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1 ees provisioned with various types of water (deionized, 1%NaCl in deionized, or tap) have greater med
3 100 ppt, respectively, could be reached for deionized and tap water solutions of PFOA using a smartp
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
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
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
16 tening, these shale samples were immersed in deionized (DI) water heated to 100 C temperature and sub
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
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
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
36 ontaining 50 seeds, with four groups tested: deionized water (G1), Fe(2+) solution (G2), Fe(3+) solut
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
42 ed of 1-pentanol and extraction solutions of deionized water and 100 mM NH4OH), more than 99.3% NaCl
45 ducted dynamic dissolution experiments under deionized water and CO(2) solution conditions to study t
48 tion of various cationic surfactants in both deionized water and high-salinity brine (22% total disso
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
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
60 rm ligand exchange column with distilled and deionized water as the mobile phase is used to separate
63 ere conducted on lithium disilicate glass in deionized water at 50 degrees C between 1 and 7.5 h.
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
70 n, a sensor regeneration can be reached with deionized water by adjustment of effective convection co
76 seawater holds promise as an alternative to deionized water for electrolyte solvents due to its ener
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
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
90 tential of the food-grade TiO2 suspension in deionized water ranged from -10 to -45 mV around pH 7, a
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
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.
102 EDCL resulted in the highest stability when deionized water was used as the aqueous phase (original
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
114 he 10th day (acute treatment) with distilled/deionized water, 10 mg/kg fluoxetine or 20 mg/kg fluoxet
116 were performed with enzyme saline solutions, deionized water, and 50% (v/v) aqueous acetone solution.
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
121 to crudely approximate cellular conditions: deionized water, aqueous methanol, and aqueous buffers a
123 etection limits of 0.2-0.5 nM perchlorate in deionized water, commercial bottled water, and tap water
125 s conducted under oxidative conditions using deionized water, dilute HNO(3), and dilute H(2)O(2) as t
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
136 lting in a product water that is essentially deionized water, often containing less than 100 mug/L or
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
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
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
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