In-Situ Construction of 2D / 2D ZnIn 2 S 4 / BiOCl Heterostructure with Enhanced Photocatalytic Activity for N 2 Fixation and Phenol Degradation

: Photocatalytic nitrogen fixation and pollutants degradation at ambient temperature and pressure as a clean and efficient means represents a sustainable direction. In this paper, novel two-dimensional (2D) ZnIn 2 S 4 / 2D BiOCl (ZIS / BOC) nanosheets heterostructures were successfully synthesized by in-situ solvothermal techniques. XPS and TEM results showed the formation of heterostructure. The photocatalytic properties of these materials were further studied by degradating phenol and nitrogen fixation under visible light irradiation. In particular, heterostructure obtained with a mass ratio of 0.5 wt % of ZnIn 2 S 4 had a good application prospect and can achieve 77.4% phenol degradation rate within 6 h and a rate of ammonium production of 14.6 µ mol · g cat − 1 · h − 1 . The reaction rate of 0.5 wt % ZIS / BOC heterostructure exhibited 8.6 and 2.6 times relative to BiOCl for the degradation of phenol and nitrogen fixation, respectively. The enhanced photocatalytic activity was attributed to the collaboration of low recombination rate of photo-generated carriers and enhanced visible light absorption. Based on capture experiments and electron spin resonance (ESR) techniques, the main active species that may appear in photocatalytic systems were explored, and the corresponding photocatalytic mechanism was also proposed appropriately. This strategy will open up new ideas for the design and manufacture of more energy-efficient materials with high photocatalytic activity. noting that the peak positions of Bi 4f, O 1s, and Cl 118 2p in the 0.5 wt% ZIS/BOC heterostructure have a certain shift with respect to BiOCl. The shift might result from a partial e - transfer from ZnIn 2 S 4 to BiOCl. Similarly, in Figure 4e-g, high resolution peaks 120 of Zn 2p were not observed, and In 3d at 441.4 and 451.8 eV, respectively, indicates that it exists in the In 3+ valence state. However, the S 2p may be because the location of binding energy is similar to that of the Bi 4f or the content is too low and not observed [43,52]. The change of banding energy of 123 elements may be ascribed to the formation of chemical band between BiOCl and ZnIn 2 S 4 . Based on 124 the XPS results and combination of literature report [53,54], owing to the strong affinity between Bi 3+ 125 and S 2− , Bi-S bond at the interface between BiOCl and ZnIn 2 S 4 may be formed during in-situ 126 solvothermal process.


Introduction
Rapid economic development and improvement of technology have an important impact on human life and quality of life. Among them, phenolic compounds have brought great convenience to human beings since they were found. However, wastewater generated in the production process is a very difficult problem and also has an indelible impact on the environment or even human health. Among phenolic-containing wastewater, phenol has the most severe toxicity. Therefore, efficient treatment of phenol compounds is of great significance to national economic and social development [1][2][3][4][5]. Moreover, nitrogen is widely found in nature and has an important impact on human life and quality of life. Particularly, efficient ammonia synthesis by chemical reaction involving nitrogen is of great significance to national economic and social development. The traditional Haber-Bosch process requires a lot of energy every year, so the search for a new high-efficiency, energy-saving, and environmentally-friendly nitrogen fixation method has attracted widespread public attention [6][7][8][9][10]. In recent decades, scientists have been working hard to find effective means to treat phenol compounds and achieve nitrogen fixation, and there has been little success [11][12][13][14][15][16][17][18][19][20][21].
In nature, green plants use solar light energy to assimilate carbon dioxide and water they absorb into organic matter. Photocatalytic as a kind of advanced oxidation process (AOPs) has attracted more and more attention recently because of its high efficiency and cleanness. Furthermore, photocatalytic degradation of pollutants and nitrogen fixation have been proved in various photocatalysts [22][23][24][25][26][27][28][29]. BiOCl, as one of the representatives of ternary oxides, has a special anisotropic layered structure with the band gap width is about 3.2 eV, and has good photocatalytic performance under ultraviolet irradiation, which is a bismuth-based compound with low cost, easy preparation, stable structure, and no toxicity, and has recently attracted widespread attention [30][31][32][33]. However, BiOCl itself cannot respond to visible light. Expanding its visible light response activity through effective modification methods has become the key to promote its industrial application. In order to solve these problems, a series of strategies have been developed to improve the performance of BiOCl [30][31][32][33][34][35][36]. Polymetallic sulfide semiconductor photocatalysis materials have been extensively studied due to their good light absorption performance and adjustable band gap [37][38][39]. Among many reported photocatalytic materials, ZnIn 2 S 4 is a direct band gap with band energy of 2.4-2.7 eV [40,41], has shown good visible light photocatalytic performance due to its unique structure and physical and chemical properties, and has overcome the disadvantage of easy corrosion of traditional sulfides. Unfortunately, the single ZnIn 2 S 4 has low transmission and separation efficiency of photogenerated carriers, and the electron (e − )/hole (h + ) pair is easy to combine, thus greatly reducing its photocatalytic performance [42][43][44]. In view of the above factors, many researches have been carried out to try to solve the above shortcomings. Furthermore, the combination of ZnIn 2 S 4 with other semiconductors to improve the photocatalytic performance of ZnIn 2 S 4 has been verified [42][43][44][45][46][47][48][49].
In this work, 2D/2D ZIS/BOC heterostructures were fabricated by in-situ solvothermal methods, and under the irradiation of visible light, photocatalytic reaction was used to degrade phenol and fix nitrogen. The activity results show that the prepared ZIS/BOC heterostructures have high photocatalytic degradation of phenol and nitrogen fixation activity. The designed interface structure of ZIS/BOC heterostructures was conducive to the separation and transfer of e − and h + , and then enhanced the photocatalytic activity. Finally, according to capture experiments and ESR techniques, the corresponding photocatalytic mechanism was proposed.

Characterization of Photocatalysts
The crystal structure of the prepared sample was investigated by XRD, as shown in Figure 1 [44]. The 0.5 wt % ZIS/BOC heterostructure presented nearly the same XRD patterns, indicating that the coupling of ZnIn 2 S 4 nanosheets showed no effect on the crystal structure of BiOCl nanosheets. However, the characteristic peaks of ZnIn 2 S 4 were not observed in the composite sample, which may be due to its low relative strength or content. Figure 2a presented the SEM image of BiOCl, where it can be seen that BiOCl is a nanosheet structure with a thickness of about 20 nm. From the inset plot of Figure 2b, it can be seen that pure ZnIn 2 S 4 are nanoparticles with a size of about 10 nm. The morphology of 0.5 wt % ZIS/BOC heterostructure exhibits a novel 2D/2D heterostructure (Figure 2b), which may be due to the directional growth of ZnIn 2 S 4 on the surface of 2D BiOCl structure. Figure 2c,d presented the element distribution diagram (EDS) of 0.5 wt % ZIS/BOC heterostructure. Moreover, the composite catalytic material contains six elements of Bi, Cl, O, S, In, and Zn can be seen from Figure 2e-j, the distribution of each element in the 0.5 wt % ZIS/BOC heterostructure is relatively uniform. Figure 3 exhibited the TEM electron micrographs of BiOCl and 0.5 wt % ZIS/BOC heterostructure. As can be seen from Figure 3a,b,    XPS was used to further confirm the presence of all elements in the heterostructure. Figure 4 shows the XPS spectroscopy of 0.5 wt % ZIS/BOC heterostructure, pure BiOCl, and ZnIn 2 S 4 . Further analysis of Figure 4a by XPS spectroscopy revealed that the sample 0.5 wt % ZIS/BOC heterostructure contained six elements of Cl, O, Bi, Zn, In, and S. Pure BiOCl contained three elements of Cl, O, and Bi, while ZnIn 2 S 4 contained three elements of Zn, In, and S. Figure 4b-g are high resolution XPS spectra corresponding to Bi 4f, O 1s, Cl 2p, Zn, 2p in 3d and S 2p, respectively. Figure 4b showed that the signal peaks with binding energies of 158.8 and 164.1 eV correspond to Bi 4f 7/2 and Bi 4f 5/2 in the 0.5 wt % ZIS/BOC composite, indicating the presence of Bi 3+ [50]. Figure 4c showed that the binding energy located at 530.4 and 529.5 eV are lattice oxygen and surface hydroxyl oxygen, respectively [34,51]. Figure 4d showed that the characteristic peaks with binding energies of 199.1 and 197.5 eV correspond to Cl 2p 1/2 and Cl 2p 3/2 [50]. It is worth noting that the peak positions of Bi 4f, O 1s, and Cl 2p in the 0.5 wt % ZIS/BOC heterostructure have a certain shift with respect to BiOCl. The shift might result from a partial e − transfer from ZnIn 2 S 4 to BiOCl. Similarly, in Figure 4e-g, high resolution peaks of Zn 2p were not observed, and In 3d at 441.4 and 451.8 eV, respectively, indicates that it exists in the In 3+ valence state. However, the S 2p may be because the location of binding energy is similar to that of the Bi 4f or the content is too low and not observed [43,52]. The change of banding energy of elements may be ascribed to the formation of chemical band between BiOCl and ZnIn 2 S 4 . Based on the XPS results and combination of literature report [53,54], owing to the strong affinity between Bi 3+ and S 2− , Bi-S bond at the interface between BiOCl and ZnIn 2 S 4 may be formed during in-situ solvothermal process.     Figure 5 are the UV-visible diffuse reflectance spectrum of the samples. As can be seen from Figure 5, BiOCl has the basic absorption edge of about 362 nm and does not respond to visible light. However, pure ZnIn 2 S 4 has strong absorption in the visible light region with absorption wavelength of 566 nm. After assembling ZnIn 2 S 4 nanosheets onto the surface of BiOCl nanosheets, the light response range of BiOCl was widened from 362 to 505 nm. The enhanced absorption in visible light region indicates that ZIS/BOC heterostructures can generate more photogenerated carriers compared to pure BiOCl and have potential capability for photocatalytic pollutants degradation and nitrogen fixation under visible light. show that the synthesized ZIS/BOC heterostructure has higher stability.

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To further investigate the photocatalytic performance of as-prepared samples, the photocatalytic 168 degradation activity of phenol on different photocatalysts are performed as shown in Figure 7. A 300 169 W metal halide lamp with a wavelength of less than 420 nm cutoff was as a visible light source, and 170 the photocatalytic activity was evaluated using phenol as a simulated pollutant. As can be seen from  In order to evaluate the catalytic performance of samples, we have investigated efficacy of as-obtained BiOCl and 0.5 wt % ZIS/BOC for photocatalytic N 2 fixation. The photocatalytic experiments are performed in N 2 -saturated water a under the irradiation of 300 W Xe lamp in ultrapure water at ambient conditions without any sacrificial agent. Figure 6 showed the performance of photocatalytic nitrogen fixation over as-prepared catalyst under visible light irradiation. As determined by the Nessler's reagent method [55], it revealed that it can hardly produce NH 4 + in the presence of only catalyst or pumping N 2 alone. While the concentration of NH 4 + increased linearly with the extension of the illumination time ( Figure 6a). Therein, 0.5 wt % ZIS/BOC heterostructure achieved a rate of ammonium production of 14.6 µmol g cat −1 ·h −1 , which is 2.6 folds higher than that of pure BiOCl (5.7 µmol g cat −1 ·h −1 ). Furthermore, neither N 2 H 4 nor H 2 has been detected during the photocatalytic process, implying the excellent selectivity for NH 3 . It is interesting that the rate of ammonium production is low in the first half hour for BiOCl, while 0.5 wt %ZIS/BOC exhibited the same NH 4 + production rate during the visible light irradiation, which may be ascribed to two aspects. First, the photocatalytic N 2 fixation is a multistep reaction. The activation of N 2 may mainly occur in the first half hour by transferring the photoexcited e − from BiOCl to chemisorbed N 2 , dissociating N≡N bond and generating N 2 H* intermediates with coupled protons [55]. Second, 0.5 wt % ZIS/BOC heterostructure may exhibit more efficient carriers transfer at the photocatalyst/solution interface than that of BiOCl, achieving faster react rate from intermediates to the final product (NH 4 + ). Also, the NH 4 + production rates are about 14.6, 10, 8.5 and 5.7 µmol g cat −1 ·h −1 , respectively, on those catalysts in an order of 0.5 wt % ZIS/BOC > 0.8 wt % ZIS/BOC > 0.3 wt % ZIS/BOC > BiOCl ( Figure 6b). As can be seen from Figure 6c, the rate of ammonium production of the prepared 0.5 wt % ZIS/BOC decreased from 14.6% to 13.7% after 5 cycles, which can be attributed to deactivation of catalyst surface sites. These results clearly show that the synthesized ZIS/BOC heterostructure has higher stability.
To further investigate the photocatalytic performance of as-prepared samples, the photocatalytic degradation activity of phenol on different photocatalysts are performed as shown in Figure 7. A 300 W metal halide lamp with a wavelength of less than 420 nm cutoff was as a visible light source, and the photocatalytic activity was evaluated using phenol as a simulated pollutant. As can be seen from Figure 7a, the concentration of phenol gradually decreases with the increase of time. The analysis results showed that pure BiOCl only degraded 13.3% of phenol under visible light irradiation for 360 min, and the pure ZnIn 2 S 4 degraded 31.5% of phenol, and 0.3 wt % ZIS-/BOC heterostructure, 0.5 wt % ZIS/BOC heterostructure and 0.8 wt % ZIS/BOC heterostructure degraded 55.4%, 77.4% and 57.4% of phenol, respectively, which is consistent with that of N 2 reduction. This may be due to the fact that excess ZnIn 2 S 4 occupies the active site and the light-shielding effect of ZnIn 2 S 4 [56]. Figure 7b is the plot of the apparent rate constants for different catalysts. It can be clearly seen that the apparent rate constant for the degradation of phenol by 0.5 wt % ZIS/BOC heterostructure is 0.00415 min −1 , which is 8.6, 2.3, 1.8, and 1.7 times than that of pure BiOCl, ZnIn 2 S 4 , 0.3 wt % ZIS/BOC heterostructure, and 0.8 wt % ZIS/BOC heterostructure, respectively, indicating that BiOCl nanosheets modified with ZnIn 2 S 4 nanosheets and can improve photocatalytic activity. Moreover, the stability was confirmed by cycle experiments using 0.5 wt % ZIS/BOC heterostructure as a photocatalyst for the degradation of phenol. As shown in Figure 8, after 5 cycles, the significant change of photocatalytic degradation rate of phenol had not been observed. In addition to this, it can be concluded that from Figure 8 that the XRD pattern after the photocatalytic reaction was approximately similar to that of the 0.5 wt % ZIS/BOC heterostructure before the photocatalytic reaction, showing that 0.5 wt % ZIS/BOC heterostructure had good stability. The activity of photocatalytic degradation of phenol by using ZnIn 2 S 4 /BiOCl heterostructures as photocatalyst were compared with previous literature report [57][58][59][60][61][62][63], as shown in Table 1. Although the as-prepared ZnIn 2 S 4 /BiOCl heterostructures exhibited the promoted visible-light-driven photocatalytic activities than that of pristine ZnIn 2 S 4 or BiOCl, its activity still needs to be further improved by other employing strategies.

Photocatalytic Mechanism
In order to further study the migration and separation efficiency of photo-generated carriers in ZIS/BOC heterostructure, fluorescence spectroscopy was performed on the prepared photocatalysts. Figure 9a showed the photoluminescence (PL) spectra of BiOCl and 0.5 wt % ZIS/BOC heterostructure at 280 nm excitation wavelength, and BiOCl has a strong fluorescence emission peak at about 391 nm. The PL intensity decreased obviously with the introduction of ZnIn 2 S 4 , indicating the effective separation of photoexcited e − and h + . To reveal the generation and separation of photogenerated charges in the samples, the photoelectrochemical properties of the samples were investigated. As shown in Figure 9b, the fast photocurrent response of the sample after visible light irradiation was observed. Moreover, the photocurrent of 0.5 wt % ZIS/BOC heterostructure is higher compared with BiOCl. Figure 9c showed the impedance spectra of BiOCl and ZIS/BOC heterostructure, with an equivalent circuit model in the inset. The ohmic resistance (R 1 ), corresponding to the intercept with the X-axis in high frequency, includes the intrinsic resistance of the photocatalyst and the electrolyte, as well as the contact resistance at the interface between the photocatalyst and the FTO glass. The semicircle in the middle frequency range corresponds to the charge transfer resistance (R 2 ). The W and CPE represent the Warburg impedance and capacitance for the double layer between photocatalyst and electrolyte, respectively [64]. Comparing the Nyquist plots of BiOCl and ZIS/BOC (Figure 9c), it is found the 0.5 wt % ZIS/BOC electrode exhibits similar ohmic resistance (R 1 ) due to the low content of ZIS in 0.5 wt % ZIS/BOC heterostructure, while 0.5 wt % ZIS/BOC heterostructure exhibits a much lower charge transfer resistance (R 2 ) value (ca. 9116 Ω) than that of BiOCl (22337 Ω), implying the more efficient carriers transfer at the photocatalyst/solution interface, which is beneficial for the photocatalysis reaction [54]. Figure 10 is a schematic diagram of the effect of free radical scavenger on the photocatalytic activity of 0.5 wt % ZIS/BOC heterostructure. The three capture agents are benzoquinone (BQ, O 2 − ), ethylenediaminetetraacetic acid (EDTA, h + ) and isopropanol (IPA,·OH), respectively. It can be clearly seen from Figure 10 that the addition of the three capture agents had a certain effect on the degradation rate of phenol compared to the absence of the capture agent. Among them, the addition of BQ minimized the degradation of phenol, which obviously inhibited the photocatalytic degradation rate of phenol. It is concluded that O 2 − was the main active species for phenol degradation. For the addition of EDTA and IPA, the activity was also inhibited, confirming that h + and OH were also involved in the photocatalytic reaction.

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The ESR capture experiment further confirmed the formation of active species. As shown in

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The bandgap of a semiconductor can be calculated by the following formula: (αhv) 1/n = A(hν-Eg),

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where α, h, ν, a, and Eg respectively represent absorption coefficient, Planck constant, photon 257 frequency, constant, and band-gap energy. Since BiOCl is an indirect transition semiconductor, it is BiOCl and ZnIn2S4 are 3.20 and 2.61 eV, respectively (Figure 12a,b). Meanwhile, BiOCl and ZnIn2S4 260 were determined to be 1.88 and 1.25 eV, respectively, according to XPS value results (Figure 12c,d).

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The calculated band position of the photocatalysts were shown in Table 2.    The bandgap of a semiconductor can be calculated by the following formula: (αhv) 1/n = A(hν-E g ), where α, h, ν, a, and E g respectively represent absorption coefficient, Planck constant, photon frequency, constant, and band-gap energy. Since BiOCl is an indirect transition semiconductor, it is calculated by substituting n = 2. Conversely, n = 0.5 for direct transition of ZnIn 2 S 4 . The band gap of BiOCl and ZnIn 2 S 4 are 3.20 and 2.61 eV, respectively (Figure 12a,b). Meanwhile, BiOCl and ZnIn 2 S 4 were determined to be 1.88 and 1.25 eV, respectively, according to XPS value results (Figure 12c,d).
The calculated band position of the photocatalysts were shown in Table 2.

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The calculated band position of the photocatalysts were shown in Table 2.
As for the photocatalytic N 2 fixation, the conduction band position of the ZnIn 2 S 4 (−1.36 eV) is more negative than E 0 (N 2 /NH 3 = −0.28 eV vs. NHE), so the photogenerated e − can further reduce the nitrogen that adsorbed on the surface of 0.5 wt % ZIS/BOC heterostructures to NH 4 + . In detail, the chemisorbed N 2 molecule is activated by photogenerated e − at the photocatalyst/solution interface [55], which is conducive to dissociating N≡N bond and generating N 2 H* intermediates with coupled protons (Equation (6)), and NH 3 * species are eventually generated (Equation (7)), which then exists in water. Finally, it was combined with H 2 O molecules to form NH 4 + in succession for cycles (Equation O2 + e − →O2 - O2 − + e − + 2H + →H2O2 H2O2 + e − →OH + OH − As for the photocatalytic N2 fixation, the conduction band position of the ZnIn2S4 (−1.36 eV) is 280 more negative than E0 (N2/NH3 = −0.28 eV vs. NHE), so the photogenerated ecan further reduce the 281 nitrogen that adsorbed on the surface of 0.5 wt% ZIS/BOC heterostructures to NH4 + . In detail, the 282 chemisorbed N2 molecule is activated by photogenerated eat the photocatalyst/solution interface 283 [55], which is conducive to dissociating N≡N bond and generating N2H* intermediates with coupled 284 protons (Equation (6)), and NH3* species are eventually generated (Equation (7)), which then exists 285 in water. Finally, it was combined with H2O molecules to form NH4 + in succession for cycles (Equation

Chemicals
All the reagents were of analytical grade and were used without any further purification.

Sample Preparation
Preparation of BiOCl nanosheets. BiOCl nanosheets were synthesized by an improved solvothermal method according to the previous report [65]. In a typical experiment, 0.9702 g (2 mmol) of Bi(NO 3 ) 3 ·5H 2 O and 0.1168 g (2 mmol) of NaCl were dissolved in 10 mL of ethylene glycol respectively, and magnetically stirred for 30 min to obtain clear and transparent solutions, which are denoted as A and B respectively. Subsequently, 0.1094 g of mannitol and 0.4 g of polyvinylpyrrolidone (PVP) were dissolved in 55 mL of water to form solution C. Firstly, solution A is added drop by drop into C, and solution B is slowly added to generate white precipitate after stirring for 5 min. The mixture was then transferred to a 100 mL Teflon-lined stainless-steel autoclave for hydrothermal reaction at 160 • C for 8 h. After the reaction was finished, the autoclave was naturally cooled to room temperature, and 15% NaOH aqueous solution was added to adjust pH to 13 after washing with water. The suspension was magnetically stirred for 3 h and washed with water to neutrality. The final samples were dried at 60 • C for 8 h, and then ground to obtain BiOCl powder.
Preparation of ZnIn 2 S 4 /BiOCl (ZIS/BOC) heterostructures. ZIS/BOC heterostructures were synthesized by an improved solvothermal method according to the previous report [66]. Firstly, 0.0036 g (0.0059 mmol) of Zn(NO 3 ) 2 ·6H 2 O, 0.0045 g (0.0118 mmol) of In(NO 3 ) 3 ·4.5H 2 O and 0.0018 g (0.0236 mmol) of Thioacetamide (TAA) were dissolved in 30 mL of ethylene glycol solution. After 20 min of magnetic stirring, 1 g of BiOCl was added to it. After 10 min of ultrasound, magnetic stirring was continued for 30 min. Then, the mixture was transferred to a 50 mL high pressure reactor lined with polytetrafluoroethylene for solvothermal reaction at 160 • C for 3 h under programmed temperature control, and the temperature was reduced to room-temperature. The yellow powder obtained after grinding is marked as 0.5 wt % ZnIn 2 S 4 /BiOCl. The amounts of Zn(NO 3 ) 2 ·6H 2 O, In(NO 3 ) 3 ·4.5H 2 O and TAA were changed to obtain 0.3 wt % and 0.8 wt % of composite catalyst ZnIn 2 S 4 /BiOCl respectively. The composite catalysts were labeled as 0.3 wt % ZIS/BOC, 0.5 wt % ZIS/BOC, and 0.8 wt %ZIS/BOC. Pure ZnIn 2 S 4 was prepared by the same method without the addition of BiOCl.

Photocatalytic Activity Measurement
Photocatalytic degradation experiment. In the photocatalytic degradation experiment, phenol was used as a simulated pollutant to evaluate the photocatalytic activity of the samples. A suspension containing 0.2 g of photocatalyst is added to 200 mL of 10 mg·L −1 phenol solution, then placed in a photo reactor, and stirred in the dark until adsorption/desorption equilibrium is reached. A 300 W metal halogen lamp with a 420 nm cut-off filter was chosen as the visible light source. After turning on the light source, the supernatant is taken out according to a certain time interval. Finally, the absorbance of different solution concentrations was measured by using the 4-aminontipyrinolimetric method.
Photocatalytic Nitrogen Fixation. In nitrogen fixation experiment, a 300 W xenon lamp (with cut-off filter λ < 420 nm) was used as the light source, and a 500 mL reactor was equipped with circulating cooling water to ensure constant temperature. In general, 200 mg of photocatalyst is uniformly dispersed in 200 mL of ultrapure water, and high-purity N 2 is pumped into the reactor for 30 min to saturate the suspension and remove the dissolved oxygen under dark conditions. Subsequently, the light source was turned on, 10 mL of supernatant was taken out every 30 min, and then centrifuged at 8500 rpm for 10 min to remove the photocatalyst. The concentration of ammonia was finally measured by Nessler's reagent spectrophotometry method [55].

Conclusions
In conclusion, 2D BiOCl nanosheets were used as a substrate for the in-situ growth of the ZnIn 2 S 4 nanosheets, and the carrier transport of the ZnIn 2 S 4 is promoted based on the 2D/2D feature of the substrate. The photocatalytic phenol degradation and nitrogen fixation efficiency of ZIS/BOC heterostructures is significantly higher than that of BiOCl. It was determined that 0.5% ZIS/BOC heterostructure was the best ratio with excellent photocatalytic performance when phenol degradation was tested. The photocatalytic degradation efficiency of phenol was 77.4% and the ammonia production rate was 14.6 µmol·g cat −1 ·h −1 under visible light irradiation. The improved photocatalytic performance is attributed to the effective transfer and separation of photogenerated carriers at the interface and the enhanced light adsorb ability. The photocatalyst still maintained relatively high performance even after 5 cycles. The result of free radical trapping experiment and ESR analysis showed that O 2 − and·OH are the main active substances in visible light-driven catalytic system. In all, an appropriate mechanism is purposed.