Abstract
Phenolic compounds are expected to be successfully removed from wastewater as pervasive environmental contaminants. For the removal of phenolic chemicals, enzymes such as horseradish peroxidase have shown to have a lot of promise. Horseradish peroxidase (HRP) was immobilized on amino functionalized metal organic frameworks (NH2-MOF-Zr) utilizing covalent bonds. The microstructural and physicochemical properties were investigated using Fourier transform infrared (FT-IR), X-Ray diffraction (XRD) analysis, and scanning electron microscopy (SEM). The free HRP and NH2-MOF-Zr@HRP were characterized by determining the activity profile as a function of kinetic behavior, pH, storage stability, effect of organic solvent, and temperature. The Km and Vmax for NH2-MOF-Zr@HRP were estimated to be 34.7 mM, 0.811 U/mL for guaiacol and 12.58 mM, 0.930 U/mL for H2O2, respectively. The optimum pH values of the enzyme activity were found as 7 and 7–7.5 for the free HRP and NH2-MOF-Zr@HRP, respectively. The optimum temperature profile of the free HRP and NH2-MOF-Zr@HRP revealed as 40 °C and 50 °C, respectively. NH2-MOF-Zr@HRP maintained 74% of its initial activity after 6 weeks of storage and 59% of its initial activity after ten consecutive cycles of the guaiacol oxidation. A substantial degree of the phenolic compounds was removed by HRP immobilized on the NH2-MOF-Zr. About 87%, 53%, and 49% of 4-methoxyphenol (4-MEP), bisphenol A (BPA), and phenol were removed by NH2-MOF-Zr@HRP during a 6-h reaction. The removal efficiency of phenol, BPA, and 4-MEP after five reuse cycles was 48%, 51%, and 62%, respectively.
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1 Introduction
Anthropogenic impacts on the biosphere have unavoidably increased due to a growing number of contaminants, such as various organic pollutants, synthetic dyes, and polycyclic aromatic hydrocarbons, making it challenging for humans to eliminate hazardous pollutants from many industries [1]. Phenolic compounds are essential components in the chemical industry. They are also regarded as pervasive environmental pollutants, though, as the wastewater that is discharged has only received partial treatment. One source of phenolic pollution is the widespread use of everyday items such phenoxy herbicides, petrochemicals, and wood preservatives [2]. For instance, bisphenol A (BPA), a substance found in many food and beverage packaging materials, is readily disposed of in home sewage when washed and sterilized repeatedly [3]. Furthermore, during long-term storage, BPA may diffuse into foods and beverages, which may cause estrogenic activity in humans [4]. In actuality, numerous phenolic substances are known to alter hormones. They have a high level of toxicity for humans and can accumulate in the body, even at low amounts. Due to their high substrate specificity, high activity under milder conditions, and biodegradable nature, various plant, and microbial oxidoreductases (Horseradish peroxidase) have recently attracted more attention for detoxifying and degrading a wide range of dyes either by precipitation or by opening the aromatic ring structure [5]. In addition to being used to identify hydrogen peroxide in industrial and biological testing, peroxidase enzymes are essential in a variety of industrial processes in the agricultural, analytical, environmental, and medicinal areas [6, 7]. However, the production cost is considerable due to its non-recyclability and instability, restricting its applicability. As a result, enhancing the stability of enzymes is a pressing issue that must be addressed. Enzyme immobilization is a type of enzyme engineering approach that can increase enzyme stability and has a wide range of applications [8]. Solid materials consistently immobilize enzymes for application in various production processes. Because enzymes are recyclable after immobilization, they are appropriate for use in some industrial domains in place of chemicals [9]. Owing to their remarkable biocompatibility, customizable porous topology, and high specific surface area, inorganic metal ions/clusters and coordinating organic linkers make up the new class of organic–inorganic hybrid porous materials known as metal–organic frameworks (MOFs), which have undergone significant development [10,11,12,13]. Additionally, because of the plentiful organic linkers, MOF has been widely employed to immobilize enzymes by porosity entrapment, covalent bonding precipitation, and absorption, which may preserve accessibility, activity, and the physical confinements of enzymes [14]. Enzyme immobilization by MOFs can also improve the enzyme’s endurance to temperature and pH changes, resulting in a more effective water treatment strategy [15]. MOFs are attracting interest in the swiftly expanding fields of retrieval, segregation, catalysis, biomedical applications, and sensing materials because of their outstanding capabilities and the extraordinary degree of variety for both the organic and inorganic components of their structures [16]. In this project, post-synthetic method was utilized to fabricate MOF materials and then immobilized enzyme. The post-synthetic method involves modifying a MOF material with functional groups that can bind to enzymes and immobilize them within the MOF structure. In this method, the MOF material is synthesized first and then functionalized with linker molecules that have affinity for the enzyme of interest. The enzyme is then added to the functionalized MOF, where it is immobilized through binding to the linker molecules [17]. Cavka et al. [18] were the first to report a zirconium(IV)-based MOF as UiO-66. UIO-66 structure is a highly porous and stable material made up of a Zr6O4 (OH)4 octahedron cluster and 12-fold linked clusters joined by a 1,4-benzenedicarboxylate ligand. Herein, amino functionalized metal organic frameworks (NH2-MOF-Zr) was chosen as a carrier for the immobilization of horseradish peroxidase to create an integrated enzyme system by covalent binding because of its extremely high stability and high biocompatibility. The carrier’s chemical structure and morphological changes before and after enzyme immobilization were studied by different techniques. Storage stability, reusability, temperature, pH, and kinetic characteristics of immobilized enzymes were compared to soluble peroxidase.
2 Materials and methods
2-Aminoterephthalic acid (ATPA) (99%), zirconium (IV) oxychloride octahydrate (ZrOCl2 · 8H2O) (99.5%), N,N-dimethylformamide (DMF) (99.8%), N-Hydroxysuccinimide (NHS) (95%), 1-Ethyl-3-(3-dimethylaminopropyl) carbodiimide (EDC) (98%), guaiacol (98%), hydrogen peroxide (H2O2) (35%), horseradish peroxidase (HRP) (lyophilized powder, ≥ 250 units/mg solid), phenol (97%), bisphenol A (BPA) (97%), and 4-methoxyphenol (4-MEP) (97%) were acquired from Merck (Darmstadt, Germany). All commercial chemicals were of analytical grade and utilized without any additional purification.
2.1 Fabrication of amino functionalized metal organic frameworks (NH2-MOF-Zr)
The NH2-MOF-Zr was fabricated according to solvothermal approach reported by Yuan et al. [19]. Generally, ZrOCl2 (15 mmol) and ATPA (15 mmol) were dissolved in 80 ml DMF. Then, the reaction mixture was moved to a 100 ml Teflon liner autoclave contained 1.5 ml of concentrated hydrochloric acid. The autoclave was capped and placed in oven for 21 h at 120 °C. The obtained material (NH2-MOF-Zr) was cooled to room temperature, then filtered, washed three times with DMF and distilled water to remove the unreacted compounds, and dried at 60 °C in drying oven.
2.2 Immobilization of HRP on NH2-MOF-Zr
The immobilization process of HRP on NH2-MOF-Zr was carried out as follows. Thirty milligrams of EDC was introduced to 10 ml of phosphate-buffered saline (50 mM PBS, pH 7.4) containing 300 mg NH2-MOF-Zr and incubated for 1 h at room temperature with constant stirring. Following that, 30 mg of NHS was added to the mixture with constant stirring for 1.5 h at room temperature. The solution was then moved to a falcon tube containing 50 units of HRP in 10 ml of PBS, and immobilization was performed end-over-end for 12 h at room temperature. The product was separated through centrifugation and underwent two phosphate-buffered saline washes. The protein content was determined using the Bradford method with bovine serum albumin as the standard [20]. The immobilization yield and recovered activity were determined using the following equations:
Immobilization Yield (IY%) = \(\frac{\mathrm A\mathrm m\mathrm o\mathrm u\mathrm n\mathrm t\;\mathrm o\mathrm f\;\mathrm p\mathrm r\mathrm o\mathrm t\mathrm e\mathrm i\mathrm n\;\mathrm i\mathrm n\mathrm t\mathrm r\mathrm o\mathrm d\mathrm u\mathrm c\mathrm e\mathrm d-\mathrm P\mathrm r\mathrm o\mathrm t\mathrm e\mathrm i\mathrm n\;\mathrm i\mathrm n\;\mathrm t\mathrm h\mathrm e\;\mathrm s\mathrm u\mathrm p\mathrm e\mathrm r\mathrm n\mathrm a\mathrm t\mathrm a\mathrm n\mathrm t}{\mathrm A\mathrm m\mathrm o\mathrm u\mathrm n\mathrm t\;\mathrm o\mathrm f\;\mathrm p\mathrm r\mathrm o\mathrm t\mathrm e\mathrm i\mathrm n\;\mathrm i\mathrm n\mathrm t\mathrm r\mathrm o\mathrm d\mathrm u\mathrm c\mathrm e\mathrm d}\times100\)
2.3 HRP activity assay
The horseradish peroxidase was evaluated according to Yuan and Jiang method [21] a 40 mM guaiacol, 50 mM Tris–HCl buffer pH 7.0, 8 mM H2O2, and the least possible amount of free enzyme or a defined weight of immobilized enzyme were supplied in a 1 ml aliquot of the reaction mixture. Once per minute, the variation in absorbance caused by guaiacol oxidation was measured. The amount of enzyme required to raise the OD to 1.0 per minute was used to define the substance’s activity per unit. This experiment was performed under standard assay parameters.
2.4 Material characterization
Using an energy dispersive X-ray spectroscopy coupled scanning electron microscope (SEM, Quanta FEG 250, FEI Co., Hillsboro, USA), the morphology of the fabricated NH2-MOF-Zr and NH2-MOF-Zr@HRP was studied. The functional groups of NH2-MOF-Zr and NH2-MOF-Zr@HRP were characterized using Fourier transform infrared spectroscopy (FTIR, PerkinElmer Spectrum 100). The X-ray diffraction patterns for all samples were recorded using the XRD system (XMD-300, Unisantis, Germany), operating at a current and voltage of 30 mA and 40 kV, respectively, and over a range of 2θ = 10–70° at a scan rate of 0.1°/step.
2.5 Operational stability and reusability of biocatalyst
The immobilized enzyme’s operational stability is an essential parameter to consider when investigating immobilization efficiency [22]. In Tris–HCl buffer (50 mM, pH 7.0) over the course of 6 weeks at 4 °C, the operational stability of immobilized and free HRP was evaluated. The amount of enzyme leached in supernatant was evaluated via determined the enzyme activity over 6 weeks. In particular, the capability to reuse expensive enzymes and the reusability property in immobilized enzymes can be viewed as an important factor of practical applications. Reusability studies were performed on the immobilized peroxidase under the previously mentioned standard conditions. It was withdrawn out of the reaction media and then washed with 50 mM Tris-HCI buffer pH 7.2. The recovered immobilized peroxidase was then reapplied for 10 cycles. As the 100% activity control, the activity observed in the initial test was utilized to determine the proportion of activity remaining after each subsequent reuse.
2.6 Effect of PH and temperature
The pH should be taken into consideration as a significant parameter in the enzymatic reactions since the activity of enzymes is significantly impacted by environmental conditions. Using 50 mM of various pH solutions (acetate buffer pH 4–6, Tris–HCl buffer pH 6.5–9), the effect of pH on the activity of immobilized and free enzymes was assessed. To determine the impact of temperature on free HRP and NH2-MOF-Zr@HRP, free HRP and NH2-MOF-Zr@HRP were incubated for 15 min at various temperatures (30–80 °C) before adding substrate. The steps for determining enzyme activity were the same as in mentioned above.
2.7 Kinetic parameters
To calculate the maximum velocity (Vmax) and Michaelis–Menten constant (Km), the free HRP and NH2-MOF-Zr@HRP activity was assessed using guaiacol and H2O2 as substrates at concentrations of 20–60 mM and 4–12 mM, respectively, under optimal temperatures and pH for each substrate. Using Origin/OriginPro 2018 software, the mathematical model Michaelis–Menten determined the enzyme’s Km and Vmax values.
2.8 Effect of organic solvent
The effect of organic solvents on the HRP biocatalyst immobilized activity was studied in the presence of 20% (v/v) ethanol, methanol, dimethyl sulfoxide (DMSO), toluene, methanol, n-hexane, isopropanol, and butan-1-ol. The immobilized HRP was incubated in the organic solvent for 30 min before the enzyme activity determination.
2.9 Biological removal of phenols
A glass reactor soaked in a water bath at 30 °C with stirring at 100 rpm served as the reaction chamber for the enzyme-mediated operations. In the current investigation, three typical phenolic compounds—phenol, bisphenol A (BPA), and 4-methoxyphenol (4-MEP) were selected. According to Cheng et al. method [23], the initial concentrations of H2O2 and phenolic compounds were established at 1 mM (standard curves are shown in supplementary file; Figs. 1-3S). In the glass reactor, phenolic compounds were dissolved in 0.1 M phosphate buffer at pH 7.0, following that, H2O2 and enzyme were added. At regular intervals (2, 4, 6, 8 h), 1 mL of the reaction mixture was withdrawn and promptly quenched with 1 mL of methanol. By using a colorimetric approach to measure the remaining phenolic compounds, the elimination efficiency was calculated [24]. The specimen containing 200 μL of peroxidase-treated phenol was mixed with potassium ferricyanide (83.4 mM, 25 μL) and 4-aminoantipyrine (21 mM, 25 μL). After 10 min, the absorbance at 505 nm was measured.
3 Results and discussion
Recently, metal organic frameworks (MOFs) have received a great deal of admiration. Due to its unique characteristics, which include a strong connection between the MOF and enzyme, tunable porosity, thermal/chemical stability, and a high surface area for optimal enzyme loading, it has the potential to immobilize enzymes [25]. Different investigations have immobilized several enzymes onto MOFs while taking into account the aforementioned characteristics of MOF, including peroxidase [26], α-amylase [27], and lipase [28]. In this work, HRP was adopted as the model enzyme for immobilization onto amino functionalized metal organic frameworks (NH2-MOF-Zr), then the parameters of immobilized enzyme were evaluated to assess the stability, catalytic activity, and reusability. Garcia et al. [29] developed UiO-66-NH2 through using 2-amino-1,4-benzenedicarboxylic acid as a ligand in UiO-66. Because of its high thermal stability, large surface area, and excellent absorption capacity, UiO-66-NH2 has received a lot of attention [30, 31]. The carrier support (NH2-MOF-Zr) was successfully prepared by solvothermal approach as illustrated in Fig. 1. HRP immobilized by covalent binding on NH2-MOF-Zr with immobilization yield (IY%) of 76.7% and activity yield (AY%) of 82%. In comparing these results with other results in the literature, laccase enzyme was immobilized on Fe3O4-NH2@MIL-100 with the recovery activity of 70% and the immobilized yield of 61.63% [32]. HRP immobilized on CuONS–PMMA with immobilization yield of 72.8% [33]. Soybean epoxide hydrolase was successfully immobilized by Cao et al. [34] on UIO-66-NH2, with an enzyme activity recovery of 88.0%. Table 1 shows a comparative result with other reported data. The good loading performance and efficiency of HRP were demonstrated by the immobilization of the enzyme by strongly covalent binding to NH2-MOF-Zr, which suggested that the development of stable crosslinking by EDC/NHS between the carrier and enzymes may have been the cause of the efficiency of HRP action. As a result of the carrier’s large surface area and likely excellent dispersion of the enzyme, the effectiveness of the enzyme was boosted as the steric barriers surrounding the active sites of the enzyme molecule were decreased [35, 36].
3.1 Surface morphology characterization
Using scanning electron microscopy, Fig. 2(a, b) shows a surface morphology of the obtained NH2-MOF-Zr and NH2-MOF-Zr@HRP. Figure 2(a) exhibits the SEM image of NH2-MOF-Zr with particle distribution as clusters of flakes with irregular shapes. A high magnification confirms the irregular shapes of these flakes-like particles. After enzyme immobilization, a minor change occurred in morphology structure of material support (NH2-MOF-Zr). SEM images showed a fibrous topology with a considerable number of linked tubules and an agglomerated structure (Fig. 2b). EDX (energy dispersive X-ray spectroscopy) confirmed the presence of zirconium in the chemical composition of amino functionalized metal organic frameworks (Fig. 3). The EDX has been acknowledged as a technique for bulk chemical compositions, with X-rays produced in a surface area around 2 µm in depth [37]. Figures 3, and the inset table confirmed the presence of C, N, O, S, and Zr in the structure of the synthesized NH2-MOF-Zr@HRP and shows that 21.79% by weight of zirconium is the presence in the chemical composition of amino functionalized metal organic frameworks.
3.2 X-ray diffraction (XRD) analysis
The changed structure of NH2-MOF-Zr before and after immobilization was investigated using the XRD. The results revealed the relatively amorphous the sample.
The formation of the hexanuclear Zr6O4(OH)4 phase (JCPDS Card No. 01–085-9069) was evidenced by reflection peaks at 2θ = 25.7°; 28.44°; 43.80°; 50.62°; and 57.34° (Fig. 4), which fit well with the results reported by Pakamorė et al. [30], Chu et al. [38], and Zinatloo et al. [39]. The diffractograms show a reduction in the intensity of the NH2-MOF-Zr peaks after immobilization, elucidating the interactions between HRP and NH2-MOF-Zr. Our results are in agreement with that found by Chen et al. [40] and Aghajanzadeh et al. [41]. A zirconium(IV)-based MOF (UiO-66-NH2) was prepared by Chen et al. [40] and applied for remove cationic dyes from aqueous solution. Also Aghajanzadeh et al. [41] used UiO-66-NH2 for remove methotrexate from aqueous solution.
3.3 FTIR spectroscopy
The FTIR spectrum of NH2-MOF-Zr and NH2-MOF-Zr@HRP are presented in Fig. 5. Asymmetric stretching vibrations of N–H can be seen at 3424 cm−1, bending frequency band of N–H at 1574 cm−1, and stretching vibration of C-N at 1255 cm−1 [42]. The stretching vibrations of the carboxylate group correspond to the characteristic band at 1387 cm−1. At 1658 cm−1, an absorption peak was observed, which was attributed to C = O stretching [43]. At 1498 cm−1, benzene rings’ stretching vibration of the aromatic C–C ring was observed. The Zr-O stretching vibration essentially causes the peak at 660 cm1 to appear [31]. Furthermore, alterations in the substrate bands upon enzyme immobilization and the appearance of the glycosidic C–O–C band at 1020 cm−1 could confirm to the occurrence of immobilized HRP. The bands peaks of amide I (C–O stretch) at 1628 cm−1, amide II (N–H in-plane bending and C–N stretch) at 1574 cm−1 and 1255 cm−1, and amide III (N–H and C–H deformation vibrations) at 1385 cm−1 were overlapped with that of 2-aminoterephthalic acid [44].
3.4 Reusability and operational stability
As compared to free enzymes, immobilized enzymes maintain their activity and can be used multiple times. The cost-effectiveness of immobilized HRP for industrial applications depends on its reusability. The oxidation of guaiacol for 10 times in succession was used to test the NH2-MOF-Zr@HRP’s reusability. After three cycles, the residual activity was 93%, after five cycles, it was 89%, and even after ten cycles, it was 59% of the initial activity, as seen in (Fig. 6a). Decreased enzymatic activity throughout the recycling cycle may be caused by high substrate concentrations and the progressive leaching of enzyme from the supporting material [45,46,47,48]. In addition, HRP activity was sustained above 50% of the initial activity up to 10 reuse cycles; hence, it can be concluded that immobilizing HRP on NH2-MOF-Zr provides a highly stable biocatalyst. According to a report on HRP immobilized on Fe3O4 magnetic nanoparticles, after 10 cycles, the enzyme preserved 55% of its initial activity [49]. In another study, peroxidase was immobilized on functionalized graphene oxide and maintained 50% of its activity after nine reuses [50].
Due to free enzymes might lose their activity relatively promptly, storage stability for a prolonged period of time is one of immobilization’s main advantages. By monitoring enzyme’s activity each week for 6 weeks at 4 °C, the storage stability of the free enzyme and NH2-MOF-Zr@HRP was investigated. As shown in (Fig. 6b), the maintained activity for free HRP and NH2-MOF-Zr@HRP at the end of the third week was 82% and 91%, respectively, of the original activities. By the end of the sixth week, the residual activity for free HRP and NH2-MOF-Zr@HRP was 31% and 74%, respectively. A slow leak observed in the HRP immobilized on NH2-MOF-Zr. Just 3.7% of the HRP that was immobilized on NH2-MOF-Zr leaked after 1 week. Nevertheless, during a period of 6 weeks, around 17.9% of the HRP immobilized on NH2-MOF-Zr leaked (Fig. 6c). The enzyme’s position in the NH2-MOF-Zr channels, which provided protection for the enzyme molecules and maintained their active conformation during long-term storage, may be responsible for the improvement in storage stability [51]. Our result demonstrated that, due to the structural stabilization of HRP molecules in NH2-MOF-Zr, the HRP immobilized on NH2-MOF-Zr possessed greater stability than the free enzyme during long-term storage. On the other hand, decreased enzymatic activity throughout the recycling phase may be attributed to elevated substrate concentrations and the progressive leaching of enzyme from the supporting material [45, 52]. In a recent study, the immobilized HRP on magnetic composite microsphere preserved 71.5% of its original activity after 60 days’ storage [53].
3.5 Impact of pH and temperature on the free and immobilized HRP
The impact of pH on the activity of free HRP and NH2-MOF-Zr@HRP for oxidation of guaiacol was investigated. An important point in the applications of NH2-MOF-Zr@HRP is the activity with varying pH. The results of the investigation on the activities of free HRP and NH2-MOF-Zr@HRP in the pH range of (4.0–9.0) are reported in (Fig. 7a). In acetate and Tris–HCl buffers, the effects of pH on free HRP and NH2-MOF-Zr@HRP were assessed. The studies indicate that free HRP has an optimal pH of 7.0, while NH2-MOF-Zr@HRP has an abroad optimum pH range (7.0–7.5). At pH 9.0, the activity of NH2-MOF-Zr@HRP was increased by twofold compared to free form. The shift in pH could be attributed to electrostatic interaction between the carrier and the enzyme. The charged carrier changes the pH at which enzymes function best once the concentration of cations near the carrier surface exceeds that of the solution [36]. Furthermore, the NH2-MOF-Zr@HRP was significantly more robust to pH variation under acidic/basic pH conditions compared to free enzyme. The shift in the optimal pH for immobilized HRP toward a higher pH is comparable with the results reported by Mohamed et al. [54], who found that HRP immobilized on cationic maize starch had an optimal pH of 7.0. The optimal pH for immobilized HRP on Fe3O4Np-PMMA shifted from pH 7.0 to 7.5, according to Abdulaal et al. [55].
One of the essential aspects for the immobilization of enzymes is the enzyme activity at different temperatures. To investigate whether the optimal temperature changes after immobilization, the enzyme activities of free HRP and NH2-MOF-Zr@HRP were evaluated at various temperatures. According to the results, the optimum activity for free HRP and NH2-MOF-Zr@HRP was observed at 40 and 50 °C, respectively (Fig. 7b). The results were presented as a percentage of the highest activity for the enzyme at temperatures between 30 and 80 °C. In the range of 30–40 °C, the relative activity of free HRP improved with increasing temperature, whereas the relative activity of NH2-MOF-Zr@HRP increased in the range of 30–50 °C. Furthermore, at 70 °C, NH2-MOF-Zr@HRP maintained 67% of its activity while free HRP maintained 38%, while at 80 °C, the relative activity of free HRP was 14% and NH2-MOF-Zr@HRP was 51%. According to the results, the material support has shielded the enzyme from undesirable alterations at high temperatures. The improvement in the optimal temperature for HRP immobilized on NH2-MOF-Zr is compatible with results reported by Melo et al. [56], which reported that HRP immobilized on chitosan/PEG nanoparticles had an optimal temperature of 50 °C. El-Naggar et al. [57] revealed that HRP immobilized on cationic microporous starch had optimal temperature at 40 °C. Keshta et al. [58] obtained that HRP immobilized on functionalized superparamagnetic Fe3O4NP performs best activity at 40 °C. Due to the interactions of HRP with the NH2-MOF-Zr enhancing the stabilization of the HRP molecule, the immobilized HRP can preserve its active configuration even at a higher temperature, which explains why the immobilized enzyme has a higher optimal temperature than the free enzyme. It’s possible that this happens because the support matrix shields the immobilized enzyme from heat and limits its mobility in response to temperature-induced denaturation, enhancing its stability over a larger temperature range. The authors [56, 59, 60] support this hypothesis.
3.6 Km and Vmax parameters
Identifying the enzyme’s kinetic parameters (Km and Vmax) are essential for determining the enzyme’s activity following immobilization processe. Michaelis constant (Km) reflects the substrate concentration capable of reaching half the Vmax of the reaction and indicates the degree of enzymatic adequacy for the substrate, while maximum velocity (Vmax) defines the maximum rate of an enzymatic reaction [61]. Upon enzymatic immobilization, alterations in kinetic parameters can be observed. The Vmax of the enzyme is significantly impacted by the fact that enzymatic immobilization does not guarantee that the enzyme molecules are bound in the proper configuration. Diffusion barriers are still another crucial factor in the alteration of kinetic parameters, particularly Km. An internal diffusion barrier restricts the diffusion of substrate molecules to the matrix by the presence of the enzyme within the matrix, which affects Km and Vmax. As a result, it is important to calculate the diffusion constant (Kα) from the Vmax/Km ratio [62]. Figure 8 shows estimated kinetic parameters from free HRP and NH2-MOF-Zr@HRP. For guaiacol, the Km values of free HRP and NH2-MOF-Zr@HRP were 25.76 and 34.70 mM and for H2O2 (9.67 and 12.58 Mm), respectively. On the other hand, the calculated values of Vmax of the free HRP and NH2-MOF-Zr@HRP were 1.095 and 0.811 U/mL for guaiacol and 1.495 and 0.930 U/mL for H2O2, respectively. The diffusion constant (Kα) significantly decreased compared to the free HRP, indicating that the alteration in the kinetic characteristics of the enzyme may be caused by changes in the conformation of the enzyme or modifications to the microenvironment upon immobilization [63]. This phenomenon could be attributed to a restriction in the substrate’s mass transfer through the reticulated networks of material support or a potential steric hindrance caused by the structural stiffness of the distorted enzyme structure after immobilization [64]. Abdulaal et al. [55] and El-Naggar et al. [57] showed an increased in km values for HRP when immobilization on PMMA incorporated with Fe3O4 and cationic microporous starch, respectively.
3.7 Effect of organic solvent on free and immobilized HRP
Figure 9 shows the effect of organic solvents on the activity of free and NH2-MOF-Zr@HRP; therefore, some routinely organic solvents, such as ethanol, methanol, dimethyl sulfoxide (DMSO), toluene, methanol, n-hexane, isopropanol, and butan-1-ol, were utilized in the enzyme activity assay to evaluate resistance. Free and NH2-MOF-Zr@HRP were incubated in the presence of solvents (20%v/v) at pH 7.0 for 30 min. For free and NH2-MOF-Zr@HRP, the highest catalytic activity was observed in isopropanol, followed by butan-1-ol and n-hexane. The free and NH2-MOF-Zr@HRP preserved 87%, 98% of their original activity in isopropanol, 84%, 96% of their original activity in butan-1-ol, and 82%, 89% of their original activity in n-hexane. Methanol caused slightly inhibition effect on NH2-MOF-Zr@HRP, where it preserved 84% of its original activity, while it caused moderate inhibition effect on free HRP (preserved 68% of its original activity). DEMSO and toluene caused inhibitory effect toward NH2-MOF-Zr@HRP less than free HRP. Due to the presence of organic solvents in wastewater, it is important to investigate the stability of enzymes in such environments. Some immobilized peroxidases have reportedly shown increased resistance to organic solvents [65, 66].
3.8 Biodegradation studies of phenolic pollutants
High quantities of phenol have been found in the effluents that originate from various locations in industrial plants [67]. HRP, as a green biocatalyst, can catalyze a wide range of compounds. In this study, phenol, BPA, and 4-MEP were chosen as targets to assess enzymatic activity. Figure 10a illustrates the change in removal efficiency over time. About 87%, 53%, and 49% of 4-MEP, BPA, and phenol were removed by NH2-MOF-Zr@HRP during a 6-h reaction; this removal was enhanced 1.89-, 1.26-, and 2.13-folds compared that by free HRP. As can be seen in Fig. 10a, immobilization significantly improved the enzymatic performance. The study’s overall results indicate that immobilization can adequately protect HRP from inactivation during the biodegradation reaction. In the recycling experiments, the biocatalytic sustainability was further evaluated. NH2-MOF-Zr@HRP were recycled after the first round of phenol, BPA, and 4-MEP removal by being withdrawn and washed and then used for the subsequent phenol, BPA, and 4-MEP removal. HRP’s biocatalytic performance decreased when reused several times, as shown in Fig. 10b. The removal efficiency of phenol, BPA, and 4-MEP after five reuse cycles was 48%, 51%, and 62%, respectively. The effect of pristine NH2-MOF-Zr and modified NH2-MOF-Zr by crosslinker (EDC/NHS) on the removal phenolic compounds, before enzyme immobilization, was displayed in Fig. 1S. The sharp decrease in the removal efficiency of phenols after EDC/NHS treatment can be attributed to the steric crowding and saturation of porous sites on the surface of MOFs by crosslinker EDC/NHS, which hinders the adsorption process of phenols.
4 Conclusion
In conclusion, we successfully fabricated the NH2-MOF-Zr using a solvothermal approach and created the NH2-MOF-Zr@HRP using EDC/NHS as cross-linker. HRP immobilized on NH2-MOF-Zr exhibited significant catalytic activity, reusability, long-term stability, reduced leaching, and organic solvent stability, indicating better mass-transfer efficiency and enzyme accessibility, likely as a result of pore-expansion in the host material. After 10 cycles of use, the NH2-MOF-Zr@HRP displays significant reusability, retaining up to 59% of its initial activity. The stability study revealed that after 6 weeks, NH2-MOF-Zr@HRP was retained 74% of its initial activity. NH2-MOF-Zr@HRP performed significantly better than free HRP enzymes in successive biodegradation studies on three phenolic compounds. During 6 h of reaction, the removal of 4-MEP, BPA, and phenol via immobilized HRP were enhanced by 1.89-, 1.26-, and 2.13-folds compared free HRP. As a result, this strategy appears to be highly useful, trustworthy, and eco-friendly, and it can be considered a technologically advantageous technique for wide use.
Data availability
Data are contained within the article.
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The Deanship of Scientific Research (DSR) at King Abdulaziz University (KAU), Jeddah, Saudi Arabia, has funded this project under grant no (G: 342–130-1443).
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Y.Q.A. carried out the literature study and drafted the manuscript. Y.Q.A. and M.Z. conceived, edited, and reviewed the manuscript. All authors have read and agreed to the published version of the manuscript.
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Zeyadi, M., Almulaiky, Y.Q. Amino functionalized metal–organic framework as eco-friendly support for enhancing stability and reusability of horseradish peroxidase for phenol removal. Biomass Conv. Bioref. (2023). https://doi.org/10.1007/s13399-023-04597-9
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DOI: https://doi.org/10.1007/s13399-023-04597-9