Subscriber access provided by RMIT University Library

Critical Review

Environmental Applications of Interfacial Materials with Special Wettability Zhangxin Wang, Menachem Elimelech, and Shihong Lin Environ. Sci. Technol., Just Accepted Manuscript • DOI: 10.1021/acs.est.5b04351 • Publication Date (Web): 01 Feb 2016 Downloaded from http://pubs.acs.org on February 4, 2016

Just Accepted “Just Accepted” manuscripts have been peer-reviewed and accepted for publication. They are posted online prior to technical editing, formatting for publication and author proofing. The American Chemical Society provides “Just Accepted” as a free service to the research community to expedite the dissemination of scientific material as soon as possible after acceptance. “Just Accepted” manuscripts appear in full in PDF format accompanied by an HTML abstract. “Just Accepted” manuscripts have been fully peer reviewed, but should not be considered the official version of record. They are accessible to all readers and citable by the Digital Object Identifier (DOI®). “Just Accepted” is an optional service offered to authors. Therefore, the “Just Accepted” Web site may not include all articles that will be published in the journal. After a manuscript is technically edited and formatted, it will be removed from the “Just Accepted” Web site and published as an ASAP article. Note that technical editing may introduce minor changes to the manuscript text and/or graphics which could affect content, and all legal disclaimers and ethical guidelines that apply to the journal pertain. ACS cannot be held responsible for errors or consequences arising from the use of information contained in these “Just Accepted” manuscripts.

Environmental Science & Technology is published by the American Chemical Society. 1155 Sixteenth Street N.W., Washington, DC 20036 Published by American Chemical Society. Copyright © American Chemical Society. However, no copyright claim is made to original U.S. Government works, or works produced by employees of any Commonwealth realm Crown government in the course of their duties.

Page 1 of 44

Environmental Science & Technology

Environmental Applications of Interfacial Materials with Special Wettability Critical Review Environmental Science & Technology

Submitted: December 24th, 2015

Zhangxin Wanga, Menachem Elimelechb, and Shihong Lina,c* a

Department of Civil and Environmental Engineering Vanderbilt University, Nashville, Tennessee 37235-1831 b

Department of Chemical and Environmental Engineering Yale University, New Haven, Connecticut 06520-8286 c

Department of Chemical and Bimolecular Engineering Vanderbilt University, Nashville, Tennessee 37235-1831

ACS Paragon Plus Environment

Environmental Science & Technology

1 2 3 4 5 6 7 8 9 10 11 12

ABSTRACT Interfacial materials with special wettability have become a burgeoning research area in materials science in the past decade. The unique surface properties of materials and interfaces generated by biomimetic approaches can be leveraged to develop effective solutions to challenging environmental problems. This critical review presents the concept, mechanisms, and fabrication techniques of interfacial materials with special wettability, and assesses the environmental applications of these materials for oil-water separation, membrane-based water purification and desalination, biofouling control, high performance vapor condensation, and atmospheric water collection. We also highlight the most promising properties of interfacial materials with special wettability that enable innovative environmental applications and discuss the practical challenges for large-scale implementation of these novel materials.

ACS Paragon Plus Environment

Page 2 of 44

Page 3 of 44

Environmental Science & Technology

13

INTRODUCTION

14 15 16 17 18 19 20 21

Recent advancements in elucidating the mechanisms of special wetting properties observed in biological surfaces have inspired the development of artificial materials with various types of special wettability1-9. This biomimetic approach emphasizes the indispensable role of appropriate surface morphology in imparting desired wetting properties that cannot be achieved by tailoring the material chemistry alone10-17. Based on this approach, a large number of techniques have been developed to fabricate interfacial materials with special wettability by either bottom-up synthesis or modification of existing substrates to acquire the requisite surface chemistry and morphology5,18-20.

22 23 24 25 26 27 28 29 30

A wide range of applications enabled by interfacial materials with special wettability have been proved conceptually or realized in practice21. These applications include selfcleaning textile22-25, oil-water separation26, anti-icing and anti-fogging glass6,27-30, atmospheric water collection31,32, chemical shielding33, corrosion control34-43, and biological adhesion mitigation3,44-50 Beyond these applications, which are of tangible daily-life benefits, novel materials with special wettability have also advanced scientific research and technological developments. For example, these materials have led to smart microfluidics with excellent friction control51-56, template driven patterning of nanoparticles57-64, and precise liquid reprography65,66.

31 32 33 34 35 36

Interfacial phenomena play a critical role in many environmental processes, including membrane-based separations67-75, adsorption76-81, biological fouling44,82-87, corrosion88-91, interfacial phase transition92-95, and catalytic surface reaction96-98. As wettability is one of the most important surface properties, the ability to engineer surface wetting may open up vast opportunities for innovating and enhancing environmental processes that are controlled or heavily affected by interfacial phenomena.

37 38 39 40 41 42 43 44

This review article provides a critical assessment of environmental applications of interfacial materials with special wetting properties. We first introduce the concept of special wettability, its enabling mechanisms, and fabrication techniques of materials with different types of special wettability. We then review various environmental applications enabled by materials with special wetting properties by examining their working mechanism and effectiveness. Finally, we discuss the practical challenges that must be addressed for these materials to realize their full application potential in environmental systems.

45 46

SURFACES WITH SPECIAL WETTABILITY

47 48 49

Surface Wetting Properties. The wettability of a solid surface is a macroscopic representation of the interaction between the liquid and the substrate solid material. The most common way to quantify surface wettability is by measuring the contact angle (CA)

ACS Paragon Plus Environment

Environmental Science & Technology

50 51

of a sessile liquid drop on a solid surface in air (Figure 1A). The alternative approach of measuring the CA of a captive bubble (Figure 1B) is also often used.

52 53 54 55 56 57 58 59 60 61 62 63

Figure 1. (A) Definition of contact angle (CA), , based on a sessile liquid drop on a solid surface. (B) Definition of CA based on a captive bubble. (C) Advancing CA,  (  ): the maximum CA of a sessile drop before its boundary expands upon increase of drop volume. (D) Receding CA,  (  ): the minimum CA of sessile drop before its boundary shrinks upon reduction of drop volume. (E) Sliding angle,  : the minimum tilting angle at which the liquid drop starts to slide along the surface. The advancing and receding CA ( and  ) can also be defined in this setting as the frontier CA and the tail CA, respectively. (F) Super-repellent surface as characterized by ultrahigh CA and ultralow  . (G) A superlyophobic but sticky surface as characterized by both very high CA and  . In extreme cases, a liquid drop can stick to a vertical or even a reversed horizontal surface of this kind. (E) Lyophilic but non-sticky surface as characterized by very low CA and  ; the liquid does not bead up or stick to the surface.

64 65 66 67 68 69 70 71 72 73

A surface is typically considered hydrophobic if the water CA is higher than 90°, or hydrophilic if the water CA is lower than 90°. The convention in the materials science community defines a superhydrophobic surface as a surface not only with a very high water CA (>150°), but also with very low CA hysteresis or sliding angle (to be defined later), usually less than 5° or 10°19,99,100. On the other hand, the definition of superhydrophilic surface is controversial. While some suggests a maximum water CA of 5° as the upper limit48,101, others confine the definition of superhydrophility to only a rough or porous surface99. Note that the classification of surface wettability also applies to oil and other low surface tension liquids, in which the “hydro” in the wettability descriptor is replaced with “oleo” (meaning oil in Latin).

74 75

CA alone, however, does not fully capture the wetting behavior of a surface. The maximum and minimum CA of a liquid droplet with a given solid-liquid boundary are

ACS Paragon Plus Environment

Page 4 of 44

Page 5 of 44

Environmental Science & Technology

76 77 78 79 80 81 82 83

defined as the advancing CA,  (Figure 1C), and the receding CA,  (Figure 1D), respectively102-104. CA hysteresis (CAH) is usually defined as the difference between  and  (i.e.  −  )105,106. As a result of pinning, CAH only occurs on surfaces with either morphological or chemical heterogeneities107,108. While CA quantifies the affinity between the liquid and the solid surface, CAH quantifies the mobility of the liquid on the solid surface. An alternative measure of the mobility of a liquid drop on a surface is the sliding angle,  , defined as the tilting angle of a flat solid surface at which the liquid drop starts to slide109 (Figure 1E).

84 85 86 87 88 89 90

As discussed earlier, a surface is typically considered superhydrophobic or superoleophobic (i.e. super-repellent) if the CA is high and CAH or  is low (Figure 1F). However, systems also exist where these two requirements are not met simultaneously. For example, a liquid drop can have both high CA and CAH so that it beads up on a vertical surface or even on a reverse horizontal surface without sliding or falling off110112 (Figure 1G). On the other hand, a system can have both low CA and CA-hysteresis, as exemplified by a surface that is highly slippery to liquids with very low CA6 (Figure 1H).

91 92 93 94 95 96 97 98 99

Special Wettability. Special wettability typically refers to surface wetting properties that are not commonly encountered in daily life. Some of the most investigated surfaces of special wettability include those that are extremely repellent to water (superhydrophobic)100, to oil (superoleophobic) 15,20,113, or simultaneously repellent to both water and oil (omniphobic) 6,11. There are also surfaces that are in-air hydrophilic but oleophobic (i.e. wetted by water but not oil in air)20; such surfaces are more challenging to develop because liquids of a lower surface tension, such as oil, usually wet a surface more readily than water which has a very high surface tension.

100 101 102 103 104

In addition to surfaces of homogeneous wettability, there exist surfaces of patterned wettability that are partially hydrophobic and partially hydrophilic114-117. Smart surfaces that can switch wettability in response to a variety of environmental stimuli have also been developed12,20,118,119. A schematic diagram illustrating the concepts and relations between different types of surface wettability is given in Figure 2A.

ACS Paragon Plus Environment

Environmental Science & Technology

105 106 107 108 109 110 111 112 113 114 115 116 117 118 119 120 121

Figure 2. (A) The relations between different types of most investigated surfaces with special wettability. A surface is considered specially wettable if it has wetting properties that are not usually observed in daily life materials, which include not only those that are super wetting or non-wetting but also those with heterogeneous and stimuli-responsive switchable wetting properties. We note that oleophilicity is not explicitly listed here, as most materials are oleophilic due to the low surface tension of oil. (B) Lotus leaf as an example of superhydrophobic surface120. (C) Fresh rose petal as an example of superhydrophobic but strongly adhesive surface111. (D) Rice leaf as an example of superhydrophobic surface with anisotropic adhesion121. (E) Sharkskin as an example of underwater superoleophobic surface16. (F) The overwing of a desert beetle Stenocara as an example of surfaces with patchy wettability (i.e., heterogeneously wettable)122. (G) Salvinia molesta as another example of heterogeneously wettable surface. The tip of the microstructure is hydrophilic while the rest of the structure is hydrophobic123. In all these examples (from Figure 2B to 2G), multi-scale surface architectures, as highlighted by scanning electron microscopy images shown below the photographic images, are critical to the special wetting property. Figures 2B to 2G are reproduced from Ref. 120, 111, 121, 16, 122, and 123, with permissions.

ACS Paragon Plus Environment

Page 6 of 44

Page 7 of 44

Environmental Science & Technology

122 123 124 125 126 127 128 129

Many of the surfaces with special wettability have their biological prototypes in nature16,17. For instance, superhydrophobic surfaces that are non-adhesive, adhesive, and directionally adhesive as can be found on a lotus leaf120,124, a rose petal110,111, and a rice leaf121,125, respectively (Figures 2B, C, D). On the other hand, underwater superoleophicity has been discovered on sharkskin126,127 (Figure 2E) or fish scales128,129, imparting the desired properties for hydrodynamic drag reduction and bio-adhesion resistance. Common to all these surfaces is the presence of a multi-scale surface texture that is the key for creating artificial surfaces with the desired special wettability13,15,16.

130 131 132 133 134 135 136

Natural surfaces can also have spatially heterogeneous surface wetting properties. For example, the hardened forewings of Namib desert beetles have microscopic bumps composed of hydrophilic tips and hydrophobic peripheries122 (Figure 2F). This unique structure is responsible for the ability of desert beetles to harvest water effectively from the atmosphere. Another example is the surface of the floating fern Salvinia molesta, which has hydrophobic microtextures with hydrophilic tips and is thus capable of retaining attached air bubbles underwater123,130(Figure 2G).

137 138

MECHANISMS AND FABRICATION TECHNIQUES

139 140 141

On a perfectly smooth (i.e., non-textured) and chemically homogeneous solid surface, the contact angle, , relates to the surface tensions between solid and liquid,  , between solid and gas,  , and between liquid and air,  , by Young’s equation131:  −  −   = 0

(1)

142 143 144

The Young’s equation can be derived from a force balance at the air-liquid-solid triple phase boundary line or by minimizing the total interfacial Gibbs free energy of the system. A CA measured on a non-textured surface is defined as the intrinsic CA ( ).

145 146 147 148 149 150 151 152 153

To date, the highest intrinsic water CA of all materials is about 130°, measured from a closely packed monolayer with –CF3 surface functional groups132,133. The Young’s relation cannot explain a plethora of superhydrophobic surfaces with CA significantly higher than 150° or oleophobic surfaces that repel liquids of very low surface tensions. The missing piece is surface texture, which has been identified as an indispensible characteristic for attaining special wetting properties in many biological and engineered surfaces. In this section, we discuss the underlying principles behind several important types of special wettability and briefly summarize the techniques used in fabricating materials with special wettability.

154 155 156

Wenzel vs. Cassie Baxter State. For a sessile liquid drop contacting a rough surface in air, there are two possible states: the Wenzel state and the Cassie-Baxter state.

ACS Paragon Plus Environment

Environmental Science & Technology

157 158 159

In the Wenzel state, the liquid fully wets the textured surface so that the liquid-solid contact area is maximized134,135. The apparent contact angle for Wenzel state,  , can be related to the intrinsic contact angle,  136: (2)  =  

160 161 162 163 164 165 166

Here,  is the surface roughness defined as ratio between the total surface area and the projected surface area, which is always greater than unity. According to eq. 2, surface roughness will always amplify the intrinsic wettability of a surface (Figure 3A), whether it is hydrophilic (   0) or hydrophobic (   0), provided the system is in a Wenzel state137. For example, an ultrahigh CA can result from a Wenzel state as long as  >90° and the surface roughness is sufficiently high. However, the liquid drops in a Wenzel state system are highly immobile due to pinning, leading to significant CAH5.

167 168 169 170 171 172 173 174 175 176 177 178

Figure 3. (A) Wenzel state: the rough surface is fully wetted by the liquid droplet; the surface roughness amplifies the intrinsic wetting properties. (B) Cassie-Baxter state: the liquid droplet is supported by a composite surface of the solid substrate and trapped air; surface roughness increases the CA whether the intrinsic CA is lower or higher than 90°. (C) A classic reentrant structure showing a local CA less than 90°11,138 (adapted from Ref.11). (D) Another typical reentrant structure (spherical particles or cylindrical fibers) with a local CA less than 90°. The structures in (C) and (D) suggests from that a Cassie-Baxter state can exist even with an intrinsic CA lower than 90°, which is only possible with reentrant surface texture. (E) Free energy of the system as a function of the position of the liquid-air interface. A system in the Cassie-Baxter state C-B1 has to overcome an energy barrier (C-B 2) to transition to Wenzel state with a lower system free energy.

179 180 181 182

Another possible wetting state is the Cassie-Baxter state in which the sessile drop is supported by a composite surface of air and the substrate solid (Figure 3B)102. The original Cassie-Baxter theory was developed for a more general scenario of a chemically heterogeneous surface. For a physically rough surface, air can be trapped in the “pockets”

ACS Paragon Plus Environment

Page 8 of 44

Page 9 of 44

Environmental Science & Technology

183 184 185 186

between the liquid and the solid substrate, in which case the Cassie-Baxter theory can apply, with air being the ultra-low surface tension “chemical heterogeneity”. 102,108. For a system in the Cassise-Baxter state, the apparent CA,  , can relate to the intrinsic CA,  , by 107 (3)  =   −  

187 188 189 190 191

where  and   are the area fractions of the solid-liquid and liquid-air (vapor) interface, respectively, satisfying the relation  +   = 1. Because air, being part of the composite surface supporting the liquid droplet, is the most hydrophobic and oleophobic material, with an intrinsic CA of 180° for any liquid,  is always higher than  .

192 193 194 195 196 197 198

In fact, it is possible that  is significantly higher than 90° even if  is lower than 90°. In other words, materials comprising hydrophilic or oleophilic smooth surfaces may lead to hydrophobic or oleophobic rough surfaces in Cassie-Baxter state, but not in Wenzel state10. Another important characteristic of a system in the Cassie-Baxter state is the weak CAH due to very low degree of pinning14,17 . Therefore, the Cassie-Baxter state is not only essential for achieving oleophobicity, but also critical for developing superrepellent surfaces with very low surface adhesion.

199 200 201 202 203 204 205

For low surface tension liquids (e.g. oil, alcohol), thermodynamic equilibrium analysis suggests that the Cassie-Baxter state is not a thermodynamic stable state, i.e., the free energy of a Cassie-Baxter system is always higher than that of a Wenzel system139,140. Therefore, unlike superhydrophobicity which can be achieved simply by introducing a high level of roughness on a low surface tension solid surface, oil repellence (oleophobicity) is more challenging to attain due to the absence of the thermodynamically stable Cassie-Baxter state for low surface tension liquids10,139,141,142.

206 207 208 209 210 211 212 213

The key to impart oleophobicity lies in the creation of a re-entrant surface texture to enable a Cassie-Baxter state that is thermodynamically metastable10,11,140,143. A re-entrant texture is a concave topography in which the solid fraction of a cross section of the composite surface decreases as the cross section approaches the “bottom surface”, such as the inverted trapezoid in Figure 3C138. Another more practical way to create re-entrant geometry is to use cylindrical or spherical textures, such as electrospun fibrous networks or deposited nanoparticle layers20. The bottom-half of such structures provides the reentrant geometry required for the existence of the metastable Cassie-Baxter state.

214 215 216 217 218 219 220

From a force balance perspective, a re-entrant structure is required to achieve a stable liquid-air-solid triple phase boundary when the local CA is lower than 90° (Figure 3C and 3D). From an energetic perspective, in order to transition from a metastable CassieBaxter state (C-B 1 in Figure 3E) to a thermodynamically stable Wenzel state, the system has to overcome an energy barrier corresponding to another Cassie-Baxter state (C-B 2, Figure 3E) of a higher system free energy144. Therefore, the system is “trapped” in the Cassie-Baxter state of lower system free energy, even if that is not a thermodynamically

ACS Paragon Plus Environment

Environmental Science & Technology

221 222 223 224 225

stable state with a global free energy minimum. A thermodynamic metastable CassieBaxter state is only possible with a re-entrant texture, because only with such a texture will the intrusion of liquid into the pore space of the composite layer expand the area of the liquid-air contact, which is energetically unfavorable due to very high surface energy of a liquid-air interface.

226 227 228 229 230 231 232 233

Transition from Cassie-Baxter state to Wenzel state can occur upon increasing hydraulic pressure or shrinking of the liquid drop due to evaporation145, in which case the superlyophobicity breaks down. Therefore, the robustness of super-liquid-repellence, i.e. the resilience of the system against the Cassie-Baxter to Wenzel transition, is an important aspect when developing super-repellent surfaces138,146,147. Numerous studies have been conducted to elucidate the geometric factors dictating such robustness, leading to smart material morphological design based on careful consideration of the local interfacial energy landscape11,140,148.

234 235 236 237 238 239 240

Oleophobic/Hydrophilic Surfaces: In-Air vs. Underwater. Because water has a higher surface tension (72.8 mN/m at 20°C) than most other liquids, interfacial thermodynamics dictate that if a surface is hydrophilic, it should as well be oleophilic in air. Therefore, it is practically infeasible for a chemically homogeneous surface to simultaneously acquire both oleophobicity and hydrophilicity in air. However, recent advances in materials science have identified the methods to engineer surfaces with this unusual wetting property149,150.

241 242 243 244 245 246 247

The key to design a surface with both in-air oleophilicity and hydrophobicity is the creation of a chemically heterogeneous surface with intercalating hydrophilic and oleophobic moieties20. In the presence of oil, the liquid-solid interface is dominated by the oleophobic constituents, which prevent the oil from wicking the surface. In contact with water, however, the surface texture reconfigures to increase the interfacial contact between the hydrophilic functional groups and water to reduce the system enthalpy via hydrogen bonding, which results in surface hydrophilicity150-152.

248 249 250 251 252 253 254

On the other hand, surfaces that are in-air hydrophilic can be underwater oleophobic. Biological examples of this underwater oleophobicity include fish scale, clamshells, and shakskin16,127. These surfaces are typically in-air superhydrophilic and thus prefer to be strongly hydrated underwater. The energetically unfavorable dehydration process, which the system has to undergo before oil contacts the surface, prevents the oil from wetting the surface underwater and provides self-cleaning function to the natural surfaces with this wetting property128,153.

255 256 257 258

Switchable Surfaces. Smart surfaces have also been developed that can switch their wetting properties in response to changes in environmental conditions12. Typical stimuli triggering change of wettability include pH119,154, temperature155,156, ultra violet (UV) radiation157,158, electrical field159,160, and magnetic field161. Many of these stimuli-

ACS Paragon Plus Environment

Page 10 of 44

Page 11 of 44

Environmental Science & Technology

259 260 261

responsive surfaces switch between hydrophobic (underwater oleophiphilic) and hydrophilic (underwater oleophobic) states and are thus suitable for controllable oil-water separation.

262 263 264 265 266 267 268 269

The most common approach to stimulate the transition of wetting properties is by chemically transforming the surface functional groups. For example, varying the pH around the pKa of the functional groups in an ionizable polymer coating can alter the surface wettability by adjusting its surface charge119,154; an uncharged hydrophobic and underwater oleophilic surface can become hydrophilic and underwater oleophobic when it is charged. Other common environmental factors that can serve as stimuli for wettability transition include UV-radiation (photo-responsive) 156-158,162 and temperature (thermal responsive) 155,163.

270 271 272 273 274 275 276 277 278 279 280

A different approach to create surfaces with switchable wettability involves a phenomenon called electrowetting on dielectric164, which has impact only on polar liquids (e.g., water) but not on non-polar liquids (e.g., oil) 160. Upon the application of a strong electric field, an originally omniphobic Cassie-Baxter surface becomes wetted by water but not by oil, therefore enabling a smart surface that switches its water affinity but maintains oleophobicity. Another interesting approach for controlling the surface wetting through transition between the Cassie-Baxter and the Wenzel states is the application of a magnetic field to alter the surface morphology161. A surface composed of ferromagnetic micro-nails with low surface tension is omniphobic due to the presence of the reentrant structure. However, in the presence of a magnetic field, the deforming surface morphology loses its reentrancy and thus render the surface omniphilic.

281 282 283 284 285 286 287 288 289

Slippery Liquid Infused Porous Surface (SLIPS). A noteworthy category of very robust omniphobic and anti-adhesion surfaces is the slippery liquid-infused porous surface (SLIPS) method, inspired by the slippery surface of pitcher plants7. A SLIPS is constructed simply by infusing a porous solid substrate with a perfluorinated lubricant. This ultralow surface tension lubricant locked up in the porous substrate does not mix with and cannot be replaced by any tested liquids in contact with the surface6. A SLIPS works with a mechanism categorically different from a Cassie-Baxter surface. For most liquids, both the CA and CAH on SLIPS are very low. Therefore, a SLIPS is considered simultaneously “slippery but wetted”165.

290 291 292 293 294 295 296

Without resorting to air pockets for supporting the contacting liquids, a SLIPS can sustain robust omniphobicity under extreme pressure6. A SLIPS does not lose its high repellence due to the evaporation of liquid droplets (in air) or the dissolution of entrapped air (underwater). Furthermore, a SLIPS is also self-repairing due to the facile reconfiguration of a disturbed lubricant liquid film6,166. Because of these advantages, a SLIPS has been proposed for many applications such as fouling inhibition167-169, enhanced condensation170, anti-icing and anti-frosting surfaces29, and drag reduction18,171.

ACS Paragon Plus Environment

Environmental Science & Technology

Page 12 of 44

297 298 299 300 301 302

Fabrication Techniques. The techniques for fabricating interfacial materials with special wettability are heavily dependent on their enabling mechanisms. These materials can be standalone, such as electrospun fiber mats 10,172,173, or be acquired by modifying substrate surfaces of different materials with a wide range of techniques. The fabrication approaches can be either top-down, such as templating and photolithography, or bottomup, such as surface sol-gel and layer-by-layer deposition18.

303 304 305 306 307 308 309 310

The fabrication of surfaces with very high water CA is relatively straightforward, as it typically only requires a highly textured surface composed of materials with low surface free energy18,19,174. A multitude of such techniques have been developed and will not to be discussed here. Selected fabrication techniques of other “more interesting” surfaces with special wettability, such as those that are omniphobic, in-air and underwater oleophobic but hydrophilic, as well as smart surfaces with stimuli-responsive switchable wettability, are listed in Table 1. Readers interested in developing surfaces with special wettability should refer to the plentiful review articles in materials science5,18-20,175

311 Table 1. Selected Fabrication Techniques for Surfaces with Special Wettability Wettability

Omniphobic

Materials (Substrate/Coatings)

Fabrication Method

Cellulose/ Poly Glycidyl methacrylate (PGMA) and pentadecafluorooctanoyl chloride

Atom Transfer Radical Polymerization (ATRP)

Glass/ Poly methyl methacrylate (PMMA) and fluorine-end-capped polyurethane

Casting

Poly 3,4-ethylenedioxythiphene (PEDOT) film / poly perfluorodecyl acrylate (PFA)

Chemical Vapor Deposition (CVD)

Poly perfluoroalkyl ethyl methacrylate (PPFEMA) / polycarprolactone (PLA)

Electrospinning and CVD

Standalone mat of PMMA and polyhedral oligomeric silsesquioxane (POSS)

Electrospinning

Any surface/ Fluorodecyl POSS

Dip-coating

Alumnia/ 1H,1H,2H,2H-perfluorooctyltrichlorosilane

Dip-coating

Glass / silica nanoparticles (SiNPs) coated by perfluoropolyether (PFPE) derivative

Dip-coating

Silicon nanostructure/ heptadecafluoro-1,1,2,2- tetrahydrodecyl trichlorosilane CF2-(CF2)7(CH2)2SiCl3

Etching and molecular phase deposition

Silicon nanostructure/cellulose nanocrystal coated by fluorinated trichlorosilane

Plasma-Etching

Acrylic fabrics/perfluoroalkyl acrylate copolymer and methoxymethyl melamine resin

Plasma and pad-dry-cure method

Standalone mat of polydimethylsiloxane (PDMS) and polytetrafluoroethylene (PTFE)

Plasma discharge

Glass/ SiNPs coated by (Tridecafluoro-1,1,2,2,-tetrahydrooctyl) trichlorosilane n-C6F13(CH2)2SiCl3

LBL assembly

Glass or Printing paper/ SiNPs coated by fluorinated diblock copolymer

Polymerization and Sol-gel

Cotton fabric/ diureapropyltriethoxysilane [bis(aminopropyl)-terminated polydimethylsiloxane] and 1H,1H,2H,2H-perfluorooctyl-triethoxysilane (PFOTES)

Sol-gel

Poly ethylene terephthalate (PET)/colloidal silica, tetraethyl orthosilicate (TEOS), and heptadecafluoro-1,1,2,2-tetrahydrodecyl triethoxysilane

Sol-gel

Polypropylene (PP) / SiNPs coated by perfluoroalkyl methacrylic copolymer

Spin-coating

Quartz glass substrates/ Aligned carbon nanotubes (ACNT) coated with heptadecafluorodecyl trimethoxysilane

Pyrolysis

Metals/ perfluorocarboxylic acid in ethanol

Solution-immersion

Ref. 176

177 178 179 10 180 142 181

182 183 184

185

186 187

188

189

190

191

40,19

Cotton textiles/ SiNPs coated by 1H,1H,2H,2H-perfluorodecyl trichlorosilane

Solution-immersion

Nylon Cotton blended fabric/ fluorosilane

Solution-immersion

Silicon wafer/ PMMA and POSS

Spraying

ACS Paragon Plus Environment

2 22 193 194

Page 13 of 44

Environmental Science & Technology

In-Air Oleophobic Hydrophilic

Underwater Oleophobic Hydrophilic

Templated PDMS, or polyurethane (PU), or ultra-high-molecular-weight polyethylene (UHMWPE), or PTFE

Template

Gold plate/ Fluorinated 3,4- ethylenedioxypyrrole (EDOP) and 3,4propylenedioxypyrrole (ProDOP) monomers

Electrochemical Polymerization and Electrodeposition

Nanopyramidal gold film/ 1H,1H,2H,- 2H-perfluorodecanethiol

Electrodeposition

Silicon/ Perfluorinated polyethylene glycol oligomers (f-PEG)

Grafting

Various substrates/ SiO2 coated with poly diallydimethylammonium chloride (PDDA) and sodium flurooctanoate (PFO)

Spray casting

152

Glass slide / Polycrystalline anatase TiO2 thin film

Sol-gel and UV illumination

198

Spin-coating

149

Dip-coating or Spin-coating

151

Stainless steel mesh / polyacrylamide hydrogel

Photoinitiated polymerization

199

Stainless steel mesh / zeolite crystal

Dip-coating and crystallization

PVDF membrane / poly(3-(N-2-methacryloxyethyl-N,N-dimethyl) ammonatopropanesultone (PMAPS) zwitterionic polyelectrolyte brush

ATRP

201

Cellulose paper / nanofibrillated cellulose hydrogel

Dip-coating and cross-linking

202

Silicon wafers or glass slides / copolymer-fluorosurfactant complex

Spin-coating

150

Sapphire with standard multi-step (RCA) cleaning method (no coating applied)

RCA cleaning

203

Brass abraded by grit silicon carbide papers (no coating applied)

Abrasion

204

Silicon wafer or Polyester fabrics/ POSS and polyethyl methacrylate (PEMA)

Spin coating or Dip coating with water annealing

Glass/ Polystyrene (PS) and montmorillonite (MMT) modified with perfluoropolyether cationic ammonium salts (FOMMT) Stainless steel mesh or polyester fabric / fluorodecyl POSS and cross-linked poly(ethylene glycol) diacrylate (x-PEGDA)

Wettability Oleophobic (w/ PFO) Oleophilic (w/ SDS) Oleophobic (w/o magnetic field) Oleophilic (w/ magnetic field)

Stimuli Responsive

Materials (Substrate/Coating) Etched aluminum surfaces/ Poly diallydimethylammonium chloride (PDDA) and poly sodium 4-styrene sulfonate (PSS) Metal electrode/Ni nanowires with hemisphere cap coated with 1H,1H,2H,2Hperfluorodecanethiol

Superhydrophilic (Temp.40°C)

Silicone substrate/ poly(Nisopropylacrylamide) (PNIPAAm)

Hydrophilic/Oleophobic (Temp=10°C) Hydrophobic/Oleophilic (Temp=40°C)

Stainless steel mesh/ Poly(methyl methacrylate)-b-poly(Nisopropylacrylamide) (PMMA-b-PNIPAAm) block copolymer

195

196

197

27,28

200

205

LBL deposition and counterion exchange

206

Template-assisted eletrodeposition

161

Polymerization

155

Solution casting

163

Omniphobic (dark) Omniphilic (w/UV)

Silicon wafer/ TiO2 and SWNT coated with 1H,1H,2H,2H-perfluorodecyltrichlorosilane (FDTS)

Composite liquid phase deposition

157

Hydrophobic (dark) Superhydrophilic (w/UV)

Copper substrate/multiwall carbon nanotubes

Spray casting

156

Superhydrophobic (dark) Superhydrophilic (w/UV)

Sapphire substrate/ZnO thin film

CVD

162

Hydrophobic/oleophilic (dark) Hydrophilic/UW Oleophobic (w/UV)

Stainless steel mesh/ aligned ZnO nanorod

In-situ crystallization

158

Oleophobic (w/ low voltage) Oleophilic (w/ high voltage)

Nanonail covered substrate/ floropolymer

Photolithography and CVD

159

Omniphobic (w/o electric field) Hydrophilic (w/electric field)

Nylon membranes/ fluorodecyl POSS and crosslinked polydimethylsiloxane (x-PDMS)

Dip-coating

160

Hydrophilic/UW Oleophobic (low pH) Hydrophobic/UW Oleophilic (high pH)

Textile or polyurethane sponge/Silica Nanoparticles grafted with Poly(2-vinylpyridine-bdimethylsiloxane) block copolymer (P2VP-bPDMS)

Block-copolymer grafting

119

Hydrophilic/UW Oleophobic (High pH) Hydrophobic/UW Oleophilic (low pH)

Nanostructured copper foil/ mixture of long chain saturated fatty acid and alkane

Solution-immersion

154

312

ACS Paragon Plus Environment

Environmental Science & Technology

313 314 315 316

ENVIRONMENTAL APPLICATIONS

317 318 319 320 321 322 323 324 325 326 327 328 329 330 331 332 333 334 335

The elucidation of the mechanisms of special wettability has led to the creation of artificial materials with special wetting properties. These advanced materials have enabled or enhanced several environmentally relevant processes, including oil-water separation, membrane processes, vapor condensation, fog collection, and biofouling mitigation. In this section we review each of these environmental applications of interfacial materials with special wettability by first introducing their environmental relevance, assessing the state of the art, and finally discussing the challenges to overcome to realize large-scale practical applications. Oil-Water Separation, A natural application for materials with special wettability is the separation of oil from water by taking advantage of the differential affinities of oil and water towards these materials26. Removing oil from water is an indispensable process for effective water reuse in many areas including oil and gas production207, as well as petrochemical, pharmaceutical, metal processing, and the food industries208. Oil-water separation also plays a crucial role in oil spill cleanup, which is of significant environmental concern209. Conventional methods for removing oily components from water include physical skimming, centrifugation, oxidation, solvent extraction, flotation, and biological degradation207,210,211. Some of these processes suffer from problems such as high energy-consumption, limited effectiveness, and extensive use of chemicals.

336

ACS Paragon Plus Environment

Page 14 of 44

Page 15 of 44

Environmental Science & Technology

337 338 339 340 341 342

Figure 4. (A) A hydrophobic/oleophilic filter for separation of oil/water mixtures. (B) A hydrophobic/oleophilic sponge for adsorbing oil from oil-in-water emulsion. (C) and (D) A hydrophilic/oleophobic filter for separation of oil/water mixtures and oil-in-water emulsion, respectively. (E) A hydrophobic/oleophilic filter switches to a hydrophilic/oleophobic filter upon exposure to an environmental stimulus, which can be UV light, temperature, electric and magnetic field, and pH.

343 344 345 346 347 348 349 350 351 352 353 354 355

Wettability based separation is a highly effective, energy efficient process for removing oil from water26,212. In general, there are two major types of wettability based oil-water separation systems: selective filters and superhydrophobic absorbents23,137. A selective filter is a porous barrier that allows selective permeation of some components but rejects the others. Many of these selective barriers are fabricated by modifying metal or polymer meshes with characteristic pore sizes of tens or even hundreds of micrometers. These filters primarily operate primarily based on selective wettability rather than size exclusion2,158,199. On the other hand, microfiltration membranes with special wettability have also been developed for highly effective oil-water separation, especially for stabilized emulsions of micrometer or submicrometer sized oil droplets201,213-215. These wettability based selective filters can effectively separate both immiscible oil water mixtures as well as dispersed oil-in-water emulsions, usually with a separation efficiency (or rejection rate) above 99%160,199,202,216,217.

356 357 358 359 360 361 362 363 364 365

Many selective filters for oil-water separation are superhydrophobic, but oleophilic (Figure 4A) 2,23,216,218-222. Although such filters are particularly suitable for water-in-oil emulsions222, they have limited applications as they do not facilitate gravity driven separation for phase separated oil-water mixtures 151 and cannot separate oil-in-water emulsion. The more recent development of superhydrophilic-oleophobic materials137,151,152,199-202,215,223-225 leads to a better route for gravity-driven separation of oil-water mixtures or oil-in-water emulsions. Another noteworthy category of materials are those with stimuli-responsive wettability119,158,160,226,227. These smart materials with controllable wetting properties have been developed both in the form of both selective filters and preferential absorbents for on-demand oil water separation.

366 367 368 369 370 371 372

Superhydrophobic absorbents are highly porous, sponge-like materials that are superhydrophobic and oleophilic. They can absorb oil from water by up to tens of times of the adsorbent original weight228-233. An interesting idea for implementing superhydrophobic absorbents for cleaning up oil spills in ocean or surface water is to equip a boat surface with these porous materials as a mobile scavenger for oil232. Effective and economical regeneration of these absorbents, however, remains a significant challenge for their large-scale practical applications.

373 374 375 376

Water Purification and Desalination Membranes. The wettability of a membrane is one of the most critical material properties that dictate its performance. Some membrane processes are strongly dependent on surface wetting property, such as membrane distillation67 and membrane-based gas stripping234,235, in which the non-

ACS Paragon Plus Environment

Environmental Science & Technology

377 378 379 380 381 382

wetting condition is pivotal to the process viability. However, even for membrane processes based on other mechanisms such as size exclusion (e.g. nano- and ultrafiltration) and solution-diffusion (e.g. reverse osmosis, forward osmosis), wettability still plays an important role in membrane performance236-242. In this subsection, we will present several examples highlighting how special wettability can markedly enhance the performance of membrane processes.

383 384 385 386 387 388 389 390 391 392 393 394 395

Membrane distillation. Membrane distillation (MD) is an emerging thermal desalination process using a hydrophobic microporous membrane67. In an MD process, a hot saline feed stream is separated from the cold pure distillate stream by a hydrophobic, porous membrane. The trans-membrane difference of partial vapor pressure induced by the temperature difference drives vapor transport across the membrane, while the hydrophobic membrane rejects the direct passage of the liquid feed solution that contains salts and other contaminants. MD can utilize low temperature waste heat to desalinate highly saline brine solutions that cannot be treated by conventional reverse osmosis desalination, such as shale gas produced water243. In addition, MD also has the advantage of small system footprint and low capital cost244. It can also be utilized as a low-cost thermal separation process in hybrid-membrane processes for resource recovery from wastewater245,246, energy recovery from waste heat247, and draw solution regeneration for forward osmosis processes248-250.

396 397 398 399 400 401 402 403 404 405 406 407

In an MD process, the hydrophobic membrane serves as a medium for water vapor transfer and as a barrier for liquid transfer. Therefore, it is of vital importance to maintain the non-wetting condition of an MD membrane to prevent the feed stream from passing through the membrane in its liquid form. Typically, MD membranes are made of hydrophobic materials such as polytetrafluoroethylene (PTFE) prepared via meltingstretching technique, and polyvinylidene fluoride (PVDF) and polypropylene (PP) prepared via phase inversion67,251. However, their application in industrial-scale systems has been hindered by low water flux and low long-term wetting resistance. In particular, if the feed stream is enriched with surface-active agents (e.g. surfactants), these membranes will be wetted by the surface-active agents and fail as a barrier for liquid transfer, resulting in significantly compromised rejection of salt and other undesirable contaminants.

408 409 410 411 412 413 414 415 416

Approaches to mitigate wetting of MD membrane include the development of composite hydrophilic/hydrophobic membranes252, superhydrophobic membranes253-255, and omniphobic membranes256. To fabricate superhydrophobic MD membranes, a commercial hydrophobic PVDF membrane was modified by coating perfluorinated TiO2 nanoparticles on the membrane surface253. Compared to the pristine PVDF membrane, the modified composite membrane showed a significant higher water CA and drastically reduced CAH. Such a membrane also showed significantly improved anti-wetting performance compared to the pristine PVDF membrane in direct contact MD experiments in which added ethanol lowered the overall surface tension of the feed solution. A similar

ACS Paragon Plus Environment

Page 16 of 44

Page 17 of 44

Environmental Science & Technology

417 418 419 420 421

approach can be applied with electrospun nanofiber mats, which offer particularly high promise for MD membranes due to their ultra-high porosity. Superhydrophobic electrospun nanofiber mats produced from a blend of silica nanoparticles and PVDF exhibited higher water flux and long-term wetting resistance compared to commercial flat sheet PTFE and PVDF membranes255.

422 423 424 425 426 427 428 429 430 431 432 433 434 435 436

Recently, an omniphobic MD membrane was developed by perfluorinating a silica fibrous membrane decorated with nanoparticles256. The fabricated omniphobic membrane was found to be superior to a commercial PTFE membrane as it resisted wetting by low surface tension liquids including mineral oil, ethanol, and decane. The oleophobicity of the fabricated MD membrane stemmed from both the low surface tension and the multiscale (i.e. both the fiber and the nanoparticle scales) re-entrant structures of the membrane10. The versatile wetting resistance of the omniphobic membrane resulted in superior anti-wetting performance in an MD process. Specifically, it was shown that with the addition of surfactants to the feed solution, the salt rejection of an MD process was drastically crippled with a PTFE membrane, but unaffected with an omniphobic membrane. Imparting MD membrane with omniphobicity is a promising direction to enhance the robustness of operation and enable MD to be more versatile in treating a wider range of feed waters. However, successful application of omniphobic membranes in MD requires further work, including assessment of long-term operation and development of scalable fabrication methods.

437 438 439 440 441 442 443

Pressure and Osmosis Driven Membrane Processes. Membrane processes based on size exclusion and osmosis mechanisms can also benefit substantially from enhanced surface wetting properties257,258. For example, it has been well established that increasing the hydrophilicity of membranes can improve membrane performance by mitigating organic or biological fouling in ultrafiltration241,259, nanofiltration236,260, reverse osmosis238,261, and forward osmosis262-264.

444 445 446 447 448 449 450 451 452 453 454 455 456

The underlying antifouling mechanism of hydrophilic membranes is attributed to the hydration layer formed on a highly hydrophilic surface. Such hydrated layers create an energetic barrier that the organic or biological foulants have to overcome (i.e. to dehydrate the surface) before they can attach onto the membrane surface265. Typical organic or biological foulants are either hydrophobic or have hydrophobic moieties, and thus have a stronger tendency to bind with a hydrophobic surface due to the long-range hydrophobic interaction in water266,267. We note that the mechanism of superhydrophilic membrane for fouling mitigation shares similarity with that of superhydrophilicunderwater oleophobic filters for oil-water separation. Numerous studies have reported the preparation of superhydrophilic membranes by coating nanoparticles237,262,268 or grafting polymers 238,269-271 that are highly hydrophilic, showing that the modified membrane with improved wettability can lead to better performance with slower flux decline over time.

ACS Paragon Plus Environment

Environmental Science & Technology

457 458 459 460 461 462 463 464 465 466 467 468 469

Surfaces with special wettability can bring anti-fouling performance to the next level. Recent studies suggest that novel ultrafiltration membranes with in-air hydrophilicity and oleophobicity offer anti-fouling performance that is unmatched by membranes that are inair oleophilic217,272. The hydrophilic/oleophobic membranes were obtained by incorporating a functional polymer that contains both hydrophilic and oleophobic moieties into a PVDF membrane. Compared to PVDF membranes without any modifier or with poly ethylene glycol (PEG)—a common surface coating agent to impart hydrophilicity—the hydropholic/oleophobic PVDF membrane demonstrated superior resistance against fouling by proteins (bovine serum albumin), natural organic matter (humic acid), oil-water emulsion, as well as bacteria (Escherichia coli and Staphylococcu aureus). The enhanced anti-fouling performance was evidenced not only by the significantly slower flux decline, but also by the remarkably higher performance recovery upon membrane cleaning217.

470 471 472 473 474 475 476 477 478 479 480 481 482 483

Biofouling Control. Biological fouling (or biofouling), the accumulation of microorganisms and their excreted matter on surfaces, has been a major challenge to the long-term performance and reliability of engineered systems. For example, biofouling of marine vessel surfaces leads to persistent detrimental impacts, including significantly increased hydrodynamic drag and expedited corrosion via microbial induced corrosion or microbial deterioration of applied anti-corrosion coating86,273-275. Typical marine biological foulants include proteins, bacteria, Ulva spores, Navicula diatoms, tubeworm larva, and barnacles, spanning a very broad size-scale, from tens of nanometers to hundreds of micrometers276,277. In addition to marine biofouling, microbial biofouling is also a major concern in numerous other environmentally relevant systems such as heat exchangers in power plants84,85, water treatment and distribution systems87,278-281, and environmental sensors275,282. Biofouling in these systems results in reduced efficiency of mass and heat transfer, pipe blockage, potential secondary contamination, and even complete failure of the systems.

484 485 486 487 488 489 490 491 492 493

For microbial fouling, a typical biofouling process has four critical stages: conditioning, attachment, colonization, and biofilm growth283. Therefore, measures to mitigate microbial fouling can either focus on hindering cell attachment or on inhibiting microbial growth. Early biofouling coatings mostly focused on inhibiting microbial growth by applying biocidal antifoulants such as tributyltin (TBT). It is estimated that TBT-based biocides have been applied to over 70% of the global marine fleet273. However, TBT-based antifouling coatings pose environmental and ecological problems by having deleterious effects on various marine organisms284,285. Consequently, regulations are being developed for a global TBT phase-out and a transition to TBT-free anti-fouling coatings273.

494 495

Engineering the surface morphology and wetting properties using a biomimetic approach may offer an alternative route for developing environmentally friendly

ACS Paragon Plus Environment

Page 18 of 44

Page 19 of 44

Environmental Science & Technology

496 497 498 499 500

antifouling coatings. For example, lotus-leaf inspired superhydrophobic surfaces haven been acclaimed for their self-cleaning property in air, as the water droplets rolling off the leaf can easily collect the contaminants on its surface 44. Excellent short-term (hours) underwater anti-microbial adhesion performance of superhydrophobic surfaces has also been widely reported286-291.

501 502 503 504 505 506 507 508 509

However, the complexity of biological fouling poses tremendous challenges for designing a long-term robust underwater anti-biofouling surface. Engineered superhydrophobic materials with a Cassie-Baxter interface are found to lose their superhydrophobicity within a moderate time frame (weeks) upon exposure to euphotic seawater277,292. This observation can partially be explained by the fact that the underwater Cassie-Baxter state is not sustainable: the air pockets in a Cassie-Baxter interface vanish overtime due to dissolution of the trapped air into the water293. Furthermore, even the short-term effectiveness of superhydrophobic surfaces is highly dependent on both the material used and the type of microorganisms involved in biofouling 289,294.

510 511 512 513 514 515 516 517 518 519 520

A more robust strategy for underwater biofouling mitigation may be to create in-air superhydrophilic surfaces that are underwater superoleophobic. Similar to the mechanism of anti-oil-fouling, the water molecules in the highly hydrated coating layer act as an energetic barrier to cell or protein adhesion, thereby preventing protein adsorption settlement of microorganisms 265,295,296. This mechanism has been adopted by several natural marine anti-fouling surfaces such as sharkskin, fish scale, and clamshell297. Following this principle, polymers with poly (ethylene glycol) side chains (i.e. PEGylated polymers) are often used to impart strong hydrophilicity for anti-biofouling surfaces298300 . Other hydrophilic surface coatings successfully implemented for biofouling mitigation include zwitterionic polymers and polymers integrating oligosaccharide moieties301.

521 522 523 524 525 526 527 528 529

It is important to stress that biofouling is a complex phenomenon and so is the mechanism for biofouling mitigation using microtextured surfaces with special wettability297. The surface wetting property might not be the only player in combating biofouling. For example, the microtexture on the sharkskin can reduce hydrodynamic drag, which in turn promotes fast water movement in the vicinity of the skin and deters the settlement of marine organisms 302-304. Therefore, the hydrodynamic aspects of the system should also be considered when designing anti-biofouling surfaces in dynamic systems. On the other hand, microtextured surfaces also discourage the settlement certain marine organisms larger than the characteristic length scale of the surface texture305.

530 531 532 533 534 535

SLIPS is another promising potential avenue for battling biofouling both in air and under water. Several representative bacteria, including Staphylococcus aureus, Pseudomona aeruginosa, and Escherichia coli have been used as model microbial foulants to challenge a PTFE-impregnated SLIPS50,167. Superior anti-adhesion performance of SLIPS was observed as compared to the pristine PTFE membrane or to a PEGylated surface167. Due to the absence of surface roughness that microorganisms can

ACS Paragon Plus Environment

Environmental Science & Technology

536 537

Page 20 of 44

anchor onto and the ultralow surface tension of the infused liquid, SLIPS can potentially be a highly robust approach for biofouling mitigation.

538 539 540 541 542 543 544 545

Enhanced Vapor Condensation. Vapor condensation plays an important role in a wide variety of natural and engineered systems. It has significant impact on several environmentally relevant processes at the water-energy nexus such as thermal power generation, heat management, water distillation, and atmospheric water collection95. Enhancing the performance of vapor condensation can result in higher efficiencies of energy generation and energy usage, or lead to more energy-efficient means of augmenting the fresh water supply.

546 547 548 549 550 551 552 553 554

Depending on the morphology of the condensate, vapor condensation is classified in two major categories: film-wise condensation (FWC) and drop-wise condensation (DWC) 306-309. FWC occurs when the condensing surface is hydrophilic, in which case the condensate forms a liquid film over the wetted condenser surface (Figure 5A). In comparison, DWC occurs on a hydrophobic condensing surface, with the condensate being discrete droplets on the surface rather than a continuous liquid film (Figure 5B). Because a liquid film of condensate creates substantial resistance to heat transfer, DWC offers a significantly higher heat transfer rate than FWC, and is therefore usually the preferred mode of condensation95.

(C) Jumping

(B) Drop-wise

(D) Flooding

HTC Enhancement

(A) Film-wise

8X

8

7X

7

6X

6

5X

5

4X

4

3X

3

2X

2

1X

1

(E) Fine-textured hydrophobic

Coarse-textured hydrophobic Smooth Hydrophobic

0

Smooth Hydrophilic 0

1

2

3

4

5

Heat Flux

555 556 557 558 559 560 561

Figure 5. (A) Film-wise condensation on a smooth hydrophilic surface. (B) Drop-wise condensation on a smooth hydrophobic surface. (C) “Jumping” condensation on a superhydrophobic surface. (D) “Flooding” condensation on a superhydrophobic surface310. (E) Heat transfer coefficient (HTC) as a function of heat flux for different condensation modes95. A higher HTC at a given heat flux indicates faster heat transfer kinetics. Figures 5A to 5D are reproduced from ref. 308 with permission. Figure 5E is adapted from ref. 95.

562 563 564

Superhydrophobic surfaces can further enhance the rate of condensation heat transfer by promoting DWC with spontaneous droplet departure95,311. With a hierarchical morphology that imparts superior anti-adhesion property, a superhydrophobic surface can

ACS Paragon Plus Environment

Page 21 of 44

Environmental Science & Technology

565 566 567 568 569 570 571 572 573

drastically increase the heat transfer rate by efficient removal of the small droplets from the condenser surface. The improvement in heat transfer performance and the associated environmental and economic benefits can be substantial. As an example, General Electric has developed a ceramic-based highly stable superhydrophobic coating that can augment the heat transfer performance of a steel surface by a factor of 5 to 8 compared to an FWC with an untreated hydrophilic surface (Figure 5E)312. This superhydrophobic coating technology has been estimated to lead to significant saving of fossil fuel for power plants, and a potential annual reduction of more than 20 million tons of CO2 emission in the United States via a 5% reduction of condenser pressure in coal power plants313.

574 575 576 577 578 579 580 581 582 583 584 585

Achieving high performance vapor condensation using superhydrophobic surfaces, however, can be technically challenging. Two modes for vapor condensation on a superhydrophobic surface are possible: the “jumping” mode and the “flooding” mode310. When the vapor saturation level is low, water droplets forming on a superhydrophobic condenser can undergo coalescence-driven ejection (Figure 5C)314, which enhances heat transfer compared to DWC on a non-textured hydrophobic surface. Such a “jump” condensation occurs only if the nucleation site density is low so that the spacing between the forming droplets is significantly larger than the length scale of the nano-textures. Recently, a superhydrophobic thermally conductive surface has been applied as the condenser for air-gap membrane distillation315. It was shown that the “jumping” mode condensation served to enhance the overall mass transfer kinetics, possibly by improving the mass transfer coefficient in the air gap.

586 587 588 589 590 591 592

For a high vapor saturation level or very high heat transfer rate, however, the nucleation site density could increase to the extent that the distance between adjacent droplets is of a length scale similar to that of the nano-texture, in which case the condenser surface, though being superhydrophobic, can be flooded by the strongly pinned condensate in a Wenzel state (Figure 5D). Such “flooding” mode of condensation yields no benefits for the heat transfer rate compared to DWC on a non-textured hydrophobic surface316,317.

593 594 595 596 597 598 599 600 601

In light of possible of different condensation modes with contrasting consequences, successful implementation of a textured superhydrophobic surface for enhancing condensation rate requires better control of nucleation density by engineering both surface chemistry and morphology. Another possible strategy to promote high performance DWC is using a SLIPS30,170. The distinct advantage of SLIPS over textured superhydrophobic surfaces is the combination of the ultra-low liquid adhesion, which is essential for efficient droplet removal, and the absence of surface roughness, which leaves no possibility for Wenzel state pinning caused by condensation in the microscopic air pockets170.

602 603 604

Overall, the development of superhydrophobic surfaces for high performance vapor condensation is still in its infancy. Although a plethora of recent studies have been conducted to further elucidate its mechanism310,316-324 or to test new materials for this

ACS Paragon Plus Environment

Environmental Science & Technology

605 606 607 608 609 610 611 612

application170,325,326, many practical considerations remain to be addressed before fullscale industrial application. In particular, uncertainties remain regarding the long-term chemical and mechanical stability of these coating materials as well as their economical and scalable fabrication. Nonetheless, the demonstrated potential enhancement of heat transfer performance by these novel materials, and the tremendous economic and environmental benefits as a consequence of such enhancement, suggest a promising future of engineering surface wetting properties for high performance vapor condensation.

613 614 615 616 617 618 619 620

Atmospheric Water Collection. Another important environmental application of interfacial materials with special wettability for vapor condensation is atmospheric water collection from fog or dew in areas where fresh water is scarce327. With suitable meteorological conditions, atmospheric water collection using well-designed water collectors, can be an energy-free approach to harvesting high-quality water to augment the fresh water supply in arid areas. The challenge, however, is efficiency, which directly impacts the unit cost of water production via fog or dew collection.

621 622 623 624 625 626 627 628

Biological systems provide significant insights for designing high performance surfaces for atmospheric water collection. Examples include water-capturing desert beetles whose overwings bear both hydrophilic and hydrophobic patches122, and watercollecting spider silk with a periodic structure comprising highly hydrophilic spindleknots and less hydrophilic joints328. These efficient natural water-collection systems suggest that an ideal fog-harvesting surface should comprise hydrophilic and hydrophobic regions, the former to promote nucleation and the latter to confine the forming droplets until they reach a critical size for droplet departure.

629 630 631 632 633 634 635 636 637 638 639 640

Following this principle, micro-patterned surfaces with heterogeneous wetting properties have been developed32,329,330. In a recent study where hydrophilic spots were created by inkjet printing of polydopamine onto a superhydrophobic surface, it was observed that a well-designed heterogeneously wettable surface can more than double the water collection rate compared to a superhydrophobic surface330. However, results from other studies with heterogeneous wettable surfaces revealed trivial32 or even negative329 impacts of patterned wettability on water collection rate. The effectiveness of a patterned superhydrophobic/superhydrophilic surface in enhancing water collection rate seems to be dependent on the pattern of the patches and the operation conditions, including the surface tilting angle331. More comprehensive and systematic investigations are needed to further unravel the influence of pattern geometry and wettability on the droplet formation rate as well as the surface mobility of the condensate droplets.

641 642

ACS Paragon Plus Environment

Page 22 of 44

Page 23 of 44

Environmental Science & Technology

643

Outlook

644 645 646 647 648 649 650 651 652 653 654

Many environmental processes are governed or heavily affected by interfacial phenomena in which surface wetting plays a critical role. Therefore, the ability to tailor surface wettability creates tremendous opportunities to develop novel environmental applications or enhance existing environmental processes. Several examples of environmental applications empowered or augmented by materials with engineered surface wettability have been discussed in this review. These include oil-water separation, membrane separations for desalination and water purification, biofouling mitigation, enhanced vapor condensation, and atmospheric water collection. Interfacial materials with special wettability have also been used in other environmentally relevant applications, such as corrosion inhibition36,332-335, drag reduction51,52,171,336, and catalytic surface reaction337-340.

655 656 657 658 659 660 661 662 663

Innovations in materials science have historically fueled advances in environmental science and engineering. This has been the case in the development of environmental catalytic materials96,97,341,342, water purification and desalination membranes343-345, environmental sensors346,347, and various environmental applications of nanomaterials348352 . Interfacial materials of special wettability have been a bourgeoning research field in materials science for the past decade; the field is still growing at a fast pace7. The science and technology in this field have gained sufficient maturity to be leveraged for developing novel solutions to pressing environmental problems in which interfacial phenomena are so pivotal.

664 665 666 667 668 669 670 671 672

Although significant progress has been made to fabricate interfacial materials with various types of special wettability, full-scale implementation of these materials in environmental applications still requires further research efforts to understand their longterm performance in complex and challenging environmental conditions. In the mean time, the materials science community continues its efforts to make materials with novel wetting properties more robust and sustainable, and to develop techniques for scalable fabrication of these materials. We believe these advances in materials design and fabrication will further enhance the development of creative and effective solutions to challenging problems concerning environmental interfaces.

673 674

Acknowledgement

675 676 677 678

We acknowledge the financial support from Bureau of Reclamation, Department of Interior, via DWPR Agreement R15AC00088, and the partial support to this effort from the Advanced Research Projects Agency-Energy (ARPA-E), U.S. Department of Energy, via Grant DE-AR0000306.

ACS Paragon Plus Environment

Environmental Science & Technology

679 680 681 682 683 684 685 686 687 688 689 690 691 692 693 694 695 696 697 698 699 700 701 702 703 704 705 706 707 708 709 710 711 712 713 714 715 716 717 718 719 720 721 722 723 724 725 726 727 728

References (1) (2) (3) (4) (5)

(6) (7) (8) (9) (10) (11) (12) (13) (14)

(15) (16) (17) (18)

(19)

Blossey, R. Self-Cleaning Surfaces-Virtual Realities. Nat Mater 2003, 2, 301– 306. Feng, L.; Zhang, Z.; Mai, Z.; Ma, Y.; Liu, B.; Jiang, L.; Zhu, D. A SuperHydrophobic and Super-Oleophilic Coating Mesh Film for the Separation of Oil and Water. Angew. Chem. Int. Ed. Engl. 2004, 43, 2012–2014. Taolei Sun; Lin Feng; Xuefeng Gao, A.; Lei Jiang. Bioinspired Surfaces with Special Wettability. Acc. Chem. Res. 2005, 38, 644–652. Liu, K.; Yao, X.; Jiang, L. Recent Developments in Bio-Inspired Special Wettability. Chem. Soc. Rev. 2010, 39, 3240–3255. Yan, Y. Y.; Gao, N.; Barthlott, W. Mimicking Natural Superhydrophobic Surfaces and Grasping the Wetting Process: a Review on Recent Progress in Preparing Superhydrophobic Surfaces. Advances in Colloid and Interface Science 2011, 169, 80–105. Wong, T.-S.; Kang, S. H.; Tang, S. K. Y.; Smythe, E. J.; Hatton, B. D.; Grinthal, A.; Aizenberg, J. Bioinspired Self-Repairing Slippery Surfaces with PressureStable Omniphobicity. Nature 2011, 477, 443–447. Wong, T.-S.; Sun, T.; Feng, L.; Aizenberg, J. Interfacial Materials with Special Wettability. MRS Bulletin 2013, 38, 366–371. Grinthal, A.; Aizenberg, J. Mobile Interfaces: Liquids as a Perfect Structural Material for Multifunctional, Antifouling Surfaces. Chem. Mater. 2013, 26, 698– 708. Kota, A. K.; Kwon, G.; Tuteja, A. The Design and Applications of Superomniphobic Surfaces. NPG Asia Materials 2014, 6, e109. Tuteja, A.; Choi, W.; Ma, M.; Mabry, J. M.; Mazzella, S. A.; Rutledge, G. C.; McKinley, G. H.; Cohen, R. E. Designing Superoleophobic Surfaces. Science 2007, 318, 1618–1622. Tuteja, A.; Choi, W.; Mabry, J. M.; McKinley, G. H.; Cohen, R. E. Robust Omniphobic Surfaces. 2008. Xia, F.; Jiang, L. Bio-Inspired, Smart, Multiscale Interfacial Materials. Adv. Mater. 2008, 20, 2842–2858. Liu, M.; Zheng, Y.; Zhai, J.; Jiang, L. Bioinspired Super-Antiwetting Interfaces with Special Liquid−Solid Adhesion. Acc. Chem. Res. 2009, 43, 368–377. Guo, Z.; Liu, W.; Su, B.-L. Superhydrophobic Surfaces: From Natural to Biomimetic to Functional. Journal of Colloid and Interface Science 2011, 353, 335–355. Tuteja, A.; Kota, A. K.; Mabry, J. M. Superoleophobic Surfaces: Design Criteria and Recent Studies. Surface Innovations 2013, 1, 71–83. Liu, M.; Wang, S.; Jiang, L. Bioinspired Multiscale Surfaces with Special Wettability. MRS Bulletin 2013, 38, 375–382. Bhushan, B.; Jung, Y. C. Natural and Biomimetic Artificial Surfaces for Superhydrophobicity, Self-Cleaning, Low Adhesion, and Drag Reduction. Progress in Materials Science 2011, 56, 1–108. Li, X.-M.; Reinhoudt, D.; Crego-Calama, M. What Do We Need for a Superhydrophobic Surface? a Review on the Recent Progress in the Preparation of Superhydrophobic Surfaces. Chemical Society Reviews 2007, 36, 1350–1368. Roach, P.; Shirtcliffe, N. J.; Newton, M. I. Progess in Superhydrophobic Surface Development. Soft Matter 2008, 4, 224–240.

ACS Paragon Plus Environment

Page 24 of 44

Page 25 of 44

729 730 731 732 733 734 735 736 737 738 739 740 741 742 743 744 745 746 747 748 749

Environmental Science & Technology

(20)

(21) (22) (23) (24)

(25)

(26) (27)

750 751 752 753 754 755 756 757 758 759 760 761 762 763 764 765 766 767 768 769 770 771 772 773 774 775 776

Liu, K.; Tian, Y.; Jiang, L. Bio-Inspired Superoleophobic and Smart Materials: Design, Fabrication, and Application. Progress in Materials Science 2013, 58, 503–564. Yao, X.; Song, Y.; Jiang, L. Applications of Bio‐Inspired Special Wettable Surfaces. Adv. Mater. 2011, 23, 719–734. Leng, B.; Shao, Z.; de With, G.; Ming, W. Superoleophobic Cotton Textiles. 2009, 25, 2456–2460. Zhang, J.; Seeger, S. Polyester Materials with Superwetting Silicone Nanofilaments for Oil/Water Separation and Selective Oil Absorption. Adv. Funct. Mater. 2011, 21, 4699–4704. Pereira, C.; Alves, C.; Monteiro, A.; Magen, C.; Pereira, A. M.; Ibarra, A.; Ibarra, M. R.; Tavares, P. B.; Araújo, J. P.; Blanco, G.; et al. Designing Novel Hybrid Materials by One-Pot Co-Condensation: From Hydrophobic Mesoporous Silica Nanoparticles to Superamphiphobic Cotton Textiles. ACS Appl. Mater. Interfaces 2011, 3, 2289–2299. Artus, G. R. J.; Zimmermann, J.; Reifler, F. A.; Brewer, S. A.; Seeger, S. A Superoleophobic Textile Repellent Towards Impacting Drops of Alkanes. Applied Surface Science 2012, 258, 3835–3840. Xue, Z.; Cao, Y.; Liu, N.; Feng, L.; Jiang, L. Special Wettable Materials for Oil/Water Separation. Journal of Materials Chemistry A 2014, 2, 2445–2460. Howarter, J. A.; Youngblood, J. P. Self‐Cleaning and Anti‐Fog Surfaces via Stimuli‐Responsive Polymer Brushes. Adv. Mater. 2007, 19, 3838–3843.

(28)

(29)

(30) (31) (32) (33) (34)

(35) (36)

Howarter, J. A.; Youngblood, J. P. Self‐Cleaning and Next Generation Anti‐Fog Surfaces and Coatings. Macromolecular Rapid Communications 2008, 29, 455–466. Kim, P.; Wong, T.-S.; Alvarenga, J.; Kreder, M. J.; Adorno-Martinez, W. E.; Aizenberg, J. Liquid-Infused Nanostructured Surfaces with Extreme Anti-Ice and Anti-Frost Performance. ACS Nano 2012, 6, 6569–6577. Wilson, P. W.; Lu, W.; Xu, H.; Kim, P.; Kreder, M. J.; Alvarenga, J.; Aizenberg, J. Inhibition of Ice Nucleation by Slippery Liquid-Infused Porous Surfaces (SLIPS). Phys. Chem. Chem. Phys. 2013, 15, 581–585. Thickett, S. C.; Neto, C.; Harris, A. T. Biomimetic Surface Coatings for Atmospheric Water Capture Prepared by Dewetting of Polymer Films. Adv. Mater. 2011, 23, 3718–3722. White, B.; Sarkar, A.; Kietzig, A.-M. Fog-Harvesting Inspired by the Stenocara Beetle—an Analysis of Drop Collection and Removal From Biomimetic Samples with Wetting Contrast. Applied Surface Science 2013, 284, 826–836. Superomniphobic Surfaces for Effective Chemical Shielding. 2012, 135, 578– 581. Wang, S.; Feng, L.; Jiang, L. One‐Step Solution‐Immersion Process for the Fabrication of Stable Bionic Superhydrophobic Surfaces. Adv. Mater. 2006, 18, 767–770. Zhongbing Huang; Ying Zhu; Jihua Zhang, A.; Yin, G. Stable Biomimetic Superhydrophobicity and Magnetization Film with Cu-Ferrite Nanorods; American Chemical Society, 2007; Vol. 111, pp. 6821–6825. Liu, T.; Chen, S.; Cheng, S.; Tian, J.; Chang, X.; Yin, Y. Corrosion Behavior of Super-Hydrophobic Surface on Copper in Seawater. Electrochimica Acta 2007, 52, 8003–8007.

ACS Paragon Plus Environment

Environmental Science & Technology

777 778 779 780 781 782 783 784 785 786 787 788 789 790 791 792 793 794 795 796 797 798 799 800 801 802 803 804 805 806 807 808 809 810 811 812 813 814 815 816 817 818 819 820 821 822 823 824 825 826

(37) (38)

(39)

(40) (41)

(42) (43)

(44) (45)

(46) (47)

(48) (49)

(50)

(51) (52)

Guo, Z.-G.; Liu, W.-M.; Su, B.-L. A Stable Lotus-Leaf-Like Water-Repellent Copper. Appl. Phys. Lett. 2008, 92, 063104. Hermelin, E.; Petitjean, J.; Lacroix, J.-C.; Chane-Ching, K. I.; Tanguy, J.; Lacaze, P.-C. Ultrafast Electrosynthesis of High Hydrophobic Polypyrrole Coatings on a Zinc Electrode: Applications to the Protection Against Corrosion. Chem. Mater. 2008, 20, 4447–4456. Zhang, F.; Zhao, L.; Chen, H.; Xu, S.; Evans, D. G.; Duan, X. Corrosion Resistance of Superhydrophobic Layered Double Hydroxide Films on Aluminum. Angew. Chem. Int. Ed. Engl. 2008, 47, 2466–2469. Meng, H.; Wang, S.; Xi, J.; Tang, Z.; Jiang, L. Facile Means of Preparing Superamphiphobic Surfaces on Common Engineering Metals. J. Phys. Chem. C 2008, 112, 11454–11458. Wu, W.; Wang, X.; Wang, D.; Chen, M.; Zhou, F.; Liu, W.; Xue, Q. Alumina Nanowire Forests via Unconventional Anodization and Super-Repellency Plus Low Adhesion to Diverse Liquids. Chemical Communications 2009, 1043– 1045. Liu, K.; Jiang, L. Metallic Surfaces with Special Wettability. Nanoscale 2011, 3, 825. Zhao, L.; Liu, Q.; Gao, R.; Wang, J.; Yang, W.; Liu, L. One-Step Method for the Fabrication of Superhydrophobic Surface on Magnesium Alloy and Its Corrosion Protection, Antifouling Performance. Corrosion Science 2014, 80, 177–183. Genzer, J.; Efimenko, K. Recent Developments in Superhydrophobic Surfaces and Their Relevance to Marine Fouling: a Review. Biofouling 2007, 22, 339– 360. Hoipkemeier-Wilson, L.; Schumacher, J. F.; Carman, M. L.; Gibson, A. L.; Feinberg, A. W.; Callow, M. E.; Finlay, J. A.; Callow, J. A.; Brennan, A. B. Antifouling Potential of Lubricious, Micro-Engineered, PDMS Elastomers Against Zoospores of the Green Fouling Alga Ulva (Enteromorpha). Biofouling 2007, 20, 53–63. Chen, L.; Liu, M.; Bai, H.; Chen, P.; Xia, F.; Han, D.; Jiang, L. Antiplatelet and Thermally Responsive Poly(N-Isopropylacrylamide) Surface with Nanoscale Topography. J. Am. Chem. Soc. 2009, 131, 10467–10472. Fan, H.; Chen, P.; Qi, R.; Zhai, J.; Wang, J.; Chen, L.; Chen, L.; Sun, Q.; Song, Y.; Han, D.; et al. Greatly Improved Blood Compatibility by Microscopic Multiscale Design of Surface Architectures. Small 2009, 5, 2144–2148. Patel, P.; Choi, C. K.; Meng, D. D. Superhydrophilic Surfaces for Antifogging and Antifouling Microfluidic Devices. Journal of Laboratory Automation 2010, 15, 114–119. Yao, X.; Dunn, S. S.; Kim, P.; Duffy, M.; Alvarenga, J.; Aizenberg, J. Fluorogel Elastomers with Tunable Transparency, Elasticity, Shape‐Memory, and Antifouling Properties. Angew. Chem. Int. Ed. Engl. 2014, 53, 4418–4422. MacCallum, N.; Howell, C.; Kim, P.; Sun, D.; Friedlander, R.; Ranisau, J.; Ahanotu, O.; Lin, J. J.; Vena, A.; Hatton, B.; et al. Liquid-Infused Silicone as a Biofouling-Free Medical Material. ACS Biomater. Sci. Eng. 2014, 1, 43–51. Watanabe, K.; Udagawa, Y.; Udagawa, H. Drag Reduction of Newtonian Fluid in a Circular Pipe with a Highly Water-Repellent Wall. J. Fluid Mech. 1999, 381, 225–238. Ou, J.; Perot, B.; Rothstein, J. P. Laminar Drag Reduction in Microchannels Using Ultrahydrophobic Surfaces. Physics of Fluids 2004, 16, 4635–4643.

ACS Paragon Plus Environment

Page 26 of 44

Page 27 of 44

827 828 829 830 831 832 833 834 835 836 837 838 839 840 841 842 843 844 845 846 847 848 849 850 851 852 853 854 855 856 857 858 859 860 861 862 863 864 865 866 867 868 869 870 871 872 873 874 875 876

Environmental Science & Technology

(53) (54) (55) (56) (57) (58)

(59) (60) (61) (62) (63) (64) (65) (66)

(67) (68)

(69) (70) (71)

Joseph, P.; Cottin-Bizonne, C.; Benoît, J. M.; Ybert, C.; Journet, C.; Tabeling, P.; Bocquet, L. Slippage of Water Past Superhydrophobic Carbon Nanotube Forests in Microchannels. Phys. Rev. Lett. 2006, 97, 156104. Ionov, L.; Houbenov, N.; Sidorenko, A.; Stamm, M.; Minko, S. Smart Microfluidic Channels. Adv. Funct. Mater. 2006, 16, 1153–1160. Steinberger, A.; Cottin-Bizonne, C.; Kleimann, P.; Charlaix, E. High Friction on a Bubble Mattress. Nat Mater 2007, 6, 665–668. Byun, D.; Kim, J.; Ko, H. S.; Park, H. C. Direct Measurement of Slip Flows in Superhydrophobic Microchannels with Transverse Grooves. Physics of Fluids 2008, 20, 113601. Aizenberg, J.; Black, A. J.; Whitesides, G. M. Control of Crystal Nucleation by Patterned Self-Assembled Monolayers. Nature 1999, 398, 495–498. Qin, D.; Xia, Y.; Xu, B.; Yang, H.; Zhu, C.; Whitesides, G. M. Fabrication of Ordered Two‐Dimensional Arrays of Micro‐ and Nanoparticles Using Patterned Self‐Assembled Monolayers as Templates. Adv. Mater. 1999, 11, 1433–1437. Aizenberg, J.; Braun, P. V.; Wiltzius, P. Patterned Colloidal Deposition Controlled by Electrostatic and Capillary Forces. Phys. Rev. Lett. 2000, 84, 2997–3000. Gu, Z. Z.; Fujishima, A.; Sato, O. Patterning of a Colloidal Crystal Film on a Modified Hydrophilic and Hydrophobic Surface. Angew. Chem. 2002, 114, 2171–2174. Huang, J.; Kim, F.; Tao, A. R.; Connor, S.; Yang, P. Spontaneous Formation of Nanoparticle Stripe Patterns Through Dewetting. Nat Mater 2005, 4, 896–900. Devasish Chowdhury; Rivka Maoz, A.; Sagiv, J. Wetting Driven Self-Assembly as a New Approach to Template-Guided Fabrication of Metal Nanopatterns. Nano Lett. 2007, 7, 1770–1778. Roie Yerushalmi; Johnny C Ho; Zachery A Jacobson, A.; Javey, A. Generic Nanomaterial Positioning by Carrier and Stationary Phase Design. Nano Lett. 2007, 7, 2764–2768. Tao, A. R.; Huang, J.; Yang, P. Langmuir−Blodgettry of Nanocrystals and Nanowires. Acc. Chem. Res. 2008, 41, 1662–1673. Tian, D.; Chen, Q.; Nie, F. Q.; Xu, J.; Song, Y.; Jiang, L. Patterned Wettability Transition by Photoelectric Cooperative and Anisotropic Wetting for Liquid Reprography. Adv. Mater. 2009, 21, 3744–3749. Nishimoto, S.; Kubo, A.; Nohara, K.; Zhang, X.; Taneichi, N.; Okui, T.; Liu, Z.; Nakata, K.; Sakai, H.; Murakami, T.; et al. TiO2-Based Superhydrophobic– Superhydrophilic Patterns: Fabrication via an Ink-Jet Technique and Application in Offset Printing. Applied Surface Science 2009, 255, 6221–6225. Lawson, K. W.; Lloyd, D. R. Membrane Distillation. J. Membr. Sci. 1997, 1–25. Hong, S.; Elimelech, M. Chemical and Physical Aspects of Natural Organic Matter (NOM) Fouling of Nanofiltration Membranes. J. Membr. Sci. 1997, 132, 159–181. Vrijenhoek, E. M.; Hong, S.; Elimelech, M. Influence of Membrane Surface Properties on Initial Rate of Colloidal Fouling of Reverse Osmosis and Nanofiltration Membranes. J. Membr. Sci. 2001, 188, 115–128. Seidel, A. Coupling Between Chemical and Physical Interactions in Natural Organic Matter (NOM) Fouling of Nanofiltration Membranes: Implications for Fouling Control. J. Membr. Sci. 2002, 203, 245–255. Li, Q.; Elimelech, M. Organic Fouling and Chemical Cleaning of Nanofiltration Membranes:  Measurements and Mechanisms. Environ. Sci. Technol. 2004,

ACS Paragon Plus Environment

Environmental Science & Technology

877 878 879 880 881 882 883 884 885 886 887 888 889 890 891 892 893 894 895 896 897 898 899 900 901 902 903 904 905 906 907 908 909 910 911 912 913 914 915 916 917 918 919 920 921 922 923 924 925 926 927

(72)

(73) (74) (75) (76) (77) (78) (79) (80) (81) (82) (83) (84) (85) (86) (87) (88) (89)

(90) (91) (92)

38, 4683–4693. Lee, S.; Elimelech, M. Relating Organic Fouling of Reverse Osmosis Membranes to Intermolecular Adhesion Forces. Environ. Sci. Technol. 2006, 40, 980–987. Tang, C. Y.; Kwon, Y.-N.; Leckie, J. O. Fouling of Reverse Osmosis and Nanofiltration Membranes by Humic Acid—Effects of Solution Composition and Hydrodynamic Conditions. J. Membr. Sci. 2007, 290, 86–94. Meng, F.; Chae, S.-R.; Drews, A.; Kraume, M.; Shin, H.-S.; Yang, F. Recent Advances in Membrane Bioreactors (MBRs): Membrane Fouling and Membrane Material. Water Research 2009, 43, 1489–1512. Souhaimi, M. K.; Matsuura, T. Membrane Distillation; Elsevier, 2011. Stumm, W.; Sigg, L.; Sulzberger, B. Chemistry of the Solid-Water Interface; University of Texas Press, 1992. Bailey, S. E.; Olin, T. J.; Bricka, R. M.; Adrian, D. D. A Review of Potentially Low-Cost Sorbents for Heavy Metals. Water Research 1999, 33, 2469–2479. Kun Yang; Lizhong Zhu, A.; Baoshan Xing. Adsorption of Polycyclic Aromatic Hydrocarbons by Carbon Nanomaterials. Environ. Sci. Technol. 2006, 40, 1855–1861. Inglezakis, V.; Poulopoulos, S. Adsorption, Ion Exchange and Catalysis; Elsevier, 2006. Ren, X.; Chen, C.; Nagatsu, M.; Wang, X. Carbon Nanotubes as Adsorbents in Environmental Pollution Management: a Review. Chemical Engineering Journal 2011, 170, 395–410. Chowdhury, Z. K. Activated Carbon; American Water Works Association, 2013. Maguire, J. J.; Betz, W. H.; Betz, L. D. Biological Fouling in Recirculating Cooling Water Systems. Ind. Eng. Chem. 1956, 48, 2162–2167. Flemming, H. C.; Schaule, G. Biofouling on Membranes - a Microbiological Approach. Desalination 1988, 70, 95–119. Flemming, H. C. Biofouling in Water Treatment. In Biofouling and Biocorrosion in Industrial Water Systems; Flemming, H.-C.; Geesey, G. G., Eds.; Springer Berlin Heidelberg: Berlin, Heidelberg, 1991; pp. 47–80. Melo, L. F.; Bott, T. R. Biofouling in Water Systems. Experimental Thermal and Fluid Science 1997, 14, 375–381. Callow, M. E.; Callow, J. A. Marine Biofouling: a Sticky Problem. Biologist 2002, 49, 1–5. Herzberg, M.; Elimelech, M. Biofouling of Reverse Osmosis Membranes: Role of Biofilm-Enhanced Osmotic Pressure. J. Membr. Sci. 2007, 295, 11–20. Javaherdashti, R. How Corrosion Affects Industry and Life. Anti-Corrosion Meth & Material 2000, 47, 30–34. Edwards, M. Controlling Corrosion in Drinking Water Distribution Systems: a Grand Challenge for the 21st Century. Water Science Technology 2004, 49, 1–8. Lytle, D. A.; Nadagouda, M. N. A Comprehensive Investigation of Copper Pitting Corrosion in a Drinking Water Distribution System. Corrosion Science 2010, 52, 1927–1938. Nawrocki, J.; Raczyk-Stanisławiak, U.; Świetlik, J.; Olejnik, A.; Sroka, M. J. Corrosion in a Distribution System: Steady Water and Its Composition. Water Research 2010, 44, 1863–1872. Khawaji, A. D.; Kutubkhanah, I. K.; Wie, J.-M. Advances in Seawater Desalination Technologies. Desalination 2008, 221, 47–69.

ACS Paragon Plus Environment

Page 28 of 44

Page 29 of 44

928 929 930 931 932 933 934 935 936 937 938 939 940 941 942 943 944 945 946 947 948 949 950 951 952 953 954 955 956 957 958 959 960 961 962 963 964 965 966 967 968 969 970 971 972 973 974 975 976 977 978

Environmental Science & Technology

(93) (94) (95) (96) (97) (98) (99) (100) (101) (102) (103) (104) (105) (106) (107) (108) (109) (110) (111) (112) (113)

(114)

Pérez-Lombard, L.; Ortiz, J.; Pout, C. A Review on Buildings Energy Consumption Information. Energy and Buildings 2008, 40, 394–398. Wang, D.; Bao, A.; Kunc, W.; Liss, W. Coal Power Plant Flue Gas Waste Heat and Water Recovery. Applied Energy 2012, 91, 341–348. Miljkovic, N.; Wang, E. N. Condensation Heat Transfer on Superhydrophobic Surfaces. MRS Bulletin 2013, 38, 397–406. Armor, J. N. Environmental Catalysis. Applied Catalysis B: Environmental 1992, 1, 221–256. Farrauto, R. J.; Heck, R. M. Environmental Catalysis Into the 21st Century. Catalysis Today 2000, 55, 179–187. Centi, G.; Ciambelli, P.; Perathoner, S.; Russo, P. Environmental Catalysis: Trends and Outlook. Catalysis Today 2002, 75, 3–15. Drelich, J.; Chibowski, E. Superhydrophilic and Superwetting Surfaces: Definition and Mechanisms of Control. Langmuir 2010, 26, 18621–18623. Ma, M.; Hill, R. M. Superhydrophobic Surfaces. Current Opinion in Colloid & Interface Science 2006, 11, 193–202. Kiyoharu Tadanaga; Junichi Morinaga; Atsunori Matsuda, A.; Minami, T. Superhydrophobic−Superhydrophilic Micropatterning on Flowerlike Alumina Coating Film by the Sol−Gel Method. Chem. Mater. 2000, 12, 590–592. Cassie, A. B. D.; Baxter, S. Wettability of Porous Surfaces. Trans. Faraday Soc. 1944, 40, 546–551. Joanny, J. F.; de Gennes, P. G. A Model for Contact Angle Hysteresis. J Chem Phys 1984, 81, 552–562. Lam, C.; Wu, R.; Li, D.; Hair, M.; Neumann, A. W. Study of the Advancing and Receding Contact Angles: Liquid Sorption as a Cause of Contact Angle Hysteresis. Advances in Colloid and Interface Science 2002, 96, 169–191. Gao, L.; McCarthy, T. J. Contact Angle Hysteresis Explained. Langmuir 2006, 22, 6234–6237. G McHale; N J Shirtcliffe, A.; Newton, M. I. Contact-Angle Hysteresis on Super-Hydrophobic Surfaces. Langmuir 2004, 20, 10146–10149. Extrand, C. W. Model for Contact Angles and Hysteresis on Rough and Ultraphobic Surfaces. Langmuir 2002, 18, 7991–7999. Extrand, C. W. Contact Angles and Hysteresis on Surfaces with Chemically Heterogeneous Islands. Langmuir 2003, 19, 3793–3796. Pierce, E.; Carmona, F. J.; Amirfazli, A. Understanding of Sliding and Contact Angle Results in Tilted Plate Experiments. Colloids and Surfaces A: Physicochemical and Engineering Aspects 2008, 323, 73–82. Lin Feng; Yanan Zhang; Jinming Xi; Ying Zhu; Nü Wang; Fan Xia, A.; Lei Jiang. Petal Effect:  a Superhydrophobic State with High Adhesive Force. Langmuir 2008, 24, 4114–4119. Bhushan, B.; Her, E. K. Fabrication of Superhydrophobic Surfaces with High and Low Adhesion Inspired From Rose Petal. Langmuir 2010, 26, 8207–8217. Liu, K.; Du, J.; Wu, J.; Jiang, L. Superhydrophobic Gecko Feet with High Adhesive Forces Towards Water and Their Bio-Inspired Materials. Nanoscale 2012, 4, 768–772. Kota, A. K.; Li, Y.; Mabry, J. M.; Tuteja, A. Hierarchically Structured Superoleophobic Surfaces with Ultralow Contact Angle Hysteresis. Adv. Mater. 2012, 24, 5838–5843. Lei Zhai; Michael C Berg; Fevzi Ç Cebeci; Yushan Kim; John M Milwid; Michael F Rubner, A.; Robert E Cohen. Patterned Superhydrophobic Surfaces:  Toward a Synthetic Mimic of the Namib Desert Beetle. Nano Lett.

ACS Paragon Plus Environment

Environmental Science & Technology

979 980 981 982 983 984 985 986 987 988 989 990 991 992 993 994 995 996 997 998 999 1000 1001 1002 1003 1004 1005 1006 1007 1008 1009 1010 1011 1012 1013 1014 1015 1016 1017 1018 1019 1020 1021 1022 1023 1024 1025 1026 1027 1028

(115)

(116) (117) (118)

(119) (120) (121) (122) (123)

(124) (125) (126) (127) (128)

(129)

(130) (131) (132)

2006, 6, 1213–1217. R P Garrod; L G Harris; W C E Schofield; J McGettrick; L J Ward; D O H Teare, A.; Badyal, J. P. S. Mimicking a Stenocara Beetle's Back for Microcondensation Using Plasmachemical Patterned Superhydrophobic−Superhydrophilic Surfaces. Langmuir 2006, 23, 689–693. JUNG, Y. C.; Bhushan, B. Wetting Behaviour During Evaporation and Condensation of Water Microdroplets on Superhydrophobic Patterned Surfaces. Journal of Microscopy 2008, 229, 127–140. Kietzig, A.-M.; Hatzikiriakos, S. G.; Englezos, P. Patterned Superhydrophobic Metallic Surfaces. Langmuir 2009, 25, 4821–4827. Wischerhoff, E.; Uhlig, K.; Lankenau, A.; Börner, H. G.; Laschewsky, A.; Duschl, C.; Lutz, J. F. Controlled Cell Adhesion on PEG‐Based Switchable Surfaces. Angew. Chem. Int. Ed. Engl. 2008, 47, 5666–5668. Zhang, L.; Zhang, Z.; Wang, P. Smart Surfaces with Switchable Superoleophilicity and Superoleophobicity in Aqueous Media: Toward Controllable Oil|[Sol]|Water Separation. NPG Asia Materials 2012, 4, e8. Ensikat, H. J.; Ditsche-Kuru, P.; Neinhuis, C.; Barthlott, W. Superhydrophobicity in Perfection: the Outstanding Properties of the Lotus Leaf. Beilstein journal of Nanotechnology 2011, 2, 152–161. Bixler, G. D.; Bhushan, B. Rice- and Butterfly-Wing Effect Inspired SelfCleaning and Low Drag Micro/Nanopatterned Surfaces in Water, Oil, and Air Flow. Nanoscale 2013, 6, 76–96. Parker, A. R.; Lawrence, C. R. Water Capture by a Desert Beetle. Nature 2001, 414, 33–34. Barthlott, W.; Schimmel, T.; Wiersch, S.; Koch, K.; Brede, M.; Barczewski, M.; Walheim, S.; Weis, A.; Kaltenmaier, A.; Leder, A.; et al. The Salvinia Paradox: Superhydrophobic Surfaces with Hydrophilic Pins for Air Retention Under Water. Adv. Mater. 2010, 22, 2325–2328. Jiang, L.; Zhao, Y.; Zhai, J. A Lotus-Leaf-Like Superhydrophobic Surface: a Porous Microsphere/Nanofiber Composite Film Prepared by Electrohydrodynamics. Angew. Chem. 2004, 116, 4438–4441. Guo, Z.; Liu, W. Biomimic From the Superhydrophobic Plant Leaves in Nature: Binary Structure and Unitary Structure. Plant Science 2007, 172, 1103–1112. Ball, P. Engineering Shark Skin and Other Solutions. Nature 1999, 400, 507– 509. Nishimoto, S.; Bhushan, B. Bioinspired Self-Cleaning Surfaces with Superhydrophobicity, Superoleophobicity, and Superhydrophilicity. RSC Adv. 2012, 3, 671–690. Liu, M.; Wang, S.; Wei, Z.; Song, Y.; Jiang, L. Bioinspired Design of a Superoleophobic and Low Adhesive Water/Solid Interface. Adv. Mater. 2009, 21, 665–669. Lin, L.; Liu, M.; Chen, L.; Chen, P.; Ma, J.; Han, D.; Jiang, L. Bio‐Inspired Hierarchical Macromolecule–Nanoclay Hydrogels for Robust Underwater Superoleophobicity. Adv. Mater. 2010, 22, 4826–4830. Amabili, M.; Giacomello, A.; Meloni, S.; Casciola, C. M. Unraveling the Salvinia Paradox: Design Principles for Submerged Superhydrophobicity. Advanced Materials Interfaces 2015, 2, n/a–n/a. de Gennes, P. G. Wetting: Statics and Dynamics. Rev. Mod. Phys. 1985, 57, 827–863. Takashi Nishino; Masashi Meguro; Katsuhiko Nakamae; Motonori Matsushita,

ACS Paragon Plus Environment

Page 30 of 44

Page 31 of 44

1029 1030 1031 1032 1033 1034 1035 1036 1037 1038 1039 1040 1041 1042 1043 1044 1045 1046 1047 1048 1049 1050 1051 1052 1053 1054 1055 1056 1057 1058 1059 1060 1061 1062 1063 1064 1065 1066 1067 1068 1069 1070 1071 1072 1073 1074 1075 1076 1077 1078 1079

Environmental Science & Technology

(133) (134) (135) (136) (137)

(138) (139) (140) (141) (142) (143) (144) (145) (146)

(147)

(148) (149)

A.; Ueda, Y. The Lowest Surface Free Energy Based on −CF3 Alignment. Langmuir 1999, 15, 4321–4323. Genzer, J.; Efimenko, K. Creating Long-Lived Superhydrophobic Polymer Surfaces Through Mechanically Assembled Monolayers. Science 2000, 290, 2130–2133. Wenzel, R. N. Resistance of Solid Surfaces to Wetting by Water. Ind. Eng. Chem. 1936, 28, 988–994. Wenzel, R. N. Surface Roughness and Contact Angle. J. Phys. Chem. 1949, 53, 1466–1467. Good, R. J. A Thermodynamic Derivation of Wenzel“S Modification of Young”S Equation for Contact Angles; Together with a Theory of Hysteresis 1. J. Am. Chem. Soc. 1952, 74, 5041–5042. Ben Wang; Li, J.; Wang, G.; Liang, W.; Zhang, Y.; Shi, L.; Guo, Z.; Liu, W. Methodology for Robust Superhydrophobic Fabrics and Sponges From in Situ Growth of Transition Metal/Metal Oxide Nanocrystals with Thiol Modification and Their Applications in Oil/Water Separation. ACS Appl. Mater. Interfaces 2013, 5, 1827–1839. Im, M.; Im, H.; Lee, J.-H.; Yoon, J.-B.; Choi, Y.-K. A Robust Superhydrophobic and Superoleophobic Surface with Inverse-Trapezoidal Microstructures on a Large Transparent Flexible Substrate. Soft Matter 2010, 6, 1401–1404. Lafuma, A.; Quéré, D. Superhydrophobic States. Nat Mater 2003, 2, 457–460. Tuteja, A.; Choi, W.; McKinley, G. H.; Cohen, R. E.; Rubner, M. F. Design Parameters for Superhydrophobicity and Superoleophobicity. MRS Bulletin 2011, 33, 752–758. Tsujii, K.; Yamamoto, T.; Onda, T.; Shibuichi, S. Super Oil-Repellent Surfaces. Angew. Chem. Int. Ed. Engl. 1997, 36, 1011–1012. Shibuichi, S.; Yamamoto, T.; Onda, T.; Tsujii, K. Super Water- and OilRepellent Surfaces Resulting From Fractal Structure. Journal of Colloid and Interface Science 1998, 208, 287–294. Marmur, A. From Hygrophilic to Superhygrophobic: Theoretical Conditions for Making High-Contact-Angle Surfaces From Low-Contact-Angle Materials. Langmuir 2008, 24, 7573–7579. Murakami, D.; Jinnai, H.; Takahara, A. Wetting Transition From the Cassie– Baxter State to the Wenzel State on Textured Polymer Surfaces. Langmuir 2014, 30, 2061–2067. Papadopoulos, P.; Mammen, L.; Deng, X.; Vollmer, D.; Butt, H.-J. How Superhydrophobicity Breaks Down. Proceedings of the National Academy of Sciences 2013, 110, 3254–3258. Zhou, H.; Wang, H.; Niu, H.; Gestos, A.; Lin, T. Robust, Self-Healing Superamphiphobic Fabrics Prepared by Two-Step Coating of FluoroContaining Polymer, Fluoroalkyl Silane, and Modified Silica Nanoparticles. Adv. Funct. Mater. 2013, 23, 1664–1670. Wang, H.; Zhou, H.; Gestos, A.; Fang, J.; Niu, H.; Ding, J.; Lin, T. Robust, Electro-Conductive, Self-Healing Superamphiphobic Fabric Prepared by OneStep Vapour-Phase Polymerisation of Poly(3,4-Ethylenedioxythiophene) in the Presence of Fluorinated Decyl Polyhedral Oligomeric Silsesquioxane and Fluorinated Alkyl Silane. Soft Matter 2013, 9, 277–282. Butt, H.-J.; Semprebon, C.; Papadopoulos, P.; Vollmer, D.; Brinkmann, M.; Ciccotti, M. Design Principles for Superamphiphobic Surfaces. Soft Matter 2012, 9, 418–428. Turri, S.; Valsecchi, R.; Viganò, M.; Levi, M. Hydrophilic–Oleophobic

ACS Paragon Plus Environment

Environmental Science & Technology

1080 1081 1082 1083 1084 1085 1086 1087 1088 1089 1090 1091 1092 1093 1094 1095 1096 1097 1098 1099 1100 1101 1102 1103 1104 1105 1106 1107 1108 1109 1110 1111 1112 1113 1114 1115 1116 1117 1118 1119 1120 1121 1122 1123 1124 1125 1126 1127 1128

(150) (151) (152) (153)

(154)

(155) (156)

(157) (158)

(159)

(160) (161) (162) (163) (164) (165)

Behaviour in Thin Films From Fluoromodified Nanoclays and Polystyrene. Polym. Bull. 2009, 63, 235–243. Brown, P. S.; Atkinson, O. D. L. A.; Badyal, J. P. S. Ultrafast Oleophobic– Hydrophilic Switching Surfaces for Antifogging, Self-Cleaning, and Oil–Water Separation. ACS Appl. Mater. Interfaces 2014, 6, 7504–7511. Kota, A. K.; Kwon, G.; Choi, W.; Mabry, J. M.; Tuteja, A. Hygro-Responsive Membranes for Effective Oil–Water Separation. Nat Comms 2012, 3, 1025. Yang, J.; Zhang, Z.; Xu, X.; Zhu, X.; Men, X.; Zhou, X. Superhydrophilic– Superoleophobic Coatings. Journal of Materials Chemistry 2012, 22, 2834– 2837. Liu, X.; Zhou, J.; Xue, Z.; Gao, J.; Meng, J.; Wang, S.; Jiang, L. Clam's Shell Inspired High‐Energy Inorganic Coatings with Underwater Low Adhesive Superoleophobicity. Adv. Mater. 2012, 24, 3401–3405. Cheng, Z.; Lai, H.; Du, Y.; Fu, K.; Hou, R.; Li, C.; Zhang, N.; Sun, K. pHInduced Reversible Wetting Transition Between the Underwater Superoleophilicity and Superoleophobicity. ACS Appl. Mater. Interfaces 2013, 6, 636–641. Sun, T.; Wang, G.; Feng, L.; Liu, B.; Ma, Y.; Jiang, L.; Zhu, D. Reversible Switching Between Superhydrophilicity and Superhydrophobicity. Angew. Chem. Int. Ed. Engl. 2004, 43, 357–360. Yang, J.; Zhang, Z.; Men, X.; Xu, X.; Zhu, X. Reversible Superhydrophobicity to Superhydrophilicity Switching of a Carbon Nanotube Film via Alternation of UV Irradiation and Dark Storage. 2010, 26, 10198–10202. Zhang, M.; Zhang, T.; Cui, T. Wettability Conversion From Superoleophobic to Superhydrophilic on Titania/Single-Walled Carbon Nanotube Composite Coatings. 2011, 27, 9295–9301. Tian, D.; Zhang, X.; Tian, Y.; Wu, Y.; Wang, X.; Zhai, J.; Jiang, L. PhotoInduced Water–Oil Separation Based on Switchable Superhydrophobicity– Superhydrophilicity and Underwater Superoleophobicity of the Aligned ZnO Nanorod Array-Coated Mesh Films. Journal of Materials Chemistry 2012, 22, 19652–19657. A Ahuja; J A Taylor; V Lifton; A A Sidorenko; T R Salamon; E J Lobaton; P Kolodner, A.; T N Krupenkin. Nanonails:  a Simple Geometrical Approach to Electrically Tunable Superlyophobic Surfaces. 2007, 24, 9–14. Kwon, G.; Kota, A. K.; Li, Y.; Sohani, A.; Mabry, J. M.; Tuteja, A. On‐Demand Separation of Oil‐Water Mixtures. Adv. Mater. 2012, 24, 3666–3671. Grigoryev, A.; Tokarev, I.; Kornev, K. G.; Luzinov, I.; Minko, S. Superomniphobic Magnetic Microtextures with Remote Wetting Control. J. Am. Chem. Soc. 2012, 134, 12916–12919. Liu, H.; Feng, L.; Zhai, J.; Jiang, L.; Zhu, D. Reversible Wettability of a Chemical Vapor Deposition Prepared ZnO Film Between Superhydrophobicity and Superhydrophilicity. Langmuir 2004, 20, 5659–5661. Xue, B.; Gao, L.; Hou, Y.; Liu, Z.; Jiang, L. Temperature Controlled Water/Oil Wettability of a Surface Fabricated by a Block Copolymer: Application as a Dual Water/Oil on–Off Switch. Adv. Mater. 2013, 25, 273–277. Mugele, F.; Baret, J.-C. Electrowetting: From Basics to Applications. J. Phys.: Condens. Matter 2005, 17, R705–R774. Nosonovsky, M. Materials Science: Slippery When Wetted. Nature 2011, 477, 412–413.

ACS Paragon Plus Environment

Page 32 of 44

Page 33 of 44

1129 1130 1131 1132 1133 1134 1135 1136 1137 1138 1139 1140 1141 1142 1143 1144 1145 1146 1147 1148 1149 1150 1151 1152 1153 1154 1155 1156 1157 1158 1159 1160 1161 1162 1163 1164 1165 1166 1167 1168 1169 1170 1171 1172 1173 1174 1175 1176 1177 1178

Environmental Science & Technology

(166) (167) (168)

(169)

(170)

(171) (172) (173) (174) (175) (176)

(177)

(178)

(179) (180) (181) (182)

Vogel, N.; Belisle, R. A.; Hatton, B.; Wong, T.-S.; Aizenberg, J. Transparency and Damage Tolerance of Patternable Omniphobic Lubricated Surfaces Based on Inverse Colloidal Monolayers. Nat Comms 2013, 4. Epstein, A. K.; Wong, T.-S.; Belisle, R. A.; Boggs, E. M.; Aizenberg, J. LiquidInfused Structured Surfaces with Exceptional Anti-Biofouling Performance. Proceedings of the National Academy of Sciences 2012, 109, 13182–13187. Howell, C.; Vu, T. L.; Lin, J. J.; Kolle, S.; Juthani, N.; Watson, E.; Weaver, J. C.; Alvarenga, J.; Aizenberg, J. Self-Replenishing Vascularized FoulingRelease Surfaces. ACS Appl. Mater. Interfaces 2014, 6, 13299–13307. Leslie, D. C.; Waterhouse, A.; Berthet, J. B.; Valentin, T. M.; Watters, A. L.; Jain, A.; Kim, P.; Hatton, B. D.; Nedder, A.; Donovan, K.; et al. A Bioinspired Omniphobic Surface Coating on Medical Devices Prevents Thrombosis and Biofouling. Nat Biotechnol 2014, 32, 1134–1140. Anand, S.; Paxson, A. T.; Dhiman, R.; Smith, J. D.; Varanasi, K. K. Enhanced Condensation on Lubricant-Impregnated Nanotextured Surfaces. ACS Nano 2012, 6, 10122–10129. Solomon, B. R.; Khalil, K. S.; Varanasi, K. K. Drag Reduction Using LubricantImpregnated Surfaces in Viscous Laminar Flow. Langmuir 2014, 30, 10970– 10976. Han, D.; Steckl, A. J. Superhydrophobic and Oleophobic Fibers by Coaxial Electrospinning. 2009, 25, 9454–9462. Guo, M.; Bin Ding; Li, X.; Wang, X.; Yu, J.; Wang, M. Amphiphobic Nanofibrous Silica Mats with Flexible and High-Heat-Resistant Properties. J. Phys. Chem. C 2009, 114, 916–921. Feng, L.; Li, S.; Li, Y.; Li, H.; Zhang, L.; Zhai, J.; Song, Y.; Liu, B.; Jiang, L.; Zhu, D. Super-Hydrophobic Surfaces: From Natural to Artificial. Adv. Mater. 2002, 14, 1857–1860. Bellanger, H.; Darmanin, T.; de Givenchy, E. T.; Guittard, F. Chemical and Physical Pathways for the Preparation of Superoleophobic Surfaces and Related Wetting Theories. Chem. Rev. 2014, 114, 2694–2716. Nyström, D.; Lindqvist, J.; Östmark, E.; Antoni, P.; Carlmark, A.; Hult, A.; Malmström, E. Superhydrophobic and Self-Cleaning Bio-Fiber Surfaces via ATRP and Subsequent Postfunctionalization. ACS Appl. Mater. Interfaces 2009, 1, 816–823. Xie, Q.; Xu, J.; Feng, L.; Jiang, L.; Tang, W.; Luo, X.; Han, C. C. Facile Creation of a Super‐Amphiphobic Coating Surface with Bionic Microstructure. Adv. Mater. 2004, 16, 302–305. Im, S. G.; Kusters, D.; Choi, W.; Baxamusa, S. H.; van de Sanden, M. C. M.; Gleason, K. K. Conformal Coverage of Poly(3,4-Ethylenedioxythiophene) Films with Tunable Nanoporosity via Oxidative Chemical Vapor Deposition. ACS Nano 2008, 2, 1959–1967. Minglin Ma; Yu Mao; Malancha Gupta; Karen K Gleason, A.; Rutledge, G. C. Superhydrophobic Fabrics Produced by Electrospinning and Chemical Vapor Deposition. Macromolecules 2005, 38, 9742–9748. Choi, W.; Tuteja, A.; Chhatre, S.; Mabry, J. M.; Cohen, R. E.; McKinley, G. H. Fabrics with Tunable Oleophobicity. Adv. Mater. 2009, 21, 2190–2195. Gao, Y.; Yangen, H.; Feng, S.; Gu, G.; Qing, F.-L. Novel Superhydrophobic and Highly Oleophobic PFPE-Modified Silica Nanocomposite. J Mater Sci 2010, 45, 460–466. Rajendra Kumar, R. T.; Mogensen, K. B.; Bøggild, P. Simple Approach to

ACS Paragon Plus Environment

Environmental Science & Technology

1179 1180 1181 1182 1183 1184 1185 1186 1187 1188 1189 1190 1191 1192 1193 1194 1195 1196 1197 1198 1199 1200 1201 1202 1203 1204 1205 1206 1207 1208 1209 1210 1211 1212 1213 1214 1215 1216 1217 1218 1219 1220 1221 1222 1223 1224 1225 1226 1227 1228

(183) (184) (185) (186) (187) (188) (189)

(190)

(191)

(192)

(193) (194)

(195)

(196) (197)

(198) (199)

Superamphiphobic Overhanging Silicon Nanostructures. J. Phys. Chem. C 2010, 114, 2936–2940. Aulin, C.; Yun, S. H.; Wågberg, L.; Lindström, T. Design of Highly Oleophobic Cellulose Surfaces From Structured Silicon Templates. ACS Appl. Mater. Interfaces 2009, 1, 2443–2452. Ceria, A.; Hauser, P. J. Atmospheric Plasma Treatment to Improve Durability of a Water and Oil Repellent Finishing for Acrylic Fabrics. Surface and Coatings Technology 2010, 204, 1535–1541. Kiuru, M.; Alakoski, E. Low Sliding Angles in Hydrophobic and Oleophobic Coatings Prepared with Plasma Discharge Method. Materials Letters 2004, 58, 2213–2216. Cao, L.; Di Gao. Transparent Superhydrophobic and Highly Oleophobic Coatings. Faraday Discuss. 2010, 146, 57–65. Xiong, D.; Liu, G.; Hong, L.; Duncan, E. J. S. Superamphiphobic Diblock Copolymer Coatings. Chem. Mater. 2011, 23, 4357–4366. Vilčnik, A.; Jerman, I.; Vuk, A. Š.; Koželj, M.; Orel, B.; Tomšič, B.; Simončič, B.; Kovač, J. Structural Properties and Antibacterial Effects of Hydrophobic and Oleophobic Sol−Gel Coatings for Cotton Fabrics. 2009, 25, 5869–5880. Masaya Hikita; Keiji Tanaka; Tetsuya Nakamura; Tisato Kajiyama, A.; Atsushi Takahara. Super-Liquid-Repellent Surfaces Prepared by Colloidal Silica Nanoparticles Covered with Fluoroalkyl Groups. 2005, 21, 7299–7302. Hsieh, C.-T.; Cheng, Y.-S.; Hsu, S.-M.; Lin, J.-Y. Water and Oil Repellency of Flexible Silica-Coated Polymeric Substrates. Applied Surface Science 2010, 256, 4867–4872. Li, H.; Wang, X.; Song, Y.; Liu, Y.; Li, Q.; Jiang, L.; Zhu, D. Super‐ “Amphiphobic” Aligned Carbon Nanotube Films. Angew. Chem. 2001, 113, 1793–1796. Xi, J.; Feng, L.; Jiang, L. A General Approach for Fabrication of Superhydrophobic and Superamphiphobic Surfaces. Appl. Phys. Lett. 2008, 92, 053102. Lee, H. J.; Owens, J. R. Design of Superhydrophobic Ultraoleophobic NyCo. J Mater Sci 2010, 45, 3247–3253. Srinivasan, S.; Chhatre, S. S.; Mabry, J. M.; Cohen, R. E.; McKinley, G. H. Solution Spraying of Poly(Methyl Methacrylate) Blends to Fabricate Microtextured, Superoleophobic Surfaces. Polymer 2011, 52, 3209–3218. Liu, X.; Wu, W.; Wang, X.; Luo, Z.; Liang, Y.; Zhou, F. A Replication Strategy for Complex Micro/Nanostructures with Superhydrophobicity and Superoleophobicity and High Contrast Adhesion. Soft Matter 2009, 5, 3097– 3105. Darmanin, T.; Guittard, F. Molecular Design of Conductive Polymers to Modulate Superoleophobic Properties. J. Am. Chem. Soc. 2009, 131, 7928– 7933. Yang Tian; Haiqing Liu, A.; Deng, Z. Electrochemical Growth of Gold Pyramidal Nanostructures:  Toward Super-Amphiphobic Surfaces. Chem. Mater. 2006, 18, 5820–5822. Akira Nakajima; Shin-ichi Koizumi; Toshiya Watanabe, A.; Kazuhito Hashimoto. Photoinduced Amphiphilic Surface on Polycrystalline Anatase TiO2 Thin Films. 2000, 16, 7048–7050. Xue, Z.; Wang, S.; Lin, L.; Chen, L.; Liu, M.; Feng, L.; Jiang, L. A Novel Superhydrophilic and Underwater Superoleophobic Hydrogel-Coated Mesh for

ACS Paragon Plus Environment

Page 34 of 44

Page 35 of 44

1229 1230 1231 1232 1233 1234 1235 1236 1237 1238 1239 1240 1241 1242 1243 1244 1245 1246 1247 1248 1249 1250 1251 1252 1253 1254 1255 1256 1257 1258 1259 1260 1261 1262 1263 1264 1265 1266 1267 1268 1269 1270 1271 1272 1273

Environmental Science & Technology

(200) (201) (202)

(203) (204) (205) (206)

(207) (208) (209) (210) (211) (212) (213) (214)

(215)

Oil/Water Separation. Adv. Mater. 2011, 23, 4270–4273. Wen, Q.; Di, J.; Jiang, L.; Yu, J.; Xu, R. Zeolite-Coated Mesh Film for Efficient Oil–Water Separation. Chem. Sci. 2013, 4, 591–595. Zhu, Y.; Zhang, F.; Wang, D.; Pei, X. F.; Zhang, W.; Jin, J. A Novel Zwitterionic Polyelectrolyte Grafted PVDF Membrane for Thoroughly Separating Oil From Water with Ultrahigh Efficiency. J. Mater. Chem. A 2013, 1, 5758–5765. Rohrbach, K.; Li, Y.; Zhu, H.; Liu, Z.; Dai, J.; Andreasen, J.; Hu, L. A Cellulose Based Hydrophilic, Oleophobic Hydrated Filter for Water/Oil Separation. Chemical Communications 2014, 50, 13296–13299. Akhtar, N.; Holm, V. R. A.; Thomas, P. J.; Svardal, B.; Askeland, S. H.; Holst, B. Underwater Superoleophobic Sapphire (0001) Surfaces. J. Phys. Chem. C 2015, 119, 15333–15338. Hejazi, V.; Nyong, A. E.; Rohatgi, P. K.; Nosonovsky, M. Wetting Transitions in Underwater Oleophobic Surface of Brass. Adv. Mater. 2012, 24, 5963–5966. Chhatre, S. S.; Tuteja, A.; Choi, W.; Revaux, A.; Smith, D.; Mabry, J. M.; McKinley, G. H.; Cohen, R. E. Thermal Annealing Treatment to Achieve Switchable and Reversible Oleophobicity on Fabrics. 2009, 25, 13625–13632. Yang, J.; Zhang, Z.; Men, X.; Xu, X.; Zhu, X.; Zhou, X.; Xue, Q. Rapid and Reversible Switching Between Superoleophobicity and Superoleophilicity in Response to Counterion Exchange. Journal of Colloid and Interface Science 2012, 366, 191–195. Fakhru’l-Razi, A.; Pendashteh, A.; Abdullah, L. C.; Biak, D. R. A.; Madaeni, S. S.; Abidin, Z. Z. Review of Technologies for Oil and Gas Produced Water Treatment. Journal of Hazardous Materials 2009, 170, 530–551. Cheryan, M.; Rajagopalan, N. Membrane Processing of Oily Streams. Wastewater Treatment and Waste Reduction. J. Membr. Sci. 1998, 151, 13– 28. Kingston, P. F. Long-Term Environmental Impact of Oil Spills. Spill Science & Technology Bulletin 2002, 7, 53–61. Rubio, J.; Souza, M. L.; Smith, R. W. Overview of Flotation as a Wastewater Treatment Technique. Minerals Engineering 2002, 15, 139–155. Gupta, V. K.; Ali, I.; Saleh, T. A.; Nayak, A.; Agarwal, S. Chemical Treatment Technologies for Waste-Water Recycling—an Overview. RSC Advances 2012, 2, 6380–6388. Zhu, Y.; Wang, D.; Jiang, L.; Jin, J. Recent Progress in Developing Advanced Membranes for Emulsified Oil/|Water Separation. NPG Asia Materials 2014, 6, e101. Chen, P.-C.; Xu, Z.-K. Mineral-Coated Polymer Membranes with Superhydrophilicity and Underwater Superoleophobicity for Effective Oil/Water Separation. Sci. Rep. 2013, 3. Gao, X.; Xu, L. P.; Xue, Z.; Feng, L.; Peng, J.; Wen, Y.; Wang, S.; Zhang, X. Dual‐Scaled Porous Nitrocellulose Membranes with Underwater Superoleophobicity for Highly Efficient Oil/Water Separation. Adv. Mater. 2014, 26, 1771–1775. Zhang, W.; Zhu, Y.; Liu, X.; Wang, D.; Li, J.; Jiang, L.; Jin, J. Salt‐Induced

1274

Fabrication of Superhydrophilic and Underwater Superoleophobic PAA‐G‐

1275 1276 1277

PVDF Membranes for Effective Separation of Oil‐in‐Water Emulsions. Angew. Chem. Int. Ed. Engl. 2014, 53, 856–860. Huang, X.; Lim, T.-T. Performance and Mechanism of a Hydrophobic–

(216)

ACS Paragon Plus Environment

Environmental Science & Technology

1278 1279 1280 1281 1282 1283 1284 1285 1286 1287 1288 1289 1290 1291 1292 1293 1294 1295 1296 1297 1298 1299 1300 1301 1302 1303 1304 1305 1306 1307 1308 1309 1310 1311 1312 1313 1314 1315 1316 1317 1318 1319 1320 1321 1322 1323 1324 1325 1326

(217) (218) (219) (220)

(221) (222)

(223)

(224)

(225)

(226) (227)

(228) (229) (230) (231)

Oleophilic Kapok Filter for Oil/Water Separation. Desalination 2006, 190, 295– 307. Zhu, X.; Loo, H.-E.; Bai, R. A Novel Membrane Showing Both Hydrophilic and Oleophobic Surface Properties and Its Non-Fouling Performances for Potential Water Treatment Applications. J. Membr. Sci. 2013, 436, 47–56. Lee, C. H.; Johnson, N.; Drelich, J.; Yap, Y. K. The Performance of Superhydrophobic and Superoleophilic Carbon Nanotube Meshes in Water– Oil Filtration. Carbon 2011, 49, 669–676. Tian, D.; Zhang, X.; Wang, X.; Zhai, J.; Jiang, L. Micro/Nanoscale Hierarchical Structured ZnO Mesh Film for Separation of Water and Oil. Phys. Chem. Chem. Phys. 2011, 13, 14606–14610. Lu, Y.; Sathasivam, S.; Song, J.; Chen, F.; Xu, W.; Carmalt, C. J.; Parkin, I. P. Creating Superhydrophobic Mild Steel Surfaces for Water Proofing and Oil– Water Separation. J. Mater. Chem. A 2014, 2, 11628–11634. Li, J.; Yan, L.; Zhao, Y.; Zha, F.; Wang, Q.; Lei, Z. One-Step Fabrication of Robust Fabrics with Both-Faced Superhydrophobicity for the Separation and Capture of Oil From Water. Phys. Chem. Chem. Phys. 2015, 17, 6451–6457. Zhang, W.; Shi, Z.; Zhang, F.; Liu, X.; Jin, J.; Jiang, L. Superhydrophobic and Superoleophilic PVDF Membranes for Effective Separation of Water‐in‐Oil Emulsions with High Flux. Adv. Mater. 2013, 25, 2071–2076. Zhang, F.; Zhang, W. B.; Shi, Z.; Wang, D.; Jin, J.; Jiang, L. Nanowire‐Haired Inorganic Membranes with Superhydrophilicity and Underwater Ultralow Adhesive Superoleophobicity for High‐Efficiency Oil/Water Separation. Adv. Mater. 2013, 25, 4192–4198. Yoon, H.; Na, S.-H.; Choi, J.-Y.; Latthe, S. S.; Swihart, M. T.; Al-Deyab, S. S.; Yoon, S. S. Gravity-Driven Hybrid Membrane for Oleophobic–Superhydrophilic Oil–Water Separation and Water Purification by Graphene. 2014, 30, 11761– 11769. Brown, P. S.; Bhushan, B. Mechanically Durable, Superoleophobic Coatings Prepared by Layer-by-Layer Technique for Anti-Smudge and Oil-Water Separation. Sci. Rep. 2015, 5, 8701. Ben Wang; Guo, Z. pH-Responsive Bidirectional Oil–Water Separation Material. Chemical Communications 2013, 49, 9416–9418. Tao, M.; Xue, L.; Liu, F.; Jiang, L. An Intelligent Superwetting PVDF Membrane Showing Switchable Transport Performance for Oil/Water Separation. Adv. Mater. 2014, 26, 2943–2948. Yuan, J.; Liu, X.; Akbulut, O.; Hu, J.; Suib, S. L.; Kong, J.; Stellacci, F. Superwetting Nanowire Membranes for Selective Absorption. Nature Nanotechnology 2008, 3, 332–336. Zhang, Y.; Wei, S.; Liu, F.; Du, Y.; Liu, S.; Ji, Y.; Yokoi, T.; Tatsumi, T.; Xiao, F.-S. Superhydrophobic Nanoporous Polymers as Efficient Adsorbents for Organic Compounds. Nano Today 2009, 4, 135–142. Cheng, M.; Gao, Y.; Guo, X.; Shi, Z.; Chen, J.-F.; Shi, F. A Functionally Integrated Device for Effective and Facile Oil Spill Cleanup. 2011, 27, 7371– 7375. Liang, H.-W.; Guan, Q.-F.; Chen, L.-F.; Zhu, Z.; Zhang, W.-J.; Yu, S. Macroscopic‐Scale Template Synthesis of Robust Carbonaceous Nanofiber Hydrogels and Aerogels and Their Applications. Angew. Chem. Int. Ed. Engl. 2012, 51, 5101–5105.

ACS Paragon Plus Environment

Page 36 of 44

Page 37 of 44

1327 1328 1329 1330 1331 1332 1333 1334 1335 1336 1337 1338 1339 1340 1341 1342 1343 1344 1345 1346 1347 1348 1349 1350 1351 1352 1353 1354 1355 1356 1357 1358 1359 1360 1361 1362 1363 1364 1365 1366 1367 1368 1369 1370 1371 1372 1373 1374 1375 1376 1377

Environmental Science & Technology

(232) (233) (234) (235) (236)

(237) (238) (239) (240)

(241)

(242) (243)

(244) (245) (246)

(247)

(248)

Wang, Z.; Xu, Y.; Liu, Y.; Shao, L. A Novel Mussel-Inspired Strategy Toward Superhydrophobic Surfaces for Self-Driven Crude Oil Spill Cleanup. J. Mater. Chem. A 2015, 3, 12171–12178. Hu, H.; Zhao, Z.; Gogotsi, Y.; Qiu, J. Compressible Carbon Nanotube– Graphene Hybrid Aerogels with Superhydrophobicity and Superoleophilicity for Oil Sorption. Environ. Sci. Technol. Lett. 2014, 1, 214–220. Baker, R. W. Future Directions of Membrane Gas Separation Technology. Ind. Eng. Chem. Res. 2002, 41, 1393–1411. Feng, C.; Khulbe, K. C.; Tabe, S. Volatile Organic Compound Removal by Membrane Gas Stripping Using Electro-Spun Nanofiber Membrane. Desalination 2012, 287, 98–102. Roudman, A. R.; DiGiano, F. A. Surface Energy of Experimental and Commercial Nanofiltration Membranes: Effects of Wetting and Natural Organic Matter Fouling. J. Membr. Sci. 2000, 175, 61–73. Luo, M.-L.; Zhao, J.-Q.; Tang, W.; Pu, C.-S. Hydrophilic Modification of Poly(Ether Sulfone) Ultrafiltration Membrane Surface by Self-Assembly of TiO2 Nanoparticles. Applied Surface Science 2005, 249, 76–84. Kang, G.; Liu, M.; Lin, B.; Cao, Y.; Yuan, Q. A Novel Method of Surface Modification on Thin-Film Composite Reverse Osmosis Membrane by Grafting Poly(Ethylene Glycol). Polymer 2007, 48, 1165–1170. Ghosh, A. K.; Jeong, B.-H.; Huang, X.; Hoek, E. M. V. Impacts of Reaction and Curing Conditions on Polyamide Composite Reverse Osmosis Membrane Properties. J. Membr. Sci. 2008, 311, 34–45. Tiraferri, A.; Kang, Y.; Giannelis, E. P.; Elimelech, M. Highly Hydrophilic ThinFilm Composite Forward Osmosis Membranes Functionalized with SurfaceTailored Nanoparticles. ACS Appl. Mater. Interfaces 2012, 4, 5044–5053. Liang, S.; Kang, Y.; Tiraferri, A.; Giannelis, E. P.; Huang, X.; Elimelech, M. Highly Hydrophilic Polyvinylidene Fluoride (PVDF) Ultrafiltration Membranes via Postfabrication Grafting of Surface-Tailored Silica Nanoparticles. ACS Appl. Mater. Interfaces 2013, 5, 6694–6703. Li, Y.; Su, Y.; Zhao, X.; He, X.; Zhang, R.; Zhao, J.; Fan, X.; Jiang, Z. Antifouling, High-Flux Nanofiltration Membranes Enabled by Dual Functional Polydopamine. Applied Materials & Interfaces 2014, 6, 5548–5557. Shaffer, D. L.; Arias Chavez, L. H.; Ben-Sasson, M.; Romero-Vargas Castrillón, S.; Yip, N. Y.; Elimelech, M. Desalination and Reuse of High-Salinity Shale Gas Produced Water: Drivers, Technologies, and Future Directions. Environ. Sci. Technol. 2013, 47, 9569–9583. Drioli, E.; Ali, A.; Macedonio, F. Membrane Distillation: Recent Developments and Perspectives. Desalination 2015, 356, 56–84. Xie, M.; Nghiem, L. D.; Price, W. E.; Elimelech, M. A Forward Osmosis– Membrane Distillation Hybrid Process for Direct Sewer Mining: System Performance and Limitations. Environ. Sci. Technol. 2013, 47, 13486–13493. Xie, M.; Nghiem, L. D.; Price, W. E.; Elimelech, M. Toward Resource Recovery From Wastewater: Extraction of Phosphorus From Digested Sludge Using a Hybrid Forward Osmosis–Membrane Distillation Process. Environ. Sci. Technol. Lett. 2014, 1, 191–195. Lin, S.; Yip, N. Y.; Cath, T. Y.; Osuji, C. O.; Elimelech, M. Hybrid Pressure Retarded Osmosis–Membrane Distillation System for Power Generation From Low-Grade Heat: Thermodynamic Analysis and Energy Efficiency. Environ. Sci. Technol. 2014, 48, 5306–5313. Wang, K. Y.; Teoh, M. M.; Nugroho, A.; Chung, T.-S. Integrated Forward

ACS Paragon Plus Environment

Environmental Science & Technology

1378 1379 1380 1381 1382 1383 1384 1385 1386 1387 1388 1389 1390 1391 1392 1393 1394 1395 1396 1397 1398 1399 1400 1401 1402 1403 1404 1405 1406 1407 1408 1409 1410 1411 1412 1413 1414 1415 1416 1417 1418 1419 1420 1421 1422 1423 1424 1425 1426 1427 1428

(249) (250) (251) (252) (253)

(254) (255) (256) (257)

(258) (259)

(260)

(261) (262)

(263)

(264)

Osmosis–Membrane Distillation (FO–MD) Hybrid System for the Concentration of Protein Solutions. Chemical Engineering Science 2011, 66, 2421–2430. Ge, Q.; Wang, P.; Wan, C.; Chung, T.-S. Polyelectrolyte-Promoted Forward Osmosis–Membrane Distillation (FO–MD) Hybrid Process for Dye Wastewater Treatment. Environ. Sci. Technol. 2012, 46, 6236–6243. Shaffer, D. L.; Werber, J. R.; Jaramillo, H.; Lin, S.; Elimelech, M. Forward Osmosis: Where Are We Now? Desalination 2015, 356, 271–284. Alkhudhiri, A.; Darwish, N.; Hilal, N. Membrane Distillation: a Comprehensive Review. Desalination 2012, 287, 2–18. Peng, P.; Fane, A. G.; Li, X. Desalination by Membrane Distillation Adopting a Hydrophilic Membrane. Desalination 2005, 173, 45–54. Razmjou, A.; Arifin, E.; Dong, G.; Mansouri, J.; Chen, V. Superhydrophobic Modification of TiO2 Nanocomposite PVDF Membranes for Applications in Membrane Distillation. J. Membr. Sci. 2012, 415-416, 850–863. Meng, S.; Ye, Y.; Mansouri, J.; Chen, V. Fouling and Crystallisation Behaviour of Superhydrophobic Nano-Composite PVDF Membranes in Direct Contact Membrane Distillation. J. Membr. Sci. 2014, 463, 102–112. Liao, Y.; Wang, R.; Fane, A. G. Fabrication of Bioinspired Composite Nanofiber Membranes with Robust Superhydrophobicity for Direct Contact Membrane Distillation. Environ. Sci. Technol. 2014, 48, 6335–6341. Lin, S.; Nejati, S.; Boo, C.; Hu, Y.; Osuji, C. O.; Elimelech, M. Omniphobic Membrane for Robust Membrane Distillation. Environ. Sci. Technol. Lett. 2014, 1, 443–447. Goosen, M. F. A.; Sablani, S. S.; Hinai, Al, H.; Obeidani, Al, S.; Al-Belushi, R.; Jackson, D. Fouling of Reverse Osmosis and Ultrafiltration Membranes: a Critical Review. Separation Science and Technology 2010, 39, 2261–2297. Rana, D.; Matsuura, T. Surface Modifications for Antifouling Membranes. Chem. Rev. 2010, 110, 2448–2471. Madaeni, S. S.; Ghaemi, N.; Alizadeh, A.; Joshaghani, M. Influence of PhotoInduced Superhydrophilicity of Titanium Dioxide Nanoparticles on the AntiFouling Performance of Ultrafiltration Membranes. Applied Surface Science 2011, 257, 6175–6180. Guo, H.; Ma, Y.; Sun, P.; Cui, S.; Qin, Z.; Liang, Y. Self-Cleaning and Antifouling Nanofiltration Membranes—Superhydrophilic Multilayered Polyelectrolyte/CSH Composite Films Towards Rejection of Dyes. RSC Advances 2015, 5, 63429–63438. Zou, L.; Vidalis, I.; Steele, D.; Michelmore, A.; Low, S. P.; Verberk, J. Q. J. C. Surface Hydrophilic Modification of RO Membranes by Plasma Polymerization for Low Organic Fouling. Journal of Membrane Science 2011, 369, 420–428. Tiraferri, A.; Kang, Y.; Giannelis, E. P.; Elimelech, M. Superhydrophilic ThinFilm Composite Forward Osmosis Membranes for Organic Fouling Control: Fouling Behavior and Antifouling Mechanisms. Environ. Sci. Technol. 2012, 46, 11135–11144. Romero-Vargas Castrillón, S.; Lu, X.; Shaffer, D. L.; Elimelech, M. Amine Enrichment and Poly(Ethylene Glycol) (PEG) Surface Modification of Thin-Film Composite Forward Osmosis Membranes for Organic Fouling Control. Journal of Membrane Science 2014, 450, 331–339. Shaffer, D. L.; Jaramillo, H.; Romero-Vargas Castrillón, S.; Lu, X.; Elimelech, M. Post-Fabrication Modification of Forward Osmosis Membranes with a Poly(Ethylene Glycol) Block Copolymer for Improved Organic Fouling Resistance. J. Membr. Sci. 2015, 490, 209–219.

ACS Paragon Plus Environment

Page 38 of 44

Page 39 of 44

1429 1430 1431 1432 1433 1434 1435 1436 1437 1438 1439 1440 1441 1442 1443 1444 1445 1446 1447 1448 1449 1450 1451 1452 1453 1454 1455 1456 1457 1458 1459 1460 1461 1462 1463 1464 1465 1466 1467 1468 1469 1470 1471 1472 1473 1474 1475 1476 1477 1478 1479

Environmental Science & Technology

(265) (266) (267) (268) (269)

(270) (271)

(272) (273) (274) (275) (276) (277)

(278)

(279) (280) (281)

(282)

Chen, S.; Li, L.; Zhao, C.; Zheng, J. Surface Hydration: Principles and Applications Toward Low-Fouling/Nonfouling Biomaterials. Polymer 2010, 51, 5283–5293. Israelachvili, J.; Pashley, R. The Hydrophobic Interaction Is Long Range, Decaying Exponentially with Distance. Nature 1982, 300, 341–342. Meyer, E. E.; Rosenberg, K. J.; Israelachvili, J. Recent Progress in Understanding Hydrophobic Interactions. Proceedings of the National Academy of Sciences 2006, 103, 15739–15746. Li, J.-H.; Xu, Y.-Y.; Zhu, L.-P.; Wang, J.-H.; Du, C.-H. Fabrication and Characterization of a Novel TiO2 Nanoparticle Self-Assembly Membrane with Improved Fouling Resistance. J. Membr. Sci. 2009, 326, 659–666. Freger, V.; Gilron, J.; Belfer, S. TFC Polyamide Membranes Modified by Grafting of Hydrophilic Polymers: an FT-IR/AFM/TEM Study. Journal of Membrane Science 2002, 209, 283–292. Wavhal, D. S.; Fisher, E. R. Hydrophilic Modification of Polyethersulfone Membranes by Low Temperature Plasma-Induced Graft Polymerization. Journal of Membrane Science 2002, 209, 255–269. Zhao, Y.-H.; Zhu, X.-Y.; Wee, K.-H.; Bai, R. Achieving Highly Effective NonBiofouling Performance for Polypropylene Membranes Modified by UVInduced Surface Graft Polymerization of Two Oppositely Charged Monomers. J. Phys. Chem. B 2010, 114, 2422–2429. Zhu, X.; Tu, W.; Wee, K.-H.; Bai, R. Effective and Low Fouling Oil/Water Separation by a Novel Hollow Fiber Membrane with Both Hydrophilic and Oleophobic Surface Properties. J. Membr. Sci. 2014, 466, 36–44. Yebra, D. M.; Kiil, S.; Dam-Johansen, K. Antifouling Technology—Past, Present and Future Steps Towards Efficient and Environmentally Friendly Antifouling Coatings. Progress in Organic Coatings 2004, 50, 75–104. Schultz, M. P.; Bendick, J. A.; Holm, E. R.; Hertel, W. M. Economic Impact of Biofouling on a Naval Surface Ship. Biofouling 2010, 27, 87–98. Delauney, L.; Compère, C.; Lehaitre, M. Biofouling Protection for Marine Environmental Sensors. Ocean Science 2010, 6, 503–511. Yang, W. J.; Neoh, K.-G.; Kang, E.-T.; Teo, S. L.-M.; Rittschof, D. Polymer Brush Coatings for Combating Marine Biofouling. Progress in Polymer Science 2014, 39, 1017–1042. Ferrari, M.; Benedetti, A.; Santini, E.; Ravera, F.; Liggieri, L.; Guzman, E.; Cirisano, F. Biofouling Control by Superhydrophobic Surfaces in Shallow Euphotic Seawater. Colloids and Surfaces A: Physicochemical and Engineering Aspects 2015, 480, 369–375. Block, J. C.; Haudidier, K.; Paquin, J. L.; Miazga, J.; Levi, Y. Biofilm Accumulation in Drinking Water Distribution Systems. Biofouling 1993, 6, 333– 343. Flemming, H.-C. Reverse Osmosis Membrane Biofouling. Experimental Thermal and Fluid Science 1997, 14, 382–391. Baker, J. S.; Dudley, L. Y. Biofouling in Membrane Systems — a Review. Desalination 1998, 118, 81–89. Kwan, S. E.; Bar-Zeev, E.; Elimelech, M. Biofouling in Forward Osmosis and Reverse Osmosis: Measurements and Mechanisms. J. Membr. Sci. 2015, 493, 703–708. Kerr, A.; Cowling, M. J.; Beveridge, C. M.; Smith, M. J.; Parr, A. C. S.; Head, R. M.; Davenport, J.; Hodgkiess, T. The Early Stages of Marine Biofouling and Its Effect on Two Types of Optical Sensors. Environment International 1998,

ACS Paragon Plus Environment

Environmental Science & Technology

1480 1481 1482 1483 1484 1485 1486 1487 1488 1489 1490 1491 1492 1493 1494 1495 1496 1497 1498 1499 1500 1501 1502 1503 1504 1505 1506 1507 1508 1509 1510 1511 1512 1513 1514 1515 1516 1517 1518 1519 1520 1521 1522 1523 1524 1525 1526 1527 1528 1529

(283)

(284) (285) (286) (287)

(288) (289)

(290)

(291) (292) (293) (294) (295)

(296)

(297)

(298)

24, 331–343. Chambers, L. D.; Stokes, K. R.; Walsh, F. C.; Wood, R. J. K. Modern Approaches to Marine Antifouling Coatings. Surface and Coatings Technology 2006, 201, 3642–3652. Terlizzi, A.; Fraschetti, S.; Gianguzza, P.; Faimali, M.; Boero, F. Environmental Impact of Antifouling Technologies: State of the Art and Perspectives. Aquatic Conservation: Marine and Freshwater Ecosystems 2001, 11, 311–317. Gittens, J. E.; Smith, T. J.; Suleiman, R.; Akid, R. Current and Emerging Environmentally-Friendly Systems for Fouling Control in the Marine Environment. Biotechnology Advances 2013, 31, 1738–1753. Tang, P.; Zhang, W.-J.; Wang, Y.; Zhang, B.; Wang, H. Effect of Superhydrophobic Surface of Titanium on Staphylococcus Aureus Adhesion. J. of Nanomater 2011, 2011, articleID178921. Privett, B. J.; Youn, J.; Hong, S. A.; Lee, J.; Han, J.; Shin, J. H.; Schoenfisch, M. H. Antibacterial Fluorinated Silica Colloid Superhydrophobic Surfaces. Langmuir 2011, 27, 9597–9601. Crick, C. R.; Ismail, S.; Pratten, J.; Parkin, I. P. An Investigation Into Bacterial Attachment to an Elastomeric Superhydrophobic Surface Prepared via Aerosol Assisted Deposition. Thin Solid Films 2011, 519, 3722–3727. Fadeeva, E.; Truong, V. K.; Stiesch, M.; Chichkov, B. N.; Crawford, R. J.; Wang, J.; Ivanova, E. P. Bacterial Retention on Superhydrophobic Titanium Surfaces Fabricated by Femtosecond Laser Ablation. Langmuir 2011, 27, 3012–3019. Freschauf, L. R.; McLane, J.; Sharma, H.; Khine, M. Shrink-Induced Superhydrophobic and Antibacterial Surfaces in Consumer Plastics. PLoS ONE 2012, 7, e40987. Pechook, S.; Sudakov, K.; Polishchuk, I.; Ostrov, I.; Zakin, V.; Pokroy, B.; Shemesh, M. Bioinspired Passive Anti-Biofouling Surfaces Preventing Biofilm Formation. J. Mater. Chem. B 2015, 3, 1371–1378. Zhang, H.; Lamb, R.; Lewis, J. Engineering Nanoscale Roughness on Hydrophobic Surface—Preliminary Assessment of Fouling Behaviour. Sci. Technol. Adv. Mater. 2005, 6, 236–239. Bobji, M. S.; Kumar, S. V.; Asthana, A.; Govardhan, R. N. Underwater Sustainability of the “Cassie” State of Wetting. Langmuir 2009, 25, 12120– 12126. Zhang, X.; Wang, L.; Levänen, E. Superhydrophobic Surfaces for the Reduction of Bacterial Adhesion. RSC Adv. 2013, 3, 12003–12020. Ista, L. K.; Callow, M. E.; Finlay, J. A.; Coleman, S. E.; Nolasco, A. C.; Simons, R. H.; Callow, J. A.; Lopez, G. P. Effect of Substratum Surface Chemistry and Surface Energy on Attachment of Marine Bacteria and Algal Spores. Appl. Environ. Microbiol. 2004, 70, 4151–4157. Zheng, J.-M.; Chin, W.-C.; Khijniak, E.; Khijniak, E., Jr.; Pollack, G. H. Surfaces and Interfacial Water: Evidence That Hydrophilic Surfaces Have Long-Range Impact. Advances in Colloid and Interface Science 2006, 127, 19–27. Bixler, G. D.; Bhushan, B. Biofouling: Lessons From Nature. Philosophical Transactions of the Royal Society of London A: Mathematical, Physical and Engineering Sciences 2012, 370, 2381–2417. Ma, H.; Hyun, J.; Stiller, P.; Chilkoti, A. “Non‐Fouling” Oligo(Ethylene Glycol)‐ Functionalized Polymer Brushes Synthesized by Surface‐Initiated Atom

ACS Paragon Plus Environment

Page 40 of 44

Page 41 of 44

1530 1531 1532 1533 1534 1535 1536 1537 1538 1539 1540 1541 1542 1543 1544 1545 1546 1547 1548 1549 1550 1551 1552 1553 1554 1555 1556 1557 1558 1559 1560 1561 1562 1563 1564 1565 1566 1567 1568 1569 1570 1571 1572 1573 1574 1575 1576 1577 1578 1579 1580

Environmental Science & Technology

(299)

(300)

(301) (302)

(303) (304) (305)

(306) (307) (308) (309) (310)

(311) (312) (313) (314) (315) (316)

Transfer Radical Polymerization. Adv. Mater. 2004, 16, 338–341. Statz, A.; Finlay, J.; Dalsin, J.; Callow, M.; Callow, J. A.; Messersmith, P. B. Algal Antifouling and Fouling-Release Properties of Metal Surfaces Coated with a Polymer Inspired by Marine Mussels. Biofouling 2007, 22, 391–399. Schilp, S.; Kueller, A.; Rosenhahn, A.; Grunze, M.; Pettitt, M. E.; Callow, M. E.; Callow, J. A. Settlement and Adhesion of Algal Cells to Hexa(Ethylene Glycol)Containing Self-Assembled Monolayers with Systematically Changed Wetting Properties. Biointerphases 2007, 2, 143–150. Krishnan, S.; Weinman, C. J.; Ober, C. K. Advances in Polymers for AntiBiofouling Surfaces. Journal of Materials Chemistry 2008, 18, 3405–3413. Carman, M. L.; Estes, T. G.; Feinberg, A. W.; Schumacher, J. F.; Wilkerson, W.; Wilson, L. H.; Callow, M. E.; Callow, J. A.; Brennan, A. B. Engineered Antifouling Microtopographies – Correlating Wettability with Cell Attachment. Biofouling 2007, 22, 11–21. Kesel, A.; Liedert, R. Learning From Nature: Non-Toxic Biofouling Control by Shark Skin Effect; Comparative Biochemistry and Physiology Part A: l, 2007. Ralston, E.; Swain, G. Bioinspiration—the Solution for Biofouling Control? Bioinspir. Biomim. 2009, 4, 015007. Schumacher, J. F.; Aldred, N.; Callow, M. E.; Finlay, J. A.; Callow, J. A.; Clare, A. S.; Brennan, A. B. Species-Specific Engineered Antifouling Topographies: Correlations Between the Settlement of Algal Zoospores and Barnacle Cyprids. Biofouling 2007, 23, 307–317. Mikic, B. B. On Mechanism of Dropwise Condensation. International Journal of Heat and Mass Transfer 1969, 12, 1311–1323. Rose, J. W. Dropwise Condensation Theory and Experiment: a Review. Proceedings of the Institution of Mechanical Engineers, Part A: Journal of Power and Energy 2002, 216, 115–128. Vemuri, S.; Kim, K. J. An Experimental and Theoretical Study on the Concept of Dropwise Condensation. International Journal of Heat and Mass Transfer 2006, 49, 649–657. Leach, R. N.; Stevens, F.; Langford, S. C.; Dickinson, J. T. Dropwise Condensation: Experiments and Simulations of Nucleation and Growth of Water Drops in a Cooling System. Langmuir 2006, 22, 8864–8872. Miljkovic, N.; Enright, R.; Nam, Y.; Lopez, K.; Dou, N.; Sack, J.; Wang, E. N. Jumping-Droplet-Enhanced Condensation on Scalable Superhydrophobic Nanostructured Surfaces. Nano Lett. 2012, 13, 179–187. Attinger, D.; Frankiewicz, C.; Betz, A. R.; Schutzius, T. M.; Ganguly, R.; Das, A.; Kim, C.-J.; Megaridis, C. M. Surface Engineering for Phase Change Heat Transfer: a Review. MRS Energy & Sustainability 2014, 1, E4. Alizadeh, A.; Bahadur, V.; Kulkarni, A.; Yamada, M.; Ruud, J. A. Hydrophobic Surfaces for Control and Enhancement of Water Phase Transitions. MRS Bulletin 2013, 38, 407–411. US Department of Energy, Annual Energy Review (2009) (accessed Aug 17, 2015). Narhe, R. D.; Khandkar, M. D.; Shelke, P. B.; Limaye, A. V.; Beysens, D. A. Condensation-Induced Jumping Water Drops. Phys. Rev. E 2009, 80, 031604. Warsinger, D. E. M.; Swaminathan, J.; Maswadeh, L. A.; Lienhard, J. H., V. Superhydrophobic Condenser Surfaces for Air Gap Membrane Distillation. J. Membr. Sci. 2015, 492, 578–587. Cheng, J.; Vandadi, A.; Chen, C.-L. Condensation Heat Transfer on Two-Tier Superhydrophobic Surfaces. Appl. Phys. Lett. 2012, 101, 131909.

ACS Paragon Plus Environment

Environmental Science & Technology

1581 1582 1583 1584 1585 1586 1587 1588 1589 1590 1591 1592 1593 1594 1595 1596 1597 1598 1599 1600 1601 1602 1603 1604 1605 1606 1607 1608 1609 1610 1611 1612 1613 1614 1615 1616 1617 1618 1619 1620 1621 1622 1623 1624 1625 1626 1627 1628 1629 1630 1631

(317) (318) (319)

(320)

(321) (322) (323) (324) (325)

(326) (327) (328) (329) (330) (331) (332)

(333) (334)

Miljkovic, N.; Enright, R.; Wang, E. N. Effect of Droplet Morphology on Growth Dynamics and Heat Transfer During Condensation on Superhydrophobic Nanostructured Surfaces. ACS Nano 2012, 6, 1776–1785. Boreyko, J. B.; Chen, C.-H. Self-Propelled Dropwise Condensate on Superhydrophobic Surfaces. Phys. Rev. Lett. 2009, 103, 184501. Dietz, C.; Rykaczewski, K.; Fedorov, A. G.; Joshi, Y. Visualization of Droplet Departure on a Superhydrophobic Surface and Implications to Heat Transfer Enhancement During Dropwise Condensation. Appl. Phys. Lett. 2010, 97, 033104. Rykaczewski, K.; Scott, J. H. J.; Rajauria, S.; Chinn, J.; Chinn, A. M.; Jones, W. Three Dimensional Aspects of Droplet Coalescence During Dropwise Condensation on Superhydrophobic Surfaces. Soft Matter 2011, 7, 8749– 8752. Kim, S.; Kim, K. J. Dropwise Condensation Modeling Suitable for Superhydrophobic Surfaces. J. Heat Transfer 2011, 133, 081502. Rykaczewski, K. Microdroplet Growth Mechanism During Water Condensation on Superhydrophobic Surfaces. Langmuir 2012, 28, 7720–7729. Ma, X.; Wang, S.; Lan, Z.; Peng, B.; Ma, H. B.; Cheng, P. Wetting Mode Evolution of Steam Dropwise Condensation on Superhydrophobic Surface in the Presence of Noncondensable Gas. J. Heat Transfer 2012, 134, 021501. Lo, C.-W.; Wang, C.-C.; Lu, M.-C. Scale Effect on Dropwise Condensation on Superhydrophobic Surfaces. ACS Appl. Mater. Interfaces 2014, 6, 14353– 14359. Chen, X.; Wu, J.; Ma, R.; Hua, M.; Koratkar, N.; Yao, S.; Wang, Z. Nanograssed Micropyramidal Architectures for Continuous Dropwise Condensation. Adv. Funct. Mater. 2011, 21, 4617–4623. Preston, D. J.; Mafra, D. L.; Miljkovic, N.; Kong, J. Scalable Graphene Coatings for Enhanced Condensation Heat Transfer. Nano Lett. 2015, 15, 2902–2909. Staff, U. N. E. P. Sourcebook of Alternative Technologies for Freshwater Augmentation in Latin America and the Caribbean; 1999. Zheng, Y.; Bai, H.; Huang, Z.; Tian, X.; Nie, F. Q.; Zhao, Y.; Zhai, J.; Jiang, L. Directional Water Collection on Wetted Spider Silk. Nature 2010, 463, 640– 643. Lee, A.; Moon, M.-W.; Lim, H.; Kim, W.-D.; Kim, H.-Y. Water Harvest via Dewing. Langmuir 2012, 28, 10183–10191. Zhang, L.; Wu, J.; Hedhili, M. N.; Yang, X.; Wang, P. Inkjet Printing for Direct Micropatterning of a Superhydrophobic Surface: Toward Biomimetic Fog Harvesting Surfaces. J. Mater. Chem. A 2015, 3, 2844–2852. Choo, S.; Choi, H.-J.; Lee, H. Water-Collecting Behavior of Nanostructured Surfaces with Special Wettability. Applied Surface Science 2015, 324, 563– 568. Xinping Ouyang; Xueqing Qiu; Hongming Lou, A.; Yang, D. Corrosion and Scale Inhibition Properties of Sodium Lignosulfonate and Its Potential Application in Recirculating Cooling Water System. Ind. Eng. Chem. Res. 2006, 45, 5716–5721. Zhang, F.; Zhao, L.; Chen, H.; Xu, S.; Evans, D. G.; Duan, X. Corrosion Resistance of Superhydrophobic Layered Double Hydroxide Films on Aluminum. Angew. Chem. Int. Ed. Engl. 2008, 47, 2466–2469. Ishizaki, T.; Masuda, Y.; Sakamoto, M. Corrosion Resistance and Durability of Superhydrophobic Surface Formed on Magnesium Alloy Coated with

ACS Paragon Plus Environment

Page 42 of 44

Page 43 of 44

1632 1633 1634 1635 1636 1637 1638 1639 1640 1641 1642 1643 1644 1645 1646 1647 1648 1649 1650 1651 1652 1653 1654 1655 1656 1657 1658 1659 1660 1661 1662 1663 1664 1665 1666 1667 1668 1669 1670 1671 1672 1673 1674 1675 1676 1677 1678 1679 1680 1681 1682

Environmental Science & Technology

(335) (336) (337) (338) (339)

(340) (341) (342) (343) (344) (345) (346) (347) (348) (349) (350) (351)

(352)

Nanostructured Cerium Oxide Film and Fluoroalkylsilane Molecules in Corrosive NaCl Aqueous Solution. Langmuir 2011, 27, 4780–4788. Mohamed, A.; Abdullah, A. M.; Younan, N. A. Corrosion Behavior of Superhydrophobic Surfaces: a Review. Arabian Journal of Chemistry 2015, 8, 749–765. Daniello, R. J.; Waterhouse, N. E.; Rothstein, J. P. Drag Reduction in Turbulent Flows Over Superhydrophobic Surfaces. Physics of Fluids 2009, 21, 085103. Yogo, K.; Ishikawa, M. Recent Progress in Environmental Catalytic Technology. Catalysis Surveys from Asia 2000, 4, 83–90. Sharma, S. D.; Singh, D.; Saini, K. K.; Kant, C.; Sharma, V.; Jain, S. C.; Sharma, C. P. Sol–Gel-Derived Super-Hydrophilic Nickel Doped TiO2 Film as Active Photo-Catalyst. Applied Catalysis A: General 2006, 314, 40–46. Yamashita, H.; Nishio, S.; Katayama, I.; Nishiyama, N.; Fujii, H. Photo-Induced Super-Hydrophilic Property and Photocatalysis on Transparent Ti-Containing Mesoporous Silica Thin Films. Catalysis Today 2006, 111, 254–258. Lv, Z.; Sun, Q.; Meng, X.; Xiao, F.-S. Superhydrophilic Mesoporous Sulfonated Melamine–Formaldehyde Resin Supported Palladium Nanoparticles as an Efficient Catalyst for Biofuel Upgrade. J. Mater. Chem. A 2013, 1, 8630–8635. Hoffmann, M. R.; Martin, S. T.; Choi, W.; Bahnemann, D. W. Environmental Applications of Semiconductor Photocatalysis. Chem. Rev. 2002, 95, 69–96. Zhang, H.; Chen, G.; Bahnemann, D. W. Photoelectrocatalytic Materials for Environmental Applications. Journal of Materials Chemistry 2009, 19, 5089– 5121. 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 : Article : Nature. Nature 2008, 452, 301–310. Geise, G. M.; Lee, H. S.; Miller, D. J.; Freeman, B. D.; McGrath, J. E.; Paul, D. R. Water Purification by Membranes: the Role of Polymer Science. J. Polym. Sci. B Polym. Phys. 2010, 48, 1685–1718. Lee, K. P.; Arnot, T. C.; Mattia, D. A Review of Reverse Osmosis Membrane Materials for Desalination—Development to Date and Future Potential. J. Membr. Sci. 2011, 370, 1–22. Ramamoorthy, R.; Dutta, P. K.; Akbar, S. A. Oxygen Sensors: Materials, Methods, Designs and Applications. J Mater Sci 2003, 38, 4271–4282. Wang, L.; Ma, W.; Xu, L.; Chen, W.; Zhu, Y.; Xu, C.; Kotov, N. A. NanoparticleBased Environmental Sensors. Materials Science and Engineering: R: Reports 2010, 70, 265–274. Wiesner, M. R.; Bottero, J.-Y. Environmental Nanotechnology; McGraw-Hill Professional, 2007. Mauter, M. S.; Elimelech, M. Environmental Applications of Carbon-Based Nanomaterials. Environ. Sci. Technol. 2008, 42, 5843–5859. Li, Q.; Mahendra, S.; Lyon, D.; Brunet, L.; Liga, M. Antimicrobial Nanomaterials for Water Disinfection and Microbial Control: Potential Applications and Implications. Water Research 2008, 42, 4591–4602. Hu, X.; Li, G.; Yu, J. C. Design, Fabrication, and Modification of Nanostructured Semiconductor Materials for Environmental and Energy Applications. Langmuir 2010, 26, 3031–3039. Perreault, F.; de Faria, A. F.; Elimelech, M. Environmental Applications of Graphene-Based Nanomaterials. Chem. Soc. Rev. 2015, 44, 5861–5896.

ACS Paragon Plus Environment

Environmental Applications

Environmental Science & Technology

Page 44 of 44

Surfaces with Special Wettability ACS Paragon Plus Environment

Environmental Applications of Interfacial Materials with Special Wettability.

Interfacial materials with special wettability have become a burgeoning research area in materials science in the past decade. The unique surface prop...
3MB Sizes 6 Downloads 11 Views