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1 be a next generation membrane for engineered osmosis.
2 ge and viscous drag forces caused by electro-osmosis.
3 ld a next generation membrane for engineered osmosis.
4 for treatment of brackish water than reverse osmosis.
5 this in turn drives water transport by local osmosis.
6 nd Cl(-) transport and the water flux due to osmosis.
7 sed on Hulett's view, the only valid view of osmosis.
8 kinetically selective organic liquid reverse osmosis.
9 anced Treatment trains incorporating reverse osmosis.
10 ges to induce liquid crystal-enabled electro-osmosis.
11 s research has demonstrated that the reverse osmosis and advanced oxidation processes (AOPs) used to
12 crater have included evaporite dissolution, osmosis and evaporation from heating associated with the
14 fluent, two types of recycled water (reverse osmosis and ozonation/activated carbon filtration), stor
19 mpulse conduction that appear to result from osmosis and to indicate accumulation of ions in the peri
20 oplastics that are commonly used for reverse osmosis and water purification membranes, medical equipm
21 st physical principles of electroneutrality, osmosis, and conservation of particles or a combination
22 xchange membranes (namely, co-ion transport, osmosis, and electro-osmosis) can detrimentally lower ef
27 mely, co-ion transport, osmosis, and electro-osmosis) can detrimentally lower efficiency by up to 26%
29 minants in industrial wastewater and reverse osmosis concentrate from municipal wastewater recycling
31 e membrane filter (RCNT-MF), for the reverse osmosis desalination that can turn salt water into fresh
32 is (e.g., forward osmosis, pressure-retarded osmosis, direct osmosis) has emerged as a new platform f
38 ith their analog separation process (reverse osmosis, electrodialysis, and capacitive deionization, r
44 lutions hindered competition between forward osmosis (FO) and pressure retarded osmosis (PRO) with ex
45 driven membrane processes (including forward osmosis (FO) and pressure retarded osmosis (PRO)) have r
46 ite (TFC) hollow fiber membranes for forward osmosis (FO) applications is presented in this study.
48 VC), membrane distillation (MD), and forward osmosis (FO) as the technologies best suited for desalin
51 igated the feasibility of applying a forward osmosis (FO) dewatering process for nutrient recovery fr
57 m uses both ultrafiltration (UF) and forward osmosis (FO) membranes in parallel to simultaneously ext
59 and the performance was evaluated in forward osmosis (FO) mode with various feed solutions: nanopure
63 mperature (UCST) as a draw solute in forward osmosis (FO) was successfully demonstrated here experime
65 m combining electrodialysis (ED) and forward osmosis (FO), driven by renewable energy (solar energy),
66 bustness and treatment capacity of a forward osmosis (FO)-membrane distillation (MD) hybrid system fo
67 nes that translate the advantages of reverse osmosis for aqueous separations to the separation of org
68 ing considered as a key component of reverse osmosis-free advanced treatment trains for potable waste
70 organic matter that was isolated by reverse osmosis from the Suwannee River in southeastern Georgia.
71 esponse to different urea gradients (induced osmosis) gave sigmaurea approximately 0.3 for the UT3 pa
72 on application of an electric field, electro-osmosis generates bulk fluid flow in the device, and a p
73 of energy storage, the transport of water by osmosis has a very significant negative impact on the fa
75 d osmosis, pressure-retarded osmosis, direct osmosis) has emerged as a new platform for applications
78 pilot-level trials using 1kD, loose reverse osmosis (LRO) and reverse osmosis (RO) spiral-wound memb
79 We report a hybrid microfiltration-forward osmosis membrane bioreactor (MF-FOMBR) for direct phosph
80 aromatic polyamide active layer of a reverse osmosis membrane upon exposure to free chlorine was quan
83 oncept of a polyelectrolyte-promoted forward osmosis-membrane distillation (FO-MD) hybrid system was
84 of polyamide (PA) nanofiltration and reverse osmosis membranes by chlorine needs to be understood in
85 t of water across apposing liquid menisci in osmosis membranes comprising short hydrophobic nanopores
86 superhydrophilic thin-film composite forward osmosis membranes functionalized with surface-tailored n
87 layers are deposited onto commercial reverse osmosis membranes without damaging them and they exhibit
88 ranes is particularly outstanding in forward osmosis mode where the driving force for water flux is a
90 eriments in both forward osmosis and reverse osmosis modes are performed with three model organic fou
92 and expand gradually to their full size via osmosis of surrounding tissue fluid, with up to a 10-fol
93 there is no direct evidence for either local osmosis or aquaporin gene expression in enterocytes.
94 nland brackish water desalination by reverse osmosis or RO, concentrate or reject disposal poses a ma
98 inable energy by combining pressure-retarded osmosis (PRO) as a power generation stage and membrane d
99 stigate the performance of pressure retarded osmosis (PRO) at the module scale, accounting for the de
100 Osmotic power generated by pressure-retarded osmosis (PRO) has attracted global attention as a clean,
104 on tested under the FO and pressure retarded osmosis (PRO) modes, respectively, while consistently ma
105 lution tested under FO and pressure retarded osmosis (PRO) modes, respectively, while maintaining low
106 high power density in the pressure-retarded osmosis (PRO) process experimentally and theoretically.
108 smotic power generation by pressure-retarded osmosis (PRO) processes, fouling on PRO membranes must b
109 e practical application of pressure retarded osmosis (PRO) technology for renewable blue energy (i.e.
110 n forward osmosis (FO) and pressure retarded osmosis (PRO) with existing water purification and power
111 g forward osmosis (FO) and pressure retarded osmosis (PRO)) have received increasing attention in rec
112 ane for fouling control in pressure-retarded osmosis (PRO), an emerging engineered osmosis process wh
113 he foremost technologies - pressure retarded osmosis (PRO), reverse electrodialysis (RED), and capaci
114 al technologies, including pressure-retarded osmosis (PRO), reverse electrodialysis (RED), and capaci
115 by thermal separation, and pressure retarded osmosis (PRO), which converts the energy of mixing to el
119 ning the centrifugal force propelled reverse osmosis process and the porous CNT-based fine scale sele
121 their advantages as draw solutes in forward osmosis process in terms of high water flux, minimum rev
122 tarded osmosis (PRO), an emerging engineered osmosis process whose advancement has been much hindered
125 or GR activity attenuation; however, reverse osmosis removed GR activity to levels below the limits o
127 ty in the polyamide active layers of reverse osmosis (RO) and nanofiltration (NF) membranes, to predi
129 nown to be insufficiently removed by reverse osmosis (RO) and nanofiltration polyamide membranes that
131 In this work, a high-performance reverse osmosis (RO) composite thin membrane using multi-walled
132 s a promising way to improve current reverse osmosis (RO) concentrate treatment processes and enables
133 energy consumption (SEC) in seawater reverse osmosis (RO) desalination due to improvements made in hy
134 is a major operational challenge in reverse osmosis (RO) desalination, motivating a search for impro
135 designed and constructed to evaluate reverse osmosis (RO) energy reduction that can be achieved using
137 ely enhanced nanofiltration (NF) and reverse osmosis (RO) membrane permeate flux and salt rejection r
140 The top polyamide layer of composite reverse osmosis (RO) membranes has a fascinatingly complex struc
141 Swelling of the active layer of reverse osmosis (RO) membranes has an important effect on permea
142 s into the polyamide active layer of reverse osmosis (RO) membranes is one of the three membrane prop
143 ts, applied to control biofouling of reverse osmosis (RO) membranes, result in membrane performance d
144 imethylamine (NDMA) by six different reverse osmosis (RO) membranes, suggesting that boron can be use
146 nts such as ultrafiltration (UF) and reverse osmosis (RO) on dissolved organic matter (DOM) is still
150 1kD, loose reverse osmosis (LRO) and reverse osmosis (RO) spiral-wound membranes showed LRO membrane
153 dimethylamine (NDMA) passing through reverse osmosis (RO) units within advanced treatment trains for
155 other organic matter (OM) isolates (reverse osmosis, RO; and "transphilic", XAD-4) from several rive
156 es new mechanism of highly efficient electro-osmosis rooted in space charging of regions with distort
158 tage enhanced tertiary processes and reverse osmosis, simultaneously increased eutrophication indirec
161 ological model which includes water entry by osmosis, the incorporation of cell wall material and the
163 formed to study the rates of AS transfer and osmosis through the membrane, and the operational parame
164 R) is an emerging technology that uses water osmosis to accomplish separation of biomass from the tre
165 microfiltration/ultrafiltration and reverse osmosis utilize porous membranes to remove suspended par
168 ater, deionised water, spring water, reverse osmosis water, and distilled water at 95 degrees C, and
169 a also perturbs epithelial ion transport and osmosis, which may be important for the long-term surviv
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