Schuyler Arna,
Pablo Illing
a,
Joshua Mendéz Harper
b and
Justin C. Burton
*a
aDepartment of Physics, Emory University, Atlanta, GA 30322, USA. E-mail: justin.c.burton@emory.edu
bDepartment of Electrical and Computer Engineering, Portland State University, Portland, OR, USA. E-mail: joshua.mendez@pdx.edu
First published on 19th May 2025
Fluid triboelectrification, also known as flow electrification, remains an under-explored yet ubiquitous phenomenon with potential applications from material science to planetary evolution. Building upon previous efforts to position water within the triboelectric series, we investigate the charge on individual, millimetric water drops falling through air. Our experiments measured the charge and mass of each drop using a Faraday cup mounted on a mass balance, and connected to an electrometer. For pure water in a glass syringe with a grounded metal tip, we find the charge per drop (Δq/Δm) was approximately −5 pC g−1 to −1 pC g−1. This was independent of the release height of the drop, tip diameter and length, tip cleaning preparation, and whether the experiment was shielded with a Faraday cage. Biasing the tip to different voltages allowed for linear control of the drop charge, and the results were consistent with known electrochemical effects, namely the Volta potential expected between most metals and bulk water (≈−0.5 V). Introducing insulating plastic materials into the experiment (from the syringe body or tip) imparted large amounts of charge on the drops with systematic charge evolution. Together these results show that the flow electrification of water is more complex than previously reported, and is driven by material-dependent electrostatic processes.
Whether triboelectric charging results from bulk material transfer, electron or ion transfer, some interfacial adsorbate, or from a combination of all these remains unclear.8 During the last few decades, however, evidence has emerged that water plays a key role in generating charge separation,8–10 stabilizing existing interfacial charge,11 and dissipating charge.12–14 A salient role of water in triboelectrification is perhaps unsurprising: materials in ambient air typically host layers of adsorbed water on their surfaces, unless they are particularly hydrophobic. Dissociated H+ and OH− ions within these layers may allow for charge exchange during collisions or frictional interactions.15,16 That water layers modulate charge exchange in systems of solids implies that triboelectrification may also occur at fluid–solid interfaces (or even fluid–fluid interfaces!).17–19 As in solid–solid triboelectrification, the chemical composition of the liquid–solid pair tunes the character of the charging. If the fluid moves relative to the solid, charge separation is known as “flow electrification”.20 For viscous fluids, the no-slip assumption implies that the shear forces at the fluid–solid boundary are smaller than those between two frictional solids. However, the contact area is orders of magnitude larger than expected for solid–solid frictional contacts21 since the liquid coats the entirety of the solid surface. Even in the absence of flow, there can be a static potential difference between a bulk solid and liquid in contact due to differences in electronic energy states.22
Flow electrification has been examined for more than a century, primarily by the petroleum and lubrication engineering industries.20,23–26 Within these contexts, electrostatic charging and discharge pose a significant hazard in dielectric and combustible hydrocarbon fuels.27–29 Consider that more than 30 unintended fuel–air mixture ignitions during vehicle refueling were reported in Germany alone between 1992 and 1995. These incidents were ultimately attributed to electrostatic accumulation and subsequent discharge of flowing liquids.30 Charging in dielectric fluids like hydrocarbons is particularly hazardous in filtration systems31,32 and pipe flow33–35 where the contact area between the liquid and wall is large. For insulating fluids, the Debye layer thickness can extend well beyond the flow boundary layer (more than a few microns). As such, ions in the Debye layer are easily entrained in flow. Additionally, because these fluids have poor conductivities, they do not readily allow for charge recombination. Although this current is often treated phenomenologically, very few studies consider the underlying mechanism of flow electrification.36–39
Flow electrification also occurs in liquids with higher conductivities like water. In 1892, inspired by observations of negative charge developed in air around waterfalls across the Alps, Lenard conducted a series of laboratory experiments to study the charging behavior of falling water drops or streams in ambient air.40 These pioneering experiments showed that the water dispensed from a reservoir collects charge while the surrounding air develops an oppositely-charged potential. Lenard noted variations in this behavior depending on the cleanliness and source of the dispensed water, among other material properties used in the experiments. The Debye length in pure water is ∼0.7 nm, orders of magnitude smaller than in dielectric liquids with very few ions. This has led to proposals to use water as a power source for nanoscopic graphene-based devices.41 Another recent study by Burgo et al. presented a triboelectric series for water flowing against materials ranging from air to copper to polytetrafluoroethylene, or PTFE. Both the magnitude and the sign of the flow electrification of water was highly dependent on the composition of the other material.42
Interestingly, Burgo et al. showed that water charged positively against all materials with the exception of air. The fact that air flow can reliably charge water and potentially other liquids is surprising since ambient air contains only ∼1 ion per mm3.12 Furthermore, under fair weather conditions, near-surface air contains slightly more positive ions than negative ones,43 suggesting that any falling drop would scavenge a net positive charge. In other words, merely collecting ions from the air is insufficient to explain the magnitude and polarity of observed flow electrification between water and air by Burgo and coworkers. Such incongruities, particularly in the context of a ubiquitous material like water, underscore the need for more detailed investigations into contact electrification across fluid–solid and fluid–fluid interfaces.
Here, we report on experiments designed to characterize the charge on individual deionized water drops falling from glass syringes with a variety of needles. The drops, which grow quasi-statically from the tip of the needle, fall into a custom-made Faraday cup, and the mass of each drop is simultaneously measured with a precision balance. In the absence of plastics, we find little or no flow electrification from the ambient environment—that is, the drop charge does not depend on deposition height, metallic tip length, flow rate, or the presence of electrostatic shielding surrounding the experiment. The charge per unit mass on each drop, Δq/Δm, ranged from −5 to −1 pC g−1, consistent with the expected Volta potential between typical metals and bulk water.22 Adding salt to the water reduces the overall charge by ∼50%. In contrast, introducing common plastic components in the experimental setup (such as a polypropylene syringe body or PTFE syringe tip) can drastically change the charge on each drop. In the case of a PTFE tip, for instance, the absolute charge-to-mass ratio can be as large as 120 pC g−1. Furthermore, the charge polarity gained by drops flowing against plastics depends on the material history (e.g. how long fluid has been flowing through a plastic tip) and environmental conditions. Our results suggest that the electrification of individual water drops flowing against metals may be understood from known electrochemical effects. However, interactions with plastics can give rise to more complex charge exchanges whose underlying mechanisms require further clarification.
To measure the mass of individual drops, the FC was placed on a precision balance (Ohaus PX623) with milligram resolution. Thus, we were able to measure the charge-to-mass ratio of each drop, Δq/Δm, and compare our data with that of previous investigations of fluid electrification.42,44,45 Lastly, we monitored the ambient conditions using a temperature and humidity sensor (Aosong AHT20). For all experiments, temperature and relative humidity (RH) varied in the range of 20–22 °C and 20–50%, respectively. The four variables—charge, mass, temperature, and RH—were sampled every ∼0.3 s across the duration of an experiment.
Depending on the inner diameter (ID) of a syringe tip (1.35–2.69 mm) and the flow rate of the syringe pump, drops were produced with a period of 5–10 s and radius of 1.85–2.35 mm. For most trials, we employed a flow rate of 350 μL min−1, but also tested a range of flow rates (35–750 μL min−1) were individual drops could be resolved by the mass balance. These results are shown in Fig. 1(e) and (f), and show little variation in drop charge and mass with the flow rate. Drops were allowed to fall 10–40 cm in air before landing in the FC. For some experiments, we minimized the influence of spurious electric fields by enclosing the entire experimental setup in a grounded Faraday cage made from aluminum wire mesh. Lastly, any metallic parts of the syringe (e.g. the tip or the metallic base of the syringe luer-lock system) were grounded to the outer shell of the FC using a small-gauge, coiled, solid-core copper wire. The solid core coil minimized any mechanical coupling between the syringe and the FC that would cause errors in mass measurements.
The charge q on a drop entering the FC is registered as a step change in the voltage V across the known feedback capacitor C of the electrometer, V = q/C. Similarly, the addition of a drop into the FC causes a stepwise jump in the mass reading. Typical recordings of charge (red curve) and mass (blue curve) for two consecutive drops are shown in Fig. 1(b). A sudden change in the balance reading indicates an impinging drop. To allow for stabilization after impact, we measured the center point on the plateau, mi, between two consecutive impinging drops, and estimated the mass of an individual drop Δm by computing the difference in readings between two neighboring plateaus Δm = mi − mi−1. We used a similar procedure to extract the charge on a falling drop: a sudden change in the electrometer output corresponds to a drop entering the FC. However, electrometers of this sensitivity are prone to drift across the measurement timescales. Thus, we calculated the charge on a drop (Δq) by subtracting the electrometer reading immediately before and after the arrival of the drop (as detected by the mass change). A zoomed-out time series showing the mass and charge evolution for 41 consecutive drops is shown in Fig. 1(c).
Most experiments were conducted with deionized, ultra pure, filtered water (ELGA Veolia Purelab Chorus 1 Reservoir). The water was handled in clean glass containers before being deposited into the testing syringe. However, we also performed experiments with salt water, glycerol, and Fluorinert FC-70. Pure NaCl and glycerol were obtained from Sigma Aldrich, and the Fluorinert was obtained from 3M. To explore the dependence of solid surface properties on the electrification of fluids, we dispensed individual drops from syringe bodies and tips of varied materials. Most experiments used an all-glass, 50 mL capacity syringe with a stainless steel luer-lock mounted at the base (Tomopal). The syringe was cleaned with pure ethanol, rinsed with deionized water, and then dried in an oven at 50 °C prior to use. The glass syringe was connected to various grounded 304 stainless steel or custom nickel-plated stainless steel syringe tips. For nearly all experiments, the tips were cleaned with ethanol and rinsed with water prior to use, but we also tried two other methods of cleaning syringe tips: rinsing them with Neutrad solution and exposing them to oxygen plasma with a custom-built oxygen plasma oven.46,47 In addition to glass and metals, we conducted experiments with plastic components since these are commonly used in fluid electrification experiments42 and broad fluid transport applications. In one set of experiments, we used 20 mL polypropylene syringes (Henke-Ject) connected to standard luer-lock syringe tips composed of a polypropylene luer base and a 304 stainless steel, flat-ended cylindrical tube (1.70 mm ID). In another set of experiments, we used the glass syringes, but all-plastic PTFE syringe tips (1.35 mm ID). All metal and plastic syringe tips were obtained from Vita Needle.
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Fig. 2 Probability distribution functions (PDF) for Δq/Δm using a glass syringe body connected to a 5 cm long, 2.39 mm ID syringe tip. The flow rate was 350 μL min−1, and data was recorded at 44–45% RH. Each distribution is computed over n ≥ 410 data points. Each panel (a–d) represents a different deposition height (h), and also includes data taken with a Faraday cage enclosing the syringe pump, cup, and balance assembly (Fig. 1(a)). The solid lines indicate the mean of each distribution, and the variance in the data primarily comes from the variance in Δq since the drop mass was fairly uniform. For completeness, for the h = 10 cm distributions, we found 〈Δqair〉 = −0.11 ± 0.02 pC, 〈Δqcage〉 = −0.13 ± 0.01 pC, 〈Δmair〉 = 0.037 ± 0.006 g, and 〈Δmcage〉 = 0.042 ± 0.005 g. For the h = 20 cm distributions, we found 〈Δqair〉 = −0.13 ± 0.04 pC, 〈Δqcage〉 = −0.14 ± 0.02 pC, 〈Δmair〉 = 0.042 ± 0.009 g, and 〈Δmcage〉 = 0.040 ± 0.004 g. For the h = 30 cm distributions, we found 〈Δqair〉 = −0.15 ± 0.04 pC, 〈Δqcage〉 = −0.15 ± 0.03 pC, 〈Δmair〉 = 0.047 ± 0.005 g, and 〈Δmcage〉 = 0.046 ± 0.003 g. Lastly, for the h = 40 cm distributions, we found 〈Δqair〉 = −0.14 ± 0.04 pC, 〈Δqcage〉 = −0.11 ± 0.02 pC, 〈Δmair〉 = 0.041 ± 0.005 g, and 〈Δmcage〉 = 0.041 ± 0.003 g. (e) Plot of 〈Δq〉 against flow rate. (f) Plot of 〈Δm〉 against flow rate. Error bars were produced from the standard deviation of per-trial means at each flow rate, and all trials were completed at h = 10 cm. |
As noted above, we cleaned the syringe needles using three different preparation methods: rinsing them with pure ethanol followed by DI water, soaking them in a Neutrad ultrasonic bath then rinsing with DI water, and exposing them to an oxygen plasma for 30 s. The effects of different cleaning procedures are summarized in Fig. 3. The histograms of Δq/Δm suggest that the charge gained by water droplets in contact with metal are independent of cleaning procedure. We note, however, that the oxygen plasma cleaning did decrease average drop mass, presumably because it changed the contact angle of the water and stainless steel contact line. This affects the formation of the drop near the attachment to the syringe tip, and ultimately the force balance that determines the maximum weight of the drop that can be supported.
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Above, ρw is the density of pure water, and ε0 is the permittivity of free space. For the typical values of Δq and Δm in our experiments, VD = −0.3 V to −0.8 V. The invariance of these measurements suggests that the potential difference between the grounded metallic syringe tip and the water drops is an inherent property of the metal–water interface. In fact, these voltage values are consistent with Volta potentials, Δψ, for metallic surfaces in contact with bulk water.22,48 Typically, Volta potentials vary from −0.3 V to −1.0 V for sp and transition metals, with a dependence on the exposed crystalline structure.22
The Volta potential is often measured with scanning Kelvin probe force microscopy,49–51 and is defined as the difference between the potential of zero charge, Upzc, and the work function of the metal, Φ:
Δψ = eUpzc − Φ = −δχM0 + gsolv(dip)0. | (2) |
The potential of zero charge is analogous to the work function when the metal is in contact with a solution instead of vacuum. The Volta potential can be thought of as the bulk potential of a solution (relative to vacuum) when in contact with a metal surface. From theory, Δψ has two contributions: a reorientation of water molecules at the metal surface, gsolv(dip)0, and a redistribution of surface metal electrons, −δχM0.52,53 To further investigate the possibility that VD is a natural electrochemical bias developed between the metal interface and the bulk water, we used a power supply to bias the voltage of our metallic syringe tips (both bare and nickel-plated 304 stainless steel) during drop deposition into the FC. The results are illustrated in Fig. 4. The voltage of the syringe tip, Vtip, was measured relative to the outer grounded shell of the FC, and VD was calculated from eqn (1).
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Fig. 4 Bias voltage applied to a 5 cm long, 2.69 mm ID syringe tip (Vtip) versus the average voltage (VD) of each drop, calculated using eqn (1). Error bars were produced from the standard deviation of n > 110 individual drops. Dashed lines depict linear fits to the data and are indicated in the legend. Data for the stainless steel tip and the nickel-plated tip were acquired at 49% and 34.5% RH, respectively. |
The data for both syringe tips can be fit to a linear relationship. The intercept with the vertical axis (Vtip = 0) agrees well with our measurements using a grounded tip (Fig. 2) – that is, it represents the Volta potential, Δψ. Interestingly, the slope of the linear fit is not unity: a small increase in Vtip leads to a slightly smaller increase in VD. This result may be expected since the applied voltage can change the distribution of electrons at the surface and the water dipole contribution to the Volta potential in eqn (2).53 Although we did not perform independent measurements of Δψ using alternative experimental techniques,48 the consistency of VD over multiple experimental conditions and its quantitative agreement with the expected values of Δψ strongly suggest their equivalency.
In order to obtain a potential difference between the interior bulk water and the ambient air, there must be a net surface charge density at the air–water interface. In water, hydroxide ions (OH−) and hydronium ions (H3O+) are expected to accumulate at the air–water interface.54 A net negative charge can be due to an imbalance in the natural ion concentration. In pure water, the concentration of each ion species is approximately 1.7 parts per billion (ppb). For a water drop of radius 2 mm, this corresponds to 1.9 × 1012 ions of each species. Additionally, the charge imbalance required to produce a potential VD = −0.5 V is about 7 × 105 elementary charges. This means that only a small fraction (less than 1 ppm) of the naturally occurring ions would need to contribute to the net charge in order to produce the expected Volta potential. A potential mechanism to produce this charge imbalance is shown in Fig. 5. A hydronium ion can source an electron from the metal surface, eventually resulting in a minute amount of hydrogen gas that either remains dissolved or escapes into the air. We note that this charge imbalance would produce negligible changes in pH, and thus absorbed gases, such as CO2, could also produce a similar charge imbalance.
Conversely, Fluorinert drops acquired significantly more negative charge than either water or glycerol, where Δq/Δm ≈ −12 pC g−1. We note the radius of Fluorinert drops ranged from 1.1–1.3 mm, much smaller than water due to their lower surface tension (18 mN m−1) and larger density (1.94 g mL−1). Triboelectrically, that Fluorinert charges negative against the metal tip (or glass syringe) is unsurprising since fluorocarbons reside at the bottom of triboseries.56 Furthermore, we suspect that these higher to charge-to-mass ratios reflect the fact that Flourinert is nonpolar, has no ions, and has an extremely high resistivity (2.3 PΩ cm, compared to 18.2 MΩ cm typical of our DI water). Lastly, the Debye length (an important parameter in flow electrification) differs significantly between the fluids used here. For salt water, the Debye length is nanometers or less, whereas, for pure water, it is approximately 1 micron. But for insulating liquids, the Debye length can be millimeters or larger. Theories considering the electronic state in the bulk (i.e. Volta potential) likely do not apply when the Debye length is close to the drop size.
From an applications perspective, the large potentials acquired by fluids with low conductivity evince the persistent electrostatic hazards present across a number of fields. Beyond industrial settings, however, the frictional charging of dielectric fluids may have important implications for geophysical processes on worlds with exotic potamologies. Saturn's moon Titan, for instance, hosts extensive river and lake systems made not of water, but of liquid methane and ethane.57 While previous work has suggested that the charging of hydrocarbon solids can impact the transport of dust on Titan, whether or not flow electrification impacts the transport of hydrocarbon liquids on Titan remains unexplored. Ultimately, we suggest that more experiments are needed to specifically investigate such insulating liquids, whose equilibrium charge may arise from a different balance of charge transfer mechanisms.
Fig. 7(c) shows Δq/Δm for drops dispensed from a glass syringe and 3 nominally identical PTFE syringe tips (2 cm long). These tips were all cleaned in the same Neutrad bath, rinsed repeatedly with DI water, and stored in a glass beaker until use. They were used sequentially in experiments on the same day with the same water. As in previous experiments, the metallic luer-lock thread of the syringe was grounded. We find that each tip produced drops with different Δq/Δm magnitudes and polarities. Whereas one tip generated negative drops with Δq/Δm of −60 pC g−1, another generated positive drops with maximum Δq/Δm of 120 pC g−1. Furthermore, as in the experiments with PPL syringes, we observed that Δq/Δm evolves with time. Our results contrast with those of Burgo et al., who report only positive charging behavior for water in contact with PTFE. We note, however, that making a one-to-one comparison between experiments is difficult due to the higher flow rates in that study (140× greater, which prevented investigation of individual drops). Additionally, their experiments used a plastic reservoir, as in Fig. 7(b).
The fact that water drops dispensed from plastic reservoirs or syringe tips gain large amounts of charge is consistent with previous experiments. For example, water drops deposited from a pipette tip can display a large positive charge, ∼100 pC or more.58 A more surprising result is the fact that we observe both negative and positive charging on water droplets interacting with PTFE tips. Like many plastics, PTFE is on the extreme lower end of the triboelectric series and is often considered to be one of the substances that most effectively gains negative charge during frictional interactions. Indeed, the positive electrification of droplets flowing on PTFE surfaces has served as the basis for a number of proposed triboelectric nano generators.59,60
Currently, we do not have a satisfactory explanation for the evolution of Δq/Δm when a plastic component is introduced into the system. The magnitude of the charge we observe in experiments with plastics is 10–100 times larger than with glass and metal (Fig. 2). It is unlikely that an electrochemical charging mechanism similar to Fig. 5 could produce such a large, and often time-varying charge. For solid–solid contacts involving hydrocarbons, microscale chemical heterogeneity along solid surfaces can lead to a large variability in charging behavior.61,62 Moreover, history dependence in solid–solid tribocharging has recently been demonstrated during repeated contacts between a sphere and a planar surface using acoustic levitation.10 In those experiments, hysteresis in water adsorption was suspected to be the primary cause of history dependence. Surprisingly, materials discharged and retested under the same humidity conditions could produce different magnitudes and signs of charge transfer. Similar variability could operate in solid–liquid contacts, explaining the apparent randomness of charge gain we observed in our experiments with plastics. Lastly, surfactants leached from plastic surfaces could also contribute to the diversity of charging behaviors reported here. We suspect that the matter of water-plastic electrification will find a more satisfactory answer in future experiments considering a broader ensemble of plastics.
Together, our results suggest that the Volta potential is but one in a myriad of potential electrification mechanisms leading to flow electrification, and motivate future experiments involving a broader range of solid–fluid (or even fluid–fluid) interactions. Furthermore, the varied magnitude and polarity of charging we observe with certain material combinations (e.g., water and plastics) undermines the usefulness of tools like triboelectric series. It has been recently shown that an organized triboelectric series can be built by rubbing identical materials together,64 implying that history dependence can be much more important for charging behavior than average, bulk material properties. Improved characterizations of fluid electrification phenomena will assuredly resolve these open questions, with implications for industry, the energy sector, and even planetary science. In the meantime, however, our work hints that triboelectric series classification for fluids should be used sparingly and judiciously.
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