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1 ees provisioned with various types of water (deionized, 1%NaCl in deionized, or tap) have greater med
2              The method is demonstrated with deionized and tap water samples spiked with carbamate in
3  100 ppt, respectively, could be reached for deionized and tap water solutions of PFOA using a smartp
4        The effect of divalent ion binding to deionized bacteriorhodopsin (dI-bR) on the thermal trans
5              Adding Ca2+ or other cations to deionized bacteriorhodopsin causes a blue to purple colo
6 esults on the M intermediate are observed if deionized blue bR (deI bbR) is treated with these deterg
7  or without pH buffers present), even though deionized blue bR containing all the lipids has no photo
8 ration and photochemical properties of dried deionized blue membrane (dIbR600; lambdamax approximatel
9 ing mechanisms of the ions to the protein of deionized bR.
10    In this study, the cavitation behavior of Deionized (DI) water and 10mM L-Histidine buffer solutio
11 , e.g., dodecyltrimethylammonium bromide, in deionized (DI) water and high-salinity brine is 1.274% a
12       Deposited QDs were then contacted with deionized (DI) water and/or varying Na(+) concentrations
13 rboxyanhydrides (NCAs), have been studied in deionized (DI) water as well as various ionic media.
14 vestigated using 0.1 M glycerol dissolved in deionized (DI) water at ambient temperature and pressure
15       THC-COOH was rapidly removed from both deionized (DI) water at pH 5.6 +/- 0.2 and Suwannee Rive
16 tening, these shale samples were immersed in deionized (DI) water heated to 100 C temperature and sub
17                 Results for 5 mM H(2)O(2) in deionized (DI) water included reduction to below the COD
18  Results showed that MON was persistent in a deionized (DI) water matrix when exposed to UV and sunli
19 ions generated by ultrasonic nebulization of deionized (DI) water stored in a variety of bottles.
20  Released by-product aerosols collected in a deionized (DI) water trap were analyzed, and the aerosol
21  0.05 ppb at 168 h and was 71% lower than in deionized (DI) water, in batch reactors spiked with 5 x
22 orption (epsilon) and quantum yield (Phi) in deionized (DI) water.
23 e solutions with high salt concentrations or deionized (DI) water.
24 trol group was administered double distilled deionized drinking water (ddw).
25 arious concentrations (1-100 ppm) of DEHP in deionized MilliQ water were tested using the functionali
26 various types of water (deionized, 1%NaCl in deionized, or tap) have greater median lifespans than th
27  NMR spectra of two kinds of blue membranes, deionized (pH 4) and acid blue at pH 1.2, were very simi
28 hod detection limits were 0.007 microg/L for deionized reagent water and 0.009 microg/L for synthesiz
29 to 95 degrees C) and in various water types (deionized, tap, river, and marine water) can erode plast
30 ated by lysing attached cells with distilled/deionized water (DDI H2O).
31 either deionized water (DFMO-) or 1% DFMO in deionized water (DFMO+).
32 ient (Zn-, 4 ppm zinc) diet and given either deionized water (DFMO-) or 1% DFMO in deionized water (D
33 n traditional EDM which is replaced with the deionized water (DI) based dielectric as a sustainable a
34 e side or symmetrically from both sides with deionized water (DIW) or 0.1 M solutions of CaCl(2), KCl
35 tration of 100 mM) for 3 h, then washed with deionized water (DW).
36 ontaining 50 seeds, with four groups tested: deionized water (G1), Fe(2+) solution (G2), Fe(3+) solut
37  nanoparticles are stored at 20 degrees C in deionized water (pH 6.7).
38 ent dissolution of AgNP exposed to ultrapure deionized water (pH approximately 7) and acetic acid (pH
39 ferent kinds of filters and one open tray of deionized water - alongside paired water samples and vis
40 nts were moistened with synthetic aquifer or deionized water according to the moisture regimes presen
41                                              Deionized water and 1.5% and 3% aqueous hydrogen peroxid
42 ed of 1-pentanol and extraction solutions of deionized water and 100 mM NH4OH), more than 99.3% NaCl
43 r the detection of phenytoin in solutions of deionized water and 100% fetal bovine serum.
44 cantly reduced the static contact angles for deionized water and artificial sweat.
45 ducted dynamic dissolution experiments under deionized water and CO(2) solution conditions to study t
46 polished MCT wafers are cleaned and dried by deionized water and compressed air, respectively.
47                                              Deionized water and ethanol at different concentrations
48 tion of various cationic surfactants in both deionized water and high-salinity brine (22% total disso
49 using voltages as low as 0.5 V(RMS) for both deionized water and physiological buffer.
50                               The CE between deionized water and PTFE can produce a surface charges d
51 performance was assessed in buffer solution, deionized water and spiked tap water.
52 r activated carbon and biochar adsorption in deionized water and stormwater was independent of target
53 tion experiments were conducted at pH 7.5 in deionized water and synthetic water with composition of
54 erties when the droplets are introduced into deionized water and the associated high polarizability o
55 situ halogenation reaction of gemfibrozil in deionized water and wastewater matrices, and to measure
56                   Nanoparticles suspended in deionized water are actively trapped using wireless diel
57 surements of serum samples diluted 1:10 with deionized water are performed, a stable background signa
58  under real conditions (using 0.5 M NaCl and deionized water as the draw and feed solutions, respecti
59  brine (1.0 M NaCl) as the draw solution and deionized water as the feed.
60 rm ligand exchange column with distilled and deionized water as the mobile phase is used to separate
61 of the buffer at the point of use, utilizing deionized water as the only carrier stream.
62 ), 2 mL H(2)O(2) (30 % m m(-1)), and 4 mL of deionized water at 180 degrees C for 2 h.
63 ere conducted on lithium disilicate glass in deionized water at 50 degrees C between 1 and 7.5 h.
64      Experiments were performed in quiescent deionized water at dissolved-air saturation of S = 20%,
65                    C0-independent removal in deionized water at low-target-adsorbate concentrations p
66 hese samples are able to form strong gels in deionized water at polymer concentrations as low as 0.25
67 ely lick small drops of gustatory stimuli or deionized water at varying non-nociceptive temperatures.
68 ared by dilution of the reaction masses with deionized water before analysis by CE/indirect UV detect
69          Atmospheric ammonia is collected in deionized water by a porous membrane diffusion scrubber
70 n, a sensor regeneration can be reached with deionized water by adjustment of effective convection co
71 ases: KOH, Ca(OH)(2), ZnCO(3), or NaOH and a deionized water control.
72                    Rinsing the cathodes with deionized water did not restore cathode performance.
73 titive effect of stormwater DOM and possibly deionized water DOM.
74                                         In a deionized water environment, the degradation of the mech
75 )/(3))O(3)-32PbTiO(3) (PMN-PT) cantilever in deionized water environment.
76  seawater holds promise as an alternative to deionized water for electrolyte solvents due to its ener
77                          The K(PE) values in deionized water for parent- and alkylated-PAHs show a go
78  such as citrates and phosphates, instead of deionized water greatly improves the efficiency of this
79  bound counterions, we used dialysis against deionized water in the presence of a strong (0.6 kV/cm)
80  counterions are removed by dialysis against deionized water in the presence of a strong electric fie
81 rations potentially suggests that DOM in the deionized water induce a competitive effect that causes
82 e air discharge and its downstream sample of deionized water is studied with a system-level computati
83 ly deplete erythrocytes from whole blood via deionized water lysis and to collect enriched leukocytes
84 abled the direct detection of crude oil in a deionized water matrix at the ppm level to ppb concentra
85 r increase the performance of QDSCs, the 30% deionized water of polysulfide electrolyte was replaced
86 ction, by impinging a high-speed microjet of deionized water on a dielectric solid surface.
87 and eco-friendly extraction solvents: either deionized water or aqueous solutions of cyclodextrins.
88  studies on DEP manipulation of DNA that use deionized water or diluted DNA buffer where living biomo
89 de cocrystallization on the MALDI plate with deionized water prior to analysis.
90 tential of the food-grade TiO2 suspension in deionized water ranged from -10 to -45 mV around pH 7, a
91       Etching of the gel-grown crystals with deionized water reveals an interpenetrating network of g
92               The protocol is completed by a deionized water rinse, which was also studied.
93 trend, residual particle concentrations from deionized water stored in Teflon bottles showed a net de
94 rations as high as 10 mg/mL were obtained in deionized water that are nearly 2 orders of magnitude hi
95                              In contact with deionized water the features of (001) surfaces barely mo
96 uced by NNK from 34% in the group given only deionized water to 12%.
97 lick chemistry, followed by self-assembly in deionized water to construct a versatile and functional
98 in dimethyl sulfoxide, and added dropwise to deionized water to form pellets of a porous PAN-chalcoge
99 yophilization process and reconstituted with deionized water to form the first layer of drug casting.
100 reated with 10 mg/kg fluoxetine or distilled/deionized water vehicle for 9 consecutive days.
101                The loss of both compounds in deionized water was observed upon exposure to natural su
102  EDCL resulted in the highest stability when deionized water was used as the aqueous phase (original
103 d to mimic different brine compositions, and deionized water was used for comparison.
104                                              Deionized water was used to induce emulsion breaking wit
105  to as high as 24.3 W/m(2) when 1 M NaCl and deionized water were feeds.
106             Recoveries for most compounds in deionized water were greater than 80%.
107 thanol, and Mercury II Chloride (HgCl(2)) in deionized water were used to visualize the tendon-to-bon
108 al salts (NaCl, KCl, MgCl2, and CaCl2) using deionized water with a known stable isotope composition.
109 d washing experiments for fabric swatches in deionized water with or without detergent showed a range
110  of 2 mL HNO(3), 0.5 mL H(2)O(2), and 0.5 mL deionized water yielded the best recovery for all elemen
111 tivity (~20 S cm(-1) in PBS, ~40 S cm(-1) in deionized water), high stretchability (> 35% strain), lo
112 Compared to well-known untreated bulk water (deionized water), the prepared AuNT water exhibits many
113 veral standard solutions (e.g. PBS, HEPES or deionized water).
114 he 10th day (acute treatment) with distilled/deionized water, 10 mg/kg fluoxetine or 20 mg/kg fluoxet
115                          Upon dissolution in deionized water, all three ARV DAs were found to spontan
116 were performed with enzyme saline solutions, deionized water, and 50% (v/v) aqueous acetone solution.
117 wn to 0.1mg/L is detected in PBS, tap water, deionized water, and bottled water.
118 air-drying, replacement of the seawater with deionized water, and substitution of the cell matrix wit
119 ns accelerate leaching of Mg(2+) by 20x over deionized water, and that leaching of Mg, Mn, Fe, Co, an
120 ous system was disrupted by adding 1.0 mL of deionized water, and two phases were formed.
121  to crudely approximate cellular conditions: deionized water, aqueous methanol, and aqueous buffers a
122                                           In deionized water, chondrocytes swelled monotonically unti
123 etection limits of 0.2-0.5 nM perchlorate in deionized water, commercial bottled water, and tap water
124                                           In deionized water, concentration thresholds increase as ta
125 s conducted under oxidative conditions using deionized water, dilute HNO(3), and dilute H(2)O(2) as t
126            Then, the soils were leached with deionized water, filtered, and analyzed for dissolved or
127 ion of boron NPs from residual boric acid in deionized water, followed by their coating with polyethy
128 here the storage solution pH equaled that of deionized water, gave values of approximately 0.5 for [C
129 rom silica surface was observed after adding deionized water, indicating that GO deposition is revers
130  masks (and one 100% cotton control mask) to deionized water, laundry detergent, and artificial saliv
131 ectrolyte blend solution and then exposed to deionized water, making the droplet interfacial layer ac
132 udied PFASs showed measurable degradation in deionized water, methanol, or isopropyl alcohol over 30
133 of Hg(2+) in various environments, including deionized water, milk, fish, and sprouted pea roots were
134                                       Within deionized water, nanoparticles form stable suspensions o
135                                              Deionized water, NaOH, HCl, and oxalate extractions show
136 lting in a product water that is essentially deionized water, often containing less than 100 mug/L or
137  hormone classes, with application to spiked deionized water, pond water, and wastewater.
138 medium (DMEM), Phosphotungstic acid (PTA) in deionized water, PTA in ethanol, and Mercury II Chloride
139 ynylestradiol in unspiked drinking water and deionized water, respectively, at levels higher than pub
140                                           In deionized water, the electrochemical system achieved 0.5
141 pulsed wave (PW) ultrasound at 205 kHz using deionized water, wastewater effluent, and its isolated o
142 th a solvent droplet containing methanol and deionized water, we generated electrospray to extract th
143                                           In deionized water, we observed that hydrophobicity is supe
144 as obtained for 168 of the 204 pesticides in deionized water, where 90% of the quantifiable pesticide
145 ibits a 30-fold rate improvement compared to deionized water, where the degradation remains incomplet
146 n and were stabilized after precipitation in deionized water.
147 ddition of the required quantity of H2O2 and deionized water.
148 e contact pressure at low kHz frequencies in deionized water.
149 on [IS]) was evaluated at 10-70 degrees C in deionized water.
150 compared to controls treated with autoclaved deionized water.
151  the MCT wafers, and the lapping solution is deionized water.
152 le and negative for toxicity when diluted in deionized water.
153 ueous media was achieved by dialysis against deionized water.
154  via the electrolysis of saline solutions or deionized water.
155 ies of AuNT water are tunable by mixing with deionized water.
156  only Hg(0) and Hg2(2+) can be methylated in deionized water.
157 estigated in simulated biological fluids and deionized water.
158 etely remove MC-LR in lake water compared to deionized water.
159 ificantly more H(2)O(2) than tea prepared on deionized water.
160  diluting the resulting oil body creams with deionized water.
161  DNA counterions by electro-dialysis against deionized water.
162 dosed with naphthalene over those dosed with deionized water.
163 s determined as 3.1 +/- 0.2 at neutral pH in deionized water.
164 n received 5 microL ciprofloxacin (0.08%) or deionized water.
165 e into crystalline colloidal arrays (CCA) in deionized water.
166 studied by measuring the flux of pH-adjusted deionized water.
167 ssemble into crystalline colloidal arrays in deionized water.
168 etween polytetrafluoroethylene particles and deionized water/O(2) interfaces, inducing the generation
169 ffect of force and test solution parameters (deionized water; water + abrasive medium; acid + abrasiv
170       Recovery experiments were performed in deionized, well, and river water.

 
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