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Hydrophilic and compressible aerogel: a novel draw agent in forward osmosis Mingchuan Yu, Hanmin Zhang, and Fenglin Yang ACS Appl. Mater. Interfaces, Just Accepted Manuscript • DOI: 10.1021/acsami.7b10229 • Publication Date (Web): 11 Sep 2017 Downloaded from http://pubs.acs.org on September 12, 2017
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ACS Applied Materials & Interfaces
Hydrophilic and compressible aerogel: a novel draw agent in forward osmosis Mingchuan Yu, Hanmin Zhang*, and Fenglin Yang
Key Laboratory of Industrial Ecology and Environmental Engineering (MOE), School of Environmental Science and Technology, Dalian University of Technology, Dalian 116011, P. R. China.
Keywords: Graphene oxide, Alginate aerogel, Forward osmosis, Draw agent, Wastewater treatment
Corresponding author. E-mail address:
[email protected] (HM. Zhang). 1 Environment ACS Paragon Plus
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ABSTRACT Forward osmosis (FO) technology is an efficient route to obtain purity water for drinking from wastewater or seawater. However, there are some challenges in draw solution to limit its application. We firstly introduce a novel sodium alginate-graphene oxide (SA-GO) aerogel as draw agent for highly efficient FO process. The GO nanosheets covalently cross-linked to SA matrix to form a three-dimensional and highly porous aerogel to provide excellent water flux and operation stability, together with the property of compressibility served by SA-GO aerogel resulting in easy water production and regeneration process. When the deionized water used as the feed solution, the SA-GO aerogel exhibited a high water flux (15.25±0.65 L m-2 h-1, abbreviated as LMH) than that of 1 mol L-1 NaCl and there was no non-reverse osmosis phenomenon. The water fluxes were stabilized in the range of 5-6.5 LMH during recycle process of absorbing and releasing water as high as 100 times. It also had a great desalination capacity (water flux was 7.49±0.61 LMH) with the seawater (Huanghai coast) as the feed solution. Moreover, the water production and regeneration process of the SA-GO aerogel can be rapidly and cost-effectively accomplished with low-strength mechanical compression (merely 1 kPa). The results present that the SA-GO aerogels as a promising innovation draw agent can make the FO process simpler, more efficient and lower energy consumption. It can be a potential material for hydration bags to fast and repeatable product fresh water from saline water or wastewater.
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1. INTRODUCTION
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With population growth and economic development, water scarcity and pollution are
3
becoming increasingly serious.1, 2 Since the middle of the 20th century, membrane filtration
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technology including microfiltration,3 ultrafiltration,4 nanofiltration5 and reverse osmosis6 has
5
been widely used in drinking water treatment, groundwater replenishment and industrial
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wastewater treatment to change the unsustainable use of water resources. Forward osmosis
7
(FO) is a membrane separation process that relies solely on osmotic pressure, which means
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that water molecules spontaneously penetrate through the semipermeable membrane from the
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feed solution side (the high water chemistry potential) to draw solution side (the low water
10
chemistry potential). FO technology with lower energy consumption of draw water process 1,
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higher water recovery rate, and smaller membrane fouling tendency is superior to other
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membrane technology and is widely investigated. There have been many successful attempts
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in desalination, power generation, industrial wastewater treatment, drug release and food
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processing. Particularly, the hydrated bag is one of FO commercial applications used in
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drinking water shortage conditions of the military, recreational and emergency rescue fields.7
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But the FO development is still facing a challenge from draw solutions. In previous researches,
17
many
18
macromolecules,10 magnetic nanoparticles,11 hydrophilic carbon quantum dots12 and so on13,
19
are developed successively. However, these draw solutions can’t fully meet the FO
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technology requirements resulting from high energy consumption of the regeneration process,
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heavy reverse osmosis, low water flux or other problems.7 Recent years, hydrogels, as an
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emerging draw agent, can completely avoid the reverse osmosis, attributing to the structure of
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the three dimensional (3D) networks of polymer chains.14-16 Nevertheless, the water flux
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(driving force) and water recovery rate of hydrogels are much low owing to large volumes of
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water entrapping into the 3D networks structure and high water retention capacity.14, 17 It
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severely restricts its development and application. In the comparison with hydrogel, aerogel,
materials,
such
as
inorganic
salts,8
natural
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synthetic
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as a kind of functional material with high porosity, low density and large specific surface area,
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has diverse physical and chemical properties according to its composition.18-28 Sun et al
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directly synthesized the ultra-flyweight aerogel by cryodesiccation and reduction reaction
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with graphene oxide and carbon nanotube. It was called “super sponge” which can still kept
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its original scale and morphology after the fatigue test of 1000 cycles.29 Therefore, we select a
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hydrophilic and resistant compressed aerogel as a new type of draw agent referring to
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hydrogel characteristics and similar draw water behavior of beverage powder used in the FO
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hydration bags.30, 31 It can maintain the property of no reverse osmosis relying on its 3D
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networks structure. Simultaneously, a higher FO driving force can be produced because its
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structure contains amount of hydrophilic functional groups on the chains and no water
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molecule inside its structure. Compared with most of draw agents, the compressible property
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of aerogel draw agent can greatly simplify its regeneration process, instantly complete the
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regeneration and water recovery to reduce the energy consumption.
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Herein, a hydrophilic and compressible sodium alginate-graphene oxide (SA-GO) aerogel was
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obtained through esterification, ionic crosslinking and lyophilization process in Figure 1 and
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employed as a draw agent in the FO process for the first time. As expected, the as-prepared
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SA-GO aerogels exhibited many favorable properties: (i) high water flux, (ii) non-reverse
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osmosis, (iii) convenient and efficient regeneration process (merely rely on 1 KPa
45
compression can simply and rapidly complete the water production), (iv) non-toxic and (v)
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stable performance in continuous reuse process.
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2. MATERIALS AND METHODS
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2.1. Materials and chemicals. All chemicals and solvents were purchased from Aladdin and
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used without purification. Sodium alginate (C6H7O6Na)n (AR), Calcium chloride anhydrous
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(CaCl2) (AR), Ethanol absolute (CH3CH2OH) (AR) and Sodium chloride (NaCl) (AR) were
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purchased from Aladdin. Graphite flake (~150 µm flakes) was purchased from Sigma-Aldrich.
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Potassium permanganate (KMnO4) (AR), Sulfuric acid (H2SO4) (AR), Phosphoric acid 4 Environment ACS Paragon Plus
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(H3PO4) (85%), Hydrogen chloride (HCl) (36% aqueous solution) and Hydrogen peroxide
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(H2O2) (30% aqueous solution) were purchased from Sinopharm Chemical Reagent. DI water
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from a Milli-Q (Millipore, USA) system was used in all experiments.
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2.2. Preparation of graphene oxide (GO). GO was prepared according to the previously
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reported method with slight modifications.32 In brief, 3.0 g natural scale graphene (1 wt equiv)
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was added into the 1000 mL round-bottomed flask and mixed in a 9:1 mixture of concentrated
59
H2SO4/H3PO4 (360:40 mL) solution under magnetic stirring. After that, 18.0 g KMnO4 (6 wt
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equiv) was slowly added to the flask under ice-cooling. The water bath was then heated to
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50 °C and stirred for 12 h. The reaction was cooled to room temperature and then the
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suspension was poured onto ice water (about 500 mL). The reaction solution needed to be
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protected from light and waited until the temperature drops to room temperature. Then, H2O2
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was slowly added dropwise to the reaction solution until the solution became golden yellow.
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For workup, the reaction solution was washed in succession with 300 mL of 0.1 M HCl
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aqueous solution (multiple times) and 300 mL of distilled water (multiple times). The treated
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solution was centrifuged (10000 rpm for 10 min) until the pH of the supernatant was closed to
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5. The GO solid was obtained by vacuum drying (room temperature).
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2.3. Synthesis of sodium alginate-graphene oxide (SA-GO) aerogel. Typically, 0.6 g
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sodium alginate (SA) was dissolved in 29.4 g of distilled water under magnetic stirring about
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12 h to form a homogeneous aqueous solution. Then, a uniform dispersion was formed after
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mixing the GO solid and the SA solution through ultrasonication for 2 h to form. The mass
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ratio of the SA and GO were 8:1, 16:1 and 80:1, respectively. After that, 0.24 M CaCl2
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aqueous solution was sprayed to the surface of the reaction solutions, and reaction solutions
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stood for 24 h at room temperature to form the hydrogels. The hydrogels were freeze-dried (-
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90 °C for 24 h) to obtain aerogels after washed with the distilled water until the aqueous
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solution had no Ca2+.
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2.4. Physical Characterization. Attenuated total reflection-fourier transform infrared
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intensity (ATR-FTIR) measurements were carried out by using a ThermoFisher 6700
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Spectrometer Spectrum (Thermo Fisher, USA) to determine the functional groups in the SA-
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GO aerogels among 4000 and 400 cm-1. Nitrogen adsorption-desorption isotherms were
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measured by Quantachrome Autosorb-1MP sorption analyzer (Quantachrome, USA). The
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specific surface areas were calculated using the BET method. Crystallographic pattern of the
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SA-GO aerogels were obtained by Empyrean X-ray diffraction (XRD) (PANalytical,
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Netherlands) using Cu-Kα radiation. Raman spectra were recorded using a DXR Smart
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Raman spectrometer (Thermo Fisher, USA). Surface morphology of the aerogels was studied
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using NOVA Nano SEM 450 scanning electron microscopy (SEM) (FEI, USA) at an
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acceleration voltage of 15 kV.
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The compressive test was performed on the home-made equipment shown in Figure S6.33
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The Dip coater (CZ-4200, HTLAB Co., Ltd.) drives the compression head up and down at a
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preset speed. The load on the sample was recorded using a pressure sensor.
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samples with a diameter of 20mm were cut into 20mm length (L/D=1) and tested at room
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temperature (25 °C) using a compression rate of 500 µm min-1 up to 50% compressive strain.
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In FO process, the ability of aerogels to absorb water was measured as draw agents in FO
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device. The water absorption capacity (Wa) (g g-1) of SA-GO aerogels was measured and
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calculated as:
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() =
33
Cylindrical
(1)
98
where mt and m0 are quality of wet (running time was t) and dry aerogel, respectively.
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2.5. FO performance. FO experiments were carried out through a lab-scale rig, as shown in
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Figure S7. Commercial Cellulose Triacetate (CTA-ES) FO membranes from Hydration
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Technologies Inc. (HTI, USA) were used, which involve a dense selective active layer onto a
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phase inversed polysulfone supporting layer. The FO membranes are immersed in DI water 2
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h before use. All FO experiments used the FO mode (the membrane orientation of the active 6 Environment ACS Paragon Plus
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layer facing the feed solution). During the FO tests, the feed solution side of the FO
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membrane (effective membrane area of 12.6 cm2) was circulated by one peristaltic pump
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(LongerPump, LongerBT100-2J). The temperatures of the feed was maintained at 25±0.5 °C.
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In FO process, the aerogel draw agents were all 0.2 g dry cylinders according with the FO
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module and DI water feed solution without special instructions. And the initial volume of the
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feed solution was 1 L. A feed container was placed on a weighing scale (MSE2203, Sartorius,
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Germany) that was connected to a computer data logging system to record weight change at
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regular time intervals (interval time is 1 min). And the used FO membrane was washed by DI
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water and then were stored in DI water.
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The water flux, Jw, (LMH) was calculated from the weight change of the feed solution using
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Equation (2). ∆
= ∆
115
(2)
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where ∆V (L) is the volume change of the feed solution over a predetermined time ∆t (h) and
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A is the effective membrane surface area (m2).
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This FO process doesn’t need to test the reverse salt flux due to structural characteristics of
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the aerogels without reverse osmosis.
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Recovery of SA-GO aerogels from their drawing water state: After an FO process, the draw
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agent needed to produce water and regenerate by a mechanical compression device. A
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commercial injection pump (LongerPump, LSP01-2A) with a computer controller was used
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for draw agent regeneration. (
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Water recovery rate (Wr) =
125
where mt, m0 and mw are quality of wet, dry aerogel and water recovery, respectively.
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3. RESULTS AND DISCUSSION
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3.1. Structure and Properties of Aerogels.
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In this paper, SA-GO aerogels were successfully synthesized by esterification, ionic
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crosslinking and lyophilization with SA, GO and CaCl2, as shown in Figure 1. During the
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synthetic route, SA was a strong hydrophilic and non-toxic raw material, and easy to form a
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gel. CaCl2 as an ion crosslinking agent can accelerate the formation of SA hydrogel in mild
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conditions. Meanwhile, GO as an auxiliary crosslinking agent (chemical crosslinking) was
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introduced to enhance the crosslinking strength, compressibility and hydrophilicity of the
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aerogel because it possessed a considerable amount of hydroxyl and epoxide functional
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groups on both surfaces of each sheet and carboxyl groups mostly at the sheet edges.34 In
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order to validate the crosslinking reaction between SA and GO and the effect of physical and
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chemical properties, a series SA-GO aerogels with various volume ratios of SA and GO
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(Table 1) were synthesized, characterized and tested.
139 140
Figure 1. Synthetic route of the SA-GO aerogels.
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Table 1. The feed amount of raw materials in the reaction. SAa) (g) GO (mg)
CaCl2b) (mL)
aqueous solution pure SA
30
0
10
SA-GO-1
30
7.5
10
SA-GO-2
30
37.5
10
SA-GO-3
30
75
10
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a)
The concentration of SA aqueous solution is 2 wt%
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b)
The concentration of CaCl2 aqueous solution is 0.24 mol L-1
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The structure information of aerogels was confirmed by ATR-FTIR (Figure 2a). The
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characteristic bands of SA aerogel at 3422 cm-1 (O-H stretching vibration) and 1615 cm-1 (-
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C=O stretching vibration of carboxylate) indicated the appearance of hydroxyl and
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carboxylate groups. The absorption bonds of GO (Figure S1) present characteristic bands at
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3312, 1720, and 1610 cm-1 attributing to stretching vibration of hydroxyl, carboxyl and
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carboxylate group, respectively.35 In comparison with the raw materials of SA and GO, a new
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band at 1740 cm-1 (-C=O stretching vibration of ester) appears after condensation reaction of
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SA and GO, inferring that a part of carboxyl groups (SA) and epoxy groups (GO) might
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convert into esters. It means crosslinking between SA and GO. The X-ray diffraction (XRD)
154
measurement further shows that GO is attached into the SA-GO aerogels (Figure S2). The
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typical diffraction peak for GO appeared at around 11 ° belonging to (001) crystallographic
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plane.33 And the diffraction peak at 23.5 ° is assigned to the amorphous morphology of pure
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SA (002). By contrast, the XRD pattern of the SA-GO aerogels gives the peak at 18.3 ° and
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its shoulder peak at 21.5 ° revealing greater amorphous morphology than pure SA (002).36
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The consequent increase of amorphous phase confirmed the successful conjugation between
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SA and GO. Otherwise, the Raman spectra of SA-GO aerogels all show two prominent peaks
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at the same range with that of GO (D band and G band), manifesting the existence of GO in
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SA-GO aerogels (Figure 2b). XPS was conducted to obtain more detailed information about
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elemental analysis and chemical structure of the aerogels. Here, the SA-GO-1 (the optimum
164
condition) was chose to make a comparative analysis with SA. As the Figure S3a shown, the
165
peaks in the full spectra indicated the existence of carbon, oxygen and calcium elements in the
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SA and SA-GO-1 aerogel. In the C1s spectrum (Figure S3b) of the SA-GO-1 aerogel, peak
167
fitting showed four different peaks: C-C/C-H/C=C (284.5 eV), C-O (286.1 eV), C=O (287.3
168
eV) and O-C=O (288.3 eV). For the SA aerogel, the C1s spectrum was deconvoluted into 9 Environment ACS Paragon Plus
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three main bands appearing at 284.6 (C-C/C-H), 286.2 (C-O) and 287.8 (O-C=O) eV. After
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introducing of GO, SA-GO-1 had more oxygen-containing groups and interacted (chemical
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crosslinking and hydrogen bonding) with SA. In addition, the peaks at 347 and 350.6 eV in
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Figure S3d and e were due to Ca2p3/2 and Ca2p1/2, respectively, indicating that the calcium
173
ion was bivalent 28, 33. All the results verify the structure of the SA-GO aerogels.
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Figure 2. (a) ATR-FTIR and (b) Raman spectra of SA-GO and pure SA aerogels.
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The morphology and microstructure of as-prepared aerogels were examined by SEM (Figure
177
3a). In the pure SA aerogel, the wall thickness of the structure is about 3.6 µm and a large
178
number of agglomerations are on its surface. It is attributed to the fact that the pure SA
179
aerogel only replied on ionic crosslinking (Ca2+) to form gel. But the wall thickness of the
180
SA-GO aerogels is thinner and a mass of deep-submicron pores (pore diameter: 100-500nm)
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are observed on the surface due to the addition of GO. The wall thickness of the SA-GO
182
aerogel became thicker with the increasing of GO content (from 0.52 to 2.3µm), and the
183
numbers of deep-submicron pores on the wall layers decreased distinctly which is consistent
184
with the variation tendency of the specific surface area data (Table 2). Among SA-GO
185
aerogels, the SA-GO-1 aerogel has more deep-submicron pores on the surface of the wall
186
which in favor to increasing the specific surface area. 37 Furthermore, it also reveals that a
187
mass of hydrophilic groups (SA) were encapsulated by the excess GO nanosheets inducing
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the compressibility and hydrophilic to be decreased. It is consistent with the water contact
189
angle and compressibility results (Table 2, Figure S4 and Figure S5). 28 10 Environment ACS Paragon Plus
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The specific surface area (SBET) and pore properties, the important affecting factors on the FO
191
performance, were obtained from the nitrogen sorption measurement (Table 2). For pure SA
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aerogel without the cross-linking of GO, its SBET is 33.42 m2 g-1, which might be induced by
193
the severe stacking and intertwining of the aerogel structure during the formation process.
194
And, as the increasing of the GO content in SA-GO aerogels, the SBET had an obvious
195
decreasing tendency. Combined with the SEM images analysis, when the GO content was
196
appropriate (at lower state), it only might be used as a crosslinking agent to crosslink the SA
197
fragments while enhancing the hydrophilic and compressibility of the aerogel. However, with
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the increasing of GO content (more than the amount required for the crosslinking agent), only
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part of GO took effect as the crosslinking agent, the residual GO might crosslink with each
200
other or induce the unformed hydrogel fragment structures to be wrapped and stacked. The
201
SEM images exhibits that the layer structure of the SA-GO-3 has serious stacking
202
phenomenon than the other two SA-GO aerogels leading to lower SBET. Moreover, as the
203
Table 2 shown, the SA-GO aerogels possess a low density in the range of 0.031-0.041 g cm-3,
204
which is comparable to those of monolithic graphene based materials.19, 29, 38 It is due to the
205
rich open-pore structures interpenetrating the skeleton of aerogel (Figure 3a). And, it also can
206
be seen that pore volume (VP) is in the range of 0.118-0.364 cm3 g-1.
207
The hydrophilicity of the aerogels can be directly proved by the water contact angle
208
measurement. As demonstrated in Figure 3b, a water droplet drops onto the SA-GO aerogel
209
surface is absorbed immediately (less than 100 ms). In other words, there was no initial
210
nonzero contact angle for the aerogels. In order to investigate the different hydrophilicity
211
between the inherent materials and aerogels, the sheets of SA-GO and SA were obtained
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through grinding and pressing of the aerogel materials. The water contact angles of SA-GO
213
and pure SA sheets followed the sequence of SA-GO-3 > SA-GO-2 > pure SA > SA-GO-1
214
(Table 2 and Figure 3c). It might be due to the excessive GO encapsulated the unformed
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were encapsulated inducing the reducing tendency of the SA-GO aerogels.39,40 In addition, the
217
hydrophilicity of aerogel status is more superior than sheet status attributed to the 3D porous
218
network structure of aerogel.
219 220
Table 2. Porous and hydrophilic properties of SA-GO and pure SA aerogels. Specific
surface Pore
area (SBET)(m2 g-1)
volume Density
Water contact
(VP)(cm3 g-1)
(g cm-3)
anglea (°) a)
pure SA
33.42
0.18
0.033
27.7
SA-GO-1
311
0.364
0.031
24.6
SA-GO-2
167.73
0.217
0.033
28.0
SA-GO-3
76.55
0.118
0.041
31.8
221
a)
222
of SA-GO aerogel materials
The water contact angles were the SA-GO sheets which were made by grinding and pressing
223
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Figure 3. (a) SEM images of the dry SA-GO and pure SA aerogels. (b) The water contact
226
angles of dry aerogel and (c) sheet states with the SA-GO and pure SA materials.
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3.2. FO performances testing.
229
The water fluxes of these dry aerogels, as shown in Figure 4a, followed the sequence of SA-
230
GO-1>SA-GO-2>SA-GO-3>pure SA, during 20 min. After introducing GO into SA aerogel,
231
the water fluxes of SA-GO aerogels are higher than that of pure SA aerogel. At an appropriate
232
GO content (SA-GO-1), the water flux was superior to others referring to the GO content had
233
an effect on the SBET, water contact angle and microstructures. Compared with traditional
234
draw agent-NaCl (1 mol L-1, abbreviated as 1 M, 11.02±0.34 L m-2 h-1, abbreviated as LMH),
235
the water flux of dry SA-GO-1 aerogel, upped to 15.25±0.65 LMH, is higher, when the
236
running time is 20 min. However, with the running time exceeding 20 min, the water fluxes of
237
aerogels were observed a significant decay trend. This phenomenon might be affected by the
238
saturated water absorption capacity of the aerogels themselves (Table S1). Combined with
239
Table S1 data, the water absorption quality of aerogel draw agents had gradually approached
240
saturation state with the extension of running time. Similar to the hydrogel, when the water
241
absorption quality of aerogel was close to the saturated state in FO process, the driving force
242
also gradually weakened.17, 41 The water flux of the SA-GO-1 presented especially obvious
243
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absorbing the massive water in short time to reach to its saturated water absorption capacity.
245
And water absorption capacities of SA-GO aerogels were all larger than pure SA aerogel
246
consisting with the results of the water flux in FO process. The Wa of SA-GO-1 aerogel
247
(17.95 g g-1) is 6.4 times, 2.99 times and 5.5 times than that of SA, SA-GO-2 and SA-GO-3
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aerogel during 20 min, respectively. Besides the reverse osmosis of the draw agents is an
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important indicator for the FO performance evaluation. It exists in most of the draw agents (in
250
addition to hydrogel) in previous reports inducing the wastage of the draw agent, the
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reduction of the water flux and the secondary pollution of the feed solution.42 But the SA-GO
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aerogel can completely avoid reverse osmosis because of its 3D network structure similar
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with hydrogel.41
254 255
Figure 4. (a) Water fluxes of SA-GO, pure SA aerogels and 1 M NaCl. (b)Effect of the
256
different water recovery rates on water flux recovery.
257 258
In regeneration process, the Wr of the wet aerogel is determined by the degree of compression
259
which can directly affect its water flux. In order to optimize the water flux of the regenerated
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wet aerogels, the different degrees of compression (water recovery rate) were investigated in
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FO process. Figure 4b exhibits the relationship of Wr with water flux in a series of
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regenerated wet SA-GO aerogels. As the Wr increases, the water fluxes of SA-GO aerogels
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showed an increasing tendency. And, in this process, it indicated that the increasing trend of
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the water flux on the Wr from 30% to 50% were more remarkable than that from 50% to 70%.
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Furthermore, when Wr reached 70%, the SA-GO aerogel structure was irreversible damaged,
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affecting its continuous use performance. Therefore the Wr (50%) was selected to dewater
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from the wet aerogel in recovery process.
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Water recovery process can be completed by mechanical compression, as shown in Figure 5,
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Video 1 and Video 2. The SA-GO-1 aerogel, as the test sample, was subjected to compression
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for this measurement. When the pressure reached 1 kPa, the aerogel can complete the
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compression and production water process in short-time. By contrast, the regeneration method
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of NaCl (traditional draw agent) is RO technology which requires high running pressure (~1.5
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MPa).41 And Razmjou et al reported a bilayer polymer hydrogels draw agent which can
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continuously product fresh water, but it also consumed larger energy (input energy from 0.5
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to 2 kW m-2) and longer regeneration time (dewatering rate from 10 to 25 LMH) than that of
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SA-GO-1 aerogel.31,
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commercialized in hydration bags.7, 46 But the production water in hydration bags contains
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glucide because of glucose or fructose as the draw agent, which leading to the limited target
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users. And the draw agents are disposable and need to be replaced frequently. If SA-GO-1
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aerogel as draw agent is used for the FO hydrated bags, the water recovery and regeneration
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process can be easily accomplished in short-time by a compression of an adult palms (2 MPa
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pressure) and the scope application of production water could increase substantially. In a
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word, the SA-GO-1 aerogel can facile and quickly accomplish this process which
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demonstrated significantly superiority than the aforementioned draw agents.
44, 45
To the best of our knowledge, FO technology has been
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Figure 5. Different state of SA-GO-1 aerogel in compression process. a) the dry state of
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aerogel. b) the wet state of aerogel. c) the compressed wet aerogel. d) the released wet aerogel.
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As a draw agent of FO technology, the re-use performance of aerogel is also an important
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index to balance the FO performance of draw agent. Therefore, we evaluate the re-use
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performance of SA-GO-1 with deionized water as feed solution in the FO continuous cycle
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test. According to the water flux results, 20 min was selected as the running time. As seen of
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Figure 6a, the initial water flux of the dry aerogel is 15.5 LMH. After the compression and
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regeneration, the wet aerogel was re-used to measure the draw-release water capacity in FO
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process. In the course of continuous cycle tests (100 cycles), the water fluxes of wet SA-GO-1
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generally kept high and stabilized in the range of 5-6.5 LMH, indicating SA-GO-1 aerogel
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can be recycled and maintain a high FO performance. The obvious attenuation of water flux
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between dry aerogel and wet aerogel is attributed to the above-mentioned water absorption
298
capacity in FO process. The SA-GO-1 aerogel showed high structure stability and repeatable
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draw-release water capacity. Furthermore, the water fluxes of wet SA-GO-1 aerogel draw
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agent are also greater than that of all most hydrogels using as draw agents.14-16, 41
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301 302
Figure 6. (a) The water fluxes of SA-GO-1 in FO continuous cycle test. (b) Desalination test
303
of SA-GO-1 aerogel.
304 305
3.3. Application of SA-GO aerogel in FO. The SA-GO-1 aerogel was selected and applied
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to seawater desalination, owing to its remarkable pure water flux (high hydrophilic), great
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mechanical strength and large specific surface area, among this series aerogels. In the
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desalination test, the seawater (Huanghai coast, conductivity is 26.8 mS cm-1 and total
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dissolved solids (TDS) is about 24800 ppm) and SA-GO-1 aerogel were used as feed solution
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and draw agent, respectively. As shown in Figure 6b, it presented a similar trend but lower
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water flux compared with the deionized water because that the seawater contains numbers of
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inorganic salts leading to a higher osmotic pressure
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water. Eventually, the high water flux and water quality were obtained in FO process. The
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water flux of dry SA-GO-1 aerogel is as high as 7.49±0.61 LMH (running time: 20 min).
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After regeneration with 50 % Wr, the water flux of the wet aerogel can still carry out
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3.18±0.39 LMH, which is higher than the pure water flux of most hydrogel draw agents.46
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Meanwhile, the conductivity and TDS of production water were 10-40 µS cm-1 and 4.5-19
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ppm, respectively, suggesting that there are no leaching ions and organics of aerogel in
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production water. Considering the above-mentioned properties, this kind of aerogel is an
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innovative and alternative draw agent in the FO process.
47
(25 atm) than that of the deionized
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4. CONCLUSIONS
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In summary, we have demonstrated, for the first time, the hydrophilic and compressible SA-
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GO aerogels as a novel kind of draw agent in FO process. The structure and properties of SA-
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GO aerogels were evaluated through the ATR-FTIR, Raman, XRD, water contact angle
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analyzer and sorption analyzer. The SA-GO aerogels with lightweight (0.031-0.041 g cm-3),
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large specific surface area (76-311 m2 g-1) and 3D hierarchically porous structure were
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constructed through SA and GO via esterification, ionic crosslinking and lyophilization.
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Particularly, the SA-GO-1 aerogel showed an excellent hydrophilicity and compressibility,
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offering suitable properties for FO process. The water flux of dry SA-GO-1 aerogel
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(15.25±0.65 LMH) was 1.46 times of 1 M NaCl (11.02±0.34 LMH), and higher than most
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hydrogel draw agents when the feed solution was DI water. For SA-GO aerogel, the reverse
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osmosis can be completely avoided and a facile recovery process can be handled owing to its
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monolith 3D framework structure. In a continuous cycle test (100 times), its water fluxes were
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basically kept high and steady (5-6.5 LMH). In the practical application of seawater
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desalination, the water fluxes of dry and wet SA-GO-1 aerogel were as high as 7.49±0.61 and
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3.18±0.39 LMH, respectively. Meanwhile, only 1kPa mechanical pressure (far less than the
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compression of an adult palms) can rapidly and cost-effectively realize the SA-GO aerogel.
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Therefore, SA-GO aerogel as FO draw agent can break through the bottleneck of reverse
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osmosis and complicated regeneration to realize production water with lower cost and higher
341
efficiency from saline water or wastewater. If applied in FO hydration bags, the aerogels
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would draw purity water from wastewater through a compression of an adult palms in many
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times, which can effectively simplify operation conditions and obviously increase the scope
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application of FO hydration bags.
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ACKNOWLEDGEMENTS
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Financial support of Natural Science Foundation of China (No. 51278079) is highly
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appreciated. 18 Environment ACS Paragon Plus
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ACS Applied Materials & Interfaces
ASSOCIATED CONTENT Supporting Information This supporting information is available free of charge via the Internet at http://pubs.acs.org.
The FT-IR spectrum of GO. The XRD spectra of GO and SA-GO aerogels. The compressibility of the dry aerogels. Compression tests of SA-GO aerogels. Schematic illustration of equipment for the compressive test. The Lab-scale FO-aerogel recovery process. Water absorption test of aerogel draw agents in FO process. The measurement of the antibacterial property of SA-GO aerogels by the bacteriostasis rate. The compression/release process of the SA-GO aerogel.
REFERENCE (1)
Klaysom, C.; Cath, T. Y.; Depuydt, T.; Vankelecom, I. F. J. Forward and Pressure Retarded Osmosis:
Potential Solutions for Global Challenges in Energy and Water Supply. Chem. Soc. Rev. 2013, 42, 6959. (2)
Shannon, M. A.; Bohn, P. W.; Elimelech, M.; Georgiadis, J. G.; Mariñas, B. J.; Mayes, A. M. Science
and Technology for Water Purification in the Coming Decades. Nature. 2008, 452, 301-310. (3)
Judd, S. J.; Hillis, P. Optimisation of Combined Coagulation and Microfiltration for Water Treatment.
Water Res. 2001, 35, 2895-2904. (4)
Gao, W.; Liang, H.; Ma, J.; Han, M.; Chen, Z.; Han, Z.; Li, G. Membrane Fouling Control in
Ultrafiltration Technology for Drinking Water Production: A Review. Desalination. 2011, 272, 1-8. (5)
Van der Bruggen, B.; Mänttäri, M.; Nyström, M. Drawbacks of Applying Nanofiltration and How to
Avoid them: A Review. Sep. Purif. Technol. 2008, 63, 251-263. (6)
Greenlee, L. F.; Lawler, D. F.; Freeman, B. D.; Marrot, B.; Moulin, P. Reverse Osmosis Desalination:
Water Sources, Technology, and Today's Challenges. Water Res. 2009, 43, 2317-2348. (7)
Cath, T. Y.; Childress, A. E.; Elimelech, M. Forward Osmosis: Principles, Applications, and Recent
Developments. J. Membrane Sci. 2006, 281, 70-87. (8)
Zhang, Y.; Pinoy, L.; Meesschaert, B.; Van der Bruggen, B. A Natural Driven Membrane Process for
Brackish and Wastewater Treatment: Photovoltaic Powered ED and FO Hybrid System. Environ. Sci. Technol. 2013, 47, 10548-10555. (9)
Kravath, R. E.; Davis, J. A. Desalination of Sea Water by Direct Osmosis. Desalination. 1975, 16, 151-
19 Environment ACS Paragon Plus
ACS Applied Materials & Interfaces
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
155. (10)
Yen, S. K.; Mehnas Haja N., F.; Su, M.; Wang, K. Y.; Chung, T. Study of Draw Solutes Using 2-
Methylimidazole-Based Compounds in Forward Osmosis. J. Membrane. Sci. 2010, 364, 242-252. (11)
Ling, M. M.; Wang, K. Y.; Chung, T. Highly Water-Soluble Magnetic Nanoparticles as Novel Draw
Solutes in Forward Osmosis for Water Reuse. Ind. Eng. Chem. Res. 2010, 49, 5869-5876. (12)
Guo, C. X.; Zhao, D.; Zhao, Q.; Wang, P.; Lu, X. Na+-Functionalized Carbon Quantum Dots: A New
Draw Solute in Forward Osmosis for Seawater Desalination. Chem. Commun. 2014, 50, 7318. (13)
Ge, Q.; Su, J.; Amy, G. L.; Chung, T. Exploration of Polyelectrolytes as Draw Solutes in Forward
Osmosis Processes. Water Res. 2012, 46, 1318-1326. (14)
Razmjou, A.; Simon, G. P.; Wang, H. Effect of Particle Size On the Performance of Forward Osmosis
Desalination by Stimuli-Responsive Polymer Hydrogels as a Draw Agent. Chem. Eng. J. 2013, 215-216, 913920. (15)
Razmjou, A.; Liu, Q.; Simon, G. P.; Wang, H. Bifunctional Polymer Hydrogel Layers as Forward
Osmosis Draw Agents for Continuous Production of Fresh Water Using Solar Energy. Environ. Sci. Technol. 2013, 47, 13160-13166. (16)
Zhang, H.; Li, J.; Cui, H.; Li, H.; Yang, F. Forward Osmosis Using Electric-Responsive Polymer
Hydrogels as Draw Agents: Influence of Freezing–Thawing Cycles, Voltage, Feed Solutions On Process Performance. Chem. Eng. J. 2015, 259, 814-819. (17)
Wang, H.; Wei, J.; Simon, G. P. Response to Osmotic Pressure versus Swelling Pressure: Comment on
“Bifunctional Polymer Hydrogel Layers as Forward Osmosis Draw Agents for Continuous Production of Fresh Water Using Solar Energy”. Environ. Sci. Technol. 2014, 48, 4214-4215. (18)
Kettunen, M.; Silvennoinen, R. J.; Houbenov, N.; Nykänen, A.; Ruokolainen, J.; Sainio, J.; Pore, V.;
Kemell, M.; Ankerfors, M.; Lindström, T.; Ritala, M.; Ras, R. H. A.; Ikkala, O. Photoswitchable Superabsorbency Based On Nanocellulose Aerogels. Adv. Funct. Mater. 2011, 21, 510-517. (19)
Sui, Z.; Cui, Y.; Zhu, J.; Han, B. Preparation of Three-Dimensional Graphene Oxide-Polyethylenimine
Porous Materials as Dye and Gas Adsorbents. ACS Appl. Mater. Inter. 2013, 5, 9172-9179. (20)
Hasegawa, G.; Shimizu, T.; Kanamori, K.; Maeno, A.; Kaji, H.; Nakanishi, K. Highly Flexible Hybrid
Polymer Aerogels and Xerogels Based on Resorcinol-Formaldehyde with Enhanced Elastic Stiffness and Recoverability: Insights into the Origin of their Mechanical Properties. Chem. Mater. 2017, 29, 2122-2134. (21)
Peng, L.; Zheng, Y.; Li, J.; Jin, Y.; Gao, C. Monolithic Neat Graphene Oxide Aerogel for Efficient
Catalysis of S -> O Acetyl Migration. ACS Catal. 2015, 5, 3387-3392.
20 Environment ACS Paragon Plus
Page 20 of 23
Page 21 of 23
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
ACS Applied Materials & Interfaces
(22)
Alhwaige, A. A.; Herbert, M. M.; Alhassan, S. M.; Ishida, H.; Qutubuddin, S.; Schiraldi, D. A.
Laponite/Multigraphene Hybrid-Reinforced Poly(Vinyl Alcohol) Aerogels. Polymer. 2016, 91, 180-186. (23)
Chabot, V.; Higgins, D.; Yu, A.; Xiao, X.; Chen, Z.; Zhang, J. A Review of Graphene and Graphene
Oxide Sponge: Material Synthesis and Applications to Energy and the Environment. Energ. Environ. Sci. 2014, 7, 1564 - 1596. (24)
Shi, K.; Yang, X.; Cranston, E. D.; Zhitomirsky, I. Efficient Lightweight Supercapacitor with
Compression Stability. Adv. Funct. Mater. 2016, 26, 6437-6445. (25)
Long, H.; Harley-Trochimczyk, A.; Pham, T.; Tang, Z.; Shi, T.; Zettl, A.; Carraro, C.; Worsley, M. A.;
Maboudian, R. High Surface Area MoS2/Graphene Hybrid Aerogel for Ultrasensitive NO2 Detection. Adv. Funct. Mater. 2016, 26, 5158-5165. (26)
Ma, C.; Du, B.; Wang, E. Self-Crosslink Method for a Straightforward Synthesis of Poly(Vinyl
Alcohol)-Based Aerogel Assisted by Carbon Nanotube. Adv. Funct. Mater. 2017, 27, 1604423. (27)
Hu, S.; Han, T.; Lin, C.; Xiang, W.; Zhao, Y.; Gao, P.; Du, F.; Li, X.; Sun, Y. Enhanced
Electrocatalysis via 3D Graphene Aerogel Engineered with a Silver Nanowire Network for Ultrahigh-Rate ZincAir Batteries. Adv. Funct. Mater. 2017, 27, 1700041. (28)
Chu, G.; Qu, D.; Zussman, E.; Xu, Y. Ice-Assisted Assembly of Liquid Crystalline Cellulose
Nanocrystals for Preparing Anisotropic Aerogels with Ordered Structures. Chem. Mater. 2017, 29, 3980-3988. (29)
Sun, H.; Xu, Z.; Gao, C. Multifunctional, Ultra-Flyweight, Synergistically Assembled Carbon Aerogels.
Adv. Mater. 2013, 25, 2554-2560. (30)
Wang, H.; Wei, J.; Simon, G. P. Response to Osmotic Pressure versus Swelling Pressure: Comment on
“Bifunctional Polymer Hydrogel Layers as Forward Osmosis Draw Agents for Continuous Production of Fresh Water Using Solar Energy”. Environ. Sci. Technol. 2014, 48, 4214-4215. (31)
Razmjou, A.; Liu, Q.; Simon, G. P.; Wang, H. Bifunctional Polymer Hydrogel Layers as Forward
Osmosis Draw Agents for Continuous Production of Fresh Water Using Solar Energy. Environ. Sci. Technol. 2013, 47, 13160-13166. (32)
Marcano, D. C.; Kosynkin, D. V.; Berlin, J. M.; Sinitskii, A.; Sun, Z.; Slesarev, A.; Alemany, L. B.; Lu,
W.; Tour, J. M. Improved Synthesis of Graphene Oxide. ACS Nano. 2010, 4, 4806-4814. (33)
Hu, H.; Zhao, Z.; Wan, W.; Gogotsi, Y.; Qiu, J. Ultralight and Highly Compressible Graphene Aerogels.
Adv. Mater. 2013, 25, 2219-2223. (34)
Titelman, G. I.; Gelman, V.; Bron, S.; Khalfin, R. L.; Cohen, Y.; Bianco-Peled, H. Characteristics and
Microstructure of Aqueous Colloidal Dispersions of Graphite Oxide. Carbon. 2005, 43, 641-649.
21 Environment ACS Paragon Plus
ACS Applied Materials & Interfaces
1 2 3 4 5 6 7 8 9 10 11 12 13 14 15 16 17 18 19 20 21 22 23 24 25 26 27 28 29 30 31 32 33 34 35 36 37 38 39 40 41 42 43 44 45 46 47 48 49 50 51 52 53 54 55 56 57 58 59 60
(35)
Bai, H.; Li, C.; Wang, X.; Shi, G. On the Gelation of Graphene Oxide. J Phys Chem C. 2011, 115,
5545-5551. (36)
Li, L.; Fang, Y.; Vreeker, R.; Appelqvist, I. Reexamining the Egg-Box Model in Calcium-Alginate Gels
with X-ray Diffraction. Biomacromolecules. 2007, 8, 464-468. (37)
Kanamori, K.; Aizawa, M.; Nakanishi, K.; Hanada, T. New Transparent Methylsilsesquioxane Aerogels
and Xerogels with Improved Mechanical Properties. Adv. Mater. 2007, 19, 1589-1593. (38)
Sui, Z.; Meng, Q.; Zhang, X.; Ma, R.; Cao, B. Green Synthesis of Carbon Nanotube-Graphene Hybrid
Aerogels and their Use as Versatile Agents for Water Purification. J Mater Chem A. 2012, 22, 8767-8771. (39)
Song, P.; Xu, Z.; Wu, Y.; Cheng Q.; Guo, Q.; Wang, H. Super-tough artificial nacre based on graphene
oxide via synergistic interface interactions of p-p stacking and hydrogen bonding . Carbon. 2017, 111, 807-812. (40)
Ding, W.; Zhou, J.; Zeng, Y.; Wang, Y.; Shi, B. Preparation of oxidized sodium alginate with different
molecularweights and its application for crosslinking collagen fiber. Carbohyd. Polym. 2017, 157, 1650–1656. (41)
Li, D.; Zhang, X.; Yao, J.; Simon, G. P.; Wang, H. Stimuli-Responsive Polymer Hydrogels as a New
Class of Draw Agent for Forward Osmosis Desalination. Chem. Commun. 2011, 47, 1710. (42)
Ge, Q.; Ling, M.; Chung, T. Draw Solutions for Forward Osmosis Processes: Developments,
Challenges, and Prospects for the Future. J. Membrane Sci. 2013, 442, 225-237. (43)
Kim, E.; Liu, Y.; Gamal El-Din, M. The Effects of Pretreatment On Nanofiltration and Reverse
Osmosis Membrane Filtration for Desalination of Oil Sands Process-Affected Water. Sep. Purif. Technol. 2011, 81, 418-428. (44)
Li, D.; Zhang, X.; Yao, J.; Simon, G. P.; Wang, H. Stimuli-Responsive Polymer Hydrogels as a New
Class of Draw Agent for Forward Osmosis Desalination. Chem. Commun. 2011, 47, 1710. (45)
Luo, H.; Wang, Q.; Zhang, T. C.; Tao, T.; Zhou, A.; Chen, L.; Bie, X. A Review On the Recovery
Methods of Draw Solutes in Forward Osmosis. Journal of Water Process Engineering. 2014, 4, 212-223. (46)
Anonymus. NASA Uses HTI’S FO Technology in Space. Membrane Technology. 2011, 2011, 2.
(47)
McCutcheon, J. R.; McGinnis, R. L.; Elimelech, M. A Novel Ammonia—Carbon Dioxide Forward
(Direct) Osmosis Desalination Process. Desalination. 2005, 174, 1 - 11. (48)
Ge, Q.; Ling, M.; Chung, T. Draw Solutions for Forward Osmosis Processes: Developments,
Challenges, and Prospects for the Future. J. Membrane. Sci. 2013, 442, 225-237.
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