Owing to the modern industrial activities, an alarming increase of toxic pollutants in the environment caused by human activities has brought to serious environmental issue, such as water pollution and air pollution, which is the most important environmental factor of disease and premature death in the world today [44]. For the growing threat of environmental pollutants, high efficiency pollutant treatment strategy is highly desired to ensure clean environment and human health. Due to high removal efficiency, great versatility, high amenability, and excellent environmental compatibility, electrochemical technology has been extensively developed as a promising method for environmental pollutants treatment [45, 46]. However, the requirement of an external power supply has become the major challenge for the practical application of electrochemical technology. Due to the invention of TENG by collecting mechanical energy from environment, SPES has been proposed as a candidate for environment treatment [47]. Furthermore, with the gradually enhanced output performance of TENG, many efforts have been devoted for removing environmental pollutants from water and air.

Water pollutants are mainly composed of inorganic, organic, and biological contaminants. As one of the most toxic pollutants, heavy metal ions can biologically accumulate upon cumulative exposure, which is not biodegradable, and thus threaten human health via the entire food chain [48]. Aiming to remove heavy metal ions from environment, Li et al. reported a water-driven TENG to extract the kinetic energy from wastewater flow, which used to drive electrochemical reaction for Pb²⁺ and Cu²⁺ removal [49]. By using the integrated SP system, 97.4% of the two metal ions was removed from the wastewater in 100 min. Through comparing the electrochemical property of Cr(VI) driven by continuous DC (CDC) and pulsed DC (PDC), Zhou et al. confirmed an enhanced efficiency of removing Cr(VI) under PDC than that of CDC due to the better utilization of ferrous ion, the lower electrode passivation, and the higher ion diffusion rate during the reaction process [50]. Therefore, they proposed an SPES based on TENG with PDC output for improving the electrochemical performance of heavy metal ion treatment. The structures of the rotary TENG and SPES are shown in Figures 2(a) and 2(b). The charge consumption under different power supply is shown in Figure 2(c). Under equal charges consuming with 0.048 C, the removal efficiency driven by PDC was increased by 53.5% compared to that of CDC.

Organic pollutants in water have also drawn wide concern because of the most toxic and potentially carcinogenic; therefore, large efforts have been devoted to removing organic pollutants from wastewater. SP electrooxidation is the common process for organic pollutants treatment by using the produced chlorine and hypochlorite. Li et al. proposed a unique SP electrooxidation system to phenol removal via creatively employing β-cyclodextrin to increase triboelectrification [51]. In the condition of wastewater wave with velocity of 1.4 m s^-1 and initial concentration of phenol with 80 mg L^-1, 90% of the phenol was removed by the generated power in 320 min. Gao et al. reported a free-standing mode TENG integrated with electrocatalytic technology for degrading 4-aminoazobenzene [52]. With a commercial aluminum panel as stator, the power density reached up to 2.28 W m^-2. Driven by the TENG, 4-aminoazobenzene can be electrochemical degradation to small molecule polymers by sensibly adjusting the potentials of electrochemical oxidation. By using the sponge to improve the contact intimacy and precharge injection to increase the surface charges in the dielectric film, Gao et al. improved the power density of a multilayer linkage TENG to 7.4 W m^-2, which was used to drive electrochemical catalysis for degrading methyl red [53]. Powered by the multilayer linkage TENG, the degradation percentage of methyl red was almost 100% after 160 min, with a color change from red to colorless. Additionally, Chen et al. fabricated an SP multifunctional system which can simultaneously realize heavy metal ions and organic pollutant removal driven by a rotary TENG [54]. The illustrations of the rotary TENG and system are shown in Figures 2(d) and 2(e). After rectifying, 100% of rhodamine B and 97.3% cupric ion were removed after 3 hours treatment (Figures 2(f) and 2(g)). Besides, Yang et al. reported an SP electrocatalytic system containing a hybrid energy cell including TENG to degrade methyl orange, which can further achieve a higher performance [55]. In this system, the generated energy can directly power the electro-degradation of methyl orange or store in an energy storage unit before utilizing for methyl orange treatment, where the removal efficiency of methyl orange reached 80% after 144 h.

Owing to merits of environmentally friendly and particularly efficient, SP electrochemical advanced oxidation system such as SP electro-Fenton process is proposed to removing organic pollutants from the water [56–58]. Feng et al. integrated a rotary TENG with an electrochemical cell to build an SP electro-Fenton system to remove dyes [59]. In this work, a modified graphite felt cathode was used to produce H₂O₂ along with •OH, and a platinum sheet anode was applied to generate active chlorine, which can be used to oxidize organic pollutants. Through power management, the electric power of integrated rotary TENG improved by 3.5 times for driving electrochemical reaction. Driving by wind flow at the speed of 6.2 m s^-1, the SP electro-Fenton system can efficiently degrade dyes without aerating oxygen, and a removal efficiency of 87.5% within 120 min was achieved. Combining with 3D printing techniques, Tian et al. prepared a 3D printed elastic TENG to form an SP electro-Fenton system for removing methylene blue, where 97.0% of methylene blue was removed within 140 min [60].

Biological contaminants such as harmful bacteria and algal blooms caused by uncontrolled discharge of wastewater are the other kinds of water pollutants. Jiang et al. reported an SP electrochemical water treatment system on the basis of an arch-shaped TENG for cleaning sterilization and algae in wastewater [61]. By extracting water wave energy, most of the bactericidals and algae treatment were cleaned by the produced Cl₂ and reduced graphene oxide. By using SPES, high removal efficiencies for three model bacteria and mixed marine algae were achieved.

Air pollution including fine air particulate matter (PM) and gaseous pollutants is a crucial toxicant caused by human activities. Generally, air pollution exposure is related to lots of chronic diseases, such as pulmonary and cardiovascular disease [62]. To clean PM 2.5, Guo et al. reported an SP triboelectric negative air ion generator (MSNG) powered by TENG [63]. Powering by TENG, the voltage of carbon fiber electrodes was over 2 000 V, which can be employed to produce negative air ions in these electrodes (Figure 2h). For demonstrating the ability to clean PM 2.5, 1\times {10}^{13} NAIs was generated by using a palm-sized MSNG, and PM 2.5 with initial concentration of 999  μg m⁻³ was quickly declined to 0  μg m⁻³ in 80 s at 0.25 Hz. Furthermore, the observable heavy smog purification processes are displayed in Figures 2(i) and 2(j), which demonstrated the high efficiency of the MSNG for air purge.

The primary pollutants of gaseous pollutants result from the original pollutants directly discharged into the atmosphere from the source, mainly including oxysulfide, oxynitride, and organic compounds [64]. For removing sulfur dioxide (SO₂) and dust, Chen et al. reported an SP air cleaning system on the basis of a rotary TENG [65]. Driven by nature wind, rotary TENG produced a high voltage about 300 V, which was applied to power the electrochemical oxidation of SO₂ without the byproducts such as ozone and NOx than conventional electrostatic precipitation. For cleaning oxynitride, Han et al. proposed an SP NO_X absorption and degradation system on the basis of a radial-engine-shaped TENG system [66]. By harvesting win energy, the SP system synchronously achieved the removal of NO_X. For cleaning formaldehyde in indoor atmosphere, Feng et al. demonstrated an SP electrostatic filter by integrating TENG with photocatalysis technology [67]. In this work, a single electrode TENG was used as power source to produce high electric field on the filtering network. Consequently, the SP electrostatic filter was demonstrated to clean formaldehyde via both electrostatic adsorption effect induced by TENG and enhanced photocatalytic effect by the photocatalyst on the SP filter networks, where the formaldehyde concentration decreased to 60% within 250 min, and a tripled increased efficiency of formaldehyde removal was achieved.

Converting energy from environment into easily storable chemical energy such as hydrogen and formic acid has drawn public attention as the alternative technology to ensure a clean and sustainable energy supply [68]. Generally, the process of clean fuel production needs an external input power, where renewable energies such as solar, wind, geothermal, and hydro have been applied along with carbon dioxide and water to generate clean fuels [69]. Owing to the ability of harvesting ambient mechanical energy, TENG-based SP electrochemical system has been demonstrated as a promising technology for clean fuel generation [70–73]. Tang et al. firstly proposed a fully SP water splitting system for producing hydrogen [74], which integrated a rotary TENG with a water splitting unit (Figures 3(a) and 3(b)). Driven by the rotary TENG at 10 Hz, the production ratio of hydrogen was up to 6.25\times {10}^{-3} mL min^-1 in 30% (w.t.) potassium hydroxide solution. As demonstrating, obvious bubbles were observed in the electrode (Figures 3(c) and 3(d)). To improve the production speed of hydrogen, introducing a hybrid cell to increase the output power of SP water splitting system is a promising strategy [75]. Yang et al. designed an SP water splitting system on the basis of a hybrid energy cell, where the hydrogen production speed had been improved to 4\times {10}^{-4} mL s^-1 [76].

As the other type of clean fuel, formic acid with characteristics of high volumetric capacity, low toxicity, and flammability under ambient condition has drawn wide attention [77]. Leung et al. presented an SP carbon dioxide reduction system that harvests energy from ocean wave for converting carbon dioxide into formic acid (Figure 3(e)) [78]. At an optimal value of discharge voltage (2.4 V) for each cycle, the system realized near 100% faradaic efficiency for shifting carbon dioxide into formic acid. Driven by TENG under a simulated waves with water surface area of 0.04 m², the system generated 2.798  μM of formic acid per day.

Ammonia (NH₃) acts a crucial role in food production, industrial manufacturing, and a predictable ideal energy carrier in the future [79]. In industry, Haber-Bosch process is commonly employed to produce NH₃ with the existence of hydrogen and external energy supply, where the challenge of grueling conditions increases the cost of production [80]. Due to a controllable operation under mild conditions utilizing mechanical energy by TENG, the SP electrocatalytic NH₃ synthesis system based on TENG provides a promising candidate for the conversion of N₂ to NH₃. Gao et al. reported an SP sustainable metal-free NH₃ production system based on a multilayer asway TENG by 3D printing technology, which can efficiency convert N₂ into NH₃ [81]. The maximum power density of 6.7 W m^-2 was realized by the printed TENG, which was used to drive the production of NH₃. By using the carbon materials from melamine sponge as the metal-free electrocatalyst, the assembled SP NH₃ production system can reach NH₃ yield of 36.41  μg h^-1 mg^-1_cat.. By introducing a high-output dual-TENG configuration, Han et al. constructed an SP electrocatalytic NH₃ synthesis system to simultaneously achieve nitrogen fixation and electrocatalytic reduction with air as the N₂ source [82]. The electrocatalytic NH₃ synthesis system mainly consisted of three parts, including TENG-1, a needle-plate, and TENG-2. Specifically, TENG-1 was used to produce high voltage, a needle-plate was utilized to fix nitrogen and produce NO_X which then flowed into a water receptacle to produce NO₃^- and NO₂^-, and TENG-2 was employed to generate pulsed DC which drove the reaction for ammonia production (Figures 3(f) and 3(g)). Driven by the gas flow, a high voltage of 7 kV supplied by TENG-1 and the output performance of 3.1 V and 8.9 mA for the cell reaction supplied by TENG-2 were achieved, respectively (Figure 3h). By employing the SP electrocatalytic NH₃ synthesis system based on above dual-TENG, 2.4  μg h^-1 of NH₃ was successfully synthesized (Figure 3(i) and 3(j)).

Besides the abovementioned works, some other SPESs such as SP electrochemical oxidation system and SP electrodeposition system were also developed to electrochemical synthesis [83–86]. Zheng et al. reported an SP electrochemical oxidation system on the basis of designed cross-linked TENG for synthesizing polyaniline [85]. As for the cross-linked TENG, the high capability of 69.9  μA and 845.6 V was achieved. By harvesting vibration energy, the SP electrochemical oxidation system was utilized as electricity source for converting aromatic amines to polyaniline. Wang et al. established a self-powered electrodeposition system for polypyrrole synthesis, where the polypyrrole as the electrode material of TENG was produced by TENG [86].

Based on TENG, lots of SP electrochemical sensors have been proposed to detect chemical substances. According to the mechanism of sensing, SP electrochemical sensor can be classified into two types including SP electrochemical passive sensor and SP electrochemical active sensor [47, 87].

SP electrochemical passive sensor is that the conventional sensors are driven by TENG for collecting mechanical energy from environment. Zhang et al. proposed an SP glucose biosensor based on contact-separation type TENG combined with lithium-ion battery [88]. The flexible TENG fabricated by a patterned polydimethylsiloxane (PDMS) film can extract energy from the motion of clapping; thus, the battery with an increased charging voltage from 400 mV to 800 mV was achieved after more than two hours, which was successfully demonstrated to power a glucose biosensor. Aiming to voluntarily supervise the water quality, Bai et al. reported an in situ SP sensing system that can convert the water wave energy to electricity based on tandem disk TENG [89]. Owing to the radial grating disk structure with swinging mass blocks, the tandem disk TENG driven by water waves can realize a conversion from low-frequency water wave motions into high-frequency output; thus, an average power density of 7.3 W m^-3 was achieved. Through rectification and energy storage, the electricity produced by TENG can be utilized to drive electronics for monitoring the water quality.

As for the SP electrochemical active sensor, a TENG is designed to actively generate electrical signal for responding the stimulation of chemical molecules or environmental factors such as ethanol, phenol, catechin, and pH, where the output performance of TENG and the target shows a linear relationship [51, 90–92]. Zhang et al. demonstrated SP sensors based on the TENGs fabricated by polyamide (PA) film and polytetrafluoroethylene (PTFE) film for detecting liquid/gaseous ethanol [90]. The TENG was mainly composed of two plates, where a layer of PA or PTFE film was pasted on a copper foil as back electrode, and a nanopore modified Al foil was used as the triboelectric electrode. Due to the degrees of wettability of the PA and PTFE films to ethanol, the output voltage of the SP sensor logarithmically declined with the concentration of ethanol solutions increasing from 20% to 80%, as well as the output signal decreased with the increase of ethanol gas concentration ranging from 40% to 80%. Lin et al. proposed a contact-separation-type TENG as an SP nanosensor toward catechin detection [91]. For this TENG, PTFE film and a layer of TiO₂ nanomaterial (nanowire and nanosheet) array were used as a pair of triboelectric materials. Because of the strong interaction between Ti atoms of TiO₂ nanomaterial and enediol group of catechin, a high sensitivity (detection limit of 5  μM) and a linear range from 10 M to 0.5 mM of the SP nanosensor were achieved, demonstrating great potential for the determination of catechin concentrations in real samples. Wu et al. reported an SP triboelectric sensor based on the sliding type TENG for detecting pH value from a periodic contact/separation motion [92]. A fork-finger structure was designed for SP triboelectric sensor, which mainly consisted of fluorinated ethylene-propylene (FEP) film and metal electrodes. The reciprocating motion between SP triboelectric sensor and buffer solution resulted in charge transfer between the adjacent Cu bottom electrodes, generating AC voltage in the external circuit. The output voltage of the SP triboelectric sensor enhanced with increased pH value due to the increased ion concentration. Therefore, the pH value of buffer solution can be actively monitored in real-time by reading the output voltage. Li et al. proposed an SP active sensor to Hg²⁺ ions monitoring based on TENG where 3-mercaptopropionic acid-modified gold nanoparticles was used as recognition element [93]. In this system, a contact-separation-type TENG was employed, which shown a layered structure based on two plates (Figure 4(a)). The output performance of TENG and the concentration of Hg²⁺ ions displayed a linear relationship because the chemical potential difference between the different triboelectric layers defined the triboelectrification effects. As shown in the inset of Figure 4(b), the output performance of the TENG declined with improving the concentration of Hg²⁺ ions, where the short-circuit current ratio was proportional to the concentration of Hg²⁺ ions in the range of 100 nM-5 000 nM. Due to the high selectivity of 3-mercaptopropionic acid toward Hg²⁺ ions, Hg²⁺ ion can be specifically detected by the proposed sensing system (Figure 4(b)). Jie et al. demonstrated an SP triboelectric sensor for monitoring dopamine in the alkaline condition on the bases of TENG, which was composed of PTFE with nanoparticle arrays and an Al film (Figures 4(c) and 4(d)) [94]. Because the nano-stick PTFE exhibits a strong interaction of dopamine, the output performance of the TENG was inversely proportional to the concentration of dopamine in the range of 10  μM-1 000  μM (Figure 4(e)). In this work, a detection limit of dopamine was 0.5  μM, which suggested an effective means of SP electrochemical sensor for dopamine detection. Wen et al. introduced an SP gas sensor on the basis of a blow-driven TENG, where a rotary TENG was applied as shown in Figure 4(f) [95]. The illustration of the SP breath analyzer is shown in Figure 4(g). Driven by mouth blowing, the output voltage of the sensor was only proportional to the concentration of alcohol in the airflow (Figure 4(h)). On the basis of blow-driven TENG, the active alcohol breath analyzer exhibited a high detection gas response of ~34 under an optimized condition. Additionally, when the blow-driven TENG was blew by a tester without drinking alcohol, the voltage drop across the sensor was almost zero due to a low sensor resistance (Figure 4(i)). While the air-flow of a tester that had been drank across the sensor, an enhanced voltage would be generated and thus could trigger the warning system (Figure 4(j)), which was caused by the dramatically increased resistance of the sensor in the breathed-out alcohol vapor.

Electrochromic devices can reversibly change their optical properties by the electrochemical redox reaction under an external electric field [96]. Applied TENG as the electricity source to provide a constant voltage, SP electrochromic device has been realized to replace batteries, which provides a promising sustainable power solution [97, 98].

Driven by a dual-mode TENG for harvesting wind and raindrop energy, Yeh et al. realized an SP smart window system [99]. The dual-mode TENG involved a single-electrode TENG on the top of the SP smart window for harvesting the energy from raindrop motions, and a contact-mode TENG assembled by elastic springs below the abovementioned single-electrode-mode TENG for collecting energy from wind energy. Both of the two TENGs consisted of a PDMS thin film adhered to a conducting substrate that were adhered to the electrochromic device with a substrate to fabricate an SP system (Figure 5(a)). The electrochromic device mainly consisted of Prussian blue (PB) nanoparticles and zinc hexacyanoferrate (ZnHCF) nanocubes as the electrochromic material and the ion storage layer. By photolithography and a template molding process, the PDMS film has a micropatterned pyramid array structure for enhancing the hydrophobic property and effect contact area of the surface. Driven by the dual-TENG, the transmittance of the electrochromic exhibited reversible variations. For gaining a more intuitive view of the change of the optical property, the transmittance of the electrochromic device was measured from 400 to 800 nm both before and after the coloring process. As shown in Figure 5(b), the transmittance declined in the full range during the coloring process, and the highest variation was realized at 695 nm, while the transmittance declined from 53.5% to 20.9%. These transmittance changes can be observed by visualization, where the color of the electrochromic device changed from transparent in bleached state to deep blue in colored state (Figure 5(c)). In this work, 32.4% of the maximum transmittance change was achieved at 695 nm, which closed to the value of 32.6% that powered by a conventional electrochemical power source.

Yang et al. reported a WO₃-based electrochromic device integrating with TENG to fabricate an SP electrochromic device [100]. The SP electrochromic device had a multilayered structure, which is displayed in Figure 5(d). Commercial glass was used as the substrate, on which there was a layer of FTO thin films acted as electrodes. The sheet resistance and transmittance of FTO film were 35-45 Ω per sq. and 80%, respectively. Between the two electrodes, there were an array of cells and a layer of WO₃ film (Figure 5(e)), and the distance between the two electrodes was around 20 mm. The cells were filled with polyelectrolyte, and the WO₃ film was about 250 nm which was densely packed nanoparticles. As shown in Figure 5(f), the fully packaged SP electrochromic device still had a transmittance of more than 70%. As shown in Figure 5(g), powered by TENG, the transmittance of electrochromic cell was drop via coloring process (Figure 5(g), (I)). When the connection of reversible switch was reversed, the electrochromic cell returned to transparency (Figure 5(g), (II)). Compared with the SP electrochromic device, the transmittance of the device greatly dropped, and a relatively stable difference of as much as 17% was maintained for wavelength that ranges from 450 nm to 650 nm (Figure 5(h)), indicating the sensitivity and the applicable to a broad range of light wavelength.

To effectively harvest acoustic energy, Qiu et al. integrated a sandwich-like structured TENG with electrochromic device for reversible color changing [101]. The TENG consisted of three layers including Cu foam, polyvinylidene fluoride (PVDF) nanofiber, and a nylon fabric. There was a thick spacer layer between the nylon fabric and PVDF nanofibers to produce more space vibration for the membrane. Driven by sound, high outputs of 25.01 mA m^-2 and 20.91  μC s^-1 were achieved for the designed TENG. The high performance of TENG enabled it to power an electrochromic device. In this system, reversible switches controlled the oxidation and reduction process and thus controlled the color change. Driven by the TENG, the color of electrochromic film changed between the transparent white and dark blue, which were controlled by the switching dote.

Material corrosion is a long-standing challenge in many engineering applications [102]. The cathodic protection is one of the most durable methods to protect the materials from corrosion, which involves sacrificial anode cathodic protection system (SACPS) and impressed current cathodic protection system (ICCPS) [103–105]. Different from SACPS, the ICCPS can protect the steel by cathodic current from a direct current source without any sacrifice of electrode materials [106]. However, the requirement of external electric energy supply limits its practical application. For solving this issue, many works have been focused on the SP anticorrosion system by integrating TENG with chemical anticorrosion protection [107–111].

Wang et al. realized an SP anticorrosion system for iron sheet driven by a high performance TENG [112]. Utilizing the fabricated nanostructures and prior-charge injection method, the charge densities were improved by 48% and 53%, respectively. The schematic image of SP anticorrosion system is depicted in Figure 6(a). Aiming to study the effect of SP anticorrosion system, the ion steel was soaked into 3.5% NaCl solution for 2 h, and the corresponding surface morphology is displayed in Figure 6(b). As displayed, almost no change of the iron sheet was observed by using TENG, while a thin rust film was produced without TENG. This result indicated a good anticorrosion property of the SP system, which exhibited a good prospect to protect materials from rusting with low energy cost.

Considering the metal corrosion is more likely to happen under ocean environmental conditions, Li et al. developed an SP system on the basis of networking TENG and supercapacitor to convert water wave to electricity for metal anticorrosion [113]. To obtain a stable and continuous output, the flexible TENG integrated with a flexible double-layer supercapacitor for harvesting the wave energy and then storing the energy in the supercapacitor. The structure and working mechanism of the SP system displayed in Figure 6(c). Driven by the water wave in the condition of 0.2 m s^-1 and 1 Hz, the protected steels injected into electrons stemmed from TENG, leading to a cathodic polarization. In this work, a declined potential of steel electrode from -0.35 V to -0.6 V indicated that the steel become more stable in the protection of designed SP system. Immersing in the solution of sodium chloride with concentration of 0.5 M, there was a thin layer of rust on the steel without the protection of SP system, while there were a few corrosion pits on the steel when the SP system was working (Figure 6(d)). These results demonstrated that the SP system significantly decreased the corrosion rate, which could be adopted in marine corrosion.

Zhu et al. designed an SP cathodic protection system based on a flexible TENG, which can harvest energy from natural rain drops and wind to drive the cathodic protection process [110]. The contact-separation-type TENG was mainly composed of PDMS film and ITO, which were acted as a pair of triboelectric layers (Figure 6(e)). The schematic diagram of the SP metal surface cathodic protection system is shown in Figure 6(f). Under stimulations at a frequency of 1 Hz, the output current of the TENG was over 130  μA, and the voltage reached about 500 V. In this SP cathodic protection system, the protected metal that was immersed into the electrolyte was acted as the cathode, while a carbon rod was used as the anode. The comparison results of the rested specimens with and without SP cathodic protection system are displayed in Figure 6(g). For the specimens protected with SP cathodic protection system, several gray distributing areas appeared on the surface of specimens. These areas enlarge with the increase of corrosion, but no apparent corrosion was observed on these samples. As for the specimen without SP cathodic protection system powered by TENG, numerous corrosion pits were found on the three surfaces of specimens, and more big pits arose on the sample that was corroded in simulated electrolyte for 72 h.