ライフサイエンスコーパス: sorption

1 il properties correlated well with bisphenol sorption.

2 not support increased PFAA removal via soil sorption.

3 uprofen demonstrated neither degradation nor sorption.

4 adjust those parameters controlling uranium sorption.

5 ereas diclofenac showed both degradation and sorption.

6 by surface charge neutralization of GO after sorption.

7 chieve removal through possible retention by sorption.

8 re resulted in decreased amounts of chromate sorption.

9 than electrostatic attraction contributed to sorption.

10 mpeting with ligand complexation, increasing sorption.

11 nal mass transfer slows down with increasing sorption.

12 I, and CNF II) were studied by dynamic vapor sorption.

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

14 It also increased moisture sorption affinity of aerogel.

15 s, dialkylamines showed a considerably lower sorption affinity than linear alkylamine analogues.

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

17 g X-ray fluorescence, X-ray diffraction, gas-sorption analysis, and adsorption isotherms/envelopes.

18 density functional theory computations, gas sorption analysis, fluorescence spectroscopy, and cyclic

19 active ingredient (factors of up to 1.4 for sorption and 1.7 for degradation).

20 e active ingredient (factors of up to 10 for sorption and 1.8 for degradation), but discrepancies wer

21 mpound-specific removal processes, primarily sorption and biotransformation.

22 curate densimetry to quantify the effects of sorption and capillary condensation, which exert a disto

23 n core gives rise to materials with enhanced sorption and catalytic properties.

24 The sponge is applicable for targeted sorption and collection due to its ferromagnetic propert

25 Sorption and degradation parameters of the insecticide b

26 of chemical sorbents that are cycled through sorption and desorption cycles for CO2 removal from ultr

27 experiments to investigate dynamic moisture sorption and desorption in markedly different materials,

28 N2 sorption and desorption isotherms show that the BNNS-10

29 el occurrence of processes like degradation, sorption and diffusive transport, at different rates in

30 tion of these two measurements, to study the sorption and mobility of polycyclic aromatic compounds (

31 Additive sorption and non-additive Cd(II) sorption behaviour is o

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

33 Whereas, the sorption and outgassing of Zircar RS-1200 was highly non

34 stinctly different materials and (2) predict sorption and outgassing under conditions that are distin

35 Their importance as a control on the sorption and redox reactivity of Mn-oxides toward Zn(II)

36 hysically (using laser diffraction, nitrogen sorption and SEM) and investigated electrochemically in

37 trollable functionalities such as switchable sorption and separation.

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

39 resses the influence of soil colloids on the sorption and transport behaviors of PPCPs through labora

40 At pH 5.0 where aggregation and net Fe(II) sorption are minimal, that exchange is quantitatively pr

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

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

43 ion of Zn(II) at pH 6.5, but enhances Zn(II) sorption at pH 7.5.

44 tion states exhibited deviations from linear sorption behavior and less Pu was adsorbed than at lower

45 However, it is not well understood how water sorption behavior is influenced by intrinsic factors tha

46 In this study, the water vapor sorption behavior of four nanocellulose samples, such as

47 s, we unambiguously showed the heterogeneous sorption behavior of nickel to CMAs.

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

49 Here, phosphorus (P) speciation and sorption behavior of suspended sediment were examined in

50 that bacterial sulfhydryl sites control the sorption behavior of these three metals, and therefore b

51 compounds with different biodegradation and sorption behavior were tested across standard OECD 308 a

52 Here we show that this anomalous sorption behaviour is a temperature-regulated guest admi

53 Additive sorption and non-additive Cd(II) sorption behaviour is observed for the binary Mont-bacte

54 GAB model was used to fit the experimental sorption behaviours.

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

56 as not due to differences in absolute Fe(II) sorption between the two solids types or competition for

57 gnificantly reduced or completely suppressed sorption (bromide, nitrite) due to competition with chlo

58 yMOF materials exhibited relatively high CO2 sorption but very low N2 sorption, making them promising

59 ly, DOM and glutathione greatly decreased Hg sorption by G. sulfurreducens PCA but showed little effe

60 or bracket-enamel shear bond strength, water sorption, CaP release, and ion recharge and re-release.

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

62 Our results show that HSBS exhibits sorption capacities for the three studied metals that ar

63 that are two to five times greater than the sorption capacities of LSBS for these metals.

64 CD-MOF have been shown to exceed the highest sorption capacities reported so far for CD-MOFs.

65 mercially available resin, exhibits superior sorption capacity and selectivity for the removal of Hg(

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

67 en tetrahedra in water causing a decrease in sorption capacity by reprecipitation of dissolved silica

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

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

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

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

72 mL(-1), preconcentration factor was 300, the sorption capacity of this new magnetic ion-imprinted pol

73 The microporosity, sorption capacity, and long-range order of the stabilize

74 r actinide removal due to its extremely high sorption capacity, but the mechanism of sorption remains

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

76 one mm(2) in size showed similar sorption characteristics to soil.

77 The Ni-MOF-74 obtained showed improved sorption characteristics towards CO2 and the refrigerant

78 unds across the various homoionic clays with sorption coefficients (Kd) decreasing as follows: Kd(Na(

79 ercompare sorption isotherms and solid-water sorption coefficients (Kd) for four organic cations (ben

80 r robust predictive models of organic cation sorption coefficients (Kd).

81 Based on 102 soot-carbon normalized sorption coefficients (KsootC) acquired at different sor

82 Organic cation sorption coefficients exhibited consistent trends for al

83 nge ions in the prediction of organic cation sorption coefficients for environmental solids.

84 Sorption coefficients measured in the high pH range indi

85 surface-associated inorganic exchange ions, sorption coefficients of 10 organic cations (including e

86 transformed to a mixture of U(IV) and U(VI) sorption complexes, and after 14 days of reaction, 100%

87 thesis was validated by the fact that the Cu sorption constants on xanthan were always higher than th

88 ), no differences were observed in the U(VI) sorption curves for the three clay minerals.

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

90 The equilibrium sorption data for OTS both with and without treatment fi

91 te well with the experimental rejections and sorption data.

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

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

94 reaction at pH 7.6 (i.e., above the Fe(II) "sorption" edge), U(VI) was transformed to a mixture of U

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

96 ree distinct regions are observed: (1) minor sorption effects in micropores at low pressures; (2) cap

97 Sorption-enhanced reactivity was independently supported

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

99 r) and GAB (Guggenheim, Anderson and deBoer) sorption equations.

100 anic carbon concentration and pH using batch sorption experiments at 5 mgC.L(-1) and 50 mgC.L(-1) nat

101 Batch sorption experiments indicate that increasing Ti concent

102 Sorption experiments indicated that SWCNTs effectively a

103 Batch sorption experiments show that siderite has a high affin

104 ic PFASs in the subsurface is unknown, batch sorption experiments were conducted using National Foam

105 Batch sorption experiments, liquid chromatography (LC) analyse

106 to clay edge sites was assessed by comparing sorption from 0.01 N KCl and 0.01 N CaCl2; however, no s

107 tion of volatiles (Solid Phase Mesh Enhanced Sorption from Headspace, SPMESH), which could then be an

108 Moreover, it realized practical gas sorption functionality in innovated metal phosphites.

109 the surface via Se-O bond as well as physic-sorption had, an average diameter of 89 nm, and were hig

110 running time, equilibrium moisture content, sorption hysteresis and sorption kinetics between these

111 del and applied to the lattice-gas model for sorption in aerogel at low temperatures, when dynamics o

112 For the two more slowly degrading compounds, sorption in OECD 309 (standard and modified) increased w

113 ill suffered from issues of interaction (oil sorption in peat) and highly nonlinear partitioning with

114 At pH 9, Pu sorption in the presence of all NOM increased relative t

115 bsence of phosphate, whereas after prolonged sorption in the presence of phosphate, the formation of

116 Sorption increased in the order bromide < nitrite < nitr

117 t important determinants of uranium-membrane sorption interactions were (i) the uranium speciation (u

118 shows that different uptake mechanisms-edge sorption, interfacial dissolution-reprecipitation-are at

119 explains the loss of flavour rather than the sorption into PET.

120 ernative method offering advantages to study sorption is column chromatography.

121 Sorption is influenced by interactions between HOCs and

122 To better understand how organic cation sorption is influenced by surface-associated inorganic e

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

124 the [Cu2(glu)2(bpa)] MOF displays a stepped sorption isotherm for the uptake of CO2 at room temperat

125 r P1 while P2 and P3 did not follow the same sorption isotherm pattern.

126 skewness to identify the linear range of the sorption isotherm.

127 ay diffraction, remarkably agreeing with the sorption isotherm.

128 ier transform infrared spectroscopy (FT-IR), sorption isotherms and antifungal activity were evaluate

129 orption techniques were used to intercompare sorption isotherms and solid-water sorption coefficients

130 from the SSLM beads, resulting in nonlinear sorption isotherms for compounds with log DMW values abo

131 aluated as a method to obtain organic cation sorption isotherms for environmental solids while using

132 Sorption isotherms for four structurally similar acids (

133 is is the first report of propane and butane sorption isotherms in shales.

134 constraints on proteins influence the water sorption isotherms of amorphous protein powders.

135 low vapor pressure at room temperature, the sorption isotherms of propane, n-butane and iso-butane w

136 Sorption isotherms were best described by the Freundlich

137 Sorption isotherms were constructed from measured aqueou

138 Moisture sorption isotherms were determined.

139 Methane and ethane sorption isotherms were measured to 35 bar.

140 Carbon dioxide sorption isotherms were studied to 30 bar.

141 ons of 10(-15) - 10(-8) M produced linear Pu sorption isotherms, demonstrating that Pu sorption to go

142 Herein, batch sorption isotherms, isothermal titration calorimetry (IT

143 Renewal of the medium resulted in linear sorption isotherms.

144 diclofenac was reflected in additional (15)N sorption isotope effects, whereas isotope fractionation

145 Equivalent Pu(IV) and Pu(V) sorption Kd values obtained at 1 and 2-week sampling tim

146 Then, the sorption kinetics behavior was accurately described by u

147 um moisture content, sorption hysteresis and sorption kinetics between these four nanocellulose sampl

148 ing a straightforward way of determining the sorption kinetics of any fluorinated contaminant, this w

149 Due to superior sorption kinetics, 0.2 wt % MCG-biochar in saturated san

150 ppears to be independent of the rapid Mn(II) sorption kinetics.

151 on model coupled with a dynamic, triple-mode sorption (Langmuir, Henry, and pooling modes) model empl

152 relatively high CO2 sorption but very low N2 sorption, making them promising materials for CO2/N2 sep

153 The sorption measurements of two shales were performed at th

154 y FTIR, magnetic hysteresis, XRD, SEM and N2-sorption measurements.

155 up to 1,276 m(2) g(-1)) was evidenced by gas-sorption measurements.

156 ter analysis times, and allow for consistent sorption measures across laboratories with distinct chro

157 how that column chromatography can reproduce sorption measures from conventional batch experiments wi

158 The underlying sorption mechanism was probed using quantum mechanical a

159 Regardless of the sorption mechanism, all known materials exhibit an isoth

160 Thus, the sorption mechanisms of the FtSs, FtSaBs, and 6:2 FtSaAm

161 ues was used to examine molybdate (MoO4(2-)) sorption mechanisms on CaAl LDHs with increasing loading

162 exchange capacity was evaluated to determine sorption mechanisms.

163 5)), demonstrating the feasibility of MOF as sorption media for treating certain nuisance components.

164 The GAB sorption model fitted for P1 while P2 and P3 did not fol

165 The linear equilibrium sorption model provided a good description of batch resu

166 re correctly described using a thermodynamic sorption model that considers two binding sites: externa

167 Our triple-mode sorption model was adaptive enough to (1) model these di

168 4(+), and Ca(2+) were derived using a 3-site sorption model.

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

170 s required for the development of predictive sorption models.

171 essed using the AM only showed DBP precursor sorption occurred in each column that decreased over tim

172 al distortion previously observed for Pu(IV) sorption occurs with Pu(V) as well.

173 on factors (BCF) in flow-through fish tests, sorption of 11 highly hydrophobic organic chemicals (HOC

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

175 Dissociation greatly affected the sorption of all acids.

176 pendent distribution ratio (DOW) to describe sorption of aromatic acids to sorbents representing diff

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

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

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

180 The observed strong sorption of hydrophobic organic contaminants (HOCs) to b

181 the influence of environmental conditions on sorption of inorganic anions (bromide, nitrite, nitrate,

182 Low sorption of ligands coupled with strong Pu complexation

183 ence of various AFFF components and enhanced sorption of long-chain fluorotelomer betaines.

184 Black carbons (BCs) dominate the sorption of many hydrophobic organic compounds (HOCs) in

185 on coefficient are commonly used to describe sorption of neutral organic compounds in environmental s

186 Sorption of organic molecules to mineral surfaces is an

187 Sorption of PACs to DOC and POC was important for the mo

188 carbon content, was observed to control the sorption of PFPAs and PFPiAs, the lack of which may be a

189 sely correlated with KOW, suggesting greater sorption of polar compounds to polar cotton.

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

191 Sorption of semivolatile organic compounds (SVOCs) onto

192 lity is an important parameter affecting the sorption of SOCs onto soils.

193 tions have impeded progress in understanding sorption of SVOCs on indoor surfaces.

194 measured in the high pH range indicated that sorption of the anions ranged over several orders of mag

195 Sorption of the different organic solutes within the mem

196 Sorption of the FtSs was driven by hydrophobic interacti

197 Sorption of the FtSs, FtSaBs, and 6:2 FtSaAm to six soil

198 sulfhydryl sites using a qBBr treatment, the sorption of the metals onto HSBS was significantly inhib

199 Transformation and sorption of these substances were assessed in targeted b

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

201 The results of this study indicate that the sorption of U(VI) on SiO2 in the presence of inorganic p

202 results show that it is important to monitor sorption of uranium to membranes, which is controlled by

203 of the anionic synthetic dyes based on their sorption on silica sorbent modified with hexadecyl group

204 No Ag internalization or sorption on the cell wall was detected.

205 s) in the rhizosphere with subsequent Zn(2+) sorption on the root plaque.

206 ers on metal sorption was studied through Cu sorption on xanthan.

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

208 ntly inhibited, indicating that the enhanced sorption onto HSBS was mainly due to the elevated concen

209 antify zinc isotope fractionation during its sorption onto kaolinite, by performing experiments under

210 In this study, we investigated Pu sorption onto Na-illite, a relevant component of potenti

211 with different levels of burnup, followed by sorption onto Zn-Fe-oxides.

212 Humidity-driven sorption opens a new approach to gas separation technolo

213 ydroxide mediated scavenging of uranium, the sorption or coprecipitation of U(VI) with poorly crystal

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

215 providing a kinetic enhancement to hydrogen sorption performance.

216 uilibrium models were studied to explain the sorption phenomenon out of which Langmuir, Dubinin-Radus

217 Combining the high sorption potential of GAC for CH3Br with the conductivit

218 d carbon nanomaterials and their general CO2 sorption potential.

219 sotherm temperature were recorded during the sorption process.

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

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

222 ntities of heavy metals, such as nickel, via sorption processes.

223 orption profiles (DVS), and dynamic dewpoint sorption profiles (DDI).

224 rated solution water activity, dynamic vapor sorption profiles (DVS), and dynamic dewpoint sorption p

225 as observed to retain both structure and gas sorption properties after prolonged exposure to heat and

226 tional materials with modified and selective sorption properties for gas substrates.

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

228 l-organic materials and control of their gas sorption properties.

229 provides a high degree of tunability in gas sorption properties.

230 h allows for extraordinary tunability in gas sorption properties.

231 196 K, under 1 atm) and acetone (5 wt %), a sorption property that was attributed to both, the restr

232 atment fitted to the Langmuir model, and the sorption rate data well fitted to the pseudo second-orde

233 2.5 wt % under the simulated flue gas), fast sorption rate, and strong process durability.

234 of empty Me,H,SiMe2 at room temperature, but sorption rates are slow, occurring over weeks to months.

235 n calculations to interpret variations in Pu sorption rates in the presence of FA.

236 Furthermore, based on these sorption reactions, we demonstrate the ability of an att

237 C) content and pH was sufficient to describe sorption reasonable well across the four soils (%OC 0.1-

238 easing Ti concentration results in higher Np sorption/reduction values at low pH.

239 high sorption capacity, but the mechanism of sorption remains unclear.

240 pH approximately 5 were conducted; the batch sorption results were modeled simultaneously using surfa

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

242 With tunable sorption selectivities, the CCMM membranes outperform fl

243 tivities result from substantially increased sorption selectivities, which is hypothetically owing to

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

245 xample), implying a potential application in sorption separation and chemical sensors.

246 rter path length than previously assumed and sorption serves as a key rate-limiting step.

247 ccurs at other times, potentially liberating sorption sites for processing of subsequent incoming pho

248 e by competitive adsorption to high-affinity sorption sites while acknowledging that toluene could ad

249 tion of Fe(III) oxides reduced the number of sorption sites, a significant fraction of the released A

250 phosphate initially involves binary surface-sorption species and evolves toward surface precipitatio

251 A sorption-spectrometric method for determination of the a

252 chemically stable to find uses in recyclable sorption, storage, and potentially separation of chemica

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

254 The batch sorption studies on silica gel (10 g/L) in the pH range

255 Gas sorption studies revealed that these polyMOF materials e

256 on (OC) forest soil which correlates well to sorption studies showing higher sorption with higher OC.

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

258 During gas sorption studies, the "closed pore" (cp) <--> "open pore

259 s comprehensively investigated using a batch sorption technique, in situ attenuated total reflection

260 ustom packed HPLC columns and standard batch sorption techniques were used to intercompare sorption i

261 determined using water activity and moisture sorption techniques.

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

263 In addition to its capabilities for gas sorption, the highly biocompatible Mg2(olz) framework wa

264 Results suggest that sorption to (sinking) POC was the dominant removal proce

265 ant impact on BCF studies and differing from sorption to Aldrich-humic acid (AHA) utilized as referen

266 wever, we do not have data for diverse HOCs' sorption to BC because it is time-consuming and labor-in

267 lowed the rates of gas (water vapor and CO2) sorption to be quantified by single crystal X-ray diffra

268 However, PAH sorption to biochar is characterized by very high (10(4)

269 Sorption to black carbons is an important sink for organ

270 Sorption to carbon-based nanomaterials is typically stud

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

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

273 Batch experiments of Eu(III) and U(VI) sorption to GO as the function of pH (1-8) and as the fu

274 tional group is the main mechanism for their sorption to GO; their complexation to the sulfonate site

275 ternary batch systems, NOM will decrease Pu sorption to goethite at all but particularly low pH cond

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

277 Pu sorption isotherms, demonstrating that Pu sorption to goethite is not concentration-dependent acro

278 Pu(IV) and Pu(V) sorption to goethite was investigated over a concentrati

279 (FA), and humic acid (HA) on plutonium (Pu) sorption to goethite was studied as a function of organi

280 e larger than corresponding KDOC, suggesting sorption to mobile particles/colloids is the dominant me

281 of debromination is limited, possibly due to sorption to natural organic matter of the sediment.

282 utaraldehyde concentrations decreased due to sorption to soil and were completely biodegraded within

283 on is hypothesized to be due to its stronger sorption to soil owing to a longer perfluoroalkyl chain

284 undance for the prediction of organic cation sorption to soils and soil minerals.

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

286 These data show that while sorption to the vessels, dissolution, and aggregation im

287 ost from solution by either precipitation or sorption to the vial walls.

288 stabilized as a result of coprecipitation or sorption to their surfaces.

289 Yet the extent of sorption, transformation, and interactions among the num

290 Sorption trends for all sorbates and carbonized sorbents

291 hich have been shown to enhance radionuclide sorption via titanium's influence on the Fe(2+)/Fe(3+) r

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

293 Sorption was investigated in batch-equilibrium experimen

294 nd separation factor (RL) indicated that the sorption was spontaneous and favorable.

295 H > 4.5 the surface charge was negative, but sorption was still detectable at pH 6 and 9.

296 impact of environmental biopolymers on metal sorption was studied through Cu sorption on xanthan.

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

298 rganics had no noticeable impact on chromate sorption, whereas concentrations of 50 mg/L or more resu

299 ates well to sorption studies showing higher sorption with higher OC.

300 Batch experiments revealed enhanced U(VI) sorption with increasing phosphate addition.