevalent seeding type

69 tting regions, limiting our understanding of dust-climate interaction.

70 tion, dynamos and winds on evolved stars, in dust clouds and on brown dwarfs.

71 impact sites, the formation of interstellar dust clouds, ballistic penetrators, spacecraft shielding

72 s are less like billiard balls and more like dust clouds, with apparent coherence only due to similar

73 er hen's egg allergen is detectable in house dust collected from different household areas and whethe

74 re workers (602 samples) using electrostatic dust collectors (EDC).

75 rtance of regional changes in land cover and dust concentrations in affecting the potential intensity

76 counting for the Sahara greening and reduced dust concentrations leads instead to an increase of TC a

77 Higher house dust concentrations of cockroach, mouse, and cat allerge

78 We observed that the dust concentrations of substances exclusively transferre

79 n changes are varied but also vegetation and dust concentrations.

80 ort on detections of [C ii] 158-mum line and dust-continuum emission from two galaxies associated wit

81 s were up to 3 orders of magnitude higher in dust deposited on the source.

82 show that Asian sources contribute 18-45% of dust deposition across our Sierra Nevada, California stu

83 The record shows that variations in glacial dust deposition variability on centennial-millennial tim

84 Lithogenic particles deriving from aeolian dust deposition, glacial runoff, or river discharges can

85 these waters, which occurs by upwelling and dust deposition.

86 led and precise age model for European loess dust deposits to date, based on 125 accelerator mass spe

87 Boron isotopes in dust differ from dissolved inputs, with an annual mean v

88 nstructed a velocity vector diagram of flour dust dispersal by each type of sifter, and measured the

89 Our results suggested that wheat flour dust dispersed by sifting (regardless of sifter) could u

90 he transfer of substances from products into dust due to direct and air-mediated transfer.

91 ith decreased wind speed, large decreases in dust emissions (29%) moderate the wintertime land-sea su

92 st farm, and (3) modeled annual average fine dust emissions from farms within 500 m and 1,000 m of th

93 mbrotrophic (rain-fed) peat bogs to quantify dust emissions from the open-pit mining and upgrading of

94 ervational analysis further reveals enhanced dust emissions in response to diminished Sahel vegetatio

95 cial dust activity and propose that European dust emissions were modulated by dominant phases of the

96 insolation, a vegetated Sahara, and reduced dust emissions.

97 yet little is known of equivalent changes in dust-emitting regions, limiting our understanding of dus

98 first report of an association between house dust endotoxin and leukocyte count in a national survey.

99 investigated the relationship between house dust endotoxin concentration and peripheral leukocyte co

100 Dust exposure significantly reduced phagocyte-mediated b

101 ironmental adjuvants, including common house dust extract (HDE), to test their role in maintaining lu

102 uate the adipogenic activity of indoor house dust extracts and a suite of semivolatile organic chemic

103 innocuous protein using TLR ligands or house dust extracts as adjuvants developed mixed eosinophilic

104 Ten of 11 house dust extracts exhibited significant triglyceride accumul

105 stained by carbon cycle feedbacks related to dust fertilization of the Southern Ocean as a consequenc

106 or stationary air and personal ambient air), dust (floor dust and surface dust), and hand wipes were

107 The extremely low dust fluxes and marine sedimentation rates in the South

108 Measured dust fluxes are greater than or equal to modern erosiona

109 ues, considering exposures from water, soil, dust, food, and air.

110 Despite the potential importance of playa dusts for cloud formation, most climate models assume th

111 Our images show a nearly circular, dust-free atmosphere, which is very compact and only wea

112 House dust from 17 Swedish homes and serum from the participat

113 ms, such as these from fugitive emissions of dusts from open-pit mining, may have long-term ecologica

114 ation between cat serum levels and household dust has been established, a finding that supports the h

115 The size and composition of these dusts, however, have not been well described.

116 esults further demonstrate the importance of dust in aerosol-cloud interactions.

117 Increased pesticide concentrations in house dust in agricultural areas have been attributed to sever

118 was to analyze the dispersal of wheat flour dust in air in order to prevent unintentional mixing.

119 ly increases the final SVOC concentration in dust in contact with the source, regardless of the vapor

120 The potential dust IN effect on cloud top temperature (CTT) in a well-

121 logen compounds (OHCs) adsorbed to household dust in home environments.

122 asurements are needed to clarify the role of dusts in aerosol-cloud interactions.

123 The dust-induced lower winds enhance stagnation of air and a

124 In relation to inhalation exposure, dust ingestion appears to be the major exposure pathway

125 ses revealed relative importance of soil and dust ingestion exposure pathways and associated Pb intak

126 ke, allowing estimation of age-specific soil/dust ingestion rates.

127 g flame retardants (EFRs) via inhalation and dust ingestion.

128 Dust inhalation or exposure to high temperatures promote

129 chemical/biological composition of inhalable dusts inside several Colorado dairy parlors.

130 Es based on estimated exposures via diet and dust intake and on measured levels in biologic samples.

131 cessity for developing a parameterization of dust IRI for climate studies.

132 Human-induced resuspension of floor dust is a dynamic process that can serve as a major indo

133 a finding that supports the hypothesis that dust is a significant exposure route for cats.

134 e microbial and allergenic content of indoor dust is associated with adverse and protective health ef

135 rmation, most climate models assume that all dust is nonhygroscopic; however, measurements are needed

136 Mineral dust is the most important natural source of atmospheric

137 "Dust" is formed by scattered single cells alternating wi

138 gher than in students' homes (median settled dust level, 0.90 vs 0.14 microg/g; P < .001).

139 that the greening of the Sahara and reduced dust loadings lead to more favorable conditions for trop

140 cted by passive sampler and in sieved vacuum dust (<150 mum).

141 Here we show that dust may also be crucial in montane forest ecosystems, d

142 Taken together, these data suggest that WTC dust may be one of the key etiological factors for those

143 BDPE was found in high concentrations in all dust (median 154 pmol/g) and food samples (median 0.7 pm

144 odels of allergic airway inflammation (house dust mice and Alternaria alternata) and OVA-induced mode

145 House dust microbiome analysis using 16S ribosomal RNA sequenc

146 preceding sensitization to the common house dust mite (HDM) allergen remains to be elucidated.

147 House dust mite (HDM) allergens are a common cause of allergy

148 Mice were sensitized with house dust mite (HDM) allergens from days 3, 15, or 60 after b

149 therapy (AIT) lack recommendations for house dust mite (HDM) allergy.

150 mice were challenged over 3 weeks with house dust mite (HDM) antigen.

151 tion of airborne allergens such as the house dust mite (HDM) effectively activates both innate and ad

152 ized through the intranasal route with house dust mite (HDM) extract derived from Dermatophagoides pt

153 mice were intranasally challenged with house dust mite (HDM) extract or PBS five days per week for fo

154 e with prolonged i.n exposure to crude house dust mite (HDM) extract.

155 e evaluated in the ovalbumin (OVA) and house dust mite (HDM) murine models.

156 were challenged with saline, DEPs, or house dust mite (HDM) or DEP+HDM.

157 y inflammation was induced following a house dust mite (HDM) sensitization protocol.

158 ce, challenged with ovalbumin (OVA) or house dust mite (HDM), and accessed for TH2 inflammation.

159 sure to common human allergens such as house dust mite (HDM), in the absence of additional adjuvants,

160 Exposure to allergens, such as house dust mite (HDM), through the skin often precedes allergi

161 gnaling induced by DCs is critical for house dust mite (HDM)-driven allergic airway inflammation (AAI

162 the therapeutic efficacy of SAHM1 in a house dust mite (HDM)-driven asthma model.

163 e Cd11c promotor) to acute and chronic house dust mite (HDM)-driven asthma models.

164 ht to address the role of B cells in a house dust mite (HDM)-driven TH2-high asthma mouse model.

165 tive immune responses in patients with house dust mite (HDM)-induced airways disease.

166 OVA- and house dust mite (HDM)-induced murine asthma models were used i

167 the stimulatory effects of IL-1beta on house dust mite (HDM)-induced release of thymic stromal lympho

168 ht to investigate the role of TPL-2 in house dust mite (HDM)-mediated allergic airway inflammation.

169 th Schistosoma mansoni or the allergen house dust mite (HDM).

170 pe mice with Aspergillus fumigatus and house dust mite allergen and compared the effects on airway eo

171 NC/Nga mice were sensitized with house dust mite allergen and treated topically with HOCl hydro

172 Dust mite allergen exposure modifies the estimated effec

173 ren with asthma are modified by the level of dust mite allergen exposure.

174 In addition, we discuss of house dust mite allergen extracts as a prototypical complex ex

175 A genome-wide interaction analysis of dust mite allergen level and lung function was performed

176 significant interaction effect on FEV1 with dust mite allergen level in PRGOAL (interaction P = 3.1

177 ociated with FEV1 in children exposed to low dust mite allergen levels, but negatively associated wit

178 re have been no genome-wide G x E studies of dust mite allergen on asthma-related phenotypes.

179 Diverse factors contribute to house dust mite allergenicity through the activation of innate

180 s of IgE specific for staple foods and house dust mite allergens in DOCK8-deficient patients and heal

181 ion downregulation in a mouse model of house dust mite allergic airway inflammation.

182 lets containing carbamylated monomeric house dust mite allergoids was to determine the most effective

183 e protease and major allergen from the house dust mite and is associated with allergic rhinitis and a

184 ore severe as the degree of sensitization to dust mite and mouse increase.

185 mice was also intranasally exposed to house dust mite antigen.

186 ent and TH2 polarization, as seen in a house dust mite exposure model.

187 oxia promoted allergic TH responses to house dust mite exposure.

188 maprit in both the ovalbumin (OVA) and house dust mite extract (HDM) murine models of respiratory inf

189 was exposed to allergens (ovalbumin or house dust mite extract) to decipher in vivo the implication o

190 eatures of allergic asthma provoked by house dust mite in vivo.

191 Dust mite is a known risk factor for asthma morbidity.

192 Our data indicate that exposure to house dust mite markedly reduces Sema3E expression in mouse ai

193 a was induced in mice using intranasal house dust mite or aerosol ova-albumin challenge, and chloroqu

194 opic dermatitis skin lesions with high house dust mite sensitization.

195 eatment with SQ (standardised quality) house dust mite sublingual tablet for 1 year resulted in a dec

196 tion day (from 11% [placebo] to 5% [SQ house dust mite sublingual tablet]) and an increased probabili

197 AR day (from 16% [placebo] to 34% [SQ house dust mite sublingual tablet]).

198 sure to certain allergens (cockroach, mouse, dust mite) was significantly associated with enhanced cy

199 of experimental asthma (ovalbumin and house dust mite); miRNAs deregulated in both models were furth

200 d children and correlated with IgE levels to dust mite, ryegrass, and fungi but not cat, ragweed, or

201 D (rfhSP-D) has been shown to suppress house dust mite- and Aspergillus fumigatus-induced allergic in

202 erated and reduces the CPT reaction in house dust mite-allergic patients.

203 by 6.2-fold in pulmonary epithelium of house dust mite-challenged mice.

204 To evaluate the use of house dust mite-impermeable bedding and its impact on severe a

205 dose-finding study, 131 patients with house dust mite-induced allergic rhinoconjunctivitis were rand

206 covered, subjected to an ovalbumin- or house dust mite-induced experimental asthma protocol.

207 Blockade of Runx2 inhibited the house dust mite-induced goblet cell differentiation with a 75%

208 -/-) mice into WT recipients increases house dust mite-induced Th2/Th17 inflammation in the airway.

209 a via regulation of immune response to house dust mite.

210 baseline and after sensitization with house dust mite.

211 House dust mite/HDM atopy patch test/APT elicits positive reac

212 nse is dominated by a single allergen (house dust mite; HDM).

213 re confirmed in reporter assays and in house-dust-mite (HDM) induced AAI and primary human bronchial

214 enome, transcriptome and microbiome of house dust mites (HDM) has shown that Staphylococcus aureus (S

215 House dust mites (HDM) may serve as carriers of bacteria respo

216 al cells, BEAS-2B, directly exposed to house dust mites (HDM) resulted in enhanced DNA damage, as mea

217 Twenty-three adults allergic to house dust mites (HDMs) (M+) and 15 nonsensitive, nonallergic

218 d countries demonstrate sensitivity to house dust mites (HDMs).

219 House dust mites have been implicated in the etiology and exac

220 llergens (ie, grass, olive/ash pollen, house dust mites), specific IgE did not show marked difference

221 2) timothy grass/birch, (3) molds, (4) house dust mites, (5) peanut/wheat flour/mugwort, (6) peanut/s

222 t allergies (e.g. grass and ragweed pollens, dust mites, and cat) and those that induce life-threaten

223 cluding rat, mouse, cockroach, cat, dog, and dust mites, measured in dust samples collected from inne

224 d against staple food antigens but not house dust mites.

225 t for local allergic rhinitis (LAR) to house dust mites.

226 For given ice water path, the CTT of dust-mixed cloud is warmer than that in relatively prist

227 ility distribution function (PDF) of CTT for dust-mixed clouds shifted to the warmer end and showed t

228 ouds, but they showed large discrepancies in dust-mixed clouds.

229 s not clear, due to the large uncertainty in dust modeling.

230 By seed classification, eyes with dust (n = 15) required a median of 3 injections, spheres

231 The adipogenic activity in house dust occurred at concentrations below EPA estimated chil

232 P-3 has been detected in the air and settled dust of homes and is expected to redistribute from its o

233 -L1 cells were exposed to extracts of indoor dust or individual SVOCs and assessed for triglyceride a

234 significantly more injections than eyes with dust or spheres.

235 The remaining dust originates regionally from the nearby Central Valle

236 Storms from different dust origins exhibited distinct bacterial communities, w

237 the quantity of the semiconductive metals in dust particles and partially by hygroscopic properties.

238 At this time, meteorites and interplanetary dust particles delivered organics such as nucleobases (t

239 The impact of authentic mineral dust particles sourced from the Gobi Desert (GDD) on the

240 To understand the photocatalytic act of dust particles, both GDD and ATD were characterized for

241 dentify the place where ice cloud mixed with dust particles.

242 oritic in origin and not from interplanetary dust particles.

243 BDE-47, -99, -100 = 0.48, p = 0.09), but not dust PBDE.

244 Centennial-scale mineral dust peaks in last glacial Greenland ice cores match the

245 s published from 1995 to 2015, we abstracted dust pesticide concentrations reported as summary statis

246 meta-regression models of published data on dust pesticide concentrations.

247 d residential use exposure pathways to house dust pesticide concentrations: meta-regression of publis

248 whether hen's egg allergen in house and bed dust plays a role in sensitization via skin.

249 tation of APase activity beneath the Saharan dust plume in the Eastern Atlantic.

250 e found little evidence of associations with dust PM2.5.

251 Among all PFAAs, only PFNA in air and vacuum dust predicted serum PFNA.

252 Dust provides ecosystem-sustaining nutrients to landscap

253 correlate with minor decreases in Greenland dust records.

254 gh boron contents (190-390 mug.g(-1)) of the dust samples are interpreted as resulting from localized

255 ociated with bacterial diversity in mattress dust samples as determined by richness (P = 8.1 x 10(-6)

256 roach, cat, dog, and dust mites, measured in dust samples collected from inner-city schools.

257 We collected 95 dust samples from dormitory common areas and student roo

258 nt correlations were found between serum and dust samples from the living rooms for BDE-47 (p < 0.035

259 ng that same school year, classroom and home dust samples linked to the students were collected and a

260 of 8 households, hen's egg was detectable in dust samples of eating area and bed.

261 les, 13 personal air samples, and 60 settled dust samples were collected from a Norwegian cohort duri

262 Dust samples were collected from the floor, elevated sur

263 Hen's egg protein levels of dust samples were measured using ELISA.

264 en was detected in 441 (99.5%) of 443 school dust samples, cat allergen in 420 samples (94.8%), and d

265 l matrices of the exposed workers and indoor dust samples.

266 bromocyclododecane (HBCDD) isomers in the 95 dust samples.

267 Strontium and neodymium isotopes in modern dust show that Asian sources contribute 18-45% of dust d

268 ther characterization (fat, feed, materials, dust, soil) and was analyzed for PCDD/Fs and DL-PCBs by

269 guidance were used to develop candidate soil/dust source partition scenarios estimating lead intake,

270 on vegetation and local climate of European dust source regions.

271 cted drier regions largely overlay the major dust sources in the United States.

272 rning, diesel vehicle, gasoline vehicle, and dust sources was similar in chemical composition between

273 ermine whether vitreous seed classification (dust, spheres, cloud) is predictive of the total number

274 were also detected and quantified in a house dust standard reference material, SRM 2585, demonstratin

275 25 additional HFRs were also screened in the dust standard, and 10 were detected in concentrations ab

276 Microorganisms carried by dust storms are transported through the atmosphere and m

277 These results show, for the first time, that dust storms from different sources display distinct bact

278 rsity of dust-borne bacterial communities in dust storms from three distinct origins (North Africa, S

279 Characterizing the dust-borne microbiome in dust storms of different origins or that followed differ

280 Dust storms were characterized by a lower abundance of s

281 economic and societal consequences of severe dust storms, this study complements the multi-model proj

282 nclude that direct transfer from source into dust substantially increases the final SVOC concentratio

283 ity showed increasing resemblance to ambient dust, suggesting mixing with local dust.

284 , but has an order of magnitude less gas and dust than its neighbour and physical conditions akin to

285 Playas emit large quantities of dust that can facilitate the activation of cloud droplet

286 ole of barrier defences we infected flies by dusting the cuticle with fungal spores.

287 In mattress dust, the genera Clostridium, Facklamia, an unclassified

288 principal source of this Fe is thought to be dust transported from southern mid-latitude deserts.

289 Seeds were classified as type 1 ("dust"), type 2 ("sphere"), or type 3 ("cloud").

290 , Der f 1, Der p 1, Mus m 1, and Rat n 1) in dust vacuumed from nearly 7000 bedrooms were measured by

291 lements the multi-model projection on future dust variations and may help improve risk management and

292 dance of a number of bacterial taxa in house dust was associated with increased or decreased asthma r

293 Settled airborne dust was collected 4 times a year from 20 German DCC (62

294 cale chondrule inclusions and sub-micrometre dust was compacted into rock.

295 ed that the level of Cr in indoor industrial dust was more than twice, compared to the background hou

296 Petcoke dust was recently reported as an environmental contamina

297 environmentally relevant levels (<20 mug of dust/well), and significant adipogenic activity was also

298 The PBDE concentrations in dust were mainly driven by BDE-209 and those of EFRs by

299 sulting from high concentrations of airborne dust) were identified as significant risk factors for ba

300 g because their photospheres are obscured by dust, which partially masks the convective patterns.