ライフサイエンスコーパス: sampler

1 nhalational exposure (via breathing zone air sampler).

2 a unique solid phase microextraction (SPME) sampler.

3 plant inspections, pitfall traps and suction sampler.

4 ent samples collected from a constant volume sampler.

5 inlet up to the ionization and reaching the sampler.

6 al depletion layer around an in situ passive sampler.

7 d samples obtained employing the high-volume sampler.

8 hich acts as a long-term passive atmospheric sampler.

9 nally collected by means of an electrostatic sampler.

10 ccumulate, resulting in a useful passive air sampler.

11 OM and checked the efficiency of the passive sampler.

12 ecies that are too large to migrate into the sampler.

13 e collected in each area using an active air sampler.

14 tics have become entangled on a towed marine sampler.

15 had PSLs detected by the breathing zone air sampler.

16 based on a novel numeration method and Gibbs sampler.

17 ance reference compounds (PRCs) from passive samplers.

18 ring which ozone was measured using personal samplers.

19 tes of spin glasses differently than thermal samplers.

20 10 m using passive aeolian airborne sediment samplers.

21 -effective compared to current polar passive samplers.

22 ing over the course of the deployment of the samplers.

23 y the spatially extensive network of passive samplers.

24 s riparius bioaccumulation tests and passive samplers.

25 e of equilibrium POPs reached in the passive samplers.

26 n sediment compared to water column-deployed samplers.

27 migration of the dissolved species into the samplers.

28 uring the main pulse observed in the passive samplers.

29 with silicone wristbands as personal passive samplers.

30 ere determined using silicone rubber passive samplers.

31 nd in three depths in the HZ using minipoint samplers.

32 outdoors at 8 locations with automatic agar samplers.

33 n comparison with four commercial bioaerosol samplers.

34 order to overcome these challenges a robotic sampler, a 2nd generation Environmental Sample Processor

35 The VAMS sampler absorbs a fixed volume of blood ( approximately

36 ter were measured using polyethylene passive samplers across Lakes Erie and Ontario during summer and

37 The resin passive samplers act as concentrators of cationic species and ca

38 an order of magnitude in the static passive sampler after the same deployment time.

39 Coalescence-based genealogy samplers also indicated that P. triticina on A. speltoid

40 In passive samplers, an increase of PAH concentrations by up to sev

41 It comprised a towed Fish underway sampler and a modified reverse flow injection analysis s

42 A was collected using a particle into liquid sampler and analyzed offline using state-of-the-art mass

43 hip between the sampling rate of the passive sampler and GOM concentrations was used to estimate dry

44 residential bedroom air collected by passive sampler and in sieved vacuum dust (<150 mum).

45 mpounds (PRCs) that are diffusing out of the sampler and into the sediment.

46 lternative methods based on elliptical slice sampler and Metropolis-adjusted Langevin algorithm.

47 We present a Boltzmann sampler and obtain the a priori probability of specific

48 p analysis system integrated with an aerosol sampler and Raman spectrometer.

49 m, we find evidence for co-variation between sampler and sensor, hinting towards an 'optimization' fo

50 ing system, which is equipped with a syringe sampler and sensors for the measurement of standard para

51 bark makes an excellent passive atmospheric sampler and that spatial analysis of tree bark POPs conc

52 h as the Fisher's ratio sampler, the Holdout sampler and the Random sampler, and apply each one to th

53 with particles collected by passive aerosol samplers and analyzed by computer-controlled scanning el

54 ted over the course of 17 days using passive samplers and analyzed in a non-targeted manner using dir

55 suitability of using silicone rubber passive samplers and caged organisms (Ruditapes philippinarum),

56 Silicone passive samplers and macroinvertebrates were used to measure tim

57 of 2-4 rings, were found in silicone passive samplers and macroinvertebrates.

58 n rural Central Appalachia using passive air samplers and personal exposures in the residents of thes

59 les that were collected using Bio-VOC breath samplers and subsequently transferred to automatic therm

60 found between PAH concentrations in passive samplers and the amount of rainfall in the study area, i

61 Tests were done to better understand the samplers and the materials used.

62 ext generation of electrowetting-coupled air samplers and thus shows strong potential toward future i

63 ar subsurface sample where roots act as the "sampler' and are already onsite.

64 odels from candidate graphs generated by RAG Sampler, and (c) RAG Designer: designs sequences that fo

65 sampler, the Holdout sampler and the Random sampler, and apply each one to the analysis of genetic p

66 chlordane concentration in polyethylene (PE) samplers, and contaminant extractability by Arenicola br

67 aerosol counterflow two-jet unit (CGU-ACTJU) sampler-and analyzed online with another FLD.

68 iffusive gradient in thin-film (DGT) passive samplers are frequently used to monitor the concentratio

69 Single-phase passive samplers are gaining acceptance as a method to measure h

70 To measure EPFRs in PM samples, high volume samplers are required and measurements are less represen

71 column experiment of uptake in polyethylene samplers are within a factor of 2 for parent- and alkyla

72 The use of NTs as spot samplers, as well as a passive sampler under controlled

73 cted using a wind direction-actuated ChemVol sampler at a single site 100 m from Interstate-96 in Det

74 nd colocated with a federal reference method sampler at three sites and for 5 weeks in summer 2009 an

75 nnovative type of data obtained with passive samplers at 20 combined sewer overflow sites (2-7 events

76 Keeping intact samplers at 4 degrees C or binding gels in solvent gave

77 ant mixtures extracted from deployed passive samplers at wastewater treatment plant effluents.

78 ing a gravitational pollen sampler (Durham's sampler), at more than 20 locations across Japan.

79 86 by gravitational pollen sampler, Durham's sampler, at more than 20 locations in the Japanese Islan

80 taneously collected using passive and active samplers: at sites in Chicago, Lancaster, UK, and Toront

81 First, a phenotype sampler based on unlabeled clustering collects a compreh

82 It is recommended that an additional sampler be used to directly collect and analyze small fi

83 the speciation of the Hg accumulated on the sampler binding layer, and the results indicated that Hg

84 al area in Germany, collected by the passive sampler Blue Rayon.

85 This significantly reduces the need for sampler calibration, making o-DGT more widely applicable

86 In this study, a passive diffusion sampler, called "peeper", was combined with Compound Spe

87 a considerable cost optimization of passive sampler campaigns and removes a critical bottleneck for

88 Intact samplers can be simply stored in polyethylene bags at am

89 Passive samplers can be used in the field (i.e., in situ) to mea

90 particles (smaller than the pore size of DGT samplers) can be abundant in certain environments, yet t

91 The suitability of passive samplers (Chemcatcher) as an alternative to grab samplin

92 es decreased 30% when comparing results from samplers closest to active wells to those farthest from

93 es decreased 30% when comparing results from samplers closest to active wells to those farthest.

94 ting, MicroFlow, In-line Extraction (TIMFIE) sampler comprises a low-tech syringe pump driven by a ru

95 es a higher transport efficiency through the sampler cone.

96 Investigated here is a novel passive sampler configuration, the Chemcatcher containing an Atl

97 ake periods, some current passive and active sampler configurations may underestimate certain SVOCs b

98 transformations using a novel approach with samplers containing synthetic FeOx embedded in diffusive

99 on (WSOC) and BrC using particle-into-liquid sampler coupled with a liquid waveguide capillary cell a

100 ny advantages compared with other bioaerosol samplers currently on the market: a potential for long s

101 ntire exhaust sampled into a constant volume sampler (CVS).

102 t two sites was calculated using the passive sampler data and a multiple-resistance model.

103 The consequence was that the DGT sampler data underestimated the dissolved metal concentr

104 age methods were designed to test for within-sampler degradation/loss for up to 2 months.

105 disrupting the depletion layer in a passive sampler deployed in sediments.

106 ing that short periodic shaking of a passive sampler deployed in static sediment enhances the rate of

107 thods included polyurethane foam passive air samplers deployed outdoors and indoors and polypropylene

108 paper reports test of a flow-through passive sampler, deployed in stormwater runoff at the outlet of

109 tions are currently used (active and passive samplers, different deployment times, different sorbents

110 We argue that this 'natural sampler DNA' (nsDNA) approach is poised to become a powe

111 n, year- round, using a gravitational pollen sampler (Durham's sampler), at more than 20 locations ac

112 ound since July 1986 by gravitational pollen sampler, Durham's sampler, at more than 20 locations in

113 iodic vibration of polyethylene (PE) passive samplers during exposure has been previously shown to en

114 e contaminant uptake in polyethylene passive samplers embedded in the columns was reduced by 95-99% f

115 d pesticides were measured using passive air samplers equipped with polyurethane foam disks to find s

116 ir concentrations using films and vegetation samplers (especially for low KOA chemicals) generally re

117 diffusing through the sediment and into the sampler exhibit the same diffusive retardation factors a

118 assively on that measured with the reference sampler exhibited an intercept not statistically differe

119 librium condition confirmation, quantitative sampler extraction, quality assurance/control issues and

120 s were observed: breakthrough of high-volume sampler filters for penta- and hexachlorobenzene and sem

121 evaporation technique via a static headspace sampler, followed by gas chromatography-mass spectrometr

122 raphy fractionation of extracts from passive samplers, followed by effect assessment using the pulse

123 ed McReynolds mixture on the membrane in the sampler for at least 10 min.

124 ble and readily deployable penlike diffusive sampler for needle traps (PDS-NT) was built and tested.

125 ion of the diffusive gradients in thin films sampler for polar organics (o-DGT) without a poly(ether

126 We provide an efficient Gibbs sampler for posterior computation along with simple proc

127 e a Bayesian Markov chain Monte Carlo (MCMC) sampler for protein multiple sequence alignment (MSA) th

128 Western US, data were collected with passive samplers for ambient GOM concentrations and dry depositi

129 prepared on plastic as potential single-use samplers for bioanalysis.

130 dog may benefit the next-generation of vapor samplers for explosives, narcotics, pathogens, or even c

131 guide future development and use of passive samplers for measuring atmospheric particulate matter.

132 ially dense data sets using low-cost passive samplers for nitrogen dioxide (NO(2)), which complement

133 one wristbands have been used as passive air samplers for quantifying exposure in the general populat

134 e Theta via the sequential Monte Carlo (SMC) samplers for static models.

135 ce, namely, their ability to serve as useful samplers from the ground-state manifolds of combinatoria

136 cantly correlated with those from active air samplers from which we conclude that the brooches could

137 The application of these samplers generally presumes that they quantify only the

138 s constant irrespective of parameters of the sampler geometry.

139 ensitivity of direct coupling of a headspace sampler (HS) with a mass spectrometer (MS), here we prop

140 isks in parallel with high volume active air samplers (HV-AAS).

141 sampling complemented deployments of passive samplers in a tropical waterway in Queensland, Australia

142 findings suggest that the deployment of DGT samplers in settings where nanoparticles are relevant (e

143 Two types of TF-SPME passive samplers, including a retracted thin film device using a

144 In this study, a medium volume sampler incorporating quartz fiber filters (QFFs) and a

145 r with a metabolite-corrected arterial blood sampler input function (BSIF).

146 side the sampler on the solute flux into the sampler is a nonlinear function of the diffusion layer t

147 The o-DGT sampler is a promising monitoring tool that is largely i

148 to determine how the performance of the DGT sampler is affected by the presence of nanoparticulate s

149 If the sampler is employed, it is not necessary to use micropip

150 n the HOC concentration in water and passive sampler is linear at equilibrium, mass transfer models a

151 for sampling purposes, the glass-fiber pad (sampler) is immersed in a container with the solution, w

152 e the method is compatible with standard air-samplers, it can be employed with minimal modification i

153 sulted in noticeable improvements in passive sampler load estimates.

154 Models for metal uptake into the sampler may need to be reconsidered.

155 These results suggest that personal passive samplers may be useful in evaluating the bioactivities o

156 ransfer results in underequilibrated passive sampler measurements that need to be corrected for equil

157 anoparticles deposited on the surface of the samplers might have acted as sorbents, slowing the migra

158 TWA concentrations underestimated mean grab sampler (n = 258) derived concentrations of atrazine, di

159 model approach to reliably transform passive sampler NO(2) data from multiweek averages to annual-ave

160 Concentrations in the PE passive samplers, normalized by their polyethylene-water partiti

161 ues was excluded by using roots as a passive sampler of bioaccessible concentrations.

162 components are integrated with a high-volume sampler of conventional construction to reduce analysis

163 fluencing ring growth since trees are active samplers of atmospheric Hg.

164 DET) gels as high-spatial-resolution passive-samplers of delta(15)NNO3 and delta(18)ONO3 to investiga

165 Samplers of different thickness were used to determine t

166 We set up a Durham sampler on the roof (30 m from the ground) of the Oita U

167 t the effect of lateral diffusion inside the sampler on the solute flux into the sampler is a nonline

168 e awake; we used a high-volume small-surface sampler or we took dust from the home vacuum.

169 copper species fluxes at the position of the sampler orifice and the exhausts of the torch are provid

170 s elemental mercury (GEM) with a passive air sampler (PAS) that uses a sulfur-impregnated carbon sorb

171 Air samples were collected using passive air samplers (PAS) consisting of sorbent-impregnated polyure

172 ational Park (KNP), Uganda using passive air samplers (PAS) with polyurethane foam (PUF) discs (PAS-P

173 sediment-water flux, biouptake, and passive sampler (PE) uptake in microcosm experiments with a fres

174 igns and validates Passive Environmental DNA Samplers (PEDS).

175 mpatibility of a passive sediment pore water sampler ("peeper") to collect 40 mL samples for CSIA of

176 Polyethylene passive samplers (PEs) were deployed in air and water during win

177 In this study, polyethylene passive samplers (PEs) were deployed throughout the lower Great

178 Polyethylene passive samplers (PEs) were simultaneously deployed in surface w

179 Polyethylene passive samplers (PEs) were used to measure concentrations of ga

180 The considered biotic and passive sampler phases include membrane and storage lipids, seru

181 icients for diverse biotic media and passive sampler phases; aquatic baseline toxicity; and relevant

182 ntation consists of one particle-into-liquid sampler (PILS) coupled with a 250 cm path length liquid

183 osol (OA) by coupling a Particle Into Liquid Sampler (PILS) to a High-Resolution Time-of-Flight Aeros

184 and after tent setup and by using active air samplers placed inside assembled tents, respectively.

185 Polar organic chemical integrative sampler (POCIS) is a passive sampling device that offers

186 iction of polar organic chemical integrative sampler (POCIS) sampling rates (Rs) for 73 compounds usi

187 By using polar organic compound integrative samplers (POCIS) at upstream and downstream sites, biolo

188 o that of polar organic chemical integrative samplers (POCIS) deployed simultaneously.

189 ing using polar organic chemical integrative samplers (POCIS).

190 The passive sampler polyoxymethylene (POM) was used to measure the e

191 e reference compounds (PRC) dosed to passive samplers prior to exposure was used to monitor the excha

192 ere, we present the Photonic Recurrent Ising Sampler (PRIS), a heuristic method tailored for parallel

193 Overall, silicone rubber passive samplers proved to be more sensitive than sentinel organ

194 Results show that (i) the GAPS passive samplers (PUF disk type) and analytical methodology are

195 ut pairs using polyurethane foam passive air samplers (PUF-PAS) from January 2012 to November 2015.

196 captured using polyurethane foam passive air samplers (PUF-PAS).

197 vs fluorescent tracer methods, while the air sampler quantified potential inhalational exposure to PS

198 in the ratios of load estimates from passive samplers relative to grab samples that ranged between 0.

199 bon-rich sediment bed in the laboratory with samplers removed every 30 days for 4 months.

200 erial footprint, ENM-CNT equilibrium passive samplers represent a promising alternative to complement

201 erence of 30 (+/-20)% when comparing ENM-CNT sampler results to grab sample data collected within 1 w

202 effective diffusion coefficient D) into the sampler's diffusion layer were calculated and compared f

203 webserver consists of three modules: (a) RAG Sampler: samples tree graph topologies from an RNA secon

204 alt occupational settings, silicone personal samplers sequestered 25 PAHs during 8- and 40-h exposure

205 rations of bacteria, an effective bioaerosol sampler should have a high sampling efficiency and a hig

206 Deployed as personal passive samplers, silicone wristbands have been shown to detect

207 t the two ends of the transect, flow-through samplers simultaneously sampled air at monthly resolutio

208 We used 123 passive NO2 samplers sited to capture within-city and near-road vari

209 Passive samplers (solid phase adsorption toxin tracking: SPATT)

210 The samplers spanned roadside, urban near traffic (</=100 m

211 Our results suggest that (1) surface samplers such as manta trawls underestimate total buoyan

212 g buoy was outfitted with an automated water sampler taking preserved samples every 6 h for 68.75 day

213 ions were collected using the Tsai diffusion sampler (TDS) for characterization and further analysis.

214 The three samplers tested are good alternatives to Bayesian Networ

215 t plastic is more likely to act as a passive sampler than as a vector of POPs, thus reflecting the PO

216 diction problems, such as the Fisher's ratio sampler, the Holdout sampler and the Random sampler, and

217 PMLs are estimated with a multivariate Gibbs sampler; the liability-scale phenotypic covariance matri

218 not vary by transport direction through the sampler thickness.

219 and PRC were shown to be good indicators of sampler-tissue equilibration status.

220 The sampler-tissue exchange was isotropic, and PRC were show

221 We introduce Transmission Tree Uniform Sampler (TiTUS), a method that uses SATISFIABILITY to al

222 Chamber air was sampled using a biofilter sampler to determine the potential for resuspension of s

223 We used a high-volume air sampler to determine whether EBOV could be detected duri

224 As such, tree bark is an ideal sampler to find POPs sources globally, regionally, or lo

225 inside the torch, i.e., close enough to the sampler to increase the fraction that can enter the mass

226 the water phase and as a passive equilibrium sampler to monitor the dechlorination product.

227 lts were grouped based on distance from each sampler to the nearest active well.

228 t silicone wristbands as noninvasive passive samplers to assess cumulative 5-day exposure of 30 indiv

229 erated vehicles and engineered purpose-built samplers to collect and examine the distribution of micr

230 on experiments with polyoxymethylene passive samplers to determine the partition coefficients at 37 d

231 erosol gas chromatograph (SV-TAG) and filter samplers to measure SOA tracers indicative of isoprene/H

232 Using passive samplers to measure the concentration of dissolved PCBs

233 approach, we use passive, personal-type air samplers to provide site-specific measurements of nitrog

234 wristbands could serve as sensitive passive samplers to screen population-wide cumulative dietary an

235 Silicone wristbands are promising passive samplers to support epidemiological studies in character

236 In a flood-specific deployment, passive sampler TWA concentrations underestimated mean grab samp

237 mend future study design, appropriateness of sampler types for different study goals, and finally, ho

238 f NTs as spot samplers, as well as a passive sampler under controlled conditions in the laboratoryyie

239 correlating bioaccumulation (CL) and passive sampler uptake (CPS) were used to assess the strength of

240 -seven studies were found where both passive sampler uptake and organism bioaccumulation were measure

241 provided direct comparisons relating passive sampler uptake and organism bioaccumulation.

242 This Critcal Review evaluates passive sampler uptake of hydrophobic organic contaminants (HOCs

243 through, degradation, particle fractions and sampler uptake periods, some current passive and active

244 ure requires several weeks (depending on the sampler used) because of prolonged equilibration times.

245 made for sample handling and storage of DGT samplers used for determination of trace organics in mon

246 e regression parameters and derive the Gibbs sampler using the conditional distributions of them.

247 asurements were made with passive and active samplers using membranes, and at one location, a Tekran

248 rease caused by lateral diffusion inside the sampler was determined to be approximately 8.8% for stan

249 n-film solid-phase microextraction (TF-SPME) sampler was developed.

250 The drone-based sampler was shown to protect the sorbent phase from exte

251 A micro reaction sampler was used to simultaneously achieve the pyrolyis

252 h), implying that the supply of SAs to o-DGT samplers was limited by the desorption release rate.

253 matic hydrocarbons into polyethylene passive samplers was measured after 7, 14, 28, and 56 days of ex

254 e effects of temperature and salinity on the sampler-water partition coefficients of PAHs and PCBs fo

255 Crucial to the measurements are sampler-water partition coefficients, which are generall

256 The performance of silicon wristband passive samplers (WB), combined with comprehensive two-dimension

257 Setting up a Durham's sampler, we measured airborne pollen identified and clas

258 side diffusive gradients in thin films (DGT) samplers, we show that the effect of lateral diffusion i

259 e) on concentrations in polyethylene passive samplers well, in most cases within 25% of experimental

260 The TD unit and auto sampler were coupled to a GC-MS using electron ionizatio

261 S) membranes deployed in flight on the drone sampler were demonstrated to extract disinfection by-pro

262 Gas-phase concentrations based on passive samplers were 1-8 pg m(-3) for BDE 47 and </= 4 pg m(-3)

263 ates a modeling exercise showed that passive samplers were a viable alternative to grab sampling sinc

264 Samplers were analyzed for 62 polycyclic aromatic hydroc

265 Silicone passive samplers were assessed for measuring personal exposure t

266 ic potency of PAH mixtures were highest when samplers were closest to active wells.

267 PAH levels were highest when samplers were closest to active wells.

268 Samplers were deployed around the greater Chicago area f

269 Passive air samplers were deployed at 23 sites across the city of Zu

270 Samplers were deployed at five depths covering 26-2535 m

271 ay 2017, a total of 243 artificial substrate samplers were deployed at five locations in the Perhenti

272 Polyethylene passive samplers were deployed during summer and fall of 2011 in

273 Polyurethane foam (PUF) disk passive air samplers were deployed for consecutive 2-month periods f

274 Passive samplers were deployed for week-long intervals in tripli

275 XAD-resin-based passive air samplers were deployed from May to September 2011 at six

276 ddress potential health impacts, passive air samplers were deployed in a rural community heavily affe

277 s is demonstrated in a field study where DGT samplers were deployed in the near-shore marine environm

278 The developed passive samplers were deployed in wastewater-dominated reaches o

279 Concurrently, passive samplers were deployed to assess porewater and overlying

280 These samplers were deployed to sample effluent of vents on su

281 Passive samplers were deployed to the seafloor at a marine Super

282 Rewarding results were found when these samplers were employed for the quantitative analysis of

283 hin-film polydimethylsiloxane (PDMS) passive samplers were exposed statically to intact fillet and fi

284 DGT samplers were exposed to solutions containing known amou

285 Random, Fisher's ratio and Holdout samplers were more accurate and robust than BNs, while p

286 t this assumption, polyethylene (PE) passive samplers were placed in an organic- and black- carbon-ri

287 The herein proposed samplers were prepared by applying a hydrophilic-lipophi

288 mounts of Hg and Zn accumulated onto the DGT samplers were quantified over hours to days, and the rat

289 The screen samplers were retrieved 24 h later and the abundances of

290 The modified DGT samplers were then deployed alongside ferrihydrite DGT d

291 s (Clip) and porewater measured with passive samplers were used to derive lipid-normalized bioaccumul

292 Polyethylene passive samplers were used to detect the vertical distribution o

293 Genetics 156:1393-1401, 2000a), a sampler which uses the full model.

294 rmined to be approximately 8.8% for standard samplers, which is considerably lower than the previous

295 o complement traditional integrative passive samplers while offering convenience over large volume gr

296 can be obviated by equilibrating a silicone sampler with chemicals in sediment, measuring chemical c

297 injected material are located closer to the sampler with less radial diffusion.

298 and spiked samples should be considered for samplers with short expiration times and labile analytes

299 es isolated from personal silicone wristband samplers within a thyroid cancer cohort.

300 ion compounds and calibration against active samplers, yielding an average congener specific concentr