ライフサイエンスコーパス: sorption

1 endows materials with high tunability in gas sorption.

2 special life stage contributed mostly to Pb sorption.

3 in sorption coefficients) on organic cation sorption.

4 the Cd exposure time and the quantity of ion sorption.

5 Fe-(oxyhydr)oxide precipitation promoted Mo sorption.

6 not support increased PFAA removal via soil sorption.

7 than electrostatic attraction contributed to sorption.

8 on and subsequent oxidation as well as As(V) sorption.

9 ty continuous phase described by Henry's law sorption.

10 isorption, chemisorption, and moisture-swing sorption.

11 cidal pharmacophore influences neonicotinoid sorption.

12 decreasing the penalty for quaternary amine sorption.

13 rreversibly bound NH(3)(g) (81%) but similar sorption activation energy (Ea) as S-150.

14 Given their slow biodegradation and limited sorption affinities, IL cations have a high potential to

15 n inhibited oxidative Tl uptake and lower Tl sorption affinity (log K(d) 6.2-6.4 at 10(-8) M Tl(I)) a

16 , a 3 x 3 tectomanganate, bind Tl with lower sorption affinity than delta-MnO(2), mainly as hydrated

17 This study determined the sorption affinity to artificial phospholipid membranes (

18 from this literature model of organic cation sorption, along with phenyltrimethylammonium Kd values,

19 Sorption and biodegradation are the two major removal pa

20 Important factors affecting sorption and biodegradation behavior of antibiotics are

21 were developed, and the results reveal that sorption and desorption depend on the crystallinity, ela

22 Sorption and desorption isotherms were developed, and th

23 The rates (k) of NH(3)(g) sorption and desorption were fastest for S-150.

24 ndependent physics and chemistry of moisture sorption and diffusion materials.

25 The ability to quantify moisture sorption and diffusion, independent of scale, using 1D l

26 This study investigates the sorption and hydrolysis of polyphosphate (a group of imp

27 h some important advances in the modeling of sorption and hygrothermal deformations of nanoporous mat

28 e outer membrane and external medium, on the sorption and methylation of Hg(II) by Geobacter sulfurre

29 Sylgard-184 showed a linear sorption and outgassing behavior with no-hysteresis over

30 In this study, the sorption and release of bisphenol A in marine water were

31 highest IECs (where steeply increasing water sorption and resultant swelling outpaces IEC increase),

32 In the field of gas sorption and storage, especially the stability and affin

33 (Fc(+)) with the latter facilitating As(III) sorption and subsequent oxidation as well as As(V) sorpt

34 r the presence of Ni(0) centers, whereas gas-sorption and thermogravimetric analysis reveal the chara

35 provided to relate measurable parameters for sorption and transport in CMS materials.

36 n surface/volume area and the TK parameters (sorption and uptake rate constants and the resulting BCF

37 eral isolated materials, as measured by N(2) sorption and X-ray diffraction.

38 situ anodic As(III) oxidation, As(V) electro-sorption, and As(V) electro-desorption are affected by a

39 rimental studies (X-ray crystallography, gas sorption, and quartz-crystal microbalance measurements)

40 implications for industrial scale-up and gas sorption applications.

41 to other nanoparticles for diverse pollutant sorption applications.

42 This implies a considerable increase in sorption as concentration falls in the natural environme

43 pH strongly affected sorption as negatively charged analytes were attracted b

44 OP-MOF framework, which exhibits interesting sorption as well as catalytic properties.

45 Current predictive models of organic cation sorption assume that sorbates interact with all sites on

46 Sorption at DAX-8, however, did not affect significantly

47 Nevertheless, the effects of NOM sorption at minerals on its redox properties are unknown

48 led with strong Pu complexation decreased Pu sorption at pH 5 and 7, relative to a ligand-free system

49 The increase in moisture enhanced the sorption at the highest RH for all the aroma compounds.

50 ironmental contaminants as well as for other sorption-based applications.

51 PCs) that exhibit stimuli-responsive dynamic sorption behavior are attracting interest for gas storag

52 rature data, and alternatives showed similar sorption behavior as PFAAs.

53 This sorption behavior can be predicted by Redlich-Peterson m

54 Here, we present data on the pH-dependent sorption behavior of 12 PFASs onto ferrihydrite.

55 Understanding the water sorption behavior of protein powders is important in app

56 ers insecticide selectivity but also impacts sorption behavior, leading to less effective removal of

57 All compounds have an ideal sorption behaviour (logarithmic increase) except 1-hexan

58 The differences in properties, such as sorption behaviour, colour, polyphenols, flavonoids, min

59 ic behavior of the interface and competitive sorption between protons and other cations for binding s

60 ncept on "breathing" MOFs is discussed. I(2) sorption, both from gas phase and from MeOH solution, in

61 Uranyl sorption by PB2MP-g-PVDF membranes was also found to be

62 it led to a variation in the coefficient of sorption by several orders of magnitude over the experim

63 able pore apertures, which exhibit excellent sorption capabilities toward water and fluorocarbon R134

64 f metal-organic frameworks with record water sorption capacities by employing anion exchange.

65 However, little is known about molecular sorption capacities in natural migration systems, render

66 eding" effects that significantly reduce the sorption capacities of polar compounds.

67 ion coefficient for quantitatively assessing sorption capacities of polar molecules during natural pe

68 f molecular indices established according to sorption capacities of polar molecules in migrating petr

69 Furthermore, we measured composite sorption capacities of up to 0.62 mol CO(2) kg(-1) and r

70 The MOF had the highest sorption capacity (289.7 mg g(-1)) and irreversibly boun

71 0 degrees C (S-150) had the highest NH(3)(g) sorption capacity (47.2-49.9 mg g(-1)), comparable to BC

72 The sorption capacity and enrichment factor (EF) of the meth

73 demonstrated by fast removal kinetics, good sorption capacity and high distribution coefficient.

74 d poly(ethylene terephthalate) exhibited low sorption capacity and only partial reversibility.

75 With a high specific surface area and sorption capacity at circumneutral pH, ferrihydrite is a

76 id not show a competitive effect on arsenate sorption capacity but had a strong impact on selenate up

77 tion lifetime spectroscopy, and enhanced gas sorption capacity compared with pure crown ethers.

78 lyurethane were found to exhibit the highest sorption capacity for bisphenol A, and it was almost irr

79 and ferrihydrite revealed a 30-times-higher sorption capacity for MMMTA to amorphous ferrihydrite th

80 with many ion-exchange sites and thus a high sorption capacity for the analyte of interest.

81 minal fluid in (2) and (3), and the extended sorption capacity in (3).

82 sis with 195 studies showed that the maximum sorption capacity is influenced by microbial Kingdoms, t

83 dsorption isotherm studies indicate that the sorption capacity of benzoic acid on these carbon nanotu

84 Sorption capacity of ENM-CNTs was between 2- and 50-fold

85 rm experiments were conducted to examine the sorption capacity of synthetic schwertmannite and basalu

86 Preconcentration factor and sorption capacity of the proposed method were 666 and 23

87 The maximum sorption capacity of the sorbent was found to be 71.4mgg

88 The top material exhibits the highest sorption capacity together with record-high extraction e

89 REE biosorption occurred between pH 5-6, and sorption capacity was reduced by ~65% at pH 2.

90 demonstrated by fast exchange kinetics, high sorption capacity, and superior selectivity, leading to

91 Enthalpies increased with sorption capacity, and the energy released per mole sorb

92 The developed SLHSPs exhibit excellent CO(2) sorption capacity, high sorption rate, long-term stabili

93 roscopy (STA-PTA-FTIR) was used to determine sorption capacity, reversibility, thermodynamics, and ki

94 optimal loading necessary for maximum CO(2) sorption capacity.

95 al metal resistance, biodiversity, and metal sorption capacity.

96 pproach based on a novel concept of relative sorption coefficient for quantitatively assessing sorpti

97 ayed decreases in cation exchange-normalized sorption coefficients (K(CEC)), by up to one order of ma

98 Sorption coefficients for 14 benzylamine derivatives wit

99 tures provided insights to explain trends in sorption coefficients that could not be described by the

100 large influence (0.5-1 order of magnitude in sorption coefficients) on organic cation sorption.

101 realistic synthesis as well as catalysis (or sorption) conditions.

102 sorbate structure moieties yielded additive sorption contributions.

103 Sorbent packed columns are used and sorption data are determined by relating sorbate retenti

104 Predictive modeling explains the sorption data in considering that only weak clay fractio

105 undlich isotherms were fitted to the epitope sorption data.

106 Plutonium sorption decreased in the presence of DFOB (relative to

107 suggest ToF-SIMS to be a method for studying sorption depth profiles of MOFs.

108 sic differences between cesium and plutonium sorption/desorption behavior (charge, cation size) and s

109 estrogens, and water chemistry influence the sorption/desorption behaviors to different degrees.

110 that nonlinear, hysteretic, and irreversible sorption/desorption had minimal impact on PFOS transport

111 tion is very restricted, which affects their sorption/desorption kinetics when used as sorbent materi

112 sults of the study suggest that rate-limited sorption/desorption may affect the field-scale transport

113 on tailing, likely reflecting differences in sorption/desorption mechanisms.

114 The projected influence of rate-limited sorption/desorption on PFOS transport at the field scale

115 rch was to examine the influence of nonideal sorption/desorption on the transport of polyfluorinated

116 , rate-limited, hysteretic, and irreversible sorption/desorption on transport was investigated throug

117 fected by aqueous pH with high oxidation and sorption/desorption rates observed at the elevated pH.

118 Our results clearly demonstrate that sorption/desorption time scales observed in batch experi

119 d extensive elution tailing, indicating that sorption/desorption was significantly nonideal.

120 The overall results indicated that sorption/desorption was significantly rate-limited and t

121 ment metal concentrations by enhancing metal sorption directly to streambed sediments.

122 model employing a continuous distribution of sorption domains was successful.

123 he hydrophobic effect were found to be major sorption driving forces for cationic/zwitterionic PFAS a

124 text]) using gravimetric type dynamic vapor sorption (DVS).

125 ium sorption than by measures of benzylamine sorption, effective cation exchange capacity alone, or a

126 to-volume in such channels magnifies the gas sorption effects and improves accuracy.

127 forces may include H-bonding as indicated by sorption enthalpy determined by variation of column temp

128 DMMTA showed very little sorption, even to amorphous ferrihydrite, which is in li

129 The supercritical excess sorption experiments confirm these findings while reveal

130 be sorbed to reactor walls and tubing using sorption experiments in which plasma was not generated.

131 Sorption experiments with synthesized goethite and ferri

132 ere investigated in five soils through batch sorption experiments.

133 were to illuminate drivers of neonicotinoid sorption for parent neonicotinoids (imidacloprid, clothi

134 III) oxidation and concomitant As(V) electro-sorption from aqueous solution.

135 enabled their interpretation relative to the sorption, gelatinization and retrogradation phenomena of

136 icroporous domains characterized by Langmuir sorption in local equilibrium with a minority continuous

137 rption, suggesting that pharmacophore-driven sorption in real waters may be diminished.

138 lfonamidoalkyl betaine (PFOSB) showed strong sorption in selected soils.

139 e of structural transitions induced by CO(2) sorption in the ZIF-8 framework.

140 The different performance of MUV-3 toward NO sorption, in comparison to ZIF-8, results from the chemi

141 Sorption increased in the order bromide < nitrite < nitr

142 ling, wet chemistry soil extraction, and a P sorption index.

143 lder on the low-temperature side, suggesting sorption-induced structural transitions.

144 he relative humidity condition, the order of sorption is keton (3-hexanone) < aldehyde (1-hexanal) <

145 he structural transformation during methanol sorption is monitored by in-situ grazing incidence X-ray

146 contaminant based on the ability to predict sorption is required by researchers and practitioners al

147 ibits a Type I low-temperature/pressure N(2) sorption isotherm (SA(BET) =408.7(2) m(2) g(-1) , 77 K).

148 the surface chemical composition, the water sorption isotherm and the glass transition temperature o

149 nced modeling of aqueous data shows that the sorption isotherm can be interpreted by three retention

150 d experimental data, including 1) a complete sorption isotherm of hydrated cement paste (including th

151 om air in that it exhibits an S-shaped water sorption isotherm with a steep pore-filling step at low

152 ay diffraction, remarkably agreeing with the sorption isotherm.

153 rbents were well-described by the Freundlich sorption isotherm.

154 eory model describes accurately the measured sorption isotherms by using a distribution of properly w

155 Analysis of the water sorption isotherms indicated that decreasing the pH indu

156 P followed second-order reaction rates, and sorption isotherms of all sorbents were well-described b

157 r activities (a(w)) for the determination of sorption isotherms of green and roasted coffee, the glas

158 Sorption isotherms were constructed from measured aqueou

159 Carbon dioxide sorption isotherms were studied to 30 bar.

160 Water sorption isotherms, polarized light and scanning electro

161 high-pressure, room temperature Xe and CO(2) sorption isotherms.

162 The widely used two-domain sorption kinetics model could not fully simulate the obs

163 The sorption kinetics of POS, OS + P and COS + P followed se

164 (tipm)(3) (NO(3) )(4) ), which exhibits fast sorption kinetics, a large capacity (291 mg g(-1) ), a h

165 Sorption linearity and reversibility are implicit in mod

166 ials and are among the most efficient NH(3) -sorption materials.

167 The sorption measurements of two shales were performed at th

168 harge, cation size) and suggests that the Cs sorption mechanism (cation exchange) is not similarly af

169 redox-active structural iron may control the sorption mechanism of redox sensitive elements on the su

170 Sorption mechanism of uranyl by poly(bis[2-(methacryloyl

171 ambient air and they are categorized by the sorption mechanism: physisorption, chemisorption, and mo

172 eview provides the fundamental insights into sorption mechanisms and biodegradation pathways of diffe

173 It remains a challenge in deciphering PFAS sorption mechanisms and predicting how AFFF plumes migra

174 This work demonstrates that while sorption mechanisms manifest in testing of all sample si

175 be quantified using a dual-mode model of the sorption mechanisms.

176 The heterogeneous sorption might result from a 'self-sacrifice' mechanism,

177 address this limitation, a two-stage kinetic sorption model is developed and incorporated into a one-

178 Here we show that the full triple-mode sorption model is robust enough to predict the dynamic u

179 A dynamic triple-mode sorption model, developed previously, was employed to de

180 and were fit sufficiently well with a linear sorption model.

181 It was found that uranyl sorption obeyed Langmuir isotherm model giving a maximum

182 d to be compound-specific, with irreversible sorption observed for GA and prolonged tailing observed

183 This enables us to differentiate between sorption occurring onto the surfaces of synthetic versus

184 The sorption of 1-hexanal, 1-hexanol, 2-hexen-1-ol and 3-hex

185 rmed to quantitatively study the equilibrium sorption of 131 environmentally relevant organic contami

186 d colloids: OC + BC were responsible for the sorption of 65% of PBDEs, followed by colloids (30%); on

187 ture of the pores, 5 features size-selective sorption of alkaline metal cations in order Li(+) > Na(+

188 We observed the preferential sorption of aromatic and carboxylic-containing species a

189 In this work, we investigate selective sorption of arsenic from simulated groundwaters at pH 8

190 The sorption of C6, C8, and C10 monoalkylated PFPAs and C6/C

191 to a conductor due to the selective and fast sorption of cadmium ion.

192 In this study, however, we found that the sorption of cationic and zwitterionic PFAS in natural so

193 Sorption of cationic PFAS correlated strongly with the s

194 A significant sorption of certain esters was observed, but as HAs were

195 It displays reversible, multistep gated sorption of CO(2) below 0.33 atm.

196 Higher sorption of DOM to E. faecalis was roughly correlated wi

197 ious investigation on the transformation and sorption of drug biomarkers in the presence of only susp

198 t the surface site showed that the oxidative sorption of ferrous iron is an energetically favored pro

199 The MDF offset occurred more during the sorption of GEM rather than during diffusion.

200 Sorption of HAs to DAX-8 was less selective and caused o

201 In this study, the sorption of Hg(II), Cd(II), and Au(III) onto Bacillus su

202 ely irreversible, with significantly greater sorption of imidacloprid than desnitro-imidacloprid.

203 lity, optical and mechanical properties, and sorption of inorganic and organic species to prospect po

204 y, was found to be a useful predictor of the sorption of ionic PFAS species.

205 Low sorption of ligands coupled with strong Pu complexation

206 egative isotope fractionation, producing the sorption of light Zn (Delta((66)Zn(sorbed-solution)) = -

207 Tools for predicting sorption of many emerging contaminants to these sorbents

208 table electrical conductivity is provided by sorption of metal ions.

209 Sorption of methylated thioarsenates, which can co-exist

210 SC-SC sorption of N(2) , CO(2) , Xe, and AcMe by p-G(2) BDS is

211 ationalize these results by (i) preferential sorption of NOM components rich in redox-active groups (

212 ter chemistry (Ca(2+) and pH) influences the sorption of nonanionic PFASs in very distinct fashions o

213 Sorption of nutrients such as phosphate (P) and silicate

214 ges in electrostatic potential influence the sorption of organic cations, seven smectites were chosen

215 aches, our findings suggest that a selective sorption of oxygen-rich compounds in HA fractions to min

216 Such sorption of PAHs increases the agglomeration rate of Nan

217 only a few cells work as 'hot spots' on the sorption of Pb NPs.

218 Multiple soil properties described sorption of PFASs better than any single property.

219 ng contributions, indicating an inner-sphere sorption of Pu on OPA components.

220 ICRMS data provided evidence of preferential sorption of specific HA fractions, primarily tannin-like

221 The sorption of thallium (Tl) onto manganese (Mn) oxides cri

222 The equilibrium sorption of the adsorbents fitted well to the Langmuir m

223 Sorption of the different organic solutes within the mem

224 Sorption of the FtSs was driven by hydrophobic interacti

225 This study examines the sorption of the uranyl peroxide nanocluster [UO(2)(O(2))

226 th the presence of V(5+) species, suggesting sorption of this species on these secondary phases.

227 We show that extremely strong sorption of Tl onto vacancy-containing layered delta-MnO

228 Indeed, sorption of two pharmaceutical compounds to 30 soils was

229 Sorption of zwitterionic PFAS, on the other hand, displa

230 ulfhydryl Bacillus subtilis' or LSBS) and to sorption onto a commercially available cation exchange r

231 Overall, this study highlights the role of sorption onto Fe-(oxyhydr)oxides in attenuating Mo in ox

232 titative and mechanistic understanding of Tl sorption onto Mn oxides, however, is limited.

233 g(-1) and shows stark selectivity for CO(2) sorption over N(2), O(2), H(2), and CH(4).

234 The sorption parameters determined from these isotherms indi

235 l technologies that rely on PFAS interfacial sorption, particularly at field-relevant PFAS concentrat

236 % vs 69%, respectively), suggesting that the sorption performance is only marginally affected by orga

237 to outperform the leading zeolites in water sorption performance, with notably facile regeneration a

238 their interactions with bentonite, and their sorption potential to the chalk rock matrix.

239 The reversibility of the second-stage sorption process is found to be compound-specific, with

240 ent of inner-sphere surface complexes in the sorption process.

241 icipate in redox reactions and influence the sorption processes at surfaces of clay minerals.

242 Understanding the sorption processes is critical to the successful design

243 Reversible sorption processes led to substantial retardation of man

244 ciation of Pu within OPA after diffusion and sorption processes.

245 aterials exhibited dramatically enhanced gas-sorption properties as compared to nonpartitioned acs-ty

246 We report for the first time the high sorption properties of a molecular rotor with no permane

247 orm for studying the transition from analyte sorption properties of small aggregates to those of bulk

248 We report a systematic investigation of the sorption properties of three source clay minerals-Na-ric

249 e-earth metal cations (RE) with improved gas-sorption properties.

250 s fitted well to the Langmuir model, and the sorption rate fitted well to a pseudo-second-order kinet

251 t the first-stage polymer/surfactant-surface sorption rate is at least 1 order of magnitude greater t

252 ibit excellent CO(2) sorption capacity, high sorption rate, long-term stability and reduced amine los

253 d at low costs, can have high specific CO(2) sorption rates (in excess of 5 mumol s(-1) g(-1) bar(-1)

254 ty of liquid sorbents with the high specific sorption rates and low regeneration energies found in ma

255 s except for PFOSB; PFOSB underwent profound sorption reduction because its speciation occurs around

256 The models differed in how we accounted for sorption-related bioavailability differences in soil and

257 The capability to increase sorption selectivities is a powerful tool to leverage di

258 Both fast uptake kinetics and great sorption selectivity toward PFOS are observed.

259 of repeating units, which eventually changes sorption selectivity.

260 d rigid MOFs have widespread applications in sorption, separation and catalysis that arise from their

261 ential to compete with target oxo-anions for sorption sites resulting in decreased removal of the tar

262 ate from fertilizer outcompetes arsenate for sorption sites, mobilizing sorbed arsenic derived from p

263 ments, contact angle measurements, and water sorption/solubility measurements.

264 This study investigated the water sorption (SOR), solubility (SOL) and cytotoxicity (CYTO)

265 However, chemical interactions involved in sorption still remain unclear, as well as wood capacity

266 We report water vapor sorption studies on four primitive cubic, pcu, pillared

267 graphy represents a promising alternative in sorption studies to reveal sorbent properties.

268 Moisture sorption studies, Karl Fischer titration, and differenti

269 humic acid) inhibited overall neonicotinoid sorption, suggesting that pharmacophore-driven sorption

270 o-called thioarsenates, leads to a low to no sorption tendency to organic C functional groups.

271 better described by phenyltrimethylammonium sorption than by measures of benzylamine sorption, effec

272 to full kinetic and thermodynamic studies of sorption, the time-dependent effects of Cd(II) penetrati

273 h electrode area of 10 x 8 cm(2) and electro-sorption time of 120 min.

274 Sulfide-reacted peat increased sorption to 98%.

275 on the landscape that is inactive for guest sorption to an active one.

276 29 +/- 0.02 angstrom), consistent with As(V) sorption to both MnO(2) and HFO.

277 Modeling of the fractionation during Fe(III) sorption to cells and Fe(II) sorption to Feppt, combined

278 dicated complete As(III) oxidation and As(V) sorption to coprecipitated hydrous ferric oxide (HFO) in

279 during Fe(III) sorption to cells and Fe(II) sorption to Feppt, combined with equilibration of sorbed

280 Neonicotinoid sorption to GAC was extensive and largely irreversible,

281 Conversely, CA, FA, and HA increased Pu sorption to goethite at pH 3, suggesting ternary complex

282 n be an additional or alternative mode of As sorption to NOM.

283 m, 79%) and remained in solution without (re)sorption to peat.

284 ver humic acid (HA) samples before and after sorption to polar Al(2)O(3) and a nonpolar sorbent (DAX-

285 an contribute to soil C accumulation through sorption to poorly crystalline minerals and coprecipitat

286 Sorption to redox-inert aluminum oxide (Al(2)O(3)) was r

287 reduction of the Pu(V) source as well as Pu sorption to soils.

288 The relative binding strength of Zn sorption to the natural particles was inversely related

289 oil organic matter (SOM) or phosphate, while sorption under field conditions is still poorly understo

290 However, the extent of sorption via complexation with oxygen-containing functio

291 lving microbial bioaugmentation and enhanced sorption was demonstrated to be effective for in situ tr

292 Moreover, the strength of sorption was estimated for three small organic compounds

293 Sorption was insensitive to pH changes except for PFOSB;

294 The thermodynamic parameters indicated that sorption was spontaneous and favourable.

295 uctural integrity and the mechanism of water sorption were corroborated using in situ single-crystal

296 The effects of soil properties on sorption were different for anionic, nonionic, and zwitt

297 tween metal nodes and localized Cd(II) after sorption, which is supported by chronoamperometry measur

298 and oxygen content and decreasing selective sorption with reaction time, support "zonal" assembly mo

299 These nanocomposite sorbents exhibit rapid sorption with saturation occurring in less than 5 min.

300 l physical and chemical properties for CO(2) sorption within gas-permeable polymer shells, creating M

301 polypropylene exhibited high and reversible sorption without noticeable desorption hysteresis.