Significance
Bulk water is a highly stable solvent, but water microdroplets possess strikingly different properties, such as the presence of hydroxyl radicals (•OH) at the microdroplet periphery. Previous studies demonstrated the recombination of •OH into H2O2 molecules and the capture of •OH by oxidizing other molecules, but the origin of the •OH has been a controversial topic with clear evidence that •OH can arise from external gases in contact with the microdroplet surface but also from the formation of the microdroplet itself. This study shows that the latter can primarily arise from contact electrification, which is shown to be a universal phenomenon for water–solid interfaces.
Keywords: contact electrification, water droplets, hydroxyl radical, hydrogen peroxide, solid–water interface
Abstract
Contact electrification between water and a solid surface is crucial for physicochemical processes at water–solid interfaces. However, the nature of the involved processes remains poorly understood, especially in the initial stage of the interface formation. Here we report that H2O2 is spontaneously produced from the hydroxyl groups on the solid surface when contact occurred. The density of hydroxyl groups affects the H2O2 yield. The participation of hydroxyl groups in H2O2 generation is confirmed by mass spectrometric detection of 18O in the product of the reaction between 4-carboxyphenylboronic acid and 18O–labeled H2O2 resulting from 18O2 plasma treatment of the surface. We propose a model for H2O2 generation based on recombination of the hydroxyl radicals produced from the surface hydroxyl groups in the water–solid contact process. Our observations show that the spontaneous generation of H2O2 is universal on the surfaces of soil and atmospheric fine particles in a humid environment.
When two materials of different chemical composition are brought into intimate contact, it is common for the two materials to become oppositely charged. Early work suggested that this charging was caused by ion transfer, but more recent work, as reviewed by Lin, Chen, and Wang (1), indicates that electron transfer plays a dominant role in liquid–solid contact electrification (CE). Of special interest is CE involving water droplets and insulators, which began in the 1990s with studies by Matsui et al.; Yatsuzuka, Mizuno, et al.; and Yatsuzuka, Higashiyama, et al. (2–4). They found that the water droplet is always positively charged when it slides over an insulator surface. They conjectured that the adsorption of negative ions from water to the insulator surface was responsible for the contact charging between the water and the insulator. More recent work (1, 5) suggests that both electron and ion transfer occur at the liquid–solid interface but that electron transfer may often predominate. In water, if an electron is to be transferred, then it may seem likely that it would originate from the hydroxide anion (OH−) causing the formation of the hydroxyl radical (•OH), which may go on to recombine with other hydroxyl radicals to generate hydrogen peroxide (H2O2). A recent publication by Ben-Amotz predicted that hydrogen bond charge transfer in water may have far-reaching chemical implications (5), and it is proposed that even transfer from H2O to form H2O+ occurs in which the H2O+ cation rapidly reacts with water to yield H3O+ and •OH (6). While evidence of the formation of H2O2 in water droplets seems to have been well established (7–14), some have claimed that it arises solely from the adsorption of ozone (O3) (10) or solely from cavitation (14). A recent study employing ultrapure nitrogen (N2) as a nebulizing gas showed, however, that H2O2 in sprayed water droplets was formed without the adsorption of ozone (13), although there can be no denying that ozone adsorption promotes H2O2 production as does oxygen (O2) adsorption (13), as is also the case for cavitation. The question has remained unsettled regarding where the electron that forms •OH goes. It has been speculated that the electron may jump onto positively charged droplets, be captured by water at the air–water interface, or go to the walls in some form of contact electrification (13). In what follows, evidence is presented that contact electrification plays a leading role, and that in the case of silica this involves hydroxyl groups on the solid surface in contact with water.
Electron transfer at a water–solid interface is induced by the overlap of electron clouds, which occurs when water molecules collide with atoms or molecules on the solid surface (15, 16). Notably, electron transfer at a water–solid interface can drive catalytic reactions and facilitate pollutant degradation (17). Liquid–solid triboelectric nanogenerators have also been designed based on this observation (1, 18). Despite advances in applications of electron transfer at water–solid interfaces, the exact nature of the physicochemical processes that accompany charge transfer is poorly understood. Recently, quantum theory calculations have been used to explain the interactions between water and atomically smooth solid surfaces by considering the coupling of water fluctuations to electronic excitations within the solid (19). In practice, atomically smooth solid surfaces do not exist in any material because of the presence of oxygen-containing chemical groups on the solid surface. Surface chemical groups may therefore play an important role in the physicochemical processes involved in electron transfer in the initial stage of water–solid contact, and in the corresponding interfacial redox chemical processes. However, the effects of surface chemical groups on the contact between water and a solid in the initial stage have usually been ignored. In research on water–solid interfaces, it is therefore crucial to understand the correlation between chemical groups and the physicochemical processes that occur in the initial stage of contact, as well as the interfacial redox chemical reaction. This study is hopefully an advance in this direction.
Results and Discussion
Spontaneous Generation of H2O2 in the Microfluidic Channel.
An ideal water–solid interface was set up by sealing a patterned polydimethylsiloxane (PDMS) slab on a flat glass substrate to produce a typical straight-channel microfluidic chip. The channel dimensions were 100 µm (width) × 20 µm (height). Deionized (DI) water was injected into the microfluidic channel to build a water–solid interface; this ruled out the effects of gas–phase species on the investigation of H2O2 spontaneous generation (Fig. 1A). An H2O2-sensitive water-soluble probe (10-acetyl-3,7-dihydroxyphenoxazine) was used to detect the production of H2O2 in the microfluidic chip (20). The resulting microfluidic chip was examined using fluorescence microscopy to establish a relationship between the water–solid interface and observed fluorescence intensity (Fig. 1B). A strong orange fluorescence emission was observed from microfluidics containing the probe under 530 nm laser excitation, as shown in Fig. 1C, but not in bulk water under the same conditions. A zoomed-in fluorescence microscopy image confirmed a fluorescence emission from the microfluidics in the straight channel (Fig. 1D). Fluorescence analysis indicated that H2O2 was generated spontaneously in the microfluidic channel. We confirmed that H2O2 was generated by collecting the water in the microfluidic channel and investigating its reaction with 4-carbonxyphenylboronic acid (4-CPB) according to a reported method (6). Mass spectrometric analysis (SI Appendix, Figs. S1 and S2) showed that typical boronic acid cleavage occurred and confirmed the presence of H2O2, in good agreement with previous literature reports (6). Fig. 1E and SI Appendix, Fig. S3 show the fluorescence emission intensity as a function of the contact time between water and the glass substrate. The fluorescence emission intensity was recorded as soon as DI water had filled the channel. The fluorescence intensity increased rapidly, and the maximum value was reached after 10 s. Quantitative analysis of H2O2 generation in the microfluidic channel was performed by using potassium titanium oxalate (PTO; K2TiO(C2O4)2H2O) according to a previously reported method (6, 21). SI Appendix, Fig. S4 shows the ultraviolet-visible (UV-vis) absorption spectra of 0.1 M PTO solutions with various concentrations of a standard H2O2 solution, and with the sample obtained from the microfluidic chip. The concentration of H2O2 in the microfluidic chip was 1.9 mg L−1 (Fig. 1F).
H2O2 Generation at Water–Solid Interface.
To investigate the origin of the spontaneous generation of H2O2, we observed the H2O2 signals from the probe at the water–glass interface as well as the signals in the channel; Fig. 2A shows the fluorescence intensity curve. The fluorescence intensity decreased along the normal direction of the glass substrate. The results indicate that the concentration of H2O2 at the water–glass interface was much higher than that in the channel. This finding shows that H2O2 generation may be dependent on the water–solid interface. Notably, the relationship between the H2O2 concentration and the water–solid interface was confirmed by determining the H2O2 concentrations in capillary devices with various diameters, as shown in Fig. 2B and SI Appendix, Fig. S5. The concentrations of H2O2 were determined by the ratio of the internal surface area of the capillary device to its volume (surface area/channel volume). The excellent linear relationship between the H2O2 concentration and the surface area/channel volume ratio shows that the spontaneous generation of H2O2 can be attributed to the effect of the water–solid interface. Notably, the concentration of H2O2 generated in the capillary device was of the same order of magnitude as that in the PDMS microfluidic channel. This result further rules out H2O2 production caused by radicals generated from newly prepared PDMS in the microfluidic device (22).
Ionic strength and pH have important effects on the water–solid interface, such as the formation of an electric double layer. We therefore investigated the spontaneous generation of H2O2 from NaOH, NaCl, and HCl solutions at various concentrations (Fig. 2C). The results show that H2O2 production decreased with increasing ionic strength. In addition, the concentration of H2O2 generated in DI water was higher than that generated in NaOH, NaCl, and HCl solutions. Among these, the NaOH solution had the least inhibitory effect on the spontaneous generation of H2O2. These data indicate that the water–solid interface may be the origin of the spontaneous generation of H2O2 under these conditions.
H2O2 Originates from the Hydroxyl Groups on the Solid Surface.
It is important to identify the O-atom source to further understand the effects of the water–solid interface on H2O2 production. We considered that possible O-atom sources at the water–solid interface include oxygen-containing groups on the solid substrate and dissolved O2 in the water. Therefore, we examined the correlation between dissolved O2 and H2O2 production (Fig. 2D). The amount of H2O2 produced remained at the same level regardless of how the amount of dissolved O2 was changed. Our observations indicate that the H2O2 generated at the water–solid interface was not produced by oxidation with dissolved O2; this finding was in good agreement with previously reported results for aqueous microdroplets (6, 23). Our results suggest that the O-atom source for H2O2 generation may come from oxygen-containing groups on the solid substrate.
We addressed the above issue by investigating the correlation between the density of hydroxyl groups on the substrate and H2O2 production. SiO2 substrates were used to prevent interference from impurity elements in the substrates. The density of hydroxyl groups on the SiO2 substrate was increased after typical O2 plasma activation treatment; this was confirmed by using infrared spectroscopy and X-ray photoelectron spectroscopy (XPS) to examine the substrate (SI Appendix, Figs. S6 and S7) (24). Fig. 3A shows that the fluorescence emission intensity of the H2O2-sensitive probe on the substrate treated with O2 plasma (Fig. 3A, Middle) was higher than that of the bare glass substrate (Fig. 3A, Top). This result shows that H2O2 production at a water–solid interface can be enhanced by increasing the hydroxyl group density on the solid substrate. The density of hydroxyl groups on the SiO2 substrate was decreased based on the modification of the substrate with 3-(methacryloyloxy) propyltrimethoxysilane (MPTMS) (SI Appendix, Fig. S8) (25). Fluorescence signals were hardly observed on the substrate, which was modified with MPTMS (Fig. 3A and B, Bottom). This result can be attributed to the decrease of the density of hydroxyl groups on the substrate caused by the reaction between the mercapto groups of MPTMS and the hydroxyl groups. Therefore, surface hydroxyl groups on the solid substrate play a key role in H2O2 production at the water–solid interface. The disappearance of the fluorescence emission from the H2O2-sensitive probe offers solid evidence that the spontaneous generation of H2O2 is determined by the presence of surface hydroxyl groups on the solid substrate.
The Use of Isotopic Labeling.
We designed an O-atom isotope experiment to further explore the origin of the oxygen atoms for the generation of H2O2 (Fig. 3C). 18O2 plasma treatment was used to create sufficient 18O-labeled hydroxyl groups on the SiO2 substrate. Spontaneous generation of H2O2 and corresponding boronic acid cleavage on the 18O-labeled SiO2 substrate was performed to determine whether surface hydroxyl groups participate in the reaction at the water–solid interface. If the surface hydroxyl group is the origin of the O atom in the generation of H2O2, then the O-atom isotope signals would be observed in 4-hydroxybenzoic acid, as shown in Fig. 3D. We therefore compared the 4-hydroxybenzoic acid productions on the SiO2 substrates treated with O2 and 18O2 plasmas. The intensity of the mass spectrometric peak at 139.04 m/z increased after isotope treatment (Fig. 3E), which suggests that the O atom in the surface hydroxyl group plays an important role in the mass balance during the reaction. Additional isotope experiments were performed to further confirm the origin of the O atom during H2O2 generation. In these experiments, H218O was used to produce H2O2 on a typical SiO2 substrate and on an 18O-labeled substrate. SI Appendix, Figs. S9 and S10 show that the intensity of the peak at 139.04 m/z obtained when H218O was used was slightly lower than that in Fig. 3E, whereas the signal observed by using H218O on the 18O-treated substrate was slightly higher. However, all the peak intensities were of the same order of magnitude. We propose that the 18O signals observed in the H218O control experiments can be attributed to the rearrangement of O atoms between water molecules absorbed on the SiO2 surface and the oxide substrate. These observations suggest that the O atoms in H2O2 generation originate from surface hydroxyl groups on the substrate.
Several previous reports have indicated that hydroxyl radicals can combine to form H2O2 in the presence of water (6, 26). We therefore speculated that some of the hydroxyl groups on the solid surface generate hydroxyl radicals during contact between water and the solid surface and then combine to form H2O2. To support our speculation, water containing DMSO, which is a typical hydroxyl radical scavenger (27), was injected into the microfluidic channel, followed by a measurement of the H2O2 generation. As shown in SI Appendix, Fig. S11, it is difficult to detect the fluorescence signal from H2O2 in the presence of DMSO. This indicates that the spontaneous generation of H2O2 can be predominantly, if not completely, attributed to the recombination of hydroxyl radicals generated from the hydroxyl groups on the solid surface when the solid substrate contacts water.
The generation of hydroxyl radicals from hydroxyl groups is accompanied by electron transfer (28). On the basis of previous investigations of electron transfer in water–solid contact electrification, we assumed that electrons can play a fundamental role in driving the spontaneous generation of H2O2. We therefore measured the current flowing from the substrate to the ground when water contacted the substrate and simultaneously observed the fluorescence signal from H2O2 generation. SI Appendix, Fig. S12 shows that current changes occur in synchronization with the generation of H2O2. We also used Kelvin probe force microscopy (KPFM) to determine the surface charge density of the substrate before and after contact with water (SI Appendix, Fig. S13). The surface charge density of the substrate changed from 113.5 to −179.7 μC m−2, which suggests that the substrate gained electrons on contact with water. Notably, it was estimated that the H2O2 generation reaction in the microfluidic channel would require a maximum of 2 × 10−15 mol electrons, which is one order of magnitude lower than the amount of charge measured during contact. This finding also suggests that the change of the surface charge density when water contacted the substrate may have multiple origins, such as ion transfer, overlap of electron clouds, and surface hydroxyl groups on the substrate (5). We do not know the fate of all the charges detected on the solid surface, but we consider that the charge transfer at the water–solid interface is sufficient to produce H2O2.
Mechanism for Spontaneous Generation of H2O2 at the Water–Silica Interface.
Our experimental results and analysis revealed that the production of H2O2 at the water–solid interface originated from the radicals generated from surface hydroxyl groups when water contacted with the solid substrate. We investigated a possible reaction pathway involved in the surface hydroxyl groups. It is well known that hydroxyl groups on the surface of oxides are amphoteric in character (29). Moreover, early research demonstrated that surface acidic hydroxyl groups (Si-OH(a)) contribute most to the generation of hydroxyl radicals (30). Thus, we investigated the correlation between the density of acidic hydroxyl groups on the SiO2 surface and the generation of H2O2 at the water–solid interface. Notably, the density of acidic hydroxyl groups was measured, based on the reaction between NaOH and the acidic hydroxyl groups reported previously (31). The density of acidic hydroxyl groups on SiO2 substrates fabricated under the same conditions in Fig. 3B is shown in SI Appendix, Fig. S14. We observed that the density of the acidic surface hydroxyl groups on SiO2 treated by O2 plasma was higher than the other two substrates. Next, the concentration of H2O2 generated on those substrates was recorded (shown in Fig. 4A). The linear relationship between H2O2 concentration and the density of acidic surface hydroxyl groups was in good agreement with the results in Fig. 2B. More importantly, we compared the density of the acidic surface hydroxyl groups before and after H2O2 generation. As shown in Fig. 4B, the density of the acidic surface hydroxyl groups decreased after the production of H2O2, which offers solid evidence that acidic hydroxyl groups act as a starting reactant in the pathway of H2O2 generation. Notably, acidic surface hydroxyl groups (Si-OH(a)) may be ionized in water to generate hydronium cations and silanolate anions (Si-O−). Thus, Si-O− groups are thought to be the initial source of O atoms to form H2O2 during the contact electrification process:
[1] |
When contact occurs between the SiO2 surface and water molecules, the electron may transfer from H2O to the solid surface (32) and thus form H2O during this process. We tested the amount of H2O2 generated on the surface of SiO2 depending on different temperatures. In order to meet the detection limit requirements, we used SiO2 powder in contact with humid air to create a solid–liquid interface with a sufficiently large area for further investigation. As shown in Fig. 4C, there was an increase in H2O2 production with increasing temperature. This result could be attributed to the kinetic energy increase caused by the rising temperature, which might enhance the probability of the contact between water molecules and the SiO2 surface and thus increase the probability of electron transfer. Moreover, the signal of H2O2 cannot be detected when the temperature is below 5 °C. This result might be ascribed to the kinetic energy of water molecules, which is too low to generate enough electrons during contact electrification for the generation of detectable amounts of H2O2. A possible reaction pathway can be written as follows:
[2] |
Typically, Si-18O- ions can work as a base to accelerate some reactions by promoting the stoichiometric deprotonation step (33, 34). Si-18O- ions could react with H2O+ to form hydroxyl radicals during the contact electrification process:
[3] |
Then, a hydroxyl radical recombination could yield H218O2:
[4] |
In fact, our proposed mechanism is built around the hypothesis that the overlap between the electron clouds of the water molecule and the solid surface during the contact will lead to the generation of H2O+ and OH•. However, various intermediates present in the above reaction pathway are difficult to test, so we believe that the mechanism of the spontaneous generation of H2O2 at the water–solid interface is still an open issue that requires further in-depth research.
In addition, we believe that the generation of H2O2 at the water–solid interface may provide a perspective on a physicochemical process similar to that in the microdroplet. We assume that the electron will transfer from one H2O molecule to another H2O molecule during their contact and that hydroxyl radicals may generate during the contact electrification. Thus, the generation of H2O2 at the water–solid interface is in good agreement with that at the surface of the microdroplets.
Universality of H2O2 Generation from Water Contact Electrification.
The universality of this phenomenon was investigated by observing the spontaneous generation of H2O2 on nine other types of substrates. As shown in SI Appendix, Fig. S15A, similar phenomena were observed on various substrates. In addition, we carried out a set of comparative experiments to investigate the changes of the surface charge before and after water–solid contact by using zeta potential measurements. SI Appendix, Fig. S16 shows the difference in zeta potential before and after the contact between water and these powder samples. It can be observed that the trend of the zeta potential difference depended on solids species in a manner consistent with the trend of the H2O2 generation on their surfaces. This result provides further proof of the importance of contact electrification in causing H2O2 production at the water–solid interface. More importantly, we tested the generation of H2O2 on the surfaces of standard soil (GBW07446) and atmospheric fine particles of 2.5 μm or smaller (PM2.5) after they had been placed in an oven at room temperature (25 °C) at various relative humidities. SI Appendix, Fig. S15B shows that H2O2 generation increased with increasing relative humidity, which is in good agreement with a previous literature report (35). To rule out in situ catalytic processes in the soil, we also investigated H2O2 generation on O2 plasma–activated and MTPMS-modified soil particles, respectively. The H2O2 generation yield was affected by changing the density of the hydroxyl groups on the surface of the soil. SI Appendix, Fig. S15C shows that H2O2 spontaneous generation also occurred at the surfaces of PM2.5 particles at various different values of the relative humidity. Note that the composition of atmospheric fine particles is very complex. Several publications have reported that the main components of China’s atmospheric fine particles include carbon black, nitrate, sulfate, and ammonium salt (36, 37). We carried out an energy dispersive X-say spectroscopy measurement to analyze the main elements contained in our atmospheric fine particles sample. As shown in SI Appendix, Fig. S17, the main elements were C, N, S, and O. We believe that the composition of atmospheric fine particles is similar to that reported previously (37). The generation of H2O2 on the surface of PM2.5 particles could be attributed to their surface hydroxyl groups and contact between water and their surface. The results of this study may therefore help us understand the mechanism of H2O2 generation in the environment and explain how nature behaves, such as the seasonality of viral respiratory infections (38). In addition, we have considered a recent report (34) that glass surfaces can act as heterogeneous catalysts to accelerate various base-catalyzed reactions. The present study may help us further understand the heterogeneous catalytic reaction at the solid–water interface and design interfacial catalysts to replace homogeneous catalysts that need to be dispersed in the bulk phase.
Conclusions
In summary, our experimental and modeling results provide direct evidence for the spontaneous generation of H2O2 at water–solid interfaces from hydroxyl groups on the solid surface. These observations give a perspective on water–solid interactions and enhance our understanding of water–solid contact electrification. The identification of H2O2 generation from the surfaces of solid and atmospheric fine particle samples shows the possibilities of developing mechanisms for pollutant degradation and transformation in the environment. When combined with materials with high catalytic activities, these phenomena could have important applications in catalytic chemistry.
Materials and Methods
Materials.
Unless otherwise stated, HCl (AR, Sinopharm Chemical Reagent Co., Ltd, China), NaOH (AR, Sinopharm Chemical Reagent Co., Ltd, China) NaCl (AR, Sinopharm Chemical Reagent Co., Ltd, China), O2 (99.999%, Wuhan Iron and Steel Group Gas Co., Ltd., China); heavy O2 (99.99%, Wuhan Niuruide Gas Co., Ltd., China), PTO dihydrate (99.99%, Sigma-Aldrich, USA); 4-CPB (99.99%, Sigma-Aldrich, USA); anhydrous dimethyl sulfoxide (99.99%, Sigma-Aldrich, USA); 10-acetyl-3,7-dihydroxyphenoxazine (KeyGEN BioTECH Co., Ltd, China); H2O standard solution (1,000 μg/mL, Beijing Northern Weiye Metrology Research Institute, China); PDMS prepolymer RTV 615 (Momentive, USA); graphite powder; CaO; ZrO; SiO2; Al2O3; MnO2, TiO2; CuO; ZnO (Shanghai Aladdin Bio-Chem Technology Co., Ltd, China); and standard soil (GBW07446, China) were used in experiments. DI water (Merck Millipore, USA) was used in all experiments. SiO2 substrates (optical grade, Sigma-Aldrich, USA), conductive glass substrates (NSG Pilkington FTO glass), and glass substrates (Jiangsu Fanchuan Co., Ltd, China) were ultrasonically cleaned with acetone, ethanol, and DI water for 30 min before use.
Fabrication of Microchannel Structure Devices.
The channel layout was drawn by L-edit software, and the mask was prepared by ultraviolet direct writing equipment. Subsequently, relief microchannels were built on the Si wafer by photolithography. The cylindrical channel (1.5 mm diameter) had a total length of 2 cm, a width of 100 μm, and a height of 20 μm. The PDMS prepolymer and the curing agent were mixed in a 9:1 mass ratio and then poured onto the silicon wafer with relief microchannel structure, decompressed and defoamed, and heat-treated at 80 °C for 30 min, and finally PDMS with a microchannel structure was obtained. To fabricate microchannel structured devices, holes were opened in the reserved position, and then PDMS monolith was attached to the clean glass substrate. A pressure of 0.1 MPa was applied externally and kept at 85 °C for 30 min to ensure stable bonding between PDMS and the glass substrate.
Qualitative Characterization of H2O2.
10-acetyl-3,7-dihydroxyphenoxazine was used in the experiments as a fluorescent indicator of H2O2. 1 mM 10-acetyl-3,7-dihydroxyphenoxazine aqueous solution was pumped into the microchannel at a flow rate of 20 μL h-1, and the monolithic device was placed under an inverted fluorescence microscope for observation. A 530 nm laser was applied as an excitation light source, the exposure time was fixed, and the change the overall fluorescence intensity in the channel was recorded. The device was placed under a microscope on its side to observe the diffusion of H2O2 from the glass surface. All fluorescence images were calculated using Image J software to obtain the average fluorescence intensity under different conditions.
To observe the effect of ionic strength on the formation of H2O2, 1 mM 10-acetyl-3,7-dihydroxyphenoxazine was added to DI water and different concentrations (10-5,10-6,10-7 and 10-8 Mol L-1) of HCl, NaCl, and NaOH solution, respectively. Different solutions were pumped into the microchannel at a flow rate of 20 μL h-1, and the maximum fluorescence intensity was recorded. The fluorescence intensity of DI water was used as the standard to qualitatively explore the relationship between ionic intensity and H2O2 generation.
To investigate the effect of dissolved O2 in the solution on the formation of H2O2, deionized water was degassed and aerated. Deionized water was continuously boiled for 30 m to achieve degassing, and another set of deionized water was continuously bubbled with O2 for 1 h to ensure higher dissolved O2 content. Untreated DI water was used as a control group, and 1 mM 10-acetyl-3,7-dihydroxyphenoxazine was added to the three groups of DI water, which were pumped into the microchannel, and the maximum fluorescence intensity was recorded.
Quantitative Characterization of H2O2.
The color reaction of PTO with H2O2 was considered as one of the methods to quantitatively characterize the concentration of H2O2. H2O2 solutions of 1, 2, 3, 4, and 5 mg L−1 were prepared using a H2O2 standard solution and were mixed with 0.3 M PTO solution in a volume ratio of 1:1. The mixed solution was detected by a UV-vis spectrometer (UV-2550, Shimadzu, Japan), the absorbance at 400 nm was taken as the characteristic value, and the standard curve was drawn according to the concentration of corresponding H2O2.
The DI water was pumped through the microchannel at 20 μL h−1 and then mixed with 0.3 M PTO solution by equal volume, and then its absorbance was measured by a UV-vis spectrometer. The absorbance at 400 nm was compared to the standard curve, and the concentration of H2O2 in deionized water was finally calculated.
To further explore the relationship between the concentration of H2O2 and the solid–liquid interface, capillaries with different diameters were used as experimental objects. First, 1 mM 10-acetyl-3,7-dihydroxyphenoxazine solution was pumped into different-diameter (50, 150, 200, 250, and 500 μm) capillaries at different flow rates, respectively. The flow rates of DI water pumped into the different capillaries were 20, 120, 320, 500, and 2,000 μL h−1, which ensured that the solution was advancing at the same rate in the capillaries. Then 0.5 mL DI water was collected at the exit of the capillary, mixed with 0.3 M PTO solution by equal volume, and its absorbance at 400 nm was measured by a UV-vis spectrometer and compared to the standard curve; finally, the concentration was calculated.
Effects of Surface Hydroxyl Groups on H2O2 Generation.
XPS and a Fourier transform infrared spectrophotometer (Bruker) were used to characterize the surface group changes of glass substrates after O2 plasma treatment. XPS was performed on a multifunctional imaging electron spectrometer (ESCALAB 250XI, Thermo) using monochromatized Al Ka radiation (1486.6 eV).
The potential changes of the glass substrate surface before and after the flow of DI water were obtained by (KPFM) experiments. Experiments were performed on a commercial atomic force microscope (AFM) instrument (Multimode 8 Bruker, USA). AFM probe (NSC18, Mikro-Mash, USA; Au coated; tip radius: 25 nm; spring constant: 2.8 N m-1) was used as the conductive tip. At the same time, we also used conductive glass as the substrate and cooperated with the electrochemical workstation to detect the drop of DI water on the O2 plasma-treated substrate and to record the change of the current.
To investigate the effect of surface hydroxyl groups on the formation of H2O2, O2 plasma was used to increase the surface hydroxyl groups and MPTMS was used to reduce the surface hydroxyl groups. An untreated glass substrate was used as the control. Next, 20 μL 1 mM 10-acetyl-3,7-dihydroxyphenoxazine solution was added dropwise to three different glass substrates, and the fluorescence images were recorded under an inverted fluorescence microscope; finally, the mean fluorescence intensity was calculated using Image J.
Next, 100 μM 4-CPB solution was pumped through the microchannel at 20 μL h−1 and a 0.5 mL sample was collected at the outlet. The samples were analyzed using liquid chromatography-mass spectrometry in negative mode, and 4-CPB, 4-carboxyphenol, 4,4'-oxybis (benzoic acid), and boric acid were observed separately. The relative abundance of 4-hydroxybenzoic acid remained low, which may have been caused by low turnover resulting from poor ionization efficiency or short reaction times when no voltage was applied.
To explore the source of O atoms during H2O2 generation, a H218O mixture and H218O water were used in the experiments. The microchannels were treated with O2 plasma and 18O2 plasma, respectively, for 20 min before bonding. Then 100 μM 4-CPB solution was pumped through the microchannel. In addition, 4-boxyphenylboronic acid was dissolved in H218O to conduct experiments, and the samples at the outlet were analyzed using high-resolution liquid chromatography-mass spectrometry, and the intensity changes of 137 m/z and 139 m/z corresponding to 4-carboxyphenol were compared.
The Boehm titration method was used to determine the hydroxyl density of the material surface. The silica glass was cut into a 0.5 × 0.5 cm square and a 2 g sample was dissolved into 25 mL anhydrous ethanol, followed by adding 75 mL of 20 wt% NaCl solution. The solution was stirred slowly and a pH meter (Mettler, SevenExcellence) was used to detect the overall pH change of the solution in real time. The pH of the solution was adjusted to 4 with 0.1 M HCl. After the pH was stabilized, 0.1 M NaOH solution was slowly added dropwise to bring the pH of the solution back to 9 and the amount of NaOH was recorded. The number of hydroxyl groups per square nanometer (N) on the surface of the material was calculated according to the following equation:
where C is the concentration of NaOH (mol/L), V (mL) is the volume of NaOH consumed as the pH rises from 4 to 9, NA is Avogadro’s constant, and S is the surface area of the sample.
Additional Information.
The formation of H2O2 on the surface of natural materials is presented in the SI Appendix.
Supplementary Material
Acknowledgments
This work is financially supported in part by grants from the Strategic Priority Research Program of the Chinese Academy of Sciences (XPDB2005), the National Nature Science Foundation of China (22193051, 22193052, 22136006, 21705057), the National Key Research and Development Program of China (2020YFA0907400), and the Youth Talent Support Program of Jianghan University. R.N.Z. acknowledges support from the US Air Force Office of Scientific Research through the Multidisciplinary University Research Initiative program (AFOSR FA9550-21-1-0170). We thank Professor P. Wang, Hong Kong Polytechnic University, Z. Q. Tian, Xiamen University, A. Colussi, California Institute of Technology, and D. Ben-Amotz, Purdue University, for helpful discussions.
Footnotes
Reviewers: V.V., University of Colorado Boulder; and Z.L.W., Georgia Institute of Technology.
The authors declare no competing interest.
This article contains supporting information online at https://www.pnas.org/lookup/suppl/doi:10.1073/pnas.2209056119/-/DCSupplemental.
Data Availability
All study data are included in the article, the SI Appendix, and the publicly available link: https://github.com/RichardZare/Contact_Electrification_PNAS_Data_Repository.
References
- 1.Lin S., Chen X., Wang Z. L., Contact electrification at the liquid-solid interface. Chem. Rev. 122, 5209–5232 (2022). [DOI] [PubMed] [Google Scholar]
- 2.Matsui M., Murasaki N., Fujibayashi K., Bao P. Y., Kishimoto Y., Electrification of pure water flowing down a trough set up with a resin sheet. J. Electrost. 31, 1–10 (1993). [Google Scholar]
- 3.Yatsuzuka K., Mizuno Y., Asano K., Electrification phenomena of pure water droplets dripping and sliding on a polymer surface. J. Electrost. 32, 157–171 (1994). [Google Scholar]
- 4.Yatsuzuka K., Higashiyama Y., Asano K., Electrification of polymer surface caused by sliding ultrapure water. IEEE Trans. Ind. Appl. 32, 825–831 (1996). [Google Scholar]
- 5.Ben-Amotz D., Electric buzz in a glass of pure water. Science 376, 800–801 (2022). [DOI] [PubMed] [Google Scholar]
- 6.Lin S., Xu L., Wang A. C., Wang Z. L., Quantifying electron transfer in liquid-solid contact electrification and the formation of electric double-layer. Nat. Commun. 11, 399 (2020). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 7.Lee J. K., et al. , Spontaneous generation of hydrogen peroxide from aqueous microdroplets. Proc. Natl. Acad. Sci. U.S.A. 116, 19294–19298 (2019). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 8.Gao D., Jin F., Lee J. K., Zare R. N., Aqueous microdroplets containing only ketones or aldehydes undergo Dakin and Baeyer-Villiger reactions. Chem. Sci. (Camb.) 10, 10974–10978 (2019). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 9.Lee J. K., et al. , Condensing water vapor to droplets generates hydrogen peroxide. Proc. Natl. Acad. Sci. U.S.A. 117, 30934–30941 (2020). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 10.Dulay M. T., et al. , Spraying small water droplets acts as a bacteriocide. QRB Discovery 1, e3 (2020). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 11.Gallo A. Jr., et al. , On the formation of hydrogen peroxide in water microdroplets. Chem. Sci. (Camb.) 13, 2574–2583 (2022). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 12.Kakeshpour T., Metaferia B., Zare R. N., Bax A., Quantitative detection of hydrogen peroxide in rain, air, exhaled breath, and biological fluids by NMR spectroscopy. Proc. Natl. Acad. Sci. U.S.A. 119, e2121542119 (2022). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 13.Mehrgardi M. A., Mofidfar M., Zare R. N., Sprayed water microdroplets are able to generate hydrogen peroxide spontaneously. J. Am. Chem. Soc. 144, 7606–7609 (2022). [DOI] [PubMed] [Google Scholar]
- 14.Nguyen D., Nguyen S. C., Revisiting the effect of the air–water interface of ultrasonically atomized water microdroplets on H2O2 formation. J. Phys. Chem. B 126, 3180–3185 (2022). [DOI] [PubMed] [Google Scholar]
- 15.Lin S., et al. , Electron transfer in nanoscale contact electrification: Effect of temperature in the metal-dielectric case. Adv. Mater. 31, e1808197 (2019). [DOI] [PubMed] [Google Scholar]
- 16.Xu C., et al. , On the electron-transfer mechanism in the contact-electrification effect. Adv. Mater. 30, e1706790 (2018). [DOI] [PubMed] [Google Scholar]
- 17.Wang Z., et al. , Contact-electro-catalysis for the degradation of organic pollutants using pristine dielectric powders. Nat. Commun. 13, 130 (2022). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 18.Xu W., et al. , A droplet-based electricity generator with high instantaneous power density. Nature 578, 392–396 (2020). [DOI] [PubMed] [Google Scholar]
- 19.Kavokine N., Bocquet M. L., Bocquet L., Fluctuation-induced quantum friction in nanoscale water flows. Nature 602, 84–90 (2022). [DOI] [PubMed] [Google Scholar]
- 20.Mohanty J. G., Jaffe J. S., Schulman E. S., Raible D. G., A highly sensitive fluorescent micro-assay of H2O2 release from activated human leukocytes using a dihydroxyphenoxazine derivative. J. Immunol. Methods 202, 133–141 (1997). [DOI] [PubMed] [Google Scholar]
- 21.Kastvig M. H., et al. , Effect of humidity on cellulose pellets loaded with potassium titanium oxide oxalate for detection of hydrogen peroxide vapor in powders. Power Tech. 366, 348–357 (2020). [Google Scholar]
- 22.Baytekin H. T., Baytekin B., Grzybowski B. A., Mechanoradicals created in “polymeric sponges” drive reactions in aqueous media. Angew. Chem. Int. Ed. Engl. 51, 3596–3600 (2012). [DOI] [PubMed] [Google Scholar]
- 23.Collin F., Chemical basis of reactive oxygen species reactivity and involvement in neurodegenerative diseases. Int. J. Mol. Sci. 20, E2407 (2019). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 24.Liu Z., Brown N. M. D., McKinley A., Characterization of oxygen plasma-modified mica surfaces using XPS and AFM. Appl. Surf. Sci. 108, 319–332 (1997). [Google Scholar]
- 25.Wu J., et al. , Surface modification of nanosilica with 3-mercaptopropyl trimethoxysilane: Experimental and theoretical study on the surface interaction. Chem. Phys. Lett. 591, 227–232 (2014). [Google Scholar]
- 26.Du S., Francisco J. S., Kais S., Study of electronic structure and dynamics of interacting free radicals influenced by water. J. Chem. Phys. 130, 124312 (2009). [DOI] [PubMed] [Google Scholar]
- 27.Panganamala R. V., Sharma H. M., Heikkila R. E., Geer J. C., Cornwell D. G., Role of hydroxyl radical scavengers dimethyl sulfoxide, alcohols and methional in the inhibition of prostaglandin biosynthesis. Prostaglandins 11, 599–607 (1976). [DOI] [PubMed] [Google Scholar]
- 28.Zhao L., et al. , Sprayed water microdroplets containing dissolved pyridine spontaneously generate pyridyl anions. Proc. Natl. Acad. Sci. U.S.A. 119, e2200991119 (2022). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 29.Boehm H. P., Acidic and basic properties of hydroxylated metal oxide surfaces. Discuss. Faraday Soc. 52, 264–275 (1971). [Google Scholar]
- 30.Li W., et al. , Relationship between surface hydroxyl groups and liquid-phase photocatalytic activity of titanium dioxide. J. Colloid Interface Sci. 444, 42–48 (2015). [DOI] [PubMed] [Google Scholar]
- 31.Salame I. I., Bandosz T. J., Surface chemistry of activated carbons: Combining the results of temperature-programmed desorption, Boehm, and potentiometric titrations. J. Colloid Interface Sci. 240, 252–258 (2001). [DOI] [PubMed] [Google Scholar]
- 32.Wang Z. L., Wang A. C., On the origin of contact-electrification. Mater. Today 30, 34–51 (2019). [Google Scholar]
- 33.Li Y., Mehari T. F., Wei Z., Liu Y., Cooks R. G., Reaction acceleration at solid/solution interfaces: Katritzky reaction catalyzed by glass particles. Angew. Chem. Int. Ed. Engl. 60, 2929–2933 (2021). [DOI] [PubMed] [Google Scholar]
- 34.Li Y., Huang K. H., Morato N. M., Cooks R. G., Glass surface as strong base, “green” heterogeneous catalyst and degradation reagent. Chem. Sci. (Camb.) 12, 9816–9822 (2021). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 35.Dulay M. T., et al. , Effect of relative humidity on hydrogen peroxide production in water droplets. QRB Discovery 2, e8 (2021). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 36.Liu L., Zhang J., Du R.et al. , Chemistry of atmospheric fine particles during the COVID-19 pandemic in a megacity of eastern China. Geophys. Res. Lett. 48, 2020GL091611 (2021). [DOI] [PMC free article] [PubMed] [Google Scholar]
- 37.Yuan Q., et al. , Atmospheric fine particles in a typical coastal port of Yangtze River Delta. J. Environ. Sci. (China) 98, 62–70 (2020). [DOI] [PubMed] [Google Scholar]
- 38.Davidse A., Zare R. N., Effect of relative humidity in air on the transmission of respiratory viruses. Front. Mol. J. 5, 5–16 (2021). [Google Scholar]
Associated Data
This section collects any data citations, data availability statements, or supplementary materials included in this article.
Supplementary Materials
Data Availability Statement
All study data are included in the article, the SI Appendix, and the publicly available link: https://github.com/RichardZare/Contact_Electrification_PNAS_Data_Repository.