Chitosan-Grafted Halloysite Nanotubes-Fe3O4 Composite for Laccase-Immobilization and Sulfamethoxazole-Degradation

A surface-engineered nano-support for enzyme laccase-immobilization was designed by grafting the surface of halloysite nanotubes (HNTs) with Fe3O4 nanoparticles and chitosan. Herein, HNTs were magnetized (HNTs-M) by a cost-effective reduction-precipitation method. The synthesized HNTs-M were grafted with 0.25%, 0.5%, 1%, and 2% chitosan (HNTs-M-chitosan), respectively. Synthesized HNTs-M-chitosan (0.25%), HNTs-M-chitosan (0.5%), HNTs-M-chitosan (1%) and HNTs-M-chitosan (2%) were linked with glutaraldehyde (GTA) for laccase immobilization. Among these formulations, HNTs-M-chitosan (1%) exhibited the highest laccase immobilization with 95.13% activity recovery and 100.12 mg/g of laccase loading. The optimized material was characterized thoroughly by scanning electron microscopy (SEM), high-resolution transmission electron microscopy (HR-TEM), X-ray powder diffraction (XRD), thermal gravimetric analysis (TGA), and vibrating sample magnetometer (VSM) analysis. The immobilized laccase (HNTs-M-chitosan (1%)-GTA-Laccase) exhibited higher pH, temperature, and storage stabilities. The HNTs-M-chitosan (1%)-GTA-Laccase possesses excellent reusability capabilities. At the end of 10 cycles of the reusability experiment, HNTs-M-chitosan (1%)-GTA-Laccase retained 59.88% of its initial activity. The immobilized laccase was utilized for redox-mediated degradation of sulfamethoxazole (SMX), resulting in 41%, 59%, and 62% degradation of SMX in the presence of 2,2′-Azino-bis(3-ethylbenzothiazoline-6-sulfonic acid) diammonium salt (ABTS), guaiacol (GUA), and syringaldehyde (SA), respectively. Repeated SMX degradation (57.10% after the sixth cycle) confirmed the potential of HNTs-M-chitosan (1%)-GTA-Laccase for environmental pollutant degradation. Thus, we successfully designed chitosan-based, rapidly separable super-magnetic nanotubes for efficacious enhancement of laccase biocatalysis, which can be applied as nano-supports for other enzymes.


Introduction
Laccase is a multi-copper oxidoreductase, which catalyzes single-electron substrate oxidation using molecular oxygen [1]. Biocatalyst enzymes have long been explored, due to their high specificity, catalytic power, and stereo-selectivity [2]. Enzyme immobilization processes gave us bio-based catalysts with enhanced properties for diverse applications [3,4]. Laccase is a capable biocatalyst for micro-pollutant removal [5]. Enormous population growth has increased the industrial agricultural demands, resulting in increasing micro-pollutant concentrations in the environment. The increased concentration of micro-pollutants in the environment due to constant release, even at trace concentrations (ng/L), from wastewater-treatment plants into water bodies is of great environmental and public health concern [6]. Hence, in this study, the pharmaceutical compound and indicator of antibiotic pollution 'sulfamethoxazole (SMX) was chosen as the target pollutant for immobilized-laccase-based bio-catalytical degradation. SMX is known for its widespread use in human and veterinary medicines, a frequent occurrence in water supplies, and resultant negative health consequences. [7].
The development of efficient nano-supports is required to use laccase for the desired environmental application [5]. There is a huge opportunity in the development of an excellent nano-supports, which can be used in enzyme-based catalysis [2]. Among various nano-supports, halloysite nanotubes (HNTs) have recently attracted significant attention [8], due to the excellent physical properties of HNTs, including their highly-modifiable surfaces, nano-tubular morphology, the nano-lumen inside the nanotube, interior and exterior modifiable surfaces, their robust nature, high surface-area (up to 184.9 m 2 /g), and large pore volume (up to 0.353 cm 3 /g) [9]. Due to these properties, HNTs are used as effective carriers for enzyme immobilization [10], drug delivery [11], adsorbents [12], photo-catalysis [13], and other applications.
However, there is still a major opportunity to further modify the HNT surface [14]. To develop HNTs as a nano-support for laccase immobilization, it is crucial to incorporate magnetic properties because magnetism allows for rapid separation from water [15]. There are many approaches available for the incorporation of magnetic nanoparticles in HNTs; however, the reduction-precipitation method is cost-effective, requires ambient temperatures, and does not utilize additional N 2 gas [16]. Hence, this study focuses on the reduction-precipitation based magnetization of HNTs. Further, functionalization of the HNTs was required for the immobilization process. Chitosan is a natural cationic polymer composed of β-1-4 linked D-glucosamine (deacetylated unit) and N-acetyl-D-glucosamine (acetylated unit) [17]. In last two decades, chitosan emerged as a highly important biopolymer that can be utilized for diverse applications [18]. Chitosan and its hybrid with other organic-inorganic materials in the form of nano/micro formulations is attracting the attention in the applications such as biomedical technology, remediation, catalysis, food packaging, and cultural heritage treatment etc. [19,20]. Polysaccharides/HNTs hybrids as smart bio-nano-composite materials for diverse applications have been reviewed by Bertolino et al., 2020 [21]. Chitosan possesses ubiquitous (-NH 2 ) functional groups. Given its natural origin, chitosan-modified HNTs have several advantages over the chemically (-NH 2 ) modified HNTs [10]. However, an optimization of the amount of chitosan onto the HNT surface for enhanced laccase immobilization and degradation of SMX has not yet been reported [22].
In this work, we developed a reduction-precipitation based procedure for the magnetization of HNTs, optimized the chitosan loading on the magnetized HNT surface for enhanced laccase immobilization, studied the biocatalytic properties of the immobilized laccase, and assessed the ability of immobilized laccase to degrade SMX in water. As a result, we developed a chitosan-based, efficient nano-support that can be applied for enzyme immobilization and environmental pollutant decontamination.

Synthesis of HNTs-M-Chitosan
The HNTs-M-chitosan was synthesized in two steps. First, pristine HNTs were modified with Fe 3 O 4 NPs [16]. Then, Fe 3 O 4 NPs-modified HNTs were functionalized with the chitosan. In the first step, 0.5-2 g of HNTs were added to 100 mL of deionized water. The mixture was ultrasonicated by Sonics Vibra-Cell VC130 Ultrasonic Processor, power-130 W, frequency-20 kHz, and amplitude-60 µM (Sonics & Materials, Inc., Newtown, CT, USA) for 1 h. The mixture was then added to the 50 mL of 3% FeCl 3 -6H 2 O solution and rapidly vortexed. Then, 0.7% of Na 2 SO 3 solution was added. The addition of Na 2 SO 3 solution turns the solution color red. Once the red color returned to yellow, 30 mL of 1 N NaOH was added. This turns the mixture black due to the colored precipitate of Fe 3 O 4 NPs-modified HNTs. The black-colored composites were magnetically recovered and washed thoroughly with distilled water, ethanol, and methanol. The obtained sample was dried in an oven at 60 • C for 48 h. The obtained sample of HNTs-M was powdered stored for further use. The chitosan modification of HNTs-M was done in a 500 mL beaker. The chitosan solutions (0.25%, 0.5%, 1% and 2%) in 50 mL of 2% acetic acid were vortexed for 4 h. The clear 0.25%, 0.5%, 1%, and 2% chitosan solutions were added to 0.5 g of HNTs-M in 50 mL distilled water and ultrasonicated Sonics Vibra-Cell VC130 Ultrasonic Processor, power-130 W, frequency-20 kHz, and amplitude-60 µM (Sonics & Materials, Inc., Newtown, CT, USA) for 15 min. The resulting mixtures were refluxed rapidly for 15 min. Then, 2 mL of 2.5% glutaraldehyde was added to the mixtures. After glutaraldehyde addition, the mixtures continued refluxing for 8 h at 50 • C. The obtained mixtures of HNTs-M-chitosan (0.25%), HNTs-M-chitosan (0.5%), HNTs-M-chitosan (1%) and HNTs-M-chitosan (2%) were separated magnetically and washed thoroughly with distilled water. The materials were dried in an oven at 60 • C and powdered for further use in enzyme immobilizations.

Laccase Immobilization on Synthesized Materials
HNTs-M-chitosan (0.25%), HNTs-M-chitosan (0.5%), HNTs-M-chitosan (1%), and HNTs-M-chitosan (2%) were cross-linked with glutaraldehyde (GTA). A total of 100 mg of materials were added to 10 mL of 2.5% GTA solution. The solution was rapidly shaken at 200 rpm for 24 h at 25 • C. The GTA linked materials were separated using a magnet and thoroughly washed with distilled water. The GTA-linked materials HNTs-M-chitosan (0.25%), HNTs-M-chitosan (5%), HNTs-M-chitosan (1%), and HNTs-M-chitosan (2%) were then added to a laccase solution (1 mg/mL) in sodium acetate buffer (100 mM, pH 4). The mixtures were continuously shaken at 200 rpm for 24 h at 20 • C. Afterward, immobilized laccase were separated magnetically and thoroughly washed with the sodium acetate buffer (100 mM, pH 4). The immobilized laccase was immediately tested for activity recovery (%) and laccase loading. The activity recovery (%) was calculated by Equation (1): where A I is the activity of the immobilized laccase, and A F is the initial free laccase activity. The laccase activity was tested in a reaction mixture containing sodium acetate buffer (100 mM, pH 4), ABTS (90 µM) and laccase/immobilized laccase. The laccase/immobilized laccase activity corresponds to the ABTS oxidation in the reaction mixture. The ABTS oxidation was measured by spectrophotometrically at 420 nm [24]. Further, to determine the laccase loading, the laccase concentration in solutions before and after immobilization were tested for protein content using the Bradford method (Pierce™ Coomassie (Bradford) Protein Assay Kit, Thermo Scientific™, Massachusetts, MA, USA) [25]. The Pierce Coomassie Protein Assay Kit is follows the principles originally described by Bradford in 1976. In the acidic condition when proteins mixed with Coomassie-dye reagent, it changes color from brown to blue as per the amount to the amount of protein present. Protein estimation was done by comparison to the color response of protein assay standards. The laccase loading (mg/g) on nanocomposites was calculated by Equation (2): where C i is the initial laccase concentration before immobilization (mg/L), C r is the retained laccase concentration after immobilization (mg/L), V is the volume of the solution in liters (L), and W is the weight of the nanocomposites in gram (g). The synthesized material with higher laccase loading and activity recovery (%) capacity was further characterized in detail and studied for laccase biocatalysis.

Characterizations of Nano-Supports
Morphological analysis was performed by scanning electron microscopy (SEM, FC-SM10, Hitachi S-4800, Ibaraki, Japan) and high-resolution transmission electron microscopy (HR-TEM, Tecnai G2 transmission electron microscope, Hillsboro, OR, USA). The crystallinity of the materials was determined using an X-ray powder diffractometer with Cu-Kα radiation (λ= 1.5418 Å) (Ultima IV/Rigaku, Tokyo, Japan). The vibrating sample magnetometer (VSM) analysis was done by Lakeshore, Model: 7407, LA, USA. Thermogravimetric analysis was performed to measure the weight (%) loss with respect to temperature from 25 to 800 • C (TA Instrument, Q600, New Castle, DE, USA). Surface charge of the materials was determined by zeta potential measurements (Zeta-potential and Particle Size Analyzer ELSZ-2000 series, Otsuka Electronics., Co., Ltd. Osaka, Japan)

Immobilized Laccase Biocatalysis
As mentioned previously, the HNTs-M-chitosan (1%)-GTA-Laccase was selected for biocatalysis studies. The laccase loading pattern on HNTs-M-chitosan (1%) was assessed by varying the initial concentration of laccase (0.2 mg/mL, 0.4 mg/mL, 0.6 mg/mL, 0.8 mg/mL, 1 mg/mL, and 1.2 mg/mL). The laccase loading was measured as previously mentioned in Equation (2) from Section 2.3. HNTs-M-chitosan (1%)-GTA-Laccase were then tested for thermal, pH, and time stabilities. Thermal stability was studied by incubating free laccase and HNTs-M-chitosan (1%)-GTA-Laccase at 60 • C for 220 min. The samples were tested every 40 min to determine relative activity (%). The time stabilities were investigated by incubating free laccase and HNTs-M-chitosan (1%)-GTA-Laccase for 30 d at 4 • C. The samples were withdrawn at every 5 d, and tested to determine relative activity (%). The pH stability study was performed by incubating 0.1 mL of free and immobilized laccase in 1 mL of different pH buffers (1-9) for 1 h at 25 • C. For this experiment 100 mM HCl-KCl buffer (for pH 1 and 2), 100 mM citrate-phosphate buffer (for pH 3, 4, 5, 6, and 7), and 100 mM Tris-HCl buffer (for pH 8 and 9) were used. After 1 h of incubation in varying pH conditions, the samples were tested to determine relative activity (%) to measure the respective pH stabilities. Furthermore, the HNTs-M-chitosan (1%)-GTA-Laccase nanocomposites were used in repeated cycle studies. The HNTs-M-chitosan (1%)-GTA-Laccase was tested for laccase activity in the 1st cycle as described above. Before the 2nd cycle, the HNTs-M-chitosan (1%)-GTA-Laccase used in the 1st cycle were washed with sodium acetate buffer (pH 4.0) three times. The washed HNTs-M-chitosan (1%)-GTA-Laccase were added to fresh reactants and the laccase activity was measured. A total of 10 of these cycles were performed to assess the potency of the HNTs-M-chitosan (1%)-GTA-Laccase. The relative activity is measured as considering the original activity before these experiments as 100%. The percent relative activity is given as Equation (3): where A a is the activity after the experiment, and A o is the original activity before experiment.

SMX Degradation by HNTs-M-Chitosan (1%)-GTA-Laccase
The SMX degradation was carried out by HNTs-M-chitosan (1%)-GTA-Laccase. The reaction mixture was as follows: 25 ppm SMX, 1 mM redox mediator (either ABTS, SA or GUA), HNTs-M-chitosan (1%)-GTA-Laccase in sodium acetate buffer, pH 4.0. The reaction was carried out with each redox mediator separately for 4 h at 200 rpm and 20 • C. The degradation of the SMX was measured with high-performance liquid chromatography (HPLC, Shimadzu LC-20AD, Kyoto, Japan) at a detection wavelength of 286 nm with a mobile phase of methanol:water (60:40) at a flow rate of 0.6 mL/min with the C18 column (Ascentis ® Express C18, Sigma-Aldrich, St. Louis, MO, USA, 2.7 µm HPLC Column 2.7 µm particle size, length × inner diameter-5 cm × 4.6 mm). The SMX degradation was measured as Equation (4): where P std is peak area of the standard SMX peak before the degradation experiment, and P deg is peak area of the SMX peak after the degradation experiment. The SMX degradation was also carried out in repeated cycles. After completion of the first cycle, the HNTs-M-chitosan (1%)-GTA-Laccase was washed thoroughly with sodium acetate reaction buffer three times. The washed HNTs-M-chitosan (1%)-GTA-Laccase was added to fresh reactants for the SMX degradation experiment for 6 cycles.

Synthesis
A schematic representation of the stepwise synthesis of HNTs-M-chitosan (1%)-GTA-Laccase is shown in Figure 1. Pristine HNTs were first super-magnetized with the Fe 3 O 4 NPs. This was done by the typical reduction precipitation method. In the reaction mechanism, the Fe 3+ ions first attach to the surface of pristine HNTs. Further addition of Na 2 SO 3 partially reduces the attached Fe 3+ ions to Fe 2+ . At the same time, addition of NaOH synthesizes Fe 3 O 4 NPs on the surface of HNTs (HNTs-M). The reduction precipitation is a highly cost-effective, easy, and reliable method compared to the typically-used co-precipitation method [22]. Where Aa is the activity after the experiment, and Ao is the original activity before experiment.

SMX Degradation by HNTs-M-Chitosan (1%)-GTA-Laccase
The SMX degradation was carried out by HNTs-M-chitosan (1%)-GTA-Laccase. The reaction mixture was as follows: 25 ppm SMX, 1 mM redox mediator (either ABTS, SA or GUA), HNTs-Mchitosan (1%)-GTA-Laccase in sodium acetate buffer, pH 4.0. The reaction was carried out with each redox mediator separately for 4 h at 200 rpm and 20 °C. The degradation of the SMX was measured with high-performance liquid chromatography (HPLC, Shimadzu LC-20AD, Kyoto, Japan) at a detection wavelength of 286 nm with a mobile phase of methanol:water (60:40) at a flow rate of 0.6 mL/min with the C18 column (Ascentis ® Express C18, Sigma-Aldrich, St. Louis, MO, USA, 2.7 μm HPLC Column 2.7 μm particle size, length × inner diameter-5 cm × 4.6 mm). The SMX degradation was measured as Equation (4): Where Pstd is peak area of the standard SMX peak before the degradation experiment, and Pdeg is peak area of the SMX peak after the degradation experiment. The SMX degradation was also carried out in repeated cycles. After completion of the first cycle, the HNTs-M-chitosan (1%)-GTA-Laccase was washed thoroughly with sodium acetate reaction buffer three times. The washed HNTs-Mchitosan (1%)-GTA-Laccase was added to fresh reactants for the SMX degradation experiment for 6 cycles.

Synthesis
A schematic representation of the stepwise synthesis of HNTs-M-chitosan (1%)-GTA-Laccase is shown in Figure 1. Pristine HNTs were first super-magnetized with the Fe3O4 NPs. This was done by the typical reduction precipitation method. In the reaction mechanism, the Fe 3+ ions first attach to the surface of pristine HNTs. Further addition of Na2SO3 partially reduces the attached Fe 3+ ions to Fe 2+ . At the same time, addition of NaOH synthesizes Fe3O4 NPs on the surface of HNTs (HNTs-M). The reduction precipitation is a highly cost-effective, easy, and reliable method compared to the typicallyused co-precipitation method [22].  It is crucial to separate the nano-supports loaded with enzyme efficaciously from solution; this simple magnetization boosts the separation potential of HNTs-M-chitosan-GTA. After magnetization, the HNTs-M surface was decorated with varying chitosan concentrations. The chitosan-modified HNTs-M (HNTs-M-chitosan) were further modified by the cross-linker GTA (HNTs-M-chitosan-GTA). The unique characteristics of GTA render it one of the most effective protein crosslinking reagents [26]. The GTA cross-links the laccase onto the HNTs-M-chitosan. The laccase-loaded HNTs-M-chitosan was further assessed for immobilization parameters and the degradation of SMX.

Characterizations
The morphology of the pristine HNTs and HNTs-M-chitosan (1%) was observed using SEM and HR-TEM ( Figure 3). Figure 3A shows bare HNTs under SEM. The surface of the tubes can be easily observed. The surface of the tubes appears unmodified, planar, and nanotubular in nature. Similar observations were noted in previous work [14]. There are different lengths and widths of the  In addition, HNTs-M-chitosan (1%) in solution have good colloidal stability. Since potential applications take place in dispersions, particle aggregation should be prevented, in order provide homogeneously distributed primary particles of high surface area [35][36][37]. Moreover, Figure 2B presents the ABTS oxidation spectra by free laccase and immobilized laccase on HNTs-M-chitosan (1%). The excellent retention of the activity by immobilized laccase can be clearly seen in the obtained spectra's ( Figure 2B). This is due to the optimized chitosan loading onto the HNTs-M surface; the laccase immobilization plateaued at the 2% chitosan concentration, likely due to saturation of chitosan on the HNTs-M surface. Hence, HNTs-M-chitosan (1%) was further characterized to study its immobilized laccase bio-catalytical properties.

Characterizations
The morphology of the pristine HNTs and HNTs-M-chitosan (1%) was observed using SEM and HR-TEM (Figure 3). Figure 3A shows bare HNTs under SEM. The surface of the tubes can be easily observed. The surface of the tubes appears unmodified, planar, and nanotubular in nature. Similar observations were noted in previous work [14]. There are different lengths and widths of the nanotubes in Figure 3A. Figure 3B shows the HNTs-M-chitosan (1%) morphology. The surface of the HNTs was clearly modified with Fe 3 O 4 NPs ( Figure 3B). The nanotubes were broadened due to the chitosan loading. Further characterization was performed with HR-TEM ( Figure 3C-E). Figure 3C shows the pristine HNTs. The inner lumen is clearly evident. The surface of HNTs is unmodified. However, the HNTs-M-chitosan (1%) surface appears intensively modified with Fe 3 O 4 NPs and chitosan. The broadened, layered morphology of the tubes may be due to the chitosan modification ( Figure 3D). Moreover, the lattice fringe region of Fe 3 O 4 NPs on HNTs was determined to be 0.29 nm ( Figure 3E), similar to that seen in prior work [38]. Thus, SEM and HR-TEM images confirmed the nanotubular morphology with desired surface modifications.
The crystallinity analysis was performed by determining the X-ray powder diffraction (XRD) patterns of pristine HNTs and HNTs-M-chitosan (1%) (Figure 4). The HNTs and HNTs-M-chitosan (1%) showed typical XRD peaks 11.82 • , 19.94 • , and 24.55 • , which mainly corresponds to HNTs crystalline planes of (001), (020) and (002), respectively (JCPDS 29-1487) [27]. The sharp peak at (2θ = 11.82 • ) in HNTs-M-chitosan (1%) indicates basal space reflections of the nanotubular multiwall structure of HNTs [27]. This suggest the HNTs nanotubular nature was consistent after the surface modifications.    It is crucial to measure the magnetic separation potential of the nanocomposite before and after laccase immobilization. Figure 6A shows the VSM analysis of HNTs-M-chitosan (1%) and HNTs-Mchitosan (1%)-GTA-Laccase. After laccase loading, the magnetization was decreased, corroborating the successful loading of the laccase onto the HNTs-M-chitosan (1%) nanotubes. The magnetic   It is crucial to measure the magnetic separation potential of the nanocomposite before and after laccase immobilization. Figure 6A shows the VSM analysis of HNTs-M-chitosan (1%) and HNTs-Mchitosan (1%)-GTA-Laccase. After laccase loading, the magnetization was decreased, corroborating the successful loading of the laccase onto the HNTs-M-chitosan (1%) nanotubes. The magnetic It is crucial to measure the magnetic separation potential of the nanocomposite before and after laccase immobilization. Figure 6A shows the VSM analysis of HNTs-M-chitosan (1%) and HNTs-M-chitosan (1%)-GTA-Laccase. After laccase loading, the magnetization was decreased, corroborating the successful loading of the laccase onto the HNTs-M-chitosan (1%) nanotubes. The magnetic saturation values found to be 25 emu/g and 21 emu/g for HNTs-M-chitosan (1%) and HNTs-M-chitosan (1%)-GTA-Laccase. The hysteresis curves confirmed the super-para-magnetic nature of both materials [10]. The surface charge of the stepwise modified materials was measured with the zeta potential analysis. The detailed results given in the Figure 6B

Bio-Catalytic Properties of HNTs-M-Chitosan (1%)-GTA-Laccase
Immobilized enzymes may display enhanced biocatalytic properties [3]. Hence, after immobilization, it is important to assess the biocatalytic properties of the immobilized enzyme. We analyzed the laccase loading pattern by varying initial laccase concentration, the thermal stability performance, the temporal stability, and the pH stability of our immobilized laccase nanocomposites (Figure 7). Figure 7A shows the laccase loading as the initial laccase concentration was increased from 0.2 to 1.2 mg/mL. The laccase loading sharply declined for initial laccase concentrations above 1 mg/mL. At the initial laccase concentration of 1 mg/mL, HNTs-M-chitosan (1%)-GTA exhibited 99.61 mg/g of laccase loading. This may be due to the saturation of sites on the HNTs-M-chitosan (1%)-GTA available for immobilization. A similar effect was observed for the loading of the enzyme naringinase on chitosan microspheres [41]. The thermal stability is shown in Figure 7B. The free laccase lost 28% of its initial activity after incubating at 60 °C for 6 h. However, HNTs-M-chitosan (1%)-GTA-Laccase only lost 15% of the initial activity. The obtained results confirm that the immobilization of laccase on the HNTs-M-chitosan (1%)-GTA nanocomposites significantly enhanced the thermal stability of laccase. The binding of the enzyme to a support provides mechanical support to prevent enzymatic denaturation at higher temperatures [5].

Bio-Catalytic Properties of HNTs-M-Chitosan (1%)-GTA-Laccase
Immobilized enzymes may display enhanced biocatalytic properties [3]. Hence, after immobilization, it is important to assess the biocatalytic properties of the immobilized enzyme. We analyzed the laccase loading pattern by varying initial laccase concentration, the thermal stability performance, the temporal stability, and the pH stability of our immobilized laccase nanocomposites (Figure 7). Figure 7A shows the laccase loading as the initial laccase concentration was increased from 0.2 to 1.2 mg/mL. The laccase loading sharply declined for initial laccase concentrations above 1 mg/mL. At the initial laccase concentration of 1 mg/mL, HNTs-M-chitosan (1%)-GTA exhibited 99.61 mg/g of laccase loading. This may be due to the saturation of sites on the HNTs-M-chitosan (1%)-GTA available for immobilization. A similar effect was observed for the loading of the enzyme naringinase on chitosan microspheres [41]. The thermal stability is shown in Figure 7B. The free laccase lost 28% of its initial activity after incubating at 60 • C for 6 h. However, HNTs-M-chitosan (1%)-GTA-Laccase only lost 15% of the initial activity. The obtained results confirm that the immobilization of laccase on the HNTs-M-chitosan (1%)-GTA nanocomposites significantly enhanced the thermal stability of laccase. The binding of the enzyme to a support provides mechanical support to prevent enzymatic denaturation at higher temperatures [5]. Polymers 2020, 12, x FOR PEER REVIEW 11 of 17 The storage stability of free laccase and HNTs-M-chitosan (1%)-GTA-Laccase is shown in Figure  7C. The free laccase activity decreased over time, resulting in 44% activity lost and after 30 days of incubation. However, HNTs-M-chitosan (1%)-GTA-Laccase displayed higher stability compared to the free laccase, losing only 30% of their initial activity after 30 days. Similar storage stability improvements for immobilized laccase compared to free laccase were previously reported [29]. The pH of the local environment affect desired application of the enzyme [30]. Hence, the pH stability of HNTs-M-chitosan (1%)-GTA-Laccase is very important. Figure 7D shows the pH stability of free laccase and HNTs-M-chitosan (1%)-GTA-Laccase. The free laccase exhibited very strong stability in the pH range of 3-5. The HNTs-M-chitosan (1%)-GTA-Laccase showed excellent catalytical performance at the pH range of 1-6. The HNTs-M-chitosan (1%)-GTA-Laccase exhibited stability across a broad pH range, significantly higher than that of free laccase, especially at pH of 1-2 and pH 6-9. This indicates that the HNTs-M-chitosan (1%)-GTA-Laccase exhibit excellent stability and biocatalytic properties across a wide pH range.
Repeated use of the immobilized laccase is essential for its economic viability [42]. The repeated cycle study of the HNTs-M-chitosan (1%)-GTA-Laccase is shown in Figure 8. A total of 10 repeated cycles were performed. At the end of the 10th cycle, HNTs-M-chitosan (1%)-GTA-Laccase retained 60% of the initial activity. This result suggests exceptional reusability for the immobilized laccase, representing a significant improvement upon recently reported nano-supports for laccase immobilization [29,31,42,43]. Thus, the biocatalytic performance of the HNTs-M-chitosan (1%)-GTA-Laccase is excellent, resulting in a wide array of potential applications. The storage stability of free laccase and HNTs-M-chitosan (1%)-GTA-Laccase is shown in Figure 7C. The free laccase activity decreased over time, resulting in 44% activity lost and after 30 days of incubation. However, HNTs-M-chitosan (1%)-GTA-Laccase displayed higher stability compared to the free laccase, losing only 30% of their initial activity after 30 days. Similar storage stability improvements for immobilized laccase compared to free laccase were previously reported [29]. The pH of the local environment affect desired application of the enzyme [30]. Hence, the pH stability of HNTs-M-chitosan (1%)-GTA-Laccase is very important. Figure 7D shows the pH stability of free laccase and HNTs-M-chitosan (1%)-GTA-Laccase. The free laccase exhibited very strong stability in the pH range of 3-5. The HNTs-M-chitosan (1%)-GTA-Laccase showed excellent catalytical performance at the pH range of 1-6. The HNTs-M-chitosan (1%)-GTA-Laccase exhibited stability across a broad pH range, significantly higher than that of free laccase, especially at pH of 1-2 and pH 6-9. This indicates that the HNTs-M-chitosan (1%)-GTA-Laccase exhibit excellent stability and biocatalytic properties across a wide pH range.
Repeated use of the immobilized laccase is essential for its economic viability [42]. The repeated cycle study of the HNTs-M-chitosan (1%)-GTA-Laccase is shown in Figure 8. A total of 10 repeated cycles were performed. At the end of the 10th cycle, HNTs-M-chitosan (1%)-GTA-Laccase retained 60% of the initial activity. This result suggests exceptional reusability for the immobilized laccase, representing a significant improvement upon recently reported nano-supports for laccase immobilization [29,31,42,43].
Thus, the biocatalytic performance of the HNTs-M-chitosan (1%)-GTA-Laccase is excellent, resulting in a wide array of potential applications.

Biocatalytic Degradation of SMX
Pollution by pharmaceutical compounds poses serious environmental issues [42]; thus, their removal from water supplies is crucial. We used SMX as an example pharmaceutical compound pollutant. The HNTs-M-chitosan (1%)-GTA-Laccase does not degrade SMX in the absence of the redox mediator, because laccase requires a redox mediator compound to degrade SMX [10]. Immobilized laccase reduces the redox mediator compound, which then catalyzes the degradation of the target pollutant [22]. In this work, we used ABTS, SA, and GUA as redox mediators. The degradation of SMX by HNTs-M-chitosan (1%)-GTA-Laccase in the presence of ABTS, SA, and GUA was analyzed by HPLC ( Figure 9A-D). Free SMX shows a clear and sharp peak at a retention time of 1.87 min ( Figure 9A). The ABTS, SA, and GUA-mediated SMX degradation products exhibited two sharp peaks at 1.87 min and 1.45 min. However, the intensity of the 1.87 min peak decreased significantly compared to the standard SMX in presence of all the redox mediators. Hence, the split in standard SMX peak at 1.87 min and significant decrease in its intensity confirms the redox mediated breakdown of SMX by HNTs-M-chitosan (1%)-GTA-Laccase. Among all redox mediators, the GUA exhibited the highest decrease in the intensity of the 1.87 min peak of standard SMX. Thus, GUA found to be the best redox mediator than the ABTS and SA. The result is consistent with the previous report [10]. This might be due to the small molecular nature and easy way oxidation by laccase. The oxidized GUA by immobilized laccase immediately gets reduced by causing oxidative degradation of the SMX. This might accelerates the SMX degradation in presence of the GUA. The schematic of immobilized laccase, structures of SMX, ABTS, SA, and GUA and degradation percentage of SMX by redox mediators are shown in Figure 10.

Biocatalytic Degradation of SMX
Pollution by pharmaceutical compounds poses serious environmental issues [42]; thus, their removal from water supplies is crucial. We used SMX as an example pharmaceutical compound pollutant. The HNTs-M-chitosan (1%)-GTA-Laccase does not degrade SMX in the absence of the redox mediator, because laccase requires a redox mediator compound to degrade SMX [10]. Immobilized laccase reduces the redox mediator compound, which then catalyzes the degradation of the target pollutant [22]. In this work, we used ABTS, SA, and GUA as redox mediators. The degradation of SMX by HNTs-M-chitosan (1%)-GTA-Laccase in the presence of ABTS, SA, and GUA was analyzed by HPLC ( Figure 9A-D). Free SMX shows a clear and sharp peak at a retention time of 1.87 min ( Figure 9A). The ABTS, SA, and GUA-mediated SMX degradation products exhibited two sharp peaks at 1.87 min and 1.45 min. However, the intensity of the 1.87 min peak decreased significantly compared to the standard SMX in presence of all the redox mediators. Hence, the split in standard SMX peak at 1.87 min and significant decrease in its intensity confirms the redox mediated breakdown of SMX by HNTs-M-chitosan (1%)-GTA-Laccase. Among all redox mediators, the GUA exhibited the highest decrease in the intensity of the 1.87 min peak of standard SMX. Thus, GUA found to be the best redox mediator than the ABTS and SA. The result is consistent with the previous report [10]. This might be due to the small molecular nature and easy way oxidation by laccase. The oxidized GUA by immobilized laccase immediately gets reduced by causing oxidative degradation of the SMX. This might accelerates the SMX degradation in presence of the GUA. The schematic of immobilized laccase, structures of SMX, ABTS, SA, and GUA and degradation percentage of SMX by redox mediators are shown in Figure 10.     The HNTs-M-chitosan (1%)-GTA-Laccase degraded 41%, 59%, and 62% of the SMX with ABTS, SA, and GUA, respectively ( Figure 10). Cost effective and efficient technologies for environmental pollutants removal are highly important [44]. Hence, GUA is known to be green, valuable, economical, and beneficial mediator for laccase-mediated bioremediation applications [45]. Further, we performed six cycles of repeated SMX degradation (Figure 11), suggesting significant potential for the use of HNTs-M-chitosan (1%)-GTA-Laccase in a continuous process. The SMX degradation was observed to be 61.32, 59.73, 58.52, 58.72, and 58.65 in first five cycles of the repeated degradation. The HNTs-M-chitosan (1%)-GTA-Laccase degraded 57.10% of the SMX in the sixth cycle ( Figure 11). This designates the strong potential of immobilized laccase. The small decrease of 4% was observed in six cycles. This might be due to the build-up of the degraded product. This result suggests that HNTs-M-chitosan (1%)-GTA-Laccase has significant potential for use in the biocatalytic degradation of pollutants, and can be applied in environmental decontamination processes. The HNTs-M-chitosan (1%)-GTA-Laccase degraded 41%, 59%, and 62% of the SMX with ABTS, SA, and GUA, respectively ( Figure 10). Cost effective and efficient technologies for environmental pollutants removal are highly important [44]. Hence, GUA is known to be green, valuable, economical, and beneficial mediator for laccase-mediated bioremediation applications [45]. Further, we performed six cycles of repeated SMX degradation (Figure 11), suggesting significant potential for the use of HNTs-M-chitosan (1%)-GTA-Laccase in a continuous process. The SMX degradation was observed to be 61.32, 59.73, 58.52, 58.72, and 58.65 in first five cycles of the repeated degradation. The HNTs-M-chitosan (1%)-GTA-Laccase degraded 57.10% of the SMX in the sixth cycle ( Figure 11). This designates the strong potential of immobilized laccase. The small decrease of 4% was observed in six cycles. This might be due to the build-up of the degraded product. This result suggests that HNTs-M-chitosan (1%)-GTA-Laccase has significant potential for use in the biocatalytic degradation of pollutants, and can be applied in environmental decontamination processes.

Conclusion
In-conclusion, we investigated the optimum loading of chitosan on the HNTs-M surface for efficacious laccase biocatalysis, and the degradation of the pharmaceutical compound SMX from water. Characterization by SEM, TEM, XRD, TGA, and VSM confirmed the successful synthesis of nano-support HNTs-M-chitosan (1%). HNTs-M-chitosan (1%)-GTA-Laccase displayed efficacious potential of redox mediated degradation of SMX. Thus, the HNTs-M-chitosan (1%)-GTA-Laccase may be an ideal system for the degradation of environmental pollutants. The developed nano-supports are economically cheap and applicable for encountering the problem of pharmaceutical compounds degradation. Additionally, the developed nano-support may be used to immobilize other enzymes to enhance their biocatalytic properties for a wide range of applications.

Conclusions
In-conclusion, we investigated the optimum loading of chitosan on the HNTs-M surface for efficacious laccase biocatalysis, and the degradation of the pharmaceutical compound SMX from water. Characterization by SEM, TEM, XRD, TGA, and VSM confirmed the successful synthesis of nano-support HNTs-M-chitosan (1%). HNTs-M-chitosan (1%)-GTA-Laccase displayed efficacious potential of redox mediated degradation of SMX. Thus, the HNTs-M-chitosan (1%)-GTA-Laccase may be an ideal system for the degradation of environmental pollutants. The developed nano-supports are economically cheap and applicable for encountering the problem of pharmaceutical compounds degradation. Additionally, the developed nano-support may be used to immobilize other enzymes to enhance their biocatalytic properties for a wide range of applications.