Super Hydrophobic SiO2/Phenolic Resin-Coated Filter Screen and Its Application in Efficient Oil–Water Separation

The discharge of industrial liquid waste continues to cause more and more environmental problems. The current research aims at developing a durable and highly efficient filter screen for oil-water separation. In this paper, hydrophobic nano-SiO2 and phenolic resin were used as raw materials. Hydrophobic SiO2 particles were fixed on the surface of the coated filter screen by heating and curing the anchored particles. The surface morphology, element composition, surface roughness and water contact angle of the prepared super hydrophobic SiO2/phenolic resin-coated filter screen were analyzed and discussed by using SEM, EDS, AFM, OCA and other instruments. The results showed that the prepared filter screen contained Si, O, C elements, which proved that the resin coating film had adhered to the filter screen surface. When the aperture of the phenolic resin-coated filter screen was 400 meshes, the drainage angle reached a maximum value of 153.8° ± 0.8°. When two layers of hydrophobic SiO2 phenolic resin were coated on the screen, the surface of the filter screen had a sufficient nano-porous structure and high roughness. The tests showed that the minimum water contact angle of the filter screen exceeded 150°, which indicated excellent chemical resistance. Through the analysis of oil-water separation efficiency of isooctane, gasoline, n-hexane, dodecane, edible oil, dichloromethane and trichloromethane, it was concluded that the lowest separation efficiency for edible oil was 97.2%, and the highest separation efficiency for n-hexane was 99.4%. After 50 cycles of separation, the oil-water separation efficiency for n-hexane was still at 99%.


Introduction
Petroleum production, transportation and usage inevitably lead to oil leakage, which seriously threatens the ecological environment. How to treat oily sewage is the key to protecting the environment. Oil-water separation technology is based on the different physical and chemical properties of oil and water, such as gravity separation technology, filtration, centrifugation, and electrochemical methods [1]. However, the separation efficiency of these conventional oil-water separation technologies is extremely low, and it is difficult to recover oil. There is a high demand in finding simpler and more efficient oil-water separation technologies. Researchers have tried to adjust the inherent wettability of the interface to improve the flow behavior of the liquid phase on the solid surface. Another possible solution is to change the resistance of the filter medium to oil and water.
Recently, the application of superhydrophobic surface preparation has attracted more and more attention, especially in the research process. Liu [2] prepared a super hydrophilic underwater and super oil-repellent mesh membrane by a two-step hydrothermal method to coat pure inorganic ZnO-Co 3 O 4 onto the surface of copper mesh. The contact angle of the oil under water could reach 159.2 • ± 1.3 • (with dichloroethane as the oil drop). Using a polyester non-woven fabric as the matrix and polyphenyloxazine (PBZ) and TiO 2 as the raw materials, Xin [3] developed a simple dip coating and thermal curing method to construct the polyphenyloxazine/TiO 2 -modified fabric, which has super hydrophobic and super lipophilic properties. It can not only efficiently separate the oil-water mixture, but it can also decompose methylene blue under ultraviolet light to achieve self-cleaning of the membrane surface. In Gondal et al. [4], the stainless steel mesh surface was coated with a WO 3 nano-structure via the spraying method to prepare the super hydrophilic underwater super oil-repellent composite mesh membrane. Under the self-gravity drive, the oil-water separation efficiency was significantly improved. Naoyuki Yokoi [5] prepared a super hydrophobic and super lipophilic mesh membrane material via the simple spraying method using alkali-treated polyester mesh as the matrix and SiO 2 and perfluorooctyl triethoxysilane as the raw materials. The produced membrane had high wear resistance, acid and alkali resistance (pH = [2][3][4][5][6][7][8][9][10][11][12][13][14], and excellent oil-water separation performance. SiO 2 nanoparticles have attracted extensive research due to their low density, high porosity, low thermal conductivity, and other advantages. Yanbao Guo [6] prepared lipophilic and hydrophobic silica sol via a sol-gel method and dipped lipophilic and hydrophobic coating on a stainless steel net. Separation experiments of various oil-water mixtures were carried out. They found that the modified mesh had better lipophilic and hydrophobic properties. Consistent lipophilicity and hydrophobicity were obtained under ultrasonic cleaning conditions and in different pH (3)(4)(5)(6)(7)(8)(9)(10)(11) solutions. The modified filter screen had good separation and reusability for different types of oil-water mixtures. Song [7] proposed a new method to construct a three-dimensional hydrophobic nano-SiO 2 porous TIM(thermal insulating material) through a micro-lotion treatment. The polymethyl-hydro-siloxane-modified TIM had a large water contact angle of 166 • and had excellent durability under high temperatures up to 400 • C, 100% high humidity and chemical attack. Liu [8] prepared SiO 2 nanospheres with surface mercaptan groups by using 3-mercaptopropyltriethoxysilane (KH590) and hydroxyl condensation reaction on the surface of silicon (SiO 2 ) particles. This material effectively absorbed more than four times the oil solvent, and the separation efficiency was more than 99%. Under strong acid and alkali conditions or a seawater environment, SiO 2 nanospheres also have more than 20 times the effective oil absorption capacity and high recoverability. To improve the thermal stability and waterproof performance of ordinary cotton, Xu [9] added hydrophobic SiO 2 particles, WPUA (waterborne polyurethane acrylate) and silica aerogel (SA) powder onto the surface of the coating film. The experimental results showed that the thermal stability of coated fabrics is significantly improved by adding aeroneneneba gel and silane-modified SiO 2 . The water contact angle of the film increased significantly when the silane-modified SiO 2 particles were mixed with SA/WPUA. Liu [10] combined a poly (methyl-3,3,3-trifluoropropyl siloxane) (PMTFPS)-modified silicon with low surface free energy fluorosilicone resin to design an ice-resistant surface with super hydrophobicity. The contact angle and rolling angle of the SiO 2 -PMTFPS coating reached 158.5 • and 1 • , respectively. After immersion in solutions of different pH and temperature, the coating had good chemical durability in an aqueous solution.
Metal porous mesh membranes (such as stainless steel mesh, copper mesh, nickel mesh, etc.) have the advantages of good flexibility, strong pressure resistance, easy surface processing, etc., and are often used as the matrix of special wetting oil-water separation membrane materials. Extensive research has been carried out to construct micro-nanorough structures, as well as the modification of hydrophilic substances on the surface of a metal mesh membrane. Lei [11] first developed a polytetrafluoroethylene coating on the surface of the stainless steel mesh, prepared a super hydrophobic and super lipophilic stainless steel mesh film material, and applied it to the study of oil-water separation. Tian [12] prepared a vertical array of micro/nano-hierarchical zinc oxide nanorods on the surface of stainless steel mesh by two solution deposition methods, obtained a super hydrophilic, underwater super hydrophobic film, and analyzed the oil-water separation mechanism in detail. Zhang [13] constructed a new type of super hydrophilic, underwater super oleophobic inorganic membrane material. The membrane was made of Cu(OH) 2 nanowires grown on a copper mesh, which can effectively separate immiscible oil/water mixture and oil in water lotion by gravity. The membrane with high separation flux did not reduce the flux for the continuous separation of 10 L of oil/water mixture. It also had excellent antifouling performance, good oil-water separation effect, and low synthesis cost. Raturi [14] prepared zinc oxide nanowires (NWs), which were coated on a stainless steel (SS) grid by chemical vapor deposition. The synthesized ZnO nws coating mesh showed super underwater hydrophilic, super hydrophobic behavior. This mesh worked in "dehydration" mode, and its super hydrophilic and underwater super hydrophobic properties allowed water to penetrate through the mesh easily while preventing oil passing. The wettability of the Z-nws coating mesh can easily change from a super hydrophilic state to super hydrophobic state by alternating annealing at 300 • C, and vice versa in a hydrogen and oxygen environment.
In summary, people began to study the surface modification of the filter screen, build nanostructures on the surface of the filter screen, and combine them with micron-sized meshes to give the filter screen super hydrophobic/super lipophilic properties. Super hydrophobic/super lipophilic materials are characterized by hydrophobic and lipophilic properties, which can effectively achieve oil-water separation, and then recover the oil. At present, a lot of effort is put into developing various oil-water separation materials with special wettability and super hydrophobicity to achieve the purpose of greatly improving oil-water separation efficiency. New technologies have been explored that can successfully prepare materials for oil-water separation, but these technologies still have many limitations in the oil-water separation process, such as complex preparation process and harsh preparation conditions. Some technologies can only be applied to special substrates, and some still need to use strong acid or strong alkaline reagents, which pollute the environment. The prepared oil-water separation materials have the disadvantages of poor stability and cannot be used for a long time. It is of great significance to rapidly produce stable and repeatable super hydrophobic and super lipophilic mesh membranes from common cheap raw materials and simple preparation methods.
Because the separation efficiency of traditional oil-water separation materials is not high, the surface roughness of a traditional phenolic resin-coated filter screen is limited, resulting in insufficient hydrophobicity, which reduces the oil-water separation efficiency of the filter screen. In this paper, hydrophobic silicon dioxide particles are introduced into the phenolic resin system by curing method, and the SiO 2 nanoparticles/phenolic resin coating film is prepared on the surface of the filter screen. Compared with the traditional phenolic resin coating film, due to the introduction of hydrophobic SiO 2 nano-examples, the phenolic resin-coated filter screen increases the surface roughness of the filter screen, improves the surface hydrophobicity of the filter screen, improves the chemical resistance of the coating film, and improves the oil-water separation efficiency.
Hydrophobic SiO 2 nanoparticles are widely used in many industrial fields due to their simple preparation, excellent performance, and easy access. Stainless steel filters have excellent mechanical, chemical and high-temperature resistance. In our current study, hydrophobic SiO 2 nanoparticles were heated and solidified on a stainless steel filter screen through phenolic resin. Experimental and analyzing equipment such as SEM (scanning electron microscope), EDS (energy dispersion spectrum), OCA (overview contact angle), etc., were employed to investigate the surface morphology, element composition, water contact angle and other parameters of a SiO 2 nano-phenolic resin filter screen. Six oilwater mixtures were used to test the oil-water separation performance of the filter screen. Obtained results were compared with those of relevant researchers. It was found that the developed filter screen has significant advantages in oil-water separation efficiency.

Research Route
The test process is shown in Figure 1. Firstly, hydrophobic nano-SiO 2 and hydrophobic SiO 2 solutions were developed. Then, the SiO 2 /phenolic resin-coated filter screen was prepared with different concentrations of SiO 2 solution. The state of hydrophobic nano-SiO 2 particles was observed by transmission electron microscope at different temperatures. The scanning electron microscope and atomic force microscope were used to observe the surface morphology of hydrophobic SiO 2 /phenolic resin-coated filter screen. EDS was used to test the element composition of the filter screen. OCA method was employed to test the rolling angle of the filter screen surface. HCL solution, NaOH solution and other reagents were used to test the chemical resistance of the filter screen. Finally, six different oil-water mixtures were used to test the oil-water separation efficiency of the filter screen.
water contact angle and other parameters of a SiO2 nano-phenolic resin filter screen. Six oil-water mixtures were used to test the oil-water separation performance of the filter screen. Obtained results were compared with those of relevant researchers. It was found that the developed filter screen has significant advantages in oil-water separation efficiency.

Research Route
The test process is shown in Figure 1. Firstly, hydrophobic nano-SiO2 and hydrophobic SiO2 solutions were developed. Then, the SiO2/phenolic resin-coated filter screen was prepared with different concentrations of SiO2 solution. The state of hydrophobic nano-SiO2 particles was observed by transmission electron microscope at different temperatures. The scanning electron microscope and atomic force microscope were used to observe the surface morphology of hydrophobic SiO2/phenolic resin-coated filter screen. EDS was used to test the element composition of the filter screen. OCA method was employed to test the rolling angle of the filter screen surface. HCL solution, NaOH solution and other reagents were used to test the chemical resistance of the filter screen. Finally, six different oil-water mixtures were used to test the oil-water separation efficiency of the filter screen.

Experimental Materials and Instruments
The main drugs and reagents required for the test are shown in Table 1. The main drugs were purchased from manufacturers, and their specifications were also tested by manufacturers. The main test equipment and instruments required for the test are shown in Table 2.

Experimental Materials and Instruments
The main drugs and reagents required for the test are shown in Table 1. The main drugs were purchased from manufacturers, and their specifications were also tested by manufacturers. The main test equipment and instruments required for the test are shown in Table 2.

Preparation of the SiO 2 /Phenolic Resin Filter Screen
A certain amount of phenolic resin was weighed and dissolved in ethyl acetate solvent using intelligent digital ultrasonic instrument for 10 to 30 min to prepare the 5% phenolic resin solution. A certain amount of hydrophobic SiO 2 was weighed and dispersed in the solvent. It was dissolved in ultrasound for 10 to 30 min to prepare hydrophobic SiO 2 dispersions of different concentrations. Spin coating phenol formaldehyde resin ethyl acetate solution and hydrophobic SiO 2 ethyl acetate solution on glass slide and filter screen were processed with a desktop homogenizer. After solidifying them in an electric thermostatic blast drying oven at 160 • C for 30 min, a super hydrophobic film and film filter screen were developed.

Characterization Analysis
The morphologies of membrane surface were observed with the SEM (SEM, Quanta FEI 450, Boynton Beach, FL, USA) after being coated with hydrophobic nano-SiO 2 . An atomic force microscope (AFM, Agilent-S5500, Agilent, Palo Alto, CA, USA) was employed to analyze the surface states of the prepared membranes. The structure and morphology of hydrophobic nano-SiO 2 were analyzed with the X-ray diffractometer (XRD, D8 Advance, Bruker, Billerica, MA, USA) CuK α Ray (λ = 1.5418 Å); The particle size distribution of hydrophobic nano-SiO 2 was observed by the transmission electron microscopy (TEM, JEM-2100, Akishima, Japan). Thermogravimetric analysis (TGA/SDTA851) was conducted to test the heat resistance of hydrophobic nano-SiO 2 . The surface roughness was tested by the atomic force microscope (AFM, Nanoscope IIIa Multimode, Santa Barbara, CA, USA).

Contact Angle Test
The contact angle, rolling angle and oil contact angle of deionized water on the film surface were measured using the contact angle measuring instrument of POWEREACH of Shanghai Zhongchen Digital Technology Equipment Co., Ltd. (Shanghai, China).
Specific process: The sample was placed on the platform of the contact angle measuring instrument, and a micro syringe was used to take 5 µL of deionized water (or isooctane) to drop it on the sample surface. The contact angle and the rolling angle were measured. The method of measuring the oil contact angle was the same as that for water contact angle.

Chemical Resistance Test
To evaluate the performance of samples under extreme pH conditions, the following experiments were conducted to test the chemical resistance of a hydrophobic SiO 2 /phenolic resin-coated filter screen.
The three filter screen samples were soaked in three solutions, respectively, sealed and left to stand. The contact angle of the sample was measured at intervals. The preparation of solution: 0.098 g of 37% HCl, was weighed and dissolved in 100 mL of deionized water to obtain an acid solution with pH = 2; then, 0.04 g of NaOH was weighed and dissolved into 100 mL of deionized water to obtain alkaline solution with pH = 13; 5 g NaCl was weighed and dissolved into 100 mL deionized water to obtain 3.5 wt.% salt solution with pH = 7. The filter screen was soaked in toluene, ethyl acetate, acetone, tetrahydrofuran, and ethanol for a certain time, and the change of water contact angle was tested on the surface of the screen before and after soaking.

Oil-Water Separation Test
Preparation process of SiO 2 /phenolic resin-coated filter screen: A small amount of Sudan II was used to dye isooctane and other oils. A small amount of methylene blue was used to dye deionized water for experimental observation. Oil-water separation device: the prepared sample was cut into a 3 × 3 cm square, placed between two clamps, and the sample was clamped and sealed. The upper and lower ends of the clamps were connected with quartz glass tubes, and the device was placed at an angle of 45 • . Oil-water separation test: an appropriate amount (about 15 g) of deionized water and appropriate amount of oil were weighed with a balance, mixed and then poured into the oil-water separation device. The super hydrophobic and super lipophilic filter screen sample can support the deionized water, but the oil passes through the screen. The trapped deionized water was weighed with a balance, and the mass of this part of deionized water was denoted by m 0 . Then, the separation efficiency of the filter screen sample is [15]: where m is the quality of deionized water.

Characterization of Hydrophobic SiO 2
Hydrophobic nano-SiO 2 was used to construct the surface structure of superhydrophobic coating film. It can be seen from Figure 2a that the morphology of hydrophobic nano-SiO 2 used was amorphous. Figure 2b shows that SiO 2 nanoparticles have good heat resistance. Its weight lost 4.2% at 316 • C because of the adsorption of a few other substances on the surface. However, between 316 and 823 • C, due to the partial decomposition of hydrophobic nano-SiO 2 , about 8.2% of the mass percentage was lost [16]. The transmission electron microscope image of hydrophobic nano-SiO2 is shown in Figure 2c. The dark part in the figure shows SiO 2 nano-particles, but the dark degree is different at different positions. Because the particles reach the nano-meter level, a large number of positive and negative charges accumulate on their surface area. The agglomeration of surface charges causes the agglomeration of nano-particles, and the van der Waals force between them was far greater than their own gravity, such that a large number of particles were concentrated together to form an agglomeration phenomenon. However, the agglomeration of SiO 2 particles affects the coating filter screen. Before the test, ultrasonic dispersion is required to inhibit the agglomeration of SiO 2 nanoparticles, which is relatively dispersed under TEM. It was observed that the SiO 2 cluster composed of SiO 2 has a diameter of tens of nanometers. It can be considered that the agglomeration of SiO 2 was effectively suppressed; SiO 2 can be used in the next experiment.

Contact Angle Analysis of the SiO2/Phenolic Resin-Coated Filter Screen
As shown in Figure 3, the mass percentage of hydrophobic nano-SiO2 was controlled to change from 15% to 40% with the filter screen as the base material. It was found that the water contact angle was gradually increased at first, and then decreased after reaching the highest point. When the content of hydrophobic nano-SiO2 increases from 15% to 30%, the water contact angle increases from 144.1° ± 0.8° to 153.5° ± 1.2° and then to 155.1° ± 1.3°, continuously. When the amount of SiO2 was 40%, the water contact angle decreased

Contact Angle Analysis of the SiO 2 /Phenolic Resin-Coated Filter Screen
As shown in Figure 3, the mass percentage of hydrophobic nano-SiO 2 was controlled to change from 15% to 40% with the filter screen as the base material. It was found that the water contact angle was gradually increased at first, and then decreased after reaching the highest point. When the content of hydrophobic nano-SiO 2 increases from 15% to 30%, the water contact angle increases from 144.1 • ± 0.8 • to 153.5 • ± 1.2 • and then to 155.1 • ± 1.3 • , continuously. When the amount of SiO 2 was 40%, the water contact angle decreased from 155.1 • ± 1.3 • to 145.9 • ± 0.9 • , and to 138.2 • ± 0.8 • , finally.

Contact Angle Analysis of the SiO2/Phenolic Resin-Coated Filter Screen
As shown in Figure 3, the mass percentage of hydrophobic nano-SiO2 wa to change from 15% to 40% with the filter screen as the base material. It was the water contact angle was gradually increased at first, and then decreased af the highest point. When the content of hydrophobic nano-SiO2 increases from the water contact angle increases from 144.1° ± 0.8° to 153.5° ± 1.2° and then 1.3°, continuously. When the amount of SiO2 was 40%, the water contact angl from 155.1° ± 1.3° to 145.9° ± 0.9°, and to 138.2° ± 0.8°, finally.

Analysis of Chemical Components on the Surface of the SiO2/Phenolic Resin-Coa Screen
A superhydrophobic SiO2/phenolic resin-coated filter screen was obtaine SiO2 nanoparticles on the surface of a phenolic resin-coated filter screen in ord the curing reaction effect of phenolic resin. In this paper, we used infrared sp

Analysis of Chemical Components on the Surface of the SiO 2 /Phenolic Resin-Coated Filter Screen
A superhydrophobic SiO 2 /phenolic resin-coated filter screen was obtained by curing SiO 2 nanoparticles on the surface of a phenolic resin-coated filter screen in order to detect the curing reaction effect of phenolic resin. In this paper, we used infrared spectroscopy to test the spectra of phenolic resin and EDS to detect the element composition of the coated filter screen to confirm the presence of SiO 2 particles in the coating film. Figure 4a shows the infrared spectrum of phenolic resin before and after curing at 160 • C. Figure 4b shows the element content of the super hydrophobic SiO 2 /phenolic resin film filter screen. From Figure 4a, by comparing the infrared spectra of phenolic resin before and after curing, the strong and wide absorption band of 3379 cm −1 of phenolic resin before and after thermal curing is the absorption peak of the -OH bond of phenol. The C-H stretching vibration absorption peak of methylene near 2732 cm −1 is not obvious. Furthermore, 1605 and 1496 cm −1 are the vibration absorption peaks of the benzene ring skeleton stretching, 1243 cm −1 is the phenol hydroxyl stretching vibration absorption peak, and 1150 cm −1 is the ether bond stretching vibration absorption peak. The shoulder peak appearing at 1651 cm −1 after curing is the carbonyl C=O stretching vibration absorption peak. The hydroxymethyl C-O is formed by curing reaction. The stretching vibration disappears at 988 cm −1 , indicating that the phenolic resin undergoes a crosslinking reaction under the curing conditions [17]. It can be seen from Figure 4b that in addition to its own elements such as Fe, Cr, Ni and Mn, the stainless-steel filter screen also contains the elements C, O and Si. The elements C and O come from the phenolic resin, and the element Si comes from the hydrophobic SiO 2 particles. The appearance of Si, O and C elements indicates that the spin-coated SiO 2 particles and phenolic resin have successfully adhered to the filter screen. curing conditions [17]. It can be seen from Figure 4b that in addition to its own elements such as Fe, Cr, Ni and Mn, the stainless-steel filter screen also contains the elements C, O and Si. The elements C and O come from the phenolic resin, and the element Si comes from the hydrophobic SiO2 particles. The appearance of Si, O and C elements indicates that the spin-coated SiO2 particles and phenolic resin have successfully adhered to the filter screen.

Influence of Filter Screens with Different Apertures on Contact Angle and Rolling Angle of Coating Film
Different filter screen apertures will affect the hydrophobicity of the SiO2/phenolic resin-coated filter screen. In order to study the relationship between the filter screen aperture and the hydrophobicity of the coated filter screen, we used filters with different apertures for the hydrophobic angle test in this paper, and the test results are shown in Figure 5.

Influence of Filter Screens with Different Apertures on Contact Angle and Rolling Angle of Coating Film
Different filter screen apertures will affect the hydrophobicity of the SiO 2 /phenolic resin-coated filter screen. In order to study the relationship between the filter screen aperture and the hydrophobicity of the coated filter screen, we used filters with different apertures for the hydrophobic angle test in this paper, and the test results are shown in Figure 5.   Figure 5 depicts the trend chart for the influence of filter screens with different apertures on the contact angle and rolling angle of the coating film. We explored the influence of filter screen apertures of 500, 450, 400, 300, 200, 150, 100 and 80 mesh on the water contact angle and rolling angle. It can be seen from Figure 5 that the water contact angle on the film filter screen is rising and the rolling angle is declining when the SiO2 is 30%, the phenolic resin is 0.5%, and the aperture is between 100 and 400 mesh. When the aperture is 400 mesh, the maximum water contact angle of the film filter screen is 153.8° ± 0.8°. When the aperture exceeds 400 mesh, the water contact angle starts to decline, and the rolling angle shows an upward trend. The possible reason is that it is difficult for the coating film to capture the air through its surface structure, thus leading to a decrease in hydrophobicity when the pore diameter increases. In addition, the smaller aperture may not only cause insufficient contact surface between water and air, but it may also increase the separation resistance during oil-water separation. In conclusion, the 400 mesh filter screen was selected as the next experimental exploration.

Surface Structure and Super Hydrophobicity of the Filter Screen with Different Layers of Film
In order to observe the influence of different layers of film on hydrophobicity, we used SEM and AFM to observe the surface morphology and surface roughness of the SiO2 film filter screen, taking the 400 mesh filter screen as an example in this paper. The test  Figure 5 depicts the trend chart for the influence of filter screens with different apertures on the contact angle and rolling angle of the coating film. We explored the influence of filter screen apertures of 500, 450, 400, 300, 200, 150, 100 and 80 mesh on the water contact angle and rolling angle. It can be seen from Figure 5 that the water contact angle on the film filter screen is rising and the rolling angle is declining when the SiO 2 is 30%, the phenolic resin is 0.5%, and the aperture is between 100 and 400 mesh. When the aperture is 400 mesh, the maximum water contact angle of the film filter screen is 153.8 • ± 0.8 • . When the aperture exceeds 400 mesh, the water contact angle starts to decline, and the rolling angle shows an upward trend. The possible reason is that it is difficult for the coating film to capture the air through its surface structure, thus leading to a decrease in hydrophobicity when the pore diameter increases. In addition, the smaller aperture may not only cause insufficient contact surface between water and air, but it may also increase the separation resistance during oil-water separation. In conclusion, the 400 mesh filter screen was selected as the next experimental exploration.

Surface Structure and Super Hydrophobicity of the Filter Screen with Different Layers of Film
In order to observe the influence of different layers of film on hydrophobicity, we used SEM and AFM to observe the surface morphology and surface roughness of the SiO 2 film filter screen, taking the 400 mesh filter screen as an example in this paper. The test results are shown in Figure 6. ture is 400 mesh, the maximum water contact angle of the film filter screen is 153.8° ± 0.8°. When the aperture exceeds 400 mesh, the water contact angle starts to decline, and the rolling angle shows an upward trend. The possible reason is that it is difficult for the coating film to capture the air through its surface structure, thus leading to a decrease in hydrophobicity when the pore diameter increases. In addition, the smaller aperture may not only cause insufficient contact surface between water and air, but it may also increase the separation resistance during oil-water separation. In conclusion, the 400 mesh filter screen was selected as the next experimental exploration.

Surface Structure and Super Hydrophobicity of the Filter Screen with Different Layers of Film
In order to observe the influence of different layers of film on hydrophobicity, we used SEM and AFM to observe the surface morphology and surface roughness of the SiO2 film filter screen, taking the 400 mesh filter screen as an example in this paper. The test results are shown in Figure 6. Based on the SEM and AFM in Figure 6, the surface of the original filter screen sample without spin coating is smooth (Figure 6(a1, a2)). The sample surface with a layer of spin coating has a certain nano-porous structure, which is combined with the micron mesh to form a certain micro-nano-structure. However, the appropriate rough structure cannot be constructed due to the thin coating; the contact angle is small and the rolling angle is large (Figure 6(b1, b2)). Thus, the surface is not super hydrophobic. The sample surface with two layers of spin coating film has an abundant nano-porous structure. The roughness Figure 6. (a1-d1) SEM images of the filter film (400 meshes), which was heated and fixed by 0, 1, 2 and 3 spin-coating phenolic resin and hydrophobic nano-silica. (a2-d2) AFM image for the front side of the filter film (400 meshes), which was heated and fixed by 0, 1, 2 and 3 spin-coating phenolic resin and hydrophobic nano-silica.
Based on the SEM and AFM in Figure 6, the surface of the original filter screen sample without spin coating is smooth (Figure 6(a1, a2)). The sample surface with a layer of spin coating has a certain nano-porous structure, which is combined with the micron mesh to form a certain micro-nano-structure. However, the appropriate rough structure cannot be constructed due to the thin coating; the contact angle is small and the rolling angle is large (Figure 6(b1, b2)). Thus, the surface is not super hydrophobic. The sample surface with two layers of spin coating film has an abundant nano-porous structure. The roughness and contact angle are substantially increased, while the rolling angle is significantly smaller. In addition, this sample has superhydrophobic properties ( Figure 6(c1, c2)). Although the surface of the sample with three layers of spin coating is superhydrophobic, the surface roughness barely changes ( Figure 6(d1, d2)). From the AFM diagram, we have observed that the original surface is relatively flat. When the hydrophobic SiO 2 nanoparticles undergo continuous coating, the sample surface roughness is increased significantly. When two layers of coating are spun, the surface roughness barely changes. According to the Cassie Baxter model, the roughness coefficient increase is the key for the construction of a super hydrophobic coating.
As shown in Figure 7, in order to explore the impact of different film layers on the filter screen, we measured the water contact angle on the phenolic resin coating without SiO 2 nanoparticles; the contact angle was 104.1 • ± 0.3 • . When a layer of SiO 2 /phenolic resin coating was applied, the contact angle of the surface water suddenly changes to 143.5 • ± 0.5 • , and the rolling angle decreased from 58.9 • to 17.1 • . When two or three layers of SiO 2 /phenolic resin coatings were applied, the contact angle of the surface water was 155.1 • ± 0.2 • and 156.2 • ± 0.2 • , respectively; no significant improvement was found. In addition, considering that the increasing number of layers will affect the efficiency of oilwater separation, the filter with two-layer SiO 2 /phenolic resin coating was finally adopted in the experiment, which not only saved the operation time of preparing the coating, but also reduced the time required for oil-water separation. To sum up, the spin coating of two-layer films was used for this experimental exploration. 2022, 15, x FOR PEER REVIEW the surface roughness barely changes ( Figure 6(d1, d2)). From the A observed that the original surface is relatively flat. When the hydro ticles undergo continuous coating, the sample surface roughness cantly. When two layers of coating are spun, the surface roughnes cording to the Cassie Baxter model, the roughness coefficient incre construction of a super hydrophobic coating.
As shown in Figure 7, in order to explore the impact of differ filter screen, we measured the water contact angle on the phenolic SiO2 nanoparticles; the contact angle was 104.1° ± 0.3°. When a layer coating was applied, the contact angle of the surface water sudden 0.5°, and the rolling angle decreased from 58.9° to 17.1°. When tw SiO2/phenolic resin coatings were applied, the contact angle of th 155.1° ± 0.2° and 156.2° ± 0.2°, respectively; no significant improv addition, considering that the increasing number of layers will affec water separation, the filter with two-layer SiO2/phenolic resin coatin in the experiment, which not only saved the operation time of prep also reduced the time required for oil-water separation. To sum u two-layer films was used for this experimental exploration.

Study on Acid, Alkali and Organic Solvent Resistance of Coated Filte
In order to test the chemical resistance of the SiO2 phenolic resi different pH solutions and different oil solvents were used to test its test results are shown in Figure 8.

Study on Acid, Alkali and Organic Solvent Resistance of Coated Filter Screen
In order to test the chemical resistance of the SiO 2 phenolic resin-coated filter screen, different pH solutions and different oil solvents were used to test its hydrophobicity. The test results are shown in Figure 8.

Study on Acid, Alkali and Organic Solvent Resistance of Coated Filter Screen
In order to test the chemical resistance of the SiO2 phenolic resin-coated filter screen, different pH solutions and different oil solvents were used to test its hydrophobicity. The test results are shown in Figure 8.  The super hydrophobic and super lipophilic coating film could be damaged under harsh application conditions such as strong acid, strong base and solvent; thus, the chemical stability of the coating film has important impact on the actual application of the coating film [18]. To judge the chemical stability of the film, the filter screen was immersed into a strong acid, strong alkali, salt solution and solvent to measure its contact angle. The sodium chloride solution environment can test the influence of three corrosion factors, water, oxygen and chloride ions. Figure 8a shows the change trend of the water contact angle of the coating samples immersed in hydrochloric acid solution with pH = 2, sodium hydroxide solution with pH = 13, 3.5 wt.% sodium chloride solution, ethanol, toluene, ethyl acetate, acetone and tetrahydrofuran with time. It can be seen from Figure 8b that the water contact angle of the film surface has no obvious change during the 400 h immersion in acid, alkali, salt solution, and the organic solvent immersion. The water contact angle of the film surface keeps above 150 • during 60 h in solvent. It has good acid and alkali resistance and solvent corrosion resistance. The test results showed that the prepared samples have excellent super hydrophobic and super lipophilic properties, acid and alkali resistance, solvent corrosion resistance, chemical stability, and high engineering application potentials.

Study on Oil-Water Separation Efficiency of the Filter Screen
In order to study the oil-water separation efficiency of a SiO 2 /phenolic resin-coated filter screen, we used different kinds of oil-water mixtures to test it and conducted 60 repeated tests on the oil-water mixture with the highest separation efficiency to verify the durability of the SiO 2 /phenolic resin-coated filter screen in this paper. The test results are shown in Figure 9.
The oil-water separation principle of the SiO 2 /phenolic resin film filter screen is shown in Figure 9a. The oil-water mixture passes through the phenolic resin film filter screen with SiO 2 particles from the top. Because of the special lipophilicity and hydrophobicity of the filter screen, the oil and water in the oil-water mixture are separated. The upper part prevents water from passing through, while the oil can smoothly pass through the filter screen to the lower part. Figure 9b is a partial enlarged view of the SiO 2 /phenolic resin-coated filter screen. Figure 9c shows a comparison between the filter screen sample and the oil-water separation efficiency of the modified fiber membrane in the literature [14] through water and different oils. In this paper, several oils such as edible oil, isooctane, gasoline, n-hexane, dodecane, dichloromethane, and trichloromethane were selected for the experiment. The oil-water separation efficiency of all oils tested reached more than 97%, and the n-hexane separation efficiency was the highest, reaching 99.4%. The lowest separation efficiency of edible oil was 97.2%, while the oil-water separation efficiency of modified fiber membrane was also positive. For hexane, the separation efficiency was the highest, about 93.1%, while the carbon tetrachloride separation efficiency was the lowest, about 91.5%. By comparing the two oil-water separation materials, it was concluded that the oil-water separation efficiency of n-hexane increased by about 6.3%. Figure 9d shows the trend chart of oil-water separation efficiency for multiple separations of the n-hexane and water mixture by the sample filter. After 50 cycles of oil-water separation, the water contact angle changed from 154.1 • to 153.2 • , while the separation efficiency decreased from 99.4% to 99%. The separation efficiency was still above 99% after multiple cycles. To sum up, the experimental results show that this type of filter screen had excellent super hydrophobic and super lipophilic performance, and its oil-water separation effect was also excellent and stable.
hydroxide solution with pH = 13, 3.5 wt.% sodium chloride solution, ethanol, toluene, ethyl acetate, acetone and tetrahydrofuran with time. It can be seen from Figure 8b that the water contact angle of the film surface has no obvious change during the 400 h immersion in acid, alkali, salt solution, and the organic solvent immersion. The water contact angle of the film surface keeps above 150° during 60 h in solvent. It has good acid and alkali resistance and solvent corrosion resistance. The test results showed that the prepared samples have excellent super hydrophobic and super lipophilic properties, acid and alkali resistance, solvent corrosion resistance, chemical stability, and high engineering application potentials.

Study on Oil-Water Separation Efficiency of the Filter Screen
In order to study the oil-water separation efficiency of a SiO2/phenolic resin-coated filter screen, we used different kinds of oil-water mixtures to test it and conducted 60 repeated tests on the oil-water mixture with the highest separation efficiency to verify the durability of the SiO2/phenolic resin-coated filter screen in this paper. The test results are shown in Figure 9.

Analysis of Oil-Water Separation Model
In order to study the oil-water separation process, we discuss the interaction between oil and water and the filter screen in the oil-water separation process, and further explain the working mechanism of the SiO 2 /phenolic resin-coated filter screen in this paper. The oil-water separation diagram is shown in Figure 10. The oil-water separation principle of the SiO2/phenolic resin film filter screen is shown in Figure 9a. The oil-water mixture passes through the phenolic resin film filter screen with SiO2 particles from the top. Because of the special lipophilicity and hydrophobicity of the filter screen, the oil and water in the oil-water mixture are separated. The upper part prevents water from passing through, while the oil can smoothly pass through the filter screen to the lower part. Figure 9b is a partial enlarged view of the SiO2/phenolic resin-coated filter screen. Figure 9c shows a comparison between the filter screen sample and the oil-water separation efficiency of the modified fiber membrane in the literature [14] through water and different oils. In this paper, several oils such as edible oil, isooctane, gasoline, n-hexane, dodecane, dichloromethane, and trichloromethane were selected for the experiment. The oil-water separation efficiency of all oils tested reached more than 97%, and the n-hexane separation efficiency was the highest, reaching 99.4%. The lowest separation efficiency of edible oil was 97.2%, while the oil-water separation efficiency of modified fiber membrane was also positive. For hexane, the separation efficiency was the highest, about 93.1%, while the carbon tetrachloride separation efficiency was the lowest, about 91.5%. By comparing the two oil-water separation materials, it was concluded that the oil-water separation efficiency of n-hexane increased by about 6.3%. Figure 9d shows the trend chart of oil-water separation efficiency for multiple separations of the n-hexane and water mixture by the sample filter. After 50 cycles of oil-water separation, the water contact angle changed from 154.1° to 153.2°, while the separation efficiency decreased from 99.4% to 99%. The separation efficiency was still above 99% after multiple cycles. To sum up, the experimental results show that this type of filter screen had excellent super hydrophobic and super lipophilic performance, and its oil-water separation effect was also excellent and stable.

Analysis of Oil-Water Separation Model
In order to study the oil-water separation process, we discuss the interaction between oil and water and the filter screen in the oil-water separation process, and further explain the working mechanism of the SiO2/phenolic resin-coated filter screen in this paper. The oil-water separation diagram is shown in Figure 10. To make the oil-water separation process clearer, we have drawn the oil-water separation model, as shown in Figure 10. Formula (1) is used to describe the model [19]: To make the oil-water separation process clearer, we have drawn the oil-water separation model, as shown in Figure 10. Formula (1) is used to describe the model [19]: In Equation (2), γ is the surface tension of the liquid; l is the perimeter of the hole; R is the radius of curvature; A is the area of the hole; θ is the forward contact angle of the membrane surface.
When θ > 90 • , the film can withstand a certain pressure because ∆p > 0. On the contrary, when θ < 90 • , liquid can spontaneously pass through the membrane, because ∆p < 0. Figure 10a is a schematic diagram of the intermediate state of water on the membrane. This membrane contains phenolic resin material, which has a certain amount of lipophilicity. The angle θ is very small and ∆p < 0, and the membrane cannot bear any pressure. When the oil contacts the membrane, it spontaneously penetrates the membrane under the action of gravity. When water contacts the membrane, the membrane is first moistened by oil, and the multi-layer structure is occupied by oil, which enhances the water resistance of the membrane. The separation membrane maintains a super hydrophobic state θ greater than 90 • and ∆p > 0, and the membrane can maintain a certain water pressure resistance within a certain maintenance range (Figure 10b). Therefore, water cannot penetrate the membrane and is trapped on the membrane. The surface free energy of the super hydrophobic and super lipophilic surfaces is between the surface tension of water (γ = 0.073 N/m) and the surface tension of the oil (usually γ = 0.020-0.030 N/m). As shown in Figure 10, the mesh is approximately cylindrical, and the super hydrophobic and filter screen is approximately a combination of many capillary structures. When the water contacts the filter screen, it takes a convex shape in the mesh. The convex shape can maintain the water under the Cassie Baxter model, making the water more mobile and excluded. When the oil contacts the filter screen, the oil can wet the mesh and present a concave shape, while the concave shape can make the oil present the Wenzel state [20] and then soak the mesh. The two curved liquid surfaces will generate a pressure pointing to water and a pressure pointing to the mesh, so that the filter screen can achieve the characteristics of oil penetration and water interception.

Conclusions
In the current research, a new filter screen was successfully designed and fabricated by heating and curing hydrophobic nano-SiO 2 /phenolic resin on the surface of a filter screen. Since the heat resistance of the hydrophobic resin filter screen is extremely strong, the coating layer fully meets the thermosetting conditions. Major conclusions based on our experimental test results are drawn as follows: (1) A superhydrophobic and lipophilic SiO 2 /phenolic resin-coated filter screen was successfully designed and fabricated by introducing hydrophobic nano-SiO 2 particles into the rotary coated phenolic resin through heating, baking, and curing. The surface roughness of the filter screen was enhanced substantially. As a result, the water contact angle and the hydrophobicity were increased, which greatly improved the efficiency of the oil-water separation. (2) The hydrophobic nano-SiO 2 concentration, the number of spinning coated SiO 2 /phenolic resin film layers, and the mesh diameter of the filter screen were analyzed deeply. These factors control the water contact angle of the SiO 2 /phenolic resin-coated filter screen. The optimized fabrication conditions were determined as: hydrophobic nano-SiO 2 with a concentration of 30%, two layers of SiO 2 /phenolic resin film by spinning coated, and pore diameter of 400. The filter screen prepared under these conditions had a large surface roughness and good hydrophobicity. (3) The highest oil-water separation efficiency of the fabricated SiO 2 /phenolic resin filter screen for n-hexane was 99.4%, which is about 6.3% higher than that of the fiber membrane. After 50 cycles of continuous oil-water separation, the oil-water separation efficiency for n-hexane was still above 99%, indicating that the coated filter screen has good durability. The preparation process of the filter screen was simple, and the various oil-water separation efficiencies was better. Informed Consent Statement: Not applicable.

Data Availability Statement:
The raw/processed data required to reproduce these findings cannot be shared at this time, as the data also form part of an ongoing study.

Conflicts of Interest:
All authors disclose that they have no relevant relationships.