戻る
「早戻しボタン」を押すと検索画面に戻ります。 [閉じる]

コーパス検索結果 (1語後でソート)

通し番号をクリックするとPubMedの該当ページを表示します
1  and organs (O), with gradation of severity (SMOG).
2 outside the affected area at the time of the smog.
3 ic ozone (O3), a major part of photochemical smog.
4 le formation is a major contributor to urban smog(1,2), but how it occurs in cities is often puzzling
5                                              SMOG 2 is a downloadable software package that reads use
6                                              SMOG 2 is bundled with XML-formatted template files that
7 ed much of Hawai'i Island in "vog" (volcanic smog), a mixture of primary volcanic sulfur dioxide (SO(
8 itric oxide emissions (NO) lead to increased smog, acid rain, climate change, and respiratory inflamm
9                    This dusty combination of smog and ethane, forming deposits several kilometres thi
10 esponses showed consistent reduction of mean SMOG and FKGL scores, only ChatGPT-4 achieved the specif
11 esses that generate both urban photochemical smog and tropospheric ozone.
12 evel (FKGL), Simple Measure of Gobbledygook (SMOG), and Gunning Fog (GFOG).
13 evel (FKGL), Simple Measure of Gobbledygook (SMOG), and Gunning Fog Index (GFOG).
14 fraction in biogenic SOA, aged photochemical smog, and BBOA.
15       Additionally, Lgr3, GababetaR1, SIFaR, Smog, and Cirl are expressed in OA neurons innervating t
16 d by a miniCAST burner combined with a micro smog chamber (MSC).
17 of the gas-phase emissions was determined by smog chamber aging experiments.
18 e oxidation of crude oil by OH radicals in a smog chamber and a flow tube reactor strongly resembled
19       Emissions were sampled into a portable smog chamber and exposed to sunlight or artificial UV li
20                                          The smog chamber data demonstrate that this misclassificatio
21 mospheric aging performed in a photochemical smog chamber did not strongly change the toxicity (oxida
22                                         FTIR/smog chamber experiments and ab initio quantum calculati
23          We present evidence from controlled smog chamber experiments and field measurements that in
24                                  Here, using smog chamber experiments under coastal atmospheric condi
25 rstand SOA formation from IVOCs, a series of smog chamber experiments was conducted with different al
26                                 Dilution and smog chamber experiments were performed to characterize
27                                Emissions and smog chamber experiments were performed to investigate S
28                                  A series of smog chamber experiments were performed to investigate t
29 on under controlled laboratory conditions in smog chamber experiments.
30 the organosulfur compounds identified in the smog chamber extracts were also measured in urban fine a
31  were photochemically oxidized in an outdoor smog chamber facility in the presence of nonacidified an
32 quantifying MVK and MACR production during a smog chamber isoprene-NO x irradiation experiment.
33 erization of organic aerosols in ambient and smog chamber measurements.
34                                              Smog chamber relative rate techniques were used to measu
35 ely realistic exposure scenario, combining a smog chamber simulating atmospheric ageing, an aerosol e
36  OP of PM in polluted urban environments and smog chamber studies.
37                                       A dual smog chamber system was used to quantify the formation r
38                                    We used a smog chamber to generate SOA from alpha-pinene, guaiacol
39 e conducted photo-oxidation experiments in a smog chamber to investigate secondary organic aerosol (S
40 rate kinetic experiments were conducted in a smog chamber using online proton transfer reaction mass
41 OA samples were prepared in an environmental smog chamber, and their composition was analyzed offline
42                   The SOA was generated in a smog chamber, collected on substrates, and aged by expos
43            After 3 h of photo-oxidation in a smog chamber, dilute emissions from both 2- and 4-stroke
44 ntial mobility analyzer, and injected into a smog chamber, where they were exposed to low vapor press
45 ntial mobility analyzer, and injected into a smog chamber, where they were exposed to the photo-oxida
46 , with SOA loading of 350 mug/m(3), and in a smog chamber, with SOA loading of 2-12 mug/m(3).
47                    The results obtained from smog chamber-generated isoprene SOA and aqueous-phase la
48 ectrometer sampling particles generated in a smog chamber.
49 om a fleet of on-road gasoline vehicles in a smog chamber.
50 ing authentic biomass-burning emissions in a smog chamber.
51 investigated in a series of photo-oxidation (smog) chamber experiments.
52             A series of sunlight-irradiated, smog-chamber experiments confirmed that the atmospheric
53 bove a simulated salt lake inside an aerosol smog-chamber, were analyzed using TERS.
54 f benzyl alcohol has been investigated using smog chambers at ICARE, FORD, and EUPHORE.
55  bag batch reactors, and outdoor Teflon-film smog chambers strongly confirm that inorganic acids, suc
56 )-initiated oxidation of MBO was examined in smog chambers under varied initial nitric oxide (NO) and
57  regulators: Lgr3, GababetaR1, SIFaR, mthl9, Smog, Cirl, and CG6067.
58 ct, diminishes stratospheric ozone, promotes smog, contaminates drinking water, acidifies rain, eutro
59 rity Oversampling Technique), to predict the smog contribution of individual vehicles.
60                                              SMOG@ctbp is an effort to simplify the use of structure-
61      The method has been integrated into the SMoG drug design package, resulting in an improved appro
62 uding those from several historically severe smog events.
63 rials Assessment Tool [PEMAT]), readability (SMOG, Flesch-Kincaid Grade Level [FKGL]), and accuracy (
64 rs for respiratory effects and photochemical smog formation are also assessed and can be reduced by 1
65 emicals (VOCs) from consumer products affect smog formation holds a partial solution.
66                                          For smog formation potential, the centralized system is pref
67 ion) to air pollution control (photochemical smog formation).
68 xide equivalents [CO(2)e]), ozone depletion, smog formation, acidification, eutrophication, carcinoge
69 one depleting chemicals, 33-52% reduction in smog-forming pollutants, 6-25% reduction in acidificatio
70 d environmental benefits in four categories (smog, global warming, respiratory effects, noncarcinogen
71                     Here, we reveal that the Smog GPCR transduces Fog signal to regulate Rho kinase a
72 e model can classify vehicles based on their smog impact, rating them on a scale from 1 (poor) to 8 (
73 -99% to global warming, ozone depletion, and smog impacts.
74 port on unexpected Fog-independent roles for Smog in maintaining epithelial integrity and organizing
75                        Exposure to the Great Smog in the first year of life increases the likelihood
76  see a global reservoir, but the methane and smog in Titan's atmosphere impedes the search for hydroc
77 of asthma between those exposed to the Great Smog in utero or the first year of life with those conce
78 oyager cameras by the photochemical haze (or smog) in Titan's stratosphere.
79 Index (CLI), Simple Measure of Gobbledygook (SMOG) index, Automated Readability Index (ARI), and Lins
80  and the Simple Measure of Gobbledygook (ie, SMOG) Index.
81 he presence of ozone (O(3)) in photochemical smog is an important health concern.
82 essing this issue requires understanding how smog is formed.
83 ssessing the contribution of each vehicle to smog is impractical.
84 periment, suggesting the legacy of the Great Smog is ongoing.
85  to global warming, human health, ozone, and smog issues, partially attributed to its diesel-consumin
86    Individually, a vehicle's contribution to smog may be small, but collectively, the vast number of
87 to intense air pollution from the 1952 Great Smog of London as a natural experiment to examine both i
88                                Photochemical smog, or ground-level ozone, has been the most recalcitr
89 rity of liquid ethane: it condenses onto the smog particles, instead of into liquid drops, at the col
90                                              Smog poses a direct threat to human health and the envir
91 layer accelerate photochemical reactions and smog production, but UV-absorbing aerosols such as miner
92 rosols such as mineral dust and soot inhibit smog production.
93  level using Simple Measure of Gobbledygook (SMOG) readability formula." We then compared responses'
94             Our data support a model wherein Smog regulates distinct myosin pools and actin cytoskele
95  one of the main components of photochemical smog, represents an important source of environmental ox
96 ve selection having acted on residues within Smog's ligand binding region, which is interesting in li
97  the PMF score, Bohm's score (LUDI), and the SMOG score for eight different test sets of protein-liga
98 nt in accuracy over previous versions of the SMoG scoring function to a better description of the ref
99 ticle, we present an improved version of the SMoG scoring function, called SMoG2001.
100 nd risk of LC using the Adventist Health and Smog Study-2 (AHSMOG-2), a cohort of health conscious no
101                                          The SMOG system provides a consistent description of the ble
102 trate mixing ratios were comparable to urban smog values, indicating active photochemistry in the pre
103 (48.85-63.77) (difficult), the mean FKGL and SMOG were 10.19 (8.93-11.72) and 11.10 (10.11-11.87) yea
104  its surface is hidden by dense orange-brown smog, which is produced in the stratosphere by photochem

 
Page Top