SPR-Enhanced Au@Fe 3 O 4 Nanozyme for the Detection of Hydroquinone

: Artiﬁcial nanozymes that are based on ferric oxides have drawn enormous attention due to their high stability, high efﬁciency, and low cost as compared with natural enzymes. Due to the unique optical plasmonic properties, gold nanoparticles (Au NPs) have been widely utilized in the ﬁelds of colorimetric, Raman, and ﬂuorescence sensing. In this work, a photo-responsive Au@Fe 3 O 4 nanozyme is prepared with outstanding peroxidase-like activity. The hot electrons of Au NPs that are excited by a surface plasmon resonance (SPR) effect of NPs improve the catalytic activity of Au@Fe 3 O 4 in oxidizing 3,3 (cid:48) ,5,5 (cid:48) -tetramethylbenzidine (TMB) and the detection of hydroquinone (HQ). The magnetic separation and reusability of the nanozyme further lower its costs. The detection linear range of the sensor is 0–30 µ M and the lowest detection limit is 0.29 µ M. Especially in the detection of real water samples, a good recovery rate is obtained, which provides promising references for the development of the HQ detection technology in seawater.


Introduction
The survival of living organisms is highly dependent on water resources. However, economic development has led to serious water pollution. Hydroquinone (HQ), as an important chemical raw material, has been widely used in various industrial sectors. According to the regulations of the US Environmental Protection Agency, HQ can cause irreversible damage to the human body even at a trace level of 3.5 mg/L, and it is difficult to degrade in the aquatic ecological environment [1]. Therefore, the accurate detection of HQ in water environments is urgent. At present, a variety of methods for HQ detection have been developed, including the electrochemical method, spectrophotometry, and the fluorescence method, but most of these methods have complicated instruments and operation and take a long time [2]. Therefore, alternative methods that are more intuitive, rapid, and sensitive need to be developed. Colorimetric sensing is a good candidate with the advantages of the visualization of experimental results, simple operation, and low cost [3]. As colorimetric sensing is a technology based on the measurement of colored compounds under visible light, the development of specific and efficient catalysts for colored substances is a very critical step [4].
Artificial nanozymes based on nanomaterials have been developed to catalyze various chromogenic substrates and construct corresponding colorimetric sensors, which have received great attention due to their high stability, high efficiency, low cost, and easy modification [5]. Researchers have developed a variety of oxidase-like or nanozymes based on noble metal-based nanomaterials, metal oxides, and carbon materials. Although the catalytic efficiency of many nanozymes has exceeded that of native enzymes, there is still a need for new nanozymes with a higher catalytic activity in the trace analytical detection at nM level. When using various nanozymes for sensing analysis, researchers found that the performance of light-responsive nanozymes was generally better than that of light-inert nanozymes, such as carbon nitride, PSMOF and CeO 2 /CoO [6]. However,
The morphology and particle size of the samples were characterized by scanning electron microscopy (SEM, SU8010). The magnetic properties of the samples were determined by electron paramagnetic resonance spectroscopy (EPR, Brooker A300) and vibrating sample magnetometry (VSM, LakeShore7404), and the pH value of the solution was measured by a PH-3D pH meter from China Shanghai Precision Scientific Instrument Co., LTD. The UV-visible absorption spectra were recorded by a UV-visible spectrophotometer (UV-8000).

Preparation of Gold NPs
The classical method to synthesize gold nanomaterials was the seed growth method, whereby spherical 16 nm gold NPs were prepared by a reduction method. Firstly, 0.8 mL 5%wt aqueous solution of HAuCl 4 ·3H 2 O and 400 mL ultra-pure water were mixed in a three-way flask, heated, and stirred to boil under magnetic stirrers, and kept boiling for 30 min. Then, 8 mL 1%wt sodium citrate solution was added and reacted for 30 min to completely reduce it. After cooling for 4-5 h, 16 nm gold NPs can be obtained, and their characteristic absorption peak was about 520 nm. A volume of 30 mL of 16 nm Au NPs was titrated to 300 mL with ultrapure water. NH 2 OH solution was added. After strong stirring for a period of time, 520µL 5%wt aqueous solution of HAuCl 4 ·3H 2 O was added into the mixed solution, and the reaction lasted for 15 min. Finally, gold NPs at 40 nm, with characteristic absorption peaks of around 525 nm, were obtained.

Preparation of Au@Fe 3 O 4 Nanozymes
An amount of 45 mg of Fe 3 O 4 was mixed with 3 mL 3-aminopropyltriethoxysilane reagent (APTES) in 30 mL absolute ethanol. After sonication for 5 min, the cells were subjected to mechanical stirring for 6 h at room temperature. Sialylation modification of Fe 3 O 4 solution was obtained by redispersing the product in 30 mL of water by magnetic separation.
30 mL of aminated Fe 3 O 4 was mixed with 30 mL of prepared Au NPs and mechanically stirred at room temperature for 3 h. The product was re-dispersed in 15 mL of water by magnetic separation to obtain Au@Fe 3 O 4 solution.

Materials Characterization
The samples were characterized by SEM, UV-Vis absorption spectroscopy, X-ray diffractometer, energy dispersive spectrometer (EDS), electron paramagnetic resonance spectroscopy (EPR), hysteresis loop measurement (VSM), and X-ray photoelectron spectroscopy (XPS). SEM was used to characterize the morphology and size of Au@Fe 3 O 4 nanocomposites. The composition of the composite was analyzed using an X-ray diffractometer with analysis conditions set at 2θ = 20-80 • , scanning speed of 10 • /min, and Cu Kα radiation. XPS was used to further characterize the chemical composition of the composite, and a C1s line with a binding energy of 284.8 eV was used for calibration. EDS was used to analyze the elemental information of Au@Fe 3 O 4 nanocomposites. •OH production was verified using EPR. The optical properties of Au@Fe 3 O 4 nanocomposites were tested using VSM. The properties of the materials were tested using UV-Vis absorption spectroscopy.

Material Characterization and Analysis
The Au@Fe 3 O 4 nanocomposite synthesis process is shown in Figure 1. First, APTES was modified on the Fe 3 O 4 surface to make it positively charged, while the -COOH of the citrate on the NPs can be dissociated into -COO − , which renders the NPs negatively charged. Subsequently, the negatively charged Au NPs are assembled in situ on aminofunctionalized Fe 3 O 4 via electrostatic interactions to form Au@Fe 3 O 4 nanozymes. As shown in Figure 2a, the prepared Au NPs have a diameter of about 16 nm, with good homogeneity [15]. Figure 2b shows that Au NPs are uniformly distributed on the Fe 3 O 4 surface. Moreover, no obvious large-scale agglomeration of Au NPs was observed. As shown in Figure 2c-e, the results of EDS elemental mapping analysis showed that Au, Fe, and O elements were uniformly distributed, further proving the successful synthesis of Au@Fe 3 O 4 nanozymes.  XPS was used to characterize the chemical states of Au, Fe, and O in Au@Fe3O4. broad spectrum in Figure S1a shows binding energy peaks for Au4f, C1s, O1s, and F respectively. As shown in Figure S1b, the binding energies corresponding to the cha teristic peaks of Au 4f5/2 and Au 4f7/2 are 86.4 eV and 82.7 eV, respectively, and the app ance of Au 4f indicates that Au is a zero-valent state [16]. As shown in Figure S1c binding energies corresponding to the characteristic peaks of Fe 2p1/2 and Fe 2p3/2 are 7 eV and 709.7 eV, respectively, in line with the standard data of Fe3O4 [17]. As show Figure S1d, the binding energy corresponding to the characteristic peak of O1s is 528. which is a typical metal-oxygen bond [18]. The XRD patterns are shown in Figure S2. The results show that Au@Fe3O4 nanozymes have been successfully prepared.
As shown in Figure S3a, neither Fe3O4 nor Au@Fe3O4 nanocomposites have re nence or coercivity at 300 K, which indicates that both samples are paramagnetic at r temperature. The saturation magnetization of Fe3O4 and Au@Fe3O4 is 81.3 emu/g and emu/g, respectively. Figure S3b demonstrates the enrichment and redispersion proce Au@Fe3O4 nanocomposites. After magnet placement, Au@Fe3O4 nanocomposites w rapidly enriched on the side of the glass bottle within 30 s. After the removal of the m   XPS was used to characterize the chemical states of Au, Fe, and O in Au@Fe3O4. T broad spectrum in Figure S1a shows binding energy peaks for Au4f, C1s, O1s, and Fe 2 respectively. As shown in Figure S1b, the binding energies corresponding to the chara teristic peaks of Au 4f5/2 and Au 4f7/2 are 86.4 eV and 82.7 eV, respectively, and the appea ance of Au 4f indicates that Au is a zero-valent state [16]. As shown in Figure S1c, t binding energies corresponding to the characteristic peaks of Fe 2p1/2 and Fe 2p3/2 are 725 eV and 709.7 eV, respectively, in line with the standard data of Fe3O4 [17]. As shown Figure S1d, the binding energy corresponding to the characteristic peak of O1s is 528.9 e which is a typical metal-oxygen bond [18]. The XRD patterns are shown in Figure S2 As shown in Figure S3a, neither Fe3O4 nor Au@Fe3O4 nanocomposites have rem nence or coercivity at 300 K, which indicates that both samples are paramagnetic at roo temperature. The saturation magnetization of Fe3O4 and Au@Fe3O4 is 81.3 emu/g and 78 emu/g, respectively. Figure S3b demonstrates the enrichment and redispersion process Au@Fe3O4 nanocomposites. After magnet placement, Au@Fe3O4 nanocomposites we rapidly enriched on the side of the glass bottle within 30 s. After the removal of the ma net, the Au@Fe3O4 nanocomposite can be redispersed by shaking or ultrasonic vibratio XPS was used to characterize the chemical states of Au, Fe, and O in Au@Fe 3 O 4 . The broad spectrum in Figure S1a shows binding energy peaks for Au4f, C1s, O1s, and Fe 2p, respectively. As shown in Figure S1b, the binding energies corresponding to the characteristic peaks of Au 4f 5/2 and Au 4f 7/2 are 86.4 eV and 82.7 eV, respectively, and the appearance of Au 4f indicates that Au is a zero-valent state [16]. As shown in Figure S1c, the binding energies corresponding to the characteristic peaks of Fe 2p 1/2 and Fe 2p 3/2 are 725.3 eV and 709.7 eV, respectively, in line with the standard data of Fe 3 O 4 [17]. As shown in Figure S1d, the binding energy corresponding to the characteristic peak of O1s is 528.9 eV, which is a typical metal-oxygen bond [18]. The XRD patterns are shown in Figure S2 [22]. In colorimetric detection, •OH can catalyze the conversion of the oxidase substrate TMB to the blue charge-transfer complex oxTMB. Importantly, the transfer of electrons from the nanozyme to the reaction medium is able to promote the generation of •OH [23,24]. For example, Abir Swaidan et al. [25]. found that a large amount of electron transfer between Cr 3+ and Cr 6+ could accelerate the decomposition of H 2 O 2 to •OH, thereby enhancing the ability to oxidize TMB. Therefore, we use the SPR effect of Au NPs to stimulate a large number of high-energy electrons. At the same time, Au NPs can also act as a fast electron transfer channel [8], Fe 2+ /Fe 3+ active ion pairs participate in REDOX reactions, and multi-factor cooperation promotes the decomposition of H 2 O 2 to •OH. After that, TMB was catalyzed to oxTMB by one-electron transfer, and the color of the solution changed from colorless to blue. The catalytic reaction process is shown in Equations (1)-(3) [1,14,26] and Figure 3. HQ is strongly reducing, which can reduce blue oxTMB to colorless TMB, so as to construct a colorimetric sensing platform for detecting HQ. The whole catalytic process is an electron transfer process from MB to H 2 O 2 with the assistance of Au and Fe 2+ /Fe 3+ as a medium.

Au@Fe3O4 Enzyme Mimetic Activity of Nanozymes
Researchers have found that Au nanozymes and Fe3O4 nanozymes can cata decomposition of H2O2 to produce •OH under acidic conditions, showing peroxid activity [7]. Au NPs can catalyze the O-O bond cleavage of H2O2 to form two •O Fe3O4 nanozymes contain Fe 2+ /Fe 3+ active ion pairs that decompose H2O2 into •OH ton mechanism [22]. In colorimetric detection, •OH can catalyze the conversio oxidase substrate TMB to the blue charge-transfer complex oxTMB. Importa transfer of electrons from the nanozyme to the reaction medium is able to prom generation of •OH [23,24]. For example, Abir Swaidan et al. [25]. found that amount of electron transfer between Cr 3+ and Cr 6+ could accelerate the decompo H2O2 to •OH, thereby enhancing the ability to oxidize TMB. Therefore, we use effect of Au NPs to stimulate a large number of high-energy electrons. At the sam Au NPs can also act as a fast electron transfer channel [8], Fe 2+ /Fe 3+ active ion pair ipate in REDOX reactions, and multi-factor cooperation promotes the decompo H2O2 to •OH. After that, TMB was catalyzed to oxTMB by one-electron transfer, color of the solution changed from colorless to blue. The catalytic reaction pr shown in Equations (1)-(3) [1,14,26] and Figure 3. HQ is strongly reducing, w reduce blue oxTMB to colorless TMB, so as to construct a colorimetric sensing p for detecting HQ. The whole catalytic process is an electron transfer process from H2O2 with the assistance of Au and Fe 2+ /Fe 3+ as a medium.  The Au@Fe3O4 peroxidase-like enzyme mimetic activity was assessed by ca the oxidation of TMB, which has a characteristic absorption peak at 652 nm. The p samples were subjected to the catalytic oxidation of TMB in 0.2 M Na2HPO4-CA pH = 4.0. To demonstrate the peroxidase-like activity of Au@Fe3O4 nanozymes, w the oxidation of TMB in the presence and absence of H2O2. As shown in Figur absorbance is almost a horizontal line in the absence of H2O2, indicating that A nanozymes, Au NPs, and Fe3O4 NPs cannot directly oxidize TMB. However, in t  Figure 4a, O 4 NPs only. This is because the Au@Fe 3 O 4 peroxidase-like enzyme couples the catalytic ability of both Au and Fe 2+ /Fe 3+ ion pairs, thus achieving high catalytic efficiency for TMB. More importantly, the catalytic performance of Au@Fe 3 O 4 nanozymes will be further improved under the simulated illumination condition of a xenon lamp, which is closely related to the SPR effect of Au NPs. The internal electrons of Au NPs escape from the surface with photon energy, which is manifested as the excited hot electrons residing on the surface of the NPs, and can provide a large number of electrons in the catalytic reaction. At the same time, Au NP can provide a fast electron transfer channel for the catalytic reaction [8], and both can cooperate to improve the catalytic performance of nanozymes. It is now generally accepted that peroxidase mimics can catalyze the decomposition of H 2 O 2 to produce •OH. To further investigate the mechanism of action of the photo-enhanced peroxidase, •OH was characterized by electron paramagnetic resonance. As shown in Chemosensors 2023, 11, x FOR PEER REVIEW 6 which is closely related to the SPR effect of Au NPs. The internal electrons of Au NP cape from the surface with photon energy, which is manifested as the excited hot elect residing on the surface of the NPs, and can provide a large number of electrons in catalytic reaction. At the same time, Au NP can provide a fast electron transfer channe the catalytic reaction [8], and both can cooperate to improve the catalytic performanc nanozymes. It is now generally accepted that peroxidase mimics can catalyze the dec position of H2O2 to produce •OH. To further investigate the mechanism of action of photo-enhanced peroxidase, •OH was characterized by electron paramagnetic resona As shown in Figure   The experimental conditions for the catalytic oxidation of TMB by Au@F nanozymes were next optimized. First, the effect of buffer solution pH on the cata activity of Au@Fe3O4 nanozymes was investigated. Figure 5a shows that Au@Fe3O4 ex its the best relative catalytic activity at pH = 4.0. Therefore, the effect of temperatur Au@Fe3O4 catalytic activity was further tested at pH = 4.0 maintenance. As shown in ure 5b, the material exhibited the best relative activity when the temperature was aro 25 °C. Then, the effect of Au@Fe3O4 concentration on the catalytic performance was te at pH 4.0 and a temperature of 25 °C. As shown in Figure 5c, the relative activit Au@Fe3O4 increased steadily from 0 µg/mL to 100 µg/mL. In the range of 100 µg/m 140 µg/mL, Au@Fe3O4 showed the best relative activity. As shown in Figure 5d, the rela The experimental conditions for the catalytic oxidation of TMB by Au@Fe 3 O 4 nanozymes were next optimized. First, the effect of buffer solution pH on the catalytic activity of Au@Fe 3 O 4 nanozymes was investigated. Figure 5a shows that Au@Fe 3 O 4 exhibits the best relative catalytic activity at pH = 4.0. Therefore, the effect of temperature on Au@Fe 3 O 4 catalytic activity was further tested at pH = 4.0 maintenance. As shown in Figure 5b, the material exhibited the best relative activity when the temperature was around 25 • C. Then, the effect of Au@Fe 3 O 4 concentration on the catalytic performance was tested at pH 4.0 and a temperature of 25 • C. As shown in Figure 5c, the relative activity of Au@Fe 3 O 4 increased steadily from 0 µg/mL to 100 µg/mL. In the range of 100 µg/mL to 140 µg/mL, Au@Fe 3 O 4 showed the best relative activity. As shown in Figure 5d, the relative activity gradually increased with the extension of reaction time from 1 to 12 min, and essentially remained stable after 12 min. Based on the above discussion, the optimal reaction pH of Au@Fe 3 O 4 peroxidases was determined to be 4.0, the optimal experimental temperature was 25 • C, the optimal addition concentration was 100 µg/mL, and the optimal reaction time was 12 min.

Colorimetric Detection
First, we detected HQ under dark conditions using the Au@Fe3O4 zyme. HQ, which is strongly reducing, can reduce the blue oxTMB so TMB solution. This macroscopic blue bleaching reaction is due to the tion in oxTMB by •OH induced by hydroquinone. The physical diag process and the reaction formula are shown in Figure S4. As shown in concluded that the peak absorbance at 652 nm decreased with increa tion. Figure 6b shows that there is a linear relationship between the p HQ concentration, and the corresponding linear fitting equation is y (R 2 = 0.991), and the lowest detection line is 1.24 µM. The above exper cate that the Au@Fe3O4 peroxidase-like enzyme can also be applied t metric detection of HQ under dark conditions.

Colorimetric Detection
First, we detected HQ under dark conditions using the Au@Fe 3 O 4 peroxidase-like enzyme. HQ, which is strongly reducing, can reduce the blue oxTMB solution to a colorless TMB solution. This macroscopic blue bleaching reaction is due to the two-electron reduction in oxTMB by •OH induced by hydroquinone. The physical diagram of the catalytic process and the reaction formula are shown in Figure S4. As shown in Figure 6a, it can be concluded that the peak absorbance at 652 nm decreased with increasing HQ concentration. Figure 6b shows that there is a linear relationship between the peak absorbance and HQ concentration, and the corresponding linear fitting equation is y = −0.0204x + 1.6918 (R 2 = 0.991), and the lowest detection line is 1.24 µM. The above experimental results indicate that the Au@Fe 3 O 4 peroxidase-like enzyme can also be applied to the fading colorimetric detection of HQ under dark conditions. tion. Figure 6b shows that there is a linear relationship between the peak absorba HQ concentration, and the corresponding linear fitting equation is y = −0.0204x + (R 2 = 0.991), and the lowest detection line is 1.24 µM. The above experimental resu cate that the Au@Fe3O4 peroxidase-like enzyme can also be applied to the fading metric detection of HQ under dark conditions.  Next, HQ was again detected using the Au@Fe 3 O 4 peroxidase under simulated illumination with a 300 W xenon lamp. As shown in Figure 7a, the peak absorbance at 652 nm decreased with increasing HQ concentration, and the initial absorbance and the amount of absorbance change were significantly larger than those under dark conditions. This is because under the light conditions, the photoexcitation SPR effect produces a large number of hot electrons, which makes the content of •OH in the solution higher, and the ability to oxidize TMB is subsequently strengthened, leading to a deeper initial color, that is, a higher absorbance. This was also confirmed by UV-Vis and EPR experiments that simulated the active part of the enzyme. When HQ is added to react with oxTMB, the fading change will be more obvious, that is, it will show a larger amount of absorbance change on the spectrum. Figure 7b shows that there is a linear relationship between the peak absorbance and HQ concentration, and the corresponding linear fitting equation is y = −0.0588x + 2.0249 (R 2 = 0.999), and the lowest detection line is 0.29 µM. Compared with dark detection, the Au@Fe 3 O 4 peroxidase-TMB colorimetric detection platform under light has a higher sensitivity. The above experimental results show that the photoexcitation SPR effect can effectively enhance the colorimetric detection performance of Au@Fe 3 O 4 peroxidases for HQ. The detection range of this experiment is 0-30 µM, and the lowest detection limit is 0.29 µM, which has certain advantages compared with other methods reported in the literature, as shown in Table 1.
The selectivity, repeatability, and stability of the sensor are crucial for practical applications. The selectivity of HQ was determined by the addition of possible interfering substances. As shown in Figure 8a, equal concentrations of phenol, resorcinol (RC), o-nitro resorcinol (ONP), Cl − , NO 3− , SO 4 2− , Cd 2+ , Ca 2+ , Cu 2+ , Fe 3+ , Hg 2+ , K + , Na + , Ni 2+ , and Pb 2+ were added. It does not substantially interfere with HQ detection, indicating that the Au@Fe 3 O 4 peroxidase-like enzyme has good selectivity. After that, the Au@Fe 3 O 4 peroxidase-like enzyme was added to the TMB solution and its stability was verified using UV-Vis absorption spectroscopy. As shown in Figure S5, its relative activity remained largely unchanged after 12 cycles, indicating a good short-term stability. Similarly, the relative activity of the samples was also largely unchanged over 15 days, indicating a good long-term stability of the material, as shown in Figure 8b. Five batches of Au@Fe 3 O 4 peroxidases were prepared under the same experimental conditions to test their absorbance after catalytic oxidation of TMB. As shown in Figure 8c, the relative activity of the five batches of samples remained essentially unchanged. After that, the reproducibility of the same Au@Fe 3 O 4 class of peroxidase samples was tested. As shown in Figure 8d, the same Au@Fe 3 O 4 class of peroxidases still maintained a high relative activity after four magnetic separation recoveries, indicating good reproducibility.
peak absorbance and HQ concentration, and the corresponding linear fitting equ y = −0.0588x + 2.0249 (R 2 = 0.999), and the lowest detection line is 0.29 µM. Compa dark detection, the Au@Fe3O4 peroxidase-TMB colorimetric detection platform un has a higher sensitivity. The above experimental results show that the photoexcita effect can effectively enhance the colorimetric detection performance of Au@Fe3O idases for HQ. The detection range of this experiment is 0-30 µM, and the lowest d limit is 0.29 µM, which has certain advantages compared with other methods rep the literature, as shown in Table 1.    To verify the utility of the Au@Fe 3 O 4 peroxidase, HQ was measured in tap water and seawater, and the recovery was calculated in real water samples. All samples were collected from Qingdao, China. Tap water and seawater samples were filtered using a nylon filter membrane with a pore size of 0.22 µM to remove solid impurities. Amounts of 8 µM, 18 µM, and 29 µM HQ were added to tap water and seawater samples, respectively, and their absorbance was tested using a UV-Vis spectrophotometer, and the measured values were calculated by linear fitting equations. As shown in Table 2, better recoveries were obtained in both tap water and seawater. These results indicate that the Au@Fe 3 O 4 peroxidase-like enzyme has a potential application in the detection of HQ for seawater anti-interference. pared under the same experimental conditions to test their absorbance after catalytic oxidation of TMB. As shown in Figure 8c, the relative activity of the five batches of samples remained essentially unchanged. After that, the reproducibility of the same Au@Fe3O4 class of peroxidase samples was tested. As shown in Figure 8d, the same Au@Fe3O4 class of peroxidases still maintained a high relative activity after four magnetic separation recoveries, indicating good reproducibility. To verify the utility of the Au@Fe3O4 peroxidase, HQ was measured in tap water and seawater, and the recovery was calculated in real water samples. All samples were collected from Qingdao, China. Tap water and seawater samples were filtered using a nylon filter membrane with a pore size of 0.22 µM to remove solid impurities. Amounts of 8 µM, 18 µM, and 29 µM HQ were added to tap water and seawater samples, respectively, and their absorbance was tested using a UV-Vis spectrophotometer, and the measured values were calculated by linear fitting equations. As shown in Table 2, better recoveries were

Conclusions
In this study, the enhancement of Au@Fe 3 O 4 peroxidase-like activity by SPR effect was successfully applied to the colorimetric detection of HQ in seawater. The results show that Au NPs excite hot electrons under light irradiation and provide a large number of electrons for the catalytic reaction. At the same time, Au NPs can be used as fast charge transfer channels, while theAu@Fe 3 O 4 ) with a large specific surface area can provide more active sites. Under the synergistic effect of multiple factors, the ability of Au@Fe 3 O 4 peroxidase to catalyze the oxidation of TMB was significantly enhanced, and the sensitivity of colorimetric detection was improved. Moreover, the Au@Fe 3 O 4 peroxidase-like nanozyme still has a certain colorimetric detection ability under dark conditions. Au@Fe 3 O 4 peroxidases can also be recovered by magnetic separation, and the economic cost of practical applications can be further reduced. The experimental results show that the minimum detection limit of HQ detection by this method can reach 0.29 µM, which has advantages compared with other methods reported in the literature. In addition, a good recovery rate was obtained in the detection of real water samples, which can provide some reference for the development of HQ detection technology in seawater. In future research, Au NPs can be coupled with other nanomaterials to construct heterostructures or metal organic frameworks (MOFs), which can further improve the performance of plasmonic or SERS-based sensors [37,38].

Institutional Review Board Statement: Not applicable.
Informed Consent Statement: Not applicable.

Data Availability Statement:
The data presented in this study are available on request from the corresponding author.