The cost of water transport for irrigating drought-endurable plants in desertification areas makes it important to develop other water sources. Research shows that freshwater produced by dewing could satisfy the water requirement during germination of desert plants, therefore, functional materials that promote dew formation provide solutions for reduction of plant irrigation costs in desertification regions. In this review, feasibility of utilizing trace irrigation for ensuring survival of desert plants has been demonstrated. The technologies of preparing water harvesting materials with modified microstructure and wettability arrangement have been introduced, it has been shown that surface embedded with a bump array which has counter wettability compared with its plane section is a common morphology adopted by current works. After comparing climates in desertification regions with those in dewing chambers, it has been found that currently, the expected values of dew productivities of most water harvesting materials in deserted areas will not be as efficient as they performed in experiments due to low relative humidity. However, hydrophobic surface with submicron scale hydrophilic spherical cavity array produced by nanosphere lithography has shown reliable prospects in reducing the energy barrier of heterogeneous nucleation and thus become a more potential medium in dew water production.

  • Water supply is the key to guarantee the survival of desert plants.

  • Water consumption of some desert plants can be satisfied by trace water produced from dewing.

  • Low moisture is an obstacle that limits the dew productivity of current dewing materials.

  • Nanosphere lithography has the potential for upgrading the dry-adaptation of dewing materials.

  • Nano-/submicron cavity is critical for realizing early nucleation.

Desertification is a natural phenomenon that is characterized with a decline of soil fertility that is caused by drought, erosion, or salinization (Verón et al. 2006; Wang 2014). Severe desertification leads to catastrophic climates such as sandstorm and smog as well as migration of residents due to farmland and infrastructure destruction (Tsunekawa & Haregeweyn 2017). Vegetation restoration is the fundamental solution for reclaiming deserted land and the key to sustaining the flora planted in desertification areas is the delivery of fresh water for seedlings timely and accurate (Fan & Zhou 2001; Li et al. 2020; Wei et al. 2021). After 10 years of exploration of the desertification reclaim in Northwest China from our research group, three recommendable viewpoints have been offered to describe the current contradiction between water supply and afforesting (Zhang 2009; Zhang & Du 2011; Du et al. 2015): first of all, in areas with weak infrastructure and serious desertification, to build water supply systems such as pump stations or pipe nets are almost unrealizable, as a result, offsite water transport, i.e., delivering water by vehicles from other cities that are more than 50 km away is the only way to reinforce fresh water. Due to the long transportation distance, the delivery charge of 1 tonne of water is up to hundreds of RMB (Renminbi, the Chinese currency), which causes high irrigation cost in the process of afforestation. In areas where water stations are available, conventional infiltrating or drop irrigation has become another option for water supply. According to the experience gained during afforestation in the Ulan Buh desert (Inner Mongolia, China), the expense of afforestation when using conventional infiltrating or drop irrigation was about 0.03 RMB/m2 per day, which was 3 times larger than that generated by utilizing of water retaining agents (absorbent resins) and 100 times larger than that generated by utilizing of water bags embedded with water conduction fiber. Therefore, when the finance for water supply is insufficient, the water conduction to plants will stop temporarily, which increases the probability that young plants are threatened by dehydration. Secondly, drought-endurable plants have been proven to be the most suitable species that are capable of long-term survival in arid/semi-arid desertification areas. Nitraria tangutorumCynomorium songaricum and Haloxylon ammodendronCistanche have been chosen by our research team as two symbiotic combinations for vegetation restoration in the desert. On the one hand, N. tangutorum and H. ammodendron floras enable an initial rehabilitation of deserted soil; C. songaricum and Cistanche are valuable Chinese traditional medicine with a market price of about 200–400 RMB/kg, which will also bring considerable economic benefits to local residents. On the other hand, the normal annual average water consumption when irrigating seeds or roots of above mentioned symbiotic combinations is only about 20 L/m2(including losses caused by evaporation and seepage), which could be satisfied by our in situ irrigation devices (Figure 1(a)) (Qu et al. 2017; Qu & Zhang 2020). Furthermore, with the help of water conducting fiber developed by our team which has adjustable water permeability that served as a junction between the water source (water pipe outlets of our in situ irrigation devices) and roots of plants (Figure 1(b)) (Du et al. 2015), the water consumption of the above mentioned symbiotic combination could be reduced to one-tenth of the normal value due to the low wastage rate (water is supplied directly by fibers near the roots which reduces losses caused by evaporation or seepage). For instance, we implemented large-scale planting of the above symbiotic combinations in MinQin county (Northwest China) (Figure 1(a)–1(c)) and Abu Dhabi desert (western of the United Arab Emirates) (Figure 1(d)), benefiting from the adjustable water conducting fiber, the monthly water consumption of nearly 60,000 m2H. ammodendron–Cistanche flora has been supported by only 2 tons of water.
Figure 1

Desertification control with trace quantity irrigation: (a)with help of the trace irrigation device, water consumption of nearly 60,000 m2 by Haloxylon ammodendron–Cistanche symbiotic flora (in MinQin county) was supported by 2 tons of water per month; (b)outlets of pipes of our trace irrigation device were embedded with self-adjustable water conduction fibers; (c) Cistanche gained near a water pipe; (d) H. ammodendron flora (irrigated with water bags that embedded with water conduction fibers) in Abu Dhabi desert (western of the United Arab Emirates).

Figure 1

Desertification control with trace quantity irrigation: (a)with help of the trace irrigation device, water consumption of nearly 60,000 m2 by Haloxylon ammodendron–Cistanche symbiotic flora (in MinQin county) was supported by 2 tons of water per month; (b)outlets of pipes of our trace irrigation device were embedded with self-adjustable water conduction fibers; (c) Cistanche gained near a water pipe; (d) H. ammodendron flora (irrigated with water bags that embedded with water conduction fibers) in Abu Dhabi desert (western of the United Arab Emirates).

Close modal

The above achievements imply that the utilization of trace quantity irrigation rather than conventional infiltrating or drop irrigation will also ensure the survival of flora while significantly reducing the consumption and cost produced by water-related works. Thirdly, drought-endurable plants such as Agropyron mongolicum, which is characterized by high cell osmotic pressure and slow metabolism, can be irrigated even by utilizing dew water. During our research in Yulin city (ShaanXi, China), we have also found that large number of dew droplets formed on the surface of local plants early in the morning. As a result, trace quantity irrigating by dew water generated from the condensation of vapor shows unique potential in realizing an in situ trace irrigation (water supply does not depend on direct water transportation, but on condensate formed by local gas–liquid transition) and reducing cost produced by water-related works to a minimum.

To harvest water from gas–liquid transition and to collect condensed water as an irrigation source for plants in arid/semi-arid areas is not an imagination. Researchers developed composite surfaces which accelerate the growth rate of dew droplets on surfaces and increase the amount of water collected from droplet detachment. The concept of such water harvesting materials is shown in Figure 2.
Figure 2

Principle of the water harvesting surface with a hydrophilic–hydrophobic pattern.

Figure 2

Principle of the water harvesting surface with a hydrophilic–hydrophobic pattern.

Close modal

The surface of such material will be modified to possess an alternating hydrophilic and hydrophobic pattern. A non-uniformly wettability distribution is a critical factor that results in the promotion of dewing efficiency. When a dew droplet is lying on a spot with a wettability gradient, the contact angle (CA) at the front and the rear of the droplet will be different (Beysens 2018). According to the Young-equation, the contact angle difference causes an imbalance of the inner pressure inside the dew droplet, which leads to the motion of the dew drop in the direction of the wettability gradient. Based on Young-equation, the driven force formed by contact angle difference is F = γlg (cosθa–cosθb)Δl, where θa, θb represent the front and rear contact angles (Figure 2) of the dew droplet that is lying on the hydrophilic–hydrophobic junction; γlg represents the surface tension of liquid–gas interfacial boundary. Driven by the force F, droplets migrate and collide with dew drops located on the hydrophilic section of hybrid surfaces. Therefore, the growth rate of the volume of droplets which lie on the hydrophilic section of a hybrid surface will be accelerated by not only the diffusion of water molecules but also the inter-droplet collision and fusion. The literature stated that after a droplet reaches its stable volume corresponding to the current temperature, the influence of inter-droplet collision on the rate of droplet growth is much greater than that of diffusion of water molecules which is caused by moisture gradient between the atmosphere and the droplet surface (Sikarwar et al. 2012). Eventually, large droplets fall from the surface and are collected by soil or containers when the gravity is greater than the adhesion force. In a word, currently, the hybrid surface, i.e., hybrid material for water harvesting is material whose surface consists of alternating hydrophilic and hydrophobic patterns which motivates the droplet migration in the direction of the hydrophilic section by an imbalanced internal force caused by a contact angle difference. Consequently, dew droplets grow due to inter-droplet collision and detach the surface due to gravity.

Water harvesting materials which have only been modified on surface wettability arrangement have been studied since 1992 (Chaudhury & Whitesides 1992). Plenty of comprehensive reviews have been offered in which the preparation processes and dewing efficiencies in condensation chamber of such materials have been reported (Brown & Bhushan 2016; Zhang et al. 2016b; Sun & Guo 2019; Chen & Zhang 2020; Yang et al. 2020; Lv et al. 2022). What these researchers had in common is that they focused on how to increase the value of the wettability gradient on the surface of water harvesting materials, i.e., to develop new preparation processes that will upgrade hydrophilic–hydrophobic patterns to superhydrophilic-superhydrophobic patterns, however, other factors or manufacturing processes that may enhance nucleation seem to be neglected by most of the previous works. For the last few years, while the development of hybrid surfaces with alternating hydrophilic and hydrophobic patterns attracted scientists' attention, other research on the influence of micromorphology on vapor nucleation has gotten underway. It has been calculated theoretically that the Gibbs' free energy barrier of gas–liquid transition on a cold concave surface is smaller than those on a convex or a flat surface. The smaller the radius of the concave surface is, the lower the value of the Gibbs' free energy barrier of condensation is and the easier the dew droplet begins to form, i.e., the smaller the subcooling temperature required to form a stable water embryo in comparison with the subcooling required in standard condition (Qian & Ma 2012; Yan et al. 2016; Cheng et al. 2020; Hu et al. 2021a). Therefore, the microstructure and wettability arrangement of a surface are two critical factors that influence the dewing process, and this review will concentrate on a water harvesting surface whose microstructure and wettability arrangement have been modified simultaneously. The preparation, mechanism and dew productivity performed in the laboratory of the above mentioned material will be introduced in the next chapters.

Hybrid surfaces prepared by physical blending method

Physical blending is a general term for a large class of methods, in which physisorption between substrates and hydrophilic/hydrophobic particles take place by spraying or bonding the particles onto the surface of substrates. The process flow of a typical amphiphilic water harvesting surface with hydrophilic bulges is shown in Figure 3 (Wang et al. 2021a). Here, a mixture consists of graphene powder, hydrophobic prepolymer, and diluent has been poured onto the substrate covered with Fe particles. After solidification of the mixture, the whole material will be composed of two layers: a film of solidified graphite embedded with Fe particles and a substrate that served as sacrifice matter. Then, the whole material has been heated in a vacuum oven at 333 K for 2 h to remove the sacrifice layer, and the appearance of material ends up looking like a soft film of graphite with bumps of hydrophilic Fe microsphere which has an amplitude of about 30 μm relative to the Graphite sheet ground level.
Figure 3

Graphical introduction of preparation of the graphite-Fe particles amphiphilic water harvesting surface.

Figure 3

Graphical introduction of preparation of the graphite-Fe particles amphiphilic water harvesting surface.

Close modal

Particles or reagents like modified SiC, Cu2O, TiO2 or ZrO2, polyurethane, or sodium alginate are commonly used components that act as hydrophilic or hydrophobic spots on the surface of substrates which are commonly made of polydimethylsiloxane, polyurethane, Cu, or Al sheets. The contour of the above mentioned particle or microsphere is convex and the amplitude from top of the particle to the surface where the particle is embedded is around 5–50 μm. Spraying, pouring and then heating at around 333–353 K by ovens are usual fabrication flows in which the particle solution makes contact and eventually bonds with the substrate (Wang et al. 2019a, 2019b, 2020; Feng et al. 2020; Nguyen et al. 2020; Wang et al. 2021a, 2021b). Weaving is another usual method to produce water harvesting materials, where textile fibers of different wettabilities form bulging cross-bedded hydrophilic or hydrophobic spots (Yu et al. 2021).

The concepts of condensation acceleration of the above mentioned amphiphilic/amphiphobic or alternating hydrophilic and hydrophobic water harvesting surfaces are also diverse. Most of them still adopt the dew harvesting principle as shown in Figure 2. However, some literature still put forward new investigations about the influence of convexity of bumps on droplet growth rate and new dew collection mode in which multi-layer is adopted to increase the opportunity of droplet shedding. Although the Gibbs' free energy barrier of condensation on concave surfaces is lower than those on convex and flat surfaces, surfaces with convex contour still produce a higher vapor concentration gradient between the atmosphere and droplet surface (Medici et al. 2014; Park et al. 2016). Most water harvesting surfaces prepared by the physical blending method have a large scale of bumps which have an amplitude of about 5–50 μm. Droplets located on these convex bulging profit will not only form a high moisture diffusion rate which accelerates the droplet growth but also form a high frequency of inter-droplet collision. Therefore, benefiting from the synergistic effect of condensation enhancement shown by prepared materials and a simple processing flow, physical blending has become a popular method in water harvesting material preparation.

In order to enhance the amount of dew collected, a multi-layer mode has been designed for thin water harvesting surfaces (Wang et al. 2019b, 2020). The concept of multi-layer mode is simple: thin films of condensation surface have been set up in a vertical direction and in a side by side arrangement, and the distance from layer to layer has been set up for about 1–2 mm. After dews appear, small drops begin to move along the wettability gradient and then collide with droplets lying on hydrophilic sections. Large droplets detach from the surface or ‘jump’ to the adjacent layer which increases the possibility of inter-droplet fusion. The ‘jumping’ of small dew drops from layer to layer is caused by energy conservation. After two small droplets mix together, the coalesced droplet releases surface energy due to the reduction of surface area. The released surface energy is to overcome the energy consumed due to friction loss and the energy needed by separating the liquid-solid, i.e., the droplet-substrate interface from each other, as the coalesced droplet leaves the layer. The rest of the energy is transformed into kinetic energy that makes the droplet ‘jump’ a short distance. To sum up, the jumping of small droplets found in multi-layer mode of water harvesting materials is worthy of attention in the field of dew droplet collection.

Hybrid surfaces prepared by chemical modification or etching

Dip-coating, hydrothermal method, UV irradiation, or even heat treatment are common techniques of chemical modification to prepare amphiphilic/amphiphobic or alternating hydrophilic and hydrophobic surfaces with structured patterns. The process of modification usually carries out on copper mesh or textile, reagents that regulate the wettability are CuO, TiO2, ZnO, Fe2O3, or other monomers. The diversity of polymer monomers is a unique advantage of chemical modification, however, the difficulty of obtaining a long range ordered microstructure is the shortage of this method as well (Ai-Khayat et al. 2017; Zhong et al. 2019; Guo & Guo 2020; Zhang et al. 2020; Lyu et al. 2021). A typical process flow of preparing such water harvesting surfaces by chemical modification is for instance as follows (Lyu et al. 2021): a piece of polyester textile was dipped into a mixture consisting of H2N-PDMS-NH2, tetraethyl orthosilicate, and triethoxy (3-glycidyloxypropyl)silane at room temperature for 10 min. After drying in an environment containing 2 mL of HCl for 9 h, the textile was then moved into an oven at 293 K for 12 h. Eventually, a hybrid textile was obtained with NH3 hydrophilic sites and hydrophobic polymer chains.

Compared with chemical modification, the etching method has the potential to produce long range ordered micromorphology while maintaining the expected wettability arrangement at the same time. Reactive or deep reactive ion etching (RIE/DRIE) and plasma dry etching are commonly used processes. Micromorphologies manufactured by etching are usually conical array, conical groove, honeycomb array, and cylindrical array. The amplitude of the microstructure (tiny cone or cylinder) is 5–50 μm away from the surface ground level. The purpose of manufacturing the above mentioned microstructures is to offer sites which realize dew droplets movement driven by the imbalance force caused by contact angle difference (Bingi & Murukeshan 2017; Brindhu & Padmanabhan 2021; Hirai et al. 2017; Wang et al. 2021b). For example, while preparing a water harvesting surface with long range ordered triangle array (Brindhu & Padmanabhan 2021), a polystyrene (PS) monolayer served as the mask was first deposited onto a silicon substrate using evaporation-induced convective self assembly technique followed by sintering at 372 K for 1 min. Then, Au was deposited onto a promoting layer of Ti using sputter deposition. The PS monolayer was removed by using adhesive tape. The whole surface was then dipped into a 16-mercaptohexadecanoic acid (MHA) solution and a 1-octadecanethiol (ODT) solution, respectively, in order to form bondings between MHA and Au spots as well as between ODT and Si substrate.

Most of the current studies focused on accelerating the frequency of large droplets shedding and ignored manufacturing microstructures that help to reduce the Gibbs' energy barrier of gas–liquid transition. It is worth mentioning that nanosphere lithography (Haynes & Van Duyue 2001) may become a major technique for the preparation of surfaces with high condensation efficiency. The schematic process flow of preparing materials with surface wettability arrangement and long range ordered surface micromorphology is shown in Figure 4. Critical factors that affect a successful production are self assembling of particles and the type of matter deposited. The grade of how large the surface can be, on which the micrometre scale spherical particles maintain a close-packed state, determines the degree of regularity of the microstructure array on the surface at the final stage of the preparation. The component that be spurted onto the substrate must be unable to react with acids and alkalis, otherwise, it will not be able to form an alternating hydrophilic and hydrophobic patterns in the final form of the material. The maneuverability of the contour and the size of the micromorphology is the most significant advantage of this method in comparison with other fabrication processes. For instance, when using silicon wafer–NaOH solution as a sacrificial layer-corrosive liquid pair, the shape of the corrosion pit can be controlled by choosing surfaces with different indices of the crystallographic plane (e.g. etching along the (001) direction of a silicon wafer to obtain an array of spherical cavities), the duration of corrosion and the concentration of the corrosive liquid. Currently, hemispherical and inverse pyramids are popular appearances at the final stage of water harvesting surfaces (Guo et al. 2015; Zhao et al. 2017a). Regular bump arrays can also be formed by using standard UV photolithography.
Figure 4

Typical process flow of preparing water harvesting surfaces with nanosphere lithography: (a) particles of micrometre scale form monolayer on a substrate by a self assembly process; (b) deposition of matters that with counter wettability to the substrate; (c) the monolayer is removed from the substrate and residues remained serve as a mask against etching; and (d) the substrate is corroded by acid or alkali, leaving substrate with hybrid wettability arrangement and a long range ordered microstructure.

Figure 4

Typical process flow of preparing water harvesting surfaces with nanosphere lithography: (a) particles of micrometre scale form monolayer on a substrate by a self assembly process; (b) deposition of matters that with counter wettability to the substrate; (c) the monolayer is removed from the substrate and residues remained serve as a mask against etching; and (d) the substrate is corroded by acid or alkali, leaving substrate with hybrid wettability arrangement and a long range ordered microstructure.

Close modal

Unfortunately, few cases have been found which introduced research on the preparation of hybrid water harvesting materials by nanosphere lithography. At the moment, materials fabricated by such method have been applied in the field of optics, photovoltaic, cancer therapy and drug delivery (Jia et al. 2020; Lee et al. 2021; Welbourne et al. 2021; Mai et al. 2022). But, at present, it is noteworthy that the utilization of gas–liquid interface deposition for the formation of a long range ordered Polystyrene microsphere monolayer on a silicon wafer has become one of the simplest and one of the most convenient techniques among other mask forming methods, and eventually, by adjusting the diameter of the Polystyrene microsphere, the minimum dimension of each micro pit on silicon wafer can be reduced to about 1 μm or even less than 1 μm which is getting closer to the same scale of the critical radius of a stable water nucleus at room temperature (nano- or submicronmetre scale) (Wu et al. 2014; Wang et al. 2015; Kismann et al. 2021). Therefore, in order to realize the reduction of the energy barrier in gas–liquid transition, it is worthwhile to sequentially investigate a feasible, systematic workflow of nanosphere lithography for manufacturing alternating hydrophilic and hydrophobic surfaces with the array that consists of nano- or submicronmetre scale of pit.

Hybrid surfaces prepared by micromanufacturing

Micro-milling, laser lithography, and 3D printing have also become adoptable techniques for preparing hybrid surfaces with microstructure. It is reported that a hydrophobic Al alloy surface with a hydrophilic microdot array has been prepared by Micro-milling method, where an Al sheet was first electrochemically etched in a 0.1 mol/L NaCl solution and dipped in a 1 wt% ethanol solution with fluoroalkylsilane for 90 min. After that, an array consisting of micro cylindrical spots has been milled on the Al sheet by a milling system. However, limited by the strength of the drilling bit, the radius of each spot was only around 300 μm – hundreds of times the critical nucleation radius (Yang et al. 2016). As a result of that, hybrid surfaces with modified surface structures manufactured by micro-milling could not achieve a distinct reduction of the energy barrier in gas–liquid transition yet.

The principle of laser lithography is similar to wet etching, in which certain features on the surface of a metallic substrate are manufactured by high power laser, for example, a TiO2 hierarchical microstructure with a certain wettability arrangement has been prepared, where a Ti sheet has been etched by a femtosecond laser system with a central wavelength of 1,030 nm, 800fs duration and a 400 kHz repetition rate. Then the modified Ti sheet has been hydrothermally treated in a 3 mol/L NaOH solution followed by a 593 K heating in an oven for 24 h. After that, the component of the Ti surface has been transformed to TiO2 by a process in which the Ti sheet has been dipped into a 1 mol/L HCl solution for 10 min and then heated at 723 K for 1 h. Eventually, a superhydrophobic surface with hierarchical microstructure has been obtained by depositing the vapor of PDMS ((C2H6OSi)n, Sylgard 184) solution onto the TiO2 sheet (Lu et al. 2019). Another representative achievement done by Laser lithography is hybrid surfaces with grooves in which a glass substrate has been first covered by a hydrophobic coating. Then a pulsed laser with a 1,064 nm wavelength, 500 kHz pulse repetition and 200 ns pulse duration penetrated from the back side of the glass substrate. The part made of glass was ablated leaving a hybrid surface that consists of hydrophilic grooves and hydrophobic tips. The minimum width of each groove was 25 μm which was only about 50 times larger than the critical nucleation radius (Li et al. 2017; Lee et al. 2018).

3D printing, which has become popular in recent years can also be used for fabricating surfaces with modified microstructure. Inspired by the shape of cactus' leaves, the typical microstructure done by 3D printing is a set of cones pointed to different directions. The dew droplet will move from the tips of each cone to the bottom part of the cone under the gradient of Laplace pressure which is caused by the contact angle difference between the front and rear sides of a single dew droplet (Li et al. 2019a). The average radius of each cone was around 100 μm and the components of such materials were mostly polymer. Limited by the incompatibility between the molten hydrophilic polymer and a hydrophobic polymer, water harvesting surfaces with different wettabilities manufactured by 3D printing are still under development.

Other variations of hybrid surface and summary

Besides surfaces prepared with physical blending, chemical modification, etching, and micromanufacturing, other efficient water harvesting materials such as metal organic frameworks (MOFs) also deserve to be mentioned (Pan et al. 2020). As a kind of water harvesting material, MOFs benefit from their high porosity and large specific surface area where water molecules are willing to be absorbed. As an example, the principle of a CaCl2-decorated photothermal Fe-ferrocene MOFs for water molecules absorption has been introduced as follows (Hu et al. 2021b): CaCl2 has been encapsulated into hollow iron-based Ferrocenyl microspheres (Fe-Fc-HCPs), which avoids the collapse of the channel between particles when vapor flows through and the leakage of deliquescent salt. In this material, CaCl2 served as a typical desiccant and the hollow of Fe-Fc-HCPs enhances light absorption by increasing the optical reflection area. At night when the temperature becomes low and the humidity rises, the adsorption of water molecules occurs due to the adsorption effect of CaCl2, while in the daytime when the temperature is getting higher and the humidity reduces, the desorption of water molecules occurs due to the photothermal heating effort of Fe-Fc-HCPs. Extra sources for heating the water molecules are not required because of the self-photothermal heating effect of Fe-Fc-HCPs charged by solar energy.

To summarize, a consideriable amount of methods are available for the preparation of alternating hydrophilic and hydrophobic surfaces with modified microstructure. Currently, whatever method is used, the prepared materials possess the following common characteristics: (1) most micromorphologies of current material are either hydrophobic bumps surrounded with a hydrophilic flat surface or an array of tiny conical grooves or bumps that trigger the droplet migrates from tip to bottom of the cone. Both structures are biomimetic, or more exactly, the ideas are based on the pattern on the back of Fog-basking beetles and the shape of cactus leaves, respectively. Other configurations of micromorphology are hydrophilic or hydrophobic cylindrical pits or band-shaped grooves surrounded by flat surfaces with counter wettability. The size of each pit or groove was more than 20 times larger than that of the critical nucleation radius. (2) The dew droplet migrates along the wettability gradient or geometrical gradient or ‘jumping’ due to the reduction of the surface energy – these are the most common mechanisms with which the water harvesting materials are adopted. The effect brought by these mechanisms is the increase of the droplet growth rate caused by inter-droplet collision and fusion and eventually, shedding of large droplets will occur frequently which increases the amount of dew water collected.

The severe climate conditions in desertification areas require a reliable functionality of water harvesting materials. In order to analyze the dew productivity of such materials and conditions including temperature and humidity in which an optimal dewing amount can be achieved, the maximum value of the dew collection rate and their experimental environments adopted by the representative literature mentioned in the previous chapter are summarized in Table 1. Meanwhile, as supplementary, dewing efficiencies and test environments of hybrid surfaces without modified microstructure have also been shown in this table. In this review, the maximum value of the dew collection rate (in g/cm2h−1) has been chosen to characterize the dew productivity. The temperature and the humidity refer to the value of the cold end temperature which also represents the temperature of the sample and the relative humidity in the dewing test chamber, respectively.

Table 1

Dew productivities and their test environments of alternating hydrophilic and hydrophobic hybrid surfaces with/without surface microstructure

No.LiteraturesComponents of surfaces (HC vs. HB)aMicrostructure of surfacesbMin. sizes of MScMax. dew productivities (g/cm2h−1)Test environments (CT vs. RH)d
Wang et al. (2021aFe particle vs. Polydimethylsiloxane (PDMS) film Irregular hydrophilic bump array ≈25 μm 0.16 296 K vs. 100% 
Wang et al. (2019a)  SiO2 particle vs. 1H, 1H, 2H, 2H-Perfluorodecyltriethoxysilane (PFDTES) particle Irregular hydrophilic bump array ≈5 μm 0.27 275 K vs. 85% 
Wang et al. (2020)  SiO2 particle vs. PFDTES particle Irregular hybrid bump array & Multi-layer ≈5 μm 0.3 275 K vs. 85% 
Feng et al. (2020)  modified Cu2O particle vs. modified ZrO2 particle Irregular hybrid bump array ≈5 μm 1.7 295 K vs. 90% 
Nguyen et al. (2020)  HB Polyurethane-Sodium alginate (PU-SA) coating Irregular bump array ≈30 μm 0.029 295 K vs. 90% 
Yu et al. (2021)  HC yarn vs. NB yarn Irregular bump array ≈300 μm 1.4 295 K vs. 100% 
Ai-Khayat et al. (2017)  Poly-4-vinylpyridine (P4VP) vs. Polystyrene film (PS) Irregular bump array ≈1 μm 0.008 275 K vs. 90% 
Zhong et al. (2019)  Cu mesh vs. Cu(OH)2 ribbon Irregular ribbon array & Multi-layer ≈1 μm 2.2 291 K vs 90% 
Guo & Guo (2020)  Cu mesh vs. CuO@TiO2 particle Irregular bump array – 0.57 295 K vs. 90% 
10 Lyu et al. (2021)  -NH2 group vs. Polydimethylsiloxane Irregular bump array ≈20 μm 3.1 283 K vs. 95% 
11 Lu et al. (2019)  TiO2 sheet vs. (C2H6OSi)n, Sylgard 184(PDMS) coating Bump array ≈10 μm 0.5 273 K vs. 30% 
12 Hu et al. (2021bCaCl2@Fe-ferrocene MOFs Porous material – 2.7gH2O/gCACL2 288 K vs. 80% 
13 Zhang et al. (2016bSteel particle vs. HB Si particle – – 0.16 293 K vs. 90% 
Fe sheet vs. HB Co particle – – 0.052 292 K vs. 80% 
HC AgOAc particle vs. Fluoromercaptan – – 0.24 301 K vs. 80% 
Steel particle vs. Hydrophobic silicon wafer – – 0.02 278 K vs. 70% 
No.LiteraturesComponents of surfaces (HC vs. HB)aMicrostructure of surfacesbMin. sizes of MScMax. dew productivities (g/cm2h−1)Test environments (CT vs. RH)d
Wang et al. (2021aFe particle vs. Polydimethylsiloxane (PDMS) film Irregular hydrophilic bump array ≈25 μm 0.16 296 K vs. 100% 
Wang et al. (2019a)  SiO2 particle vs. 1H, 1H, 2H, 2H-Perfluorodecyltriethoxysilane (PFDTES) particle Irregular hydrophilic bump array ≈5 μm 0.27 275 K vs. 85% 
Wang et al. (2020)  SiO2 particle vs. PFDTES particle Irregular hybrid bump array & Multi-layer ≈5 μm 0.3 275 K vs. 85% 
Feng et al. (2020)  modified Cu2O particle vs. modified ZrO2 particle Irregular hybrid bump array ≈5 μm 1.7 295 K vs. 90% 
Nguyen et al. (2020)  HB Polyurethane-Sodium alginate (PU-SA) coating Irregular bump array ≈30 μm 0.029 295 K vs. 90% 
Yu et al. (2021)  HC yarn vs. NB yarn Irregular bump array ≈300 μm 1.4 295 K vs. 100% 
Ai-Khayat et al. (2017)  Poly-4-vinylpyridine (P4VP) vs. Polystyrene film (PS) Irregular bump array ≈1 μm 0.008 275 K vs. 90% 
Zhong et al. (2019)  Cu mesh vs. Cu(OH)2 ribbon Irregular ribbon array & Multi-layer ≈1 μm 2.2 291 K vs 90% 
Guo & Guo (2020)  Cu mesh vs. CuO@TiO2 particle Irregular bump array – 0.57 295 K vs. 90% 
10 Lyu et al. (2021)  -NH2 group vs. Polydimethylsiloxane Irregular bump array ≈20 μm 3.1 283 K vs. 95% 
11 Lu et al. (2019)  TiO2 sheet vs. (C2H6OSi)n, Sylgard 184(PDMS) coating Bump array ≈10 μm 0.5 273 K vs. 30% 
12 Hu et al. (2021bCaCl2@Fe-ferrocene MOFs Porous material – 2.7gH2O/gCACL2 288 K vs. 80% 
13 Zhang et al. (2016bSteel particle vs. HB Si particle – – 0.16 293 K vs. 90% 
Fe sheet vs. HB Co particle – – 0.052 292 K vs. 80% 
HC AgOAc particle vs. Fluoromercaptan – – 0.24 301 K vs. 80% 
Steel particle vs. Hydrophobic silicon wafer – – 0.02 278 K vs. 70% 

aHC refers to hydrophilic and HB refers to hydrophobic.

bThe term ‘hybrid’ refers to alternating hydrophilic and hydrophobic patterns.

cMS refers to microstructure.

dCT refers to cold end temperature, RH refers to relative humidity.

According to the data shown in Table 1, several conclusions can be summarized: (1) At present, almost all contours of the microstructure adopted by hybrid surfaces are convex. Alternating hydrophilic and hydrophobic surfaces with cavity arrays are gaps that are worth to be studied. (2) The dimensions of the microstructure in most of the works are still larger than that of the critical nucleation radius (≈1 μm or smaller) which makes the reduction of the free energy barrier in gas–liquid transition inapparent. (3) After analyzing the experimental configurations adopted by the literatures listed in Table 1, two parameters that influence an accurate measurement of dew productivity have not been introduced in detail: firstly, when large droplets roll off, they sweep other droplets on the path, which causes a sudden unpredictable increase in droplet volume, due to the randomness of the volume and number of droplets be swept by each dewing test. Therefore, to measure the weight that represents the final dew production of each sample accurately, one should consider the impact of ‘inter-droplet sweeping’ on ‘net’ dew productivity which is caused only by surface features such as wettability or geometrical gradient. Secondly, information about droplets roll off and be collected from other non-measuring surfaces, such as from the frame that holds the sample, which would amplify the final value of dew production when ‘unexpected’ dew water is weighed was insufficient. Therefore, an analysis of reasons for the max. dew productivity fluctuation could be further investigated only when the above mentioned ‘distractors’ are eliminated or when they are accurately observed, i.e., the weight increment of dew water contributed by ‘sweeping’ and droplet falling from non-measuring surfaces could be measured. (4) The dew productivities of most hybrid surfaces are no more than 0.6 g/cm2h−1 or slightly larger than 1 g/cm2h−1. It is questionable whether such a tiny amount of dew water will match the demand of drought-endurable plants. Besides, almost all relative humidities in test chambers are higher than 80%. In order to compare the relative humidities in desertification areas with those in test chambers and analyze the applicability of the water harvesting material in desert areas, the climates in various types of desertification areas have been listed in Table 2.

Table 2

Climates in desertification areas

No.ReferencesLocationsReasons of desertificationTemperatures (K) vs. Relative humidities (%)
Li et al. (2019bFuYuan county, YunNan province, China Karst rocky desertification area Annually: ≈287 K (max. 312 K-min. 263 K) vs. 53% in Jan., 46% in Apr., 80% in Jul., 77% in Oct. (max. 100%-min. 21%) 
Zhao et al. (2017bNingXia Hui Autonomous Region, China Wind erosion and salinization in the north and central regions; water erosion in the south region Annually (1980–2013): ≈281 K vs. 54% in the north, ≈292 K vs. 56% in the central, ≈289 K vs. 64% in the south 
Wen et al. (2020)  QingHai-Tibetan Plateau, China Wind erosion and drought Annually (2011–2018): ≈278 K (max. 287 K in Jul. to min. 268 K in Apr.) vs. ≈65%(max. 90% in Jun. to min. 38% in May.) 
Zhang et al. (2016aSandy desert in the north of ShanXi province, China Wind erosion and drought Annually (1980–2014): ≈278–280 K vs. ≈50%-60% 
Chen et al. (2021)  XinJiang Uygur Autonomous Region, China Wind erosion and drought Annually (1999–2017): ≈281 K (max. 308 K-min.273 K) vs. Annually (1999–2014): 50%–54%(max. 56%-min.38% in August) 
Conca et al. (2010)  Abu Dhabi, Dubai, AlAin in the UAE Drought and heat Annual temperature (1982–2009) in Abu Dhabi: 299–302 K, Dubai: 298–302 K, AlAin: 300–303 K vs. Annual relative humidity (1982–2009) in Abu Dhabi: 65–58%, Dubai: 57–46%, AlAin: 36 − 50% 
Chukwu & Okeke (2015)  Umudike, Nigeria Flood and heat, desertification is not as serious as land in North China Annually (1983–2013): ≈299–300 K vs. ≈64−74% 
No.ReferencesLocationsReasons of desertificationTemperatures (K) vs. Relative humidities (%)
Li et al. (2019bFuYuan county, YunNan province, China Karst rocky desertification area Annually: ≈287 K (max. 312 K-min. 263 K) vs. 53% in Jan., 46% in Apr., 80% in Jul., 77% in Oct. (max. 100%-min. 21%) 
Zhao et al. (2017bNingXia Hui Autonomous Region, China Wind erosion and salinization in the north and central regions; water erosion in the south region Annually (1980–2013): ≈281 K vs. 54% in the north, ≈292 K vs. 56% in the central, ≈289 K vs. 64% in the south 
Wen et al. (2020)  QingHai-Tibetan Plateau, China Wind erosion and drought Annually (2011–2018): ≈278 K (max. 287 K in Jul. to min. 268 K in Apr.) vs. ≈65%(max. 90% in Jun. to min. 38% in May.) 
Zhang et al. (2016aSandy desert in the north of ShanXi province, China Wind erosion and drought Annually (1980–2014): ≈278–280 K vs. ≈50%-60% 
Chen et al. (2021)  XinJiang Uygur Autonomous Region, China Wind erosion and drought Annually (1999–2017): ≈281 K (max. 308 K-min.273 K) vs. Annually (1999–2014): 50%–54%(max. 56%-min.38% in August) 
Conca et al. (2010)  Abu Dhabi, Dubai, AlAin in the UAE Drought and heat Annual temperature (1982–2009) in Abu Dhabi: 299–302 K, Dubai: 298–302 K, AlAin: 300–303 K vs. Annual relative humidity (1982–2009) in Abu Dhabi: 65–58%, Dubai: 57–46%, AlAin: 36 − 50% 
Chukwu & Okeke (2015)  Umudike, Nigeria Flood and heat, desertification is not as serious as land in North China Annually (1983–2013): ≈299–300 K vs. ≈64−74% 

According to the temperatures and relative humidities shown in Table 2, it is implied that in places suffering from desertification, the relative humidities are generally less than 70%: in FuYuan county (YunNan province, Southeast China) for instance, where the climate is not as dry as that of cities in North and Northwest China (NingXia, ShanXi or XinJiang province), the humidity reached 80% in July and came down to 46% in January. The humidity occasionally rose to nearly 100%, but remained most of the time less than 64%. In Umudike, Nigeria where the climate is also not as dry as that of cities in North Nigeria, the annual humidities (1983–2013) were still less than or slightly larger than 70%. In NingXia and ShanXi provinces (North China) the largest annual humidities before the year 2014 were less than 65%, respectively, while in QingHai-Tibetan Plateau (China), the humidity (from the year 2011 to 2018) rose up to 90% in June and came down to 38% in May, the annual value was about 65%. In Abu Dhabi, Dubai, and AlAin (the UAE), the largest annual humidities (from the year 1982 to 2009) were 65, 57, and 50%, respectively. Therefore, it is unusual for desertification areas to have an annual relative humidity of more than 80%. This is unfriendly to the application of the water harvesting materials described in the previous chapter. By comparison between the artificial test environments (seventh column in Table 1) and the natural environments (fifth column in Table 2), the relative humidities during dewing experiments for most of the materials are more than 80% while the relative humidities in most areas listed in Table 2 are less than 70%. Hence, due to the insufficient air humidity, it is questionable whether current water harvesting materials will still reach their optimal dew productivity when utilized in desertification areas.

In the previous section, we have shown that low environmental humidity is the bottleneck that limits the utilization of hybrid surfaces in the field of water harvesting in an outdoor environment. In this chapter, methods that will improve the applicability and increase the dewing amount of surfaces with modified morphology and wettability arrangement are introduced.

The key to dew formation in low humidity or a small subcooling environment is to minimize the Gibbs free energy barrier of gas–liquid transition when vapor nucleates on the cold surface. The latter is also called heterogeneous nucleation, and certain artificial surface properties such as wettability and microstructure arrangement will make dewing easier, i.e., dewing in an unsaturated air condition or dewing in a small subcooling condition. A hydrophilic surface and concave surface whose radius is as small as the critical radius of a stable water nucleus at a given temperature will both dramatically reduce the Gibbs free energy barrier of the gas–liquid transition. It has been demonstrated that the free energy barrier for the formation of a liquid nucleus on a flat hydrophilic surface could be 117 times smaller than that on the flat hydrophobic surface (Varanasi et al. 2009). The nucleation rate on a hydrophilic surface could be zillions of orders of magnitude (≈10129 times) higher than that on the hydrophobic surface (Varanasi et al. 2009). It has also been proved that a distinct advantage of heterogeneous nucleation on a concave spherical surface of radius R over a flat surface occurs when 2R < 10r is satisfied, where r represents the critical radius of a stable water nucleus at a certain temperature. Conversely, the disadvantage of heterogeneous nucleation on a convex spherical surface of radius R over a flat surface also occurs when 2R < 10r is satisfied (Qian & Ma 2012). This phenomenon dissipates rapidly when 2R > 10r for both concave and convex surfaces, hence, only nanoscale or submicrometer scale surface features will really affect vapor nucleation. On the other hand, at the macroscopic level, the moisture concentration gradient above convex surfaces is larger than that above concave and flat surfaces, which means that dew droplets obtain a faster growth rate at the early stage of condensation on convex surfaces (Medici et al. 2014; Park et al. 2016).

In conclusion, surfaces with modified microstructure and wettability arrangement would have a superiority in heterogeneous nucleation in a low humidity environment, when further investigations carried out in the following research directions: (1) nanosphere lithography which is capable of fabricating concave array, in which the dimension of each cavity can be limited to nano- or submicron scale, should be adopted as one of the important methods of water harvesting surface preparation. (2) By utilizing nanosphere lithography, a hydrophobic surface with a hydrophilic spherical cavity array is an optimal option of water harvesting material, if the radius of a single spherical cavity can be reduced to the dimension that is close to the critical radius of a stable water nucleus at a certain temperature. (3) If preparing of nano- or submicron scale spherical cavity is infeasible, a hydrophobic surface with a hydrophilic spherical bump array is an optimal option for water harvesting material. It should be noted that the radius of hydrophilic particles embedded in a hydrophobic surface can not be equal to or less than the critical radius of a stable water nucleus at a certain temperature.

In this review, the possibility of trace quantity irrigation for providing fresh water to desert plants has been confirmed. According to our findings that the actual water consumption of some desert plants can be satisfied by the dew water produced from heterogeneous nucleation, the idea of preparing modified functional surfaces for accelerating the dew droplet growth rate during heterogeneous nucleation has been introduced.

Physical blending, chemical modification, etching, and micromanufacturing are reliable technologies for wettability and microfeature modification of water harvesting materials. At present, most of the existing materials prepared by the above mentioned methods possess a hybrid morphology in which bump array has a counter wettability to the plane section of the surface. By comparing the environmental conditions required by such materials in condensation experiments with climates in desertification areas, it is deduced that the dew productivities performed by current water harvesting materials in desertification regions characterzied by low relative humidity will not be as efficient as those shown in test chambers. The challenge that needs to be overcome and the potential of surfaces with modified wettability and microstructure in achieving in situ water harvesting in low humidity condition is reflected in the following two aspects: (1) reliable methods need to be developed and the process of nanosphere lithography needs to be improved in order to promote the feasibility of producing surfaces embedded with nano- or submicron scale cavity. (2) Hydrophobic surfaces embedded with nano- or submicron scale hydrophilic spherical cavity array prepared by nanosphere lithography can reduce the Gibbs free energy barrier for generating a stable water nucleus and will thus achieve gas–liquid transition in a small subcooling or in a low humidity environment.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

Ai-Khayat
O.
,
Hong
J. K.
,
Beck
D. M.
,
Minett
A. I.
&
Neto
C.
2017
Patterned polymer coatings increase the efficiency of dew harvesting
.
ACS Applied Materials & Interfaces
9
(
15
),
13676
13684
.
doi:10.1021/acsami.6b16248
.
Beysens
D.
2018
Dew Water
.
River Publishers
,
Denmark and The Netherlands
.
Bingi
J.
&
Murukeshan
V. M.
2017
Speckle lithography for fabricating biomimetic spindle structures of desert beetle skin
.
Biomedical Physics & Engineering Express
3
(
2
),
025003
.
doi:10.1088/2057-1976/aa5d28
.
Brindhu
M. S.
&
Padmanabhan
V.
2021
Wettability contrast in the hexagonally patterned gold substrate of distinct morphologies for enhanced fog harvesting
.
Langmuir
37
(
27
),
8281
8289
.
doi:10.1021/acs.langmuir.1c01065
.
Brown
P. S.
&
Bhushan
B.
2016
Bioinspired materials for water supply and management: water collection, water purification and separation of water from oil
.
Philosophical Transactions of the Royal Society of London, Series A: Mathematical, Physical and Engineering Sciences
374
(
2073
),
20160135
.
doi:10.1098/rsta.2016.0135
.
Chaudhury
M. K. W.
&
Whitesides
G. M.
1992
How to make water run uphill
.
Science
256
(
5063
),
1539
1541
.
doi:10.1126/science.256.5063.1539
.
Chen
Z.
&
Zhang
Z. Z.
2020
Recent progress in beetle-inspired superhydrophilic superhydrophobic micropatterned water-collection materials
.
Water Science & Technology
82
(
2
),
207
226
.
doi:10.2166/wst.2020.238
.
Chen
C.
,
Jing
C. Q.
,
Xing
W. Y.
,
Dong
X. J.
,
Fu
H. Y.
&
Guo
W. Z.
2021
Desert grassland dynamics in the last 20 years and its response to climate change in Xinjiang
.
Acta Prataculturae Sinica
30
(
3
),
1
14
.
doi:10.11686/cyxb2020143
.
Cheng
N.
,
Guo
R.
,
Shuai
S. S.
,
Wang
J.
,
Xia
M. X.
,
Li
J. G.
,
Ren
Z. M.
,
Li
J. S.
&
Wang
Q.
2020
Influence of static magnetic field on the heterogeneous nucleation behavior of Al on single crystal Al2O3 substrate
.
Materialia
13
,
100847
.
doi:10.1016/j.mtla.2020.100847
.
Chukwu
G. U.
&
Okeke
C. T.
2015
Assessment of the effects of climate change on solar radiation, relative humidity and temperature in southeastern Nigeria
.
International Journal of Innovative Scientific & Engineering
3
(
1
),
27
41
.
Conca
W.
,
Al-Nuaimi
K.
&
Nagelkerke
N.
2010
The complexity of regional warming in the United Arab Emirates in the period 1982–2009
.
International Jounral of Global Warming
2
(
3
),
225
233
.
doi:10.1504/IJGW.2010.036134
.
Du
H. M.
,
Zhang
Z. Z.
,
Wu
M. M.
&
Zhao
J.
2015
Water-conducting characteristics and micro-dynamic self-adjusting behavior of polyacrylamide/montinorillonite coating
.
Journal of Wuhan University of Technology (Materials Science Edition)
30
(
6
),
1191
1197
.
doi:10.1007/s11595-015-1294-3
.
Fan
S. Y.
&
Zhou
L. H.
2001
Desertification control in China: possible solutions
.
Ambio
30
(
6
),
384
385
.
doi:10.2307/4315170
.
Feng
J.
,
Zhong
L. S.
&
Guo
Z. G.
2020
Sprayed hieratical biomimetic superhydrophilic-superhydrophobic surface for efficient fog harvesting
.
Chemical Engineering Journal
388
,
124283
.
doi:10.1016/j.cej.2020.124283
.
Guo
X. L.
&
Guo
Z. G.
2020
Hybrid hydrophilic–hydrophobic CuO@TiO2-coated copper mesh for efficient water harvesting
.
Langmuir
36
(
1
),
64
73
.
doi:10.1021/acs.langmuir.9b03224
.
Guo
P. Q.
,
He
J.
,
Zhou
S. Q.
,
Yang
X.
,
Li
S. Z.
,
Sheng
J.
,
Wang
D.
,
Yu
T. B.
,
Ye
J. C.
&
Cui
Y.
2015
Large-area nanosphere self-assembly by a micro-propulsive injection method for high throughput periodic surface nanotexturing
.
Nano Letters
15
(
7
),
4591
4598
.
doi:10.1021/acs.nanolett.5b01202
.
Haynes
C. L.
&
Van Duyue
R. P.
2001
Nanosphere lithography: a versatile nanofabrication tool for studies of size-dependent nanoparticle optics
.
The Journal of Physical Chemistry B
105
(
24
),
5599
5611
.
doi:10.1021/jp010657m
.
Hirai
Y.
,
Mayama
H.
,
Matsuo
Y.
&
Shimomura
M.
2017
Uphill water transport on a wettability-patterned surface: experimental and theoretical results
.
ACS Applied Materials & Interfaces
9
(
18
),
15814
15821
.
doi:10.1021/acsami.7b00806
.
Hu
L. N.
,
Lu
H.
,
Ma
X. J.
&
Chen
X. D.
2021a
Heterogeneous nucleation on surfaces of the three-dimensional cylindrical substrate
.
Journal of Crystal Growth
575
,
126340
.
doi:10.1016/j.jcrysgro.2021.126340
.
Hu
Y.
,
Fang
Z.
,
Ma
X.
,
Wan
X. Y.
,
Wang
S. L.
,
Fan
S. K.
,
Ye
Z. Z.
&
Peng
X. S.
2021b
CaCl2 nanocrystals decorated photothermal Fe-ferrocene MOFs hollow microspheres for atmospheric water harvesting
.
Applied Materialstoday
23
,
101076
.
doi:10.1016/j.apmt.2021.101076
.
Jia
M.
,
Zhang
Y. Y.
,
Li
Z. X.
,
Crouch
E.
,
Doble
S.
,
Avenoso
J.
,
Yan
H.
,
Ni
C. Y.
&
Gundlach
L.
2020
A versatile strategy for controlled assembly of plasmonic metal/semiconductor hemispherical nano-heterostructure arrays
.
Nanoscale
12
(
33
),
17530
17537
.
doi:10.1039/D0NR03551C
.
Kismann
M.
,
Riedl
T.
&
Lindner
J. K. N.
2021
Ordered arrays of Si nanopillars with alternating diameters fabricated by nanosphere lithography and metal-assisted chemical etching
.
Materials Science in Semiconductor Processing
128
,
105746
.
doi:10.1016/j.mssp.2021.105746
.
Lee
D. K.
,
Choi
S. Y.
,
Park
M. S.
&
Cho
Y. H.
2018
Wetting properties of hybrid structure with hydrophilic ridges and hydrophobic channels
.
Applied Physics A: Materials Science and Processing
124
(
2
),
1
7
.
doi:10.1007/s00339-018-1595-4
.
Lee
D. M.
,
Hsu
M. Y.
,
Tang
Y. L.
&
Liu
S. J.
2021
Manufacture of binary nanofeatured polymeric films using nanosphere lithography and ultraviolet roller imprinting
.
Materials
14
(
7
),
1669
.
doi:10.3390/ma14071669
.
Li
D. K.
,
Cho
Y. H.
,
Lee
J. W.
&
Park
M. S.
2017
Wettability of microstructured Pyrex glass with hydrophobic and hydrophilic properties
.
Surface and Coatings Technology
319
,
213
218
.
doi:10.1016/j.surfcoat.2017.04.022
.
Li
X. J.
,
Yang
Y.
,
Liu
L. Y.
,
Chen
Y. Y.
,
Chu
M.
,
Sun
H. F.
,
Shan
W. T.
&
Chen
Y.
2019a
3D-printed cactus-inspired spine structures for highly efficient water collection
.
Advanced Materials Interfaces
7
(
3
),
1901752
.
doi:10.1002/admi.202070012
.
Li
S.
,
Xue
L.
,
Wang
J.
,
Ren
H. D.
,
Yao
X. H.
,
Leng
X. H.
&
Wu
Z. Y.
2019b
The dynamics of bare rock surface temperature, air temperature and relative humidity in karst rocky desertification area
.
Chinese Journal of Ecology
38
(
2
),
436
443
.
doi:10.13292/j.1000-4890.201902.024
.
Li
H.
,
Renssen
H.
&
Roche
D. M.
2020
Modeling climate-vegetation interactions during the last interglacial: the impact of biogeophysical feedbacks in North Africa
.
Quaternary Science Reviews
249
,
106609
.
doi:10.1016/j.quascirev.2020.106609
.
Lu
J. L.
,
Ngo
C. V.
,
Singh
S. C.
,
Yang
J. J.
,
Xin
W.
,
Yu
Z.
&
Guo
C. L.
2019
Bioinspired hierarchical surfaces fabricated by femtosecond laser and hydrothermal method for water harvesting
.
Langmuir
35
(
9
),
3562
3567
.
doi:10.1021/acs.langmuir.8b04295
.
Lv
F. Y.
,
Zhao
F.
,
Cheng
D. L.
,
Dong
Z. G.
,
Jia
H. W.
,
Xiao
X.
&
Orejon
D.
2022
Bioinspired functional SLIPSs and wettability gradient surfaces and their synergistic cooperation and opportunities for enhanced condensate and fluid transport
.
Advances in Colloid and Interface Science
299
,
102564
.
doi:10.1016/j.cis.2021.102564
.
Lyu
P.
,
Zhang
X. Y.
,
Shang
B.
,
Liu
X.
&
Deng
Z. W.
2021
One-step preparation of hydrophobic surfaces containing hydrophilic groups for efficient water harvesting
.
Langmuir
37
(
31
),
9630
9636
.
doi:10.1021/acs.langmuir.1c01756
.
Mai
U.
,
Park
S. Y.
,
Kiba
T.
,
Takayam
J.
,
Hiura
S.
,
Murayama
A.
,
Kawamura
M.
&
Abe
Y.
2022
Optical characterization and emission enhancement property of Ag nanomesh structure fabricated by nanosphere lithography
.
Surface and Coatings Technology
435
,
128258
.
doi:10.1016/j.surfcoat.2022.128258
.
Medici
M. G.
,
Mongruel
A.
,
Royon
L.
&
Beysens
D.
2014
Edge effects on water droplet condensation
.
Physical Review E
90
(
6
),
062403
.
doi:10.1103/PhysRevE.90.062403
.
Nguyen
L. T.
,
Bai
Z. Q.
,
Zhu
J. J.
,
Gao
C.
,
Liu
X. J.
,
Wagaye
B. T.
,
Li
J. C.
,
Zhang
B.
&
Guo
J. S.
2020
Three-Dimensional multilayer vertical filament meshes for enhancing efficiency in fog water harvesting
.
ACS OMEGA
6
(
5
),
3910
3920
.
doi:10.1021/acsomega.0c05776
.
Pan
T. T.
,
Yang
K. J.
&
Han
Y.
2020
Recent progress of atmospheric water harvesting using metal-organic frameworks
.
Chemical Research in Chinese Universities
36
,
33
40
.
doi:10.1007/s40242-020-9093-6
.
Park
K. C.
,
Kim
P.
,
Grinthal
A.
,
He
N.
,
Fox
D.
,
Weaver
J. C.
&
Aizenberg
J.
2016
Condensation on slippery asymmetric bumps
.
Nature
531
,
78
82
.
doi:10.1038/nature16956
.
Qu
Y. P.
&
Zhang
Z. Z.
2020
The design and application of non-pressure infiltrating irrigation in desertification control
.
Sustainability
12
(
4
),
1547
.
doi:10.3390/su12041547
.
Qu
Y. P.
,
Zhang
Z. Z.
&
Li
C. L.
2017
Preparation and water retention properties of montmorillonite modified by EL-10 emulsifying agent
.
Journal of Wuhan University of Technology (Materials Science Edition)
32
(
4
),
806
811
.
doi:10.1007/s11595-017-1672-0
.
Sikarwar
B. S.
,
Khandekar
S.
,
Agrawal
S.
,
Kumar
S.
&
Muralidhar
K.
2012
Dropwise condensation studies on multiple scales
.
Heat Transfer Engineering
33
(
4–5
),
301
341
.
doi:10.1080/01457632.2012.611463
.
Tsunekawa
A.
&
Haregeweyn
N.
2017
Development of next-generation Sustainable Land Management (SLM) framework to combat desertification
.
Impact
2017
(
7
),
26
28(3)
.
doi:10.21820/23987073.2017.7.26
.
Varanasi
K. K.
,
Hsu
M.
,
Bhate
N.
,
Yang
W. S.
&
Deng
T.
2009
Spatial control in the heterogeneous nucleation of water
.
Applied Physics Letters
95
,
094101
.
doi:10.1063/1.3200951
.
Verón
S. R.
,
Paruelo
J. M.
&
Oesterheld
M.
2006
Assessing desertification
.
Journal of Arid Environments
66
(
4
),
751
763
.
doi:10.1016/j.jaridenv.2006.01.021
.
Wang
T.
2014
Aeolian desertification and its control in Northern China
.
International Soil and Water Conservation Research
2
(
4
),
34
41
.
doi:10.1016/S2095-6339(15)30056-3
.
Wang
D. P.
,
Zhao
A. W.
,
Li
L.
,
He
Q. Y.
,
Guo
H. Y.
,
Sun
H. H.
&
Gao
Q.
2015
Bioinspired ribbed hair arrays with robust superhydrophobicity fabricated by micro/nanosphere lithography and plasma etching
.
RSC Advances
5
(
117
),
96404
96411
.
doi:10.1039/c5ra18439h
.
Wang
X. K.
,
Zeng
J.
,
Yu
X. Q.
,
Liang
C. H.
&
Zhang
Y. F.
2019a
Superamphiphobic coatings with polymer-wrapped particles: enhancing water harvesting
.
Journal of Materials Chemistry A
7
(
10
),
5426
5433
.
doi:10.1039/C8TA12372A
.
Wang
X. K.
,
Zeng
J.
,
Yu
X. Q.
,
Liang
C. H.
&
Zhang
Y. F.
2019b
Water harvesting method via a hybrid superwettable coating with superhydrophobic and superhydrophilic nanoparticles
.
Applied Surface Science
465
,
986
994
.
doi:10.1016/j.apsusc.2018.09.210
.
Wang
X. K.
,
Zeng
J.
,
Yu
X. Q.
,
Liang
C. H.
&
Zhang
Y. F.
2020
Beetle-like droplet-jumping superamphiphobic coatings for enhancing fog collection of sheet arrays
.
RSC Advances
10
,
282
288
.
doi:10.1039/C9RA09329J
.
Wang
H.
,
Wang
D. T.
,
Zhang
X. Y.
&
Zhang
Z. Z.
2021a
Modified PDMS with inserted hydrophilic particles for water harvesting
.
Composites Science and Technology
213
,
108954
.
doi:10.1016/j.compscitech.2021.108954
.
Wang
X. K.
,
Zeng
J.
,
Li
J.
,
Yu
X. Q.
,
Wang
Z. K.
&
Zhang
Y. F.
2021b
Beetle and cactus-inspired surface endows continuous and directional droplet jumping for efficient water harvesting
.
Journal of Materials Chemistry A
9
(
3
),
1507
1516
.
doi:10.1039/D0TA10123K
.
Wei
W.
,
Guo
Z. C.
,
Shi
P. J.
,
Zhou
L.
,
Wang
X. F.
,
Li
Z. Y.
,
Pang
S. F.
&
Xie
B. B.
2021
Spatiotemporal changes of land desertification sensitivity in northwest China from 2000 to 2017
.
Journal of Geographical Sciences
31
(
1
),
46
68
.
doi:10.1007/s11442-021-1832-1
.
Welbourne
E. N.
,
Vemulkar
T.
&
Cowburn
R. P.
2021
High-yield fabrication of perpendicularly magnetised synthetic antiferromagnetic nanodiscs
.
Nano Research
14
,
3873
3878
.
doi:10.1007/s12274-021-3307-1
.
Wen
J.
,
Qin
R. M.
,
Zhang
S. X.
,
Yang
X. Y.
&
Xu
M. H.
2020
Effects of long-term warming on the aboveground biomass and species diversity in an alpine meadow on the Qinghai-Tibetan Plateau of China
.
Journal of Arid Land
12
(
2
),
252
266
.
doi:10.1007/s40333-020-0064-z
.
Yan
D. M.
,
Zeng
Q.
,
Xu
S. L.
,
Zhang
Q.
&
Wang
J. Y.
2016
Heterogeneous nucleation on concave rough surfaces: thermodynamic analysis and implications for nucleation design
.
The Journal of Physical Chemistry, C. Nanomaterials and Interfaces
120
(
19
),
10368
10380
.
doi:10.1021/acs.jpcc.6b01693
.
Yang
X. L.
,
Liu
X.
,
Lu
Y.
,
Song
J. L.
,
Huang
S.
,
Zhou
S. N.
,
Jin
Z. J.
&
Xu
W. J.
2016
Controllable water adhesion and anisotropic sliding on patterned superhydrophobic surface for droplet manipulation
.
The Journal of Physical Chemistry C
120
(
13
),
7233
7240
.
doi:10.1021/acs.jpcc.6b02067
.
Yang
Y. M.
,
Xu
L. P.
,
Zhang
X. J.
&
Wang
S. T.
2020
Bioinspired wettable-nonwettable micropatterns for emerging applications
.
Journal of Materials Chemistry. B
8
(
36
),
8101
8115
.
doi:10.1039/D0TB01382J
.
Yu
Z. H.
,
Zhang
H. M.
,
Huang
J. Y.
,
Li
S. H.
,
Zhang
S. N.
,
Cheng
Y.
,
Mao
J. J.
,
Dong
X. L.
,
Gao
S. W.
,
Wang
S. C.
,
Chen
Z.
,
Jiang
Y. X.
&
Lai
Y. K.
2021
Namib desert beetle inspired special patterned fabric with programmable and gradient wettability for efficient fog harvesting
.
Journal of Materials Science & Technology
61
,
85
92
.
doi:10.1016/j.jmst.2020.05.054
.
Zhang
Z. Z.
2009
Preparation and characteristic of self-regulation water-transmitting coating fiber
.
Journal of Wuhan University of Technology (Materials Science Edition)
24
(
4
),
520
524
.
doi:10.1007/s11595-009-4520-z
.
Zhang
Z. Z.
&
Du
H. M.
2011
Micro-dynamic behavior and self-adjusting water transmit mechanism of water-transferring composite
.
Journal of Wuhan University of Technology (Materials Science Edition)
26
(
6
),
1193
1199
.
doi:10.1007/s11595-011-0389-8
.
Zhang
L. Q.
,
Zhang
H.
,
Li
J.
&
Li
J. C.
2016a
Climate change in sandy desertification area of the Northern Shanxi from 1980 to 2014
.
Journal of Desert Research
36
(
4
),
1116
1125
.
doi:10.7522/j.issn.1000-694X.2016.00010
.
Zhang
N. S.
,
Huang
J. Y.
,
Chen
Z.
&
Lai
Y. K.
2016b
Bioinspired special wettability surfaces: from fundamental research to water harvesting applications
.
Small
13
(
3
),
1602992
.
doi:10.1002/smll.201602992
.
Zhang
Y.
,
Zhong
L. S.
&
Guo
Z. G.
2020
A hybrid stainless-steel mesh with nano-array structure applied for efficient fog harvesting by tuning wetting
.
Chemistry Letters
49
(
1
),
79
82
.
doi:10.1246/cl.190799
.
Zhao
X. Y.
,
Wen
J. H.
,
Zhang
M. N.
,
Wang
D. H.
,
Wang
Y. X.
,
Chen
L.
,
Zhang
Y. J.
,
Yang
J. H.
&
Du
Y. W.
2017a
Design of hybrid nanostructural arrays to manipulate SERS-Active substrates by nanosphere lithography
.
ACS Applied Materials & Interfaces
9
(
8
),
7710
7716
.
doi:10.1021/acsami.6b14008
.
Zhao
Z. W.
,
Zhang
L. P.
,
Li
X.
,
Wang
Y. X.
&
Wang
S. L.
2017b
Monitoring vegetation dynamics during the growing season in Ningxia based on MOD13Q1 data
.
Progress in Geography
36
(
6
),
741
752
.
doi:10.18306/dlkxjz.2017.06.009
.
This is an Open Access article distributed under the terms of the Creative Commons Attribution Licence (CC BY 4.0), which permits copying, adaptation and redistribution, provided the original work is properly cited (http://creativecommons.org/licenses/by/4.0/).