Galactomannans for Entrapment of Gliomastix murorum Laccase and Their Use in Reactive Blue 2 Decolorization

In the present study, a novel laccase from ascomycete Gliomastix murorum was produced in agro-industrial wastes and entrapped in galactomannan beads for Reactive Blue 2 (Rb-2) decolorization. The maximum laccase production in agave bagasse-based medium occurred at 72 h (1798.6 UL−1). Entrapped laccase decolorized ˃80% of 0.5 mM Rb-2 in 2 h without the addition of redox mediator. Km for Rb-2 substrate was 1.42 mM, with a Vmax of 1.19 µmol min−1 for entrapped laccase. Galactomannan matrices produce stability to acid pH (2–5) and temperatures from 20–70 °C. Reusability assays showed that entrapped laccase could retain efficient Rb-2 decolorization of ˃80% six times. In general, galactomannan used for entrapment of laccase provides economic advantages in large-scale wastewater treatment due to its natural origin and efficient results.


Introduction
Organic synthetic dyes represent one of biggest contamination problems generated by textile, paper, plastics, pharmaceutical, food, and cosmetics industries [1][2][3]. Dyes are discharged into aquatic environments, damaging ecosystems due to their toxicity. Consequently, there is a reduction in photosynthetic activity by the obstruction of solar rays. In addition, dyes represent a risk to human health due to their potential mutagenic and carcinogenic effects [4]. Reactive anthraquinoic dyes have a stable aromatic structure, which makes their elimination difficult. These dyes represent around 20-30% of dyes used worldwide [5]. They have a low fixation in cotton, wool garments, and others during the dyeing stage, which means around 8-35% of dyes applied are discharged into residual effluents [6,7].
Reactive Blue 2 (Rb-2) is an anthraquinoic dye, its structure is a triazine with amino and sulfate groups, giving it high stability and resistance to degradation by biological systems and chemical treatments [8,9]. Due to this problem, several efforts have been made to remove Rb-2 from the environment. Traditionally, different physical treatments have been proposed to eliminate this pollutant, such as filtration, sedimentation, and adsorption, which generate fewer toxic by-products. However, these techniques do not Sustainability 2021, 13, 9019 2 of 12 achieve mineralization of the pollutant [1]. In addition, advanced oxidation systems such as electrooxidation, electrocoagulation, chemical coagulation, photodegradation, and coupled systems have also been evaluated (biologically advanced systems) [10][11][12]. Wastewater treatment requires high energy loads and also chemical compounds, which represent an increase in toxicity of treated effluents [13].
Some strategies with biological treatments, mainly anaerobic systems, have been incorporated into the degradation of reactive anthraquinoic dyes, with elimination reaching 90% with residence times ranging from 8-24 h [14]. The use of these systems for colorant elimination is an economically and environmentally sustainable option. However, only a proportion of pollutants are adsorbed onto the granules' surfaces (the same happens with physical processes), and the absorbed colorant fails to mineralize completely, generating highly toxic degradation by-products [15]. Likewise, biological systems with selective bacteria [2], fungi [16,17], and enzymes [18] have been incorporated to eliminate these pollutants.
In the degradation of reactive anthraquinoic dye using catalysts, enzymes are responsible for hydrolyzing and oxidizing contaminants. The use of specific enzymes for pollutant degradation reduces operating times and costs, and allows optimization of the treatment. Laccases are enzymes commonly called blue multicopper oxidases, and they are the most widely distributed of all the large blue copper-containing proteins [19]. They are produced by a wide variety of microorganisms such as bacteria [20], yeast [21], and fungi [22] isolated from different environments [23]. Basidiomycete and bacterial laccases have been widely reported; however, using these enzymes for dye removal requires the use of redox mediators [19,24] Mtibaa et al. [20] reported ascomycete laccases that do not require the incorporation of this type of mediator. Refs [25][26][27] Data of laccase production from the genus Gliomastix is limited. In Mexico, there are many environments in which to obtain microorganisms capable of producing these kinds of enzyme [21,22].
The challenge in catalyst application in residual effluent treatment is the immobilization and/or trapping of enzymes in a system that facilitates recovery for reuse. Different hydrogels for enzyme immobilization have been used, such as: poly hydroxyethyl methacrylate-co-vinylene carbonate p (HEMMA-co-VC), chitosan [28], genipin-activated chitosan [24], polyacrylamide-alginate cryogel [29], Ca-alginate [25], and others. Galactomannans are polysaccharides used as thickeners and emulsifiers in the food industry, their main advantage is that they are obtained from the endosperm seeds of numerous plants, mainly legumes [26,27], which means that it is an economical option for enzymatic trapping. For this reason, the main objective of this work was to evaluate the degradation of Rb-2 in synthetic water using ascomycete laccase Gliomastix murorum sp. HP3 trapped in galactomannan beads.

Materials
Galactomannan polysaccharide (M.W. of approx. 310 kDa) from Ceratonia siliqua (algarrobo) seeds, lignin alkali and Reactive Blue 2 (Cibacron Blue 3GA) were purchased from Sigma-Aldrich ® (Merck KGaA, Darmstadt, Germany). Agave bagasse, which is an agro-industrial waste derived from agave distillates, was supplied by a local distiller company; before use, it was ground and sieved to a particle size less than 0.149 mm.

Isolation, Screening, and Identification of Laccase-Producing Microorganism
Isolations were made from soil samples from Tamuín, San Luis Potosí, Mexico. Sample suspensions in sterile distilled water with 1% Tween 80 were diluted in a ratio of 10 mL of water for each gram of soil. They were incubated for 1 h at room temperature (25 • C) and agitation (250 rpm). Decimal dilutions were made from 10 −1 to 10,000 −1 in sterile 150 mM NaCl, and 100 µL in Petri dishes of 10 cm diameter were inoculated with Küster medium [30], formulated with (g L −1 ): glycerol, 10 18. Isolated colonies were collected and passed on a fresh agar medium, then biomass was recovered and stored in 20% glycerol at −20 • C.
Screening of laccase-producing strains was performed in agar plates using 1% lignin as the sole carbon source to replace soluble starch in Küster medium. The appearance of a brown halo around the colony was considered positive for laccase production.
The selected strain was identified by molecular analysis. A fresh microorganism culture was used to DNA extraction with a commercially available kit, Dneasy ® Plant Mini Kit (Qiagen, Hilden, Germany). The PCR was made using OneTaq ® DNA polymerase (New England Biolabs, Ipswich, MA, USA) on a 96-well thermal cycler (Veriti ™ , Applied Biosystems, Foster City, CA, USA). The primers ITS1 and ITS4 [31] were employed to amplify approximately 600 bp fragments from the transcribed spacer region in the nuclear ribosomal repeat unit. The PCR product was sequenced by Macrogen USA Corp. (Rockville, MD, USA). Consensus sequences were analyzed using the CLC Main Workbench 5.5 software (CLCBio, Aarhus, Denmark). The BLAST algorithm was used to compare obtained sequences with the nucleotide GenBank database [32]. A phylogenetic tree was built where the evolutionary distances were computed using the Maximum Composite Likelihood method [33].

Culture Conditions
The culture medium was optimized for laccase production as described in Supplementary Data. The effect of nitrogen, carbon, and co-substrate was studied by multivariate and surface response experimental designs. The optimized medium contained (g L −1 ): glucose, 12.0; agave bagasse, 28.0; urea, 2.6; NaCl, 2.0; K 2 HPO 4 , 2.0; MgSO 4 ·7H 2 O, 0.05; CaCO 3 , 0.02; FeSO 4 ·7H 2 O, 0.01, and was inoculated with 5 × 10 5 spores m L −1 of a fresh surface culture and incubated at 30 • C in Erlenmeyer flasks with orbital shaking at 250 rpm. Laccase activity was monitored for 120 h. The biomass generation was estimated by weight difference. The reducing sugars quantification was performed using Miller's DNS method [34]. A standard glucose curve was used as a reference.

Enzyme Extraction
The culture of Gliomastix murorum was stopped at 72 h to obtain the maximum production of laccase activity. The extracellular extract was recovered by centrifugation at 10,000 rpm for 10 min at 4 • C and frozen at −20 • C until its subsequent use.

Activity Assays
Laccase activity was determined by monitoring the oxidation of 7.5 mM ABTS (2,2 azino bis (3 ethylbenzthiazoline-6-sulfonic acid)) in 100 mM citrate-phosphate buffer, pH 6 at λ max = 405 nm. Assays were carried out in a 96-well plate in 200 µL (estimated 0.6 cm path length) of reaction volume, which was incubated at 37 • C and monitored every 30 s in a microplate spectrophotometer (Epoch TM 2, BioTek TM ). One unit of enzymatic activity corresponds to 1.0 µmol of ABTS oxidized per minute under test conditions. An ABTS molar extinction coefficient of 36.8 mM −1 cm −1 was used [35].
Reactive Blue 2 (Rb-2) was evaluated as a substrate for laccase. Enzyme activity was tested under the same pH (6), temperature (37 • C), and stirring conditions as per ABTS. In contrast to this, the Rb-2 assay was monitored at λ max = 610 nm. One unit of enzymatic activity corresponds to 1.0 µmol of Rb-2 degraded per minute under test conditions. The molar extinction coefficient came from a standard curve (8.4 mM −1 cm −1 ).

Preparation of Galactomannan/Laccase Beads
Galactomannan (1.8 g L −1 ) was dissolved in distilled water. Laccase extract (50:50) v/v was prepared. First, galactomannan solution was heated in a 1500 W microwave oven on high power for 15 s; then when the mix was cold (25 • C), the laccase extract was added. The mixture was stirred using a magnetic stirrer to ensure complete mixing. For bead preparation, the mixture was added dropwise to a beaker containing 100 mL of acetone Sustainability 2021, 13, 9019 4 of 12 at 4 • C, and it was left under constant orbital shaking at 50 rpm for 1 h. The beads were recovered using a strainer and placed on a glass plate for 10 min at 25 • C to ensure complete evaporation of the acetone. The enzymatic activity (EA) was measured in the beads that were obtained. The beads were stored at 4 • C for later use. A schematic illustration of bead preparation is shown in Figure 1.
Sustainability 2021, x, x FOR PEER REVIEW 4 of 13 on high power for 15 s; then when the mix was cold (25 °C), the laccase extract was added. The mixture was stirred using a magnetic stirrer to ensure complete mixing. For bead preparation, the mixture was added dropwise to a beaker containing 100 mL of acetone at 4 °C, and it was left under constant orbital shaking at 50 rpm for 1 h. The beads were recovered using a strainer and placed on a glass plate for 10 min at 25 °C to ensure complete evaporation of the acetone. The enzymatic activity (EA) was measured in the beads that were obtained. The beads were stored at 4 °C for later use. A schematic illustration of bead preparation is shown in Figure 1.

Reactive Blue 2 Decolorization Assays
The Rb-2 decolorization by galactomannan entrapped laccase was conducted in conical tubes containing 5.0 mL of 0.5 mM Rb-2 (dissolved in 100 mM citrate-phosphate, pH 6) and 3 beads of entrapped laccase (0.39 mU mg −1 of catalyst). A simultaneous experiment with equal activity units of free laccase and the same reaction conditions was performed. Samples were incubated on an orbital shaker at 250 rpm and 37 °C. A sample (200 µL) was taken every 20 min and analyzed spectrophotometrically at λmax = 610 nm. The extent of decolorization was expressed in terms of a percentage calculated as follows: where A0 is the initial absorbance and At is the absorbance of test sample. All samples were analyzed in triplicate.
To determine the possible adsorption of Rb-2 on galactomannan beads, control experiments with galactomannan enzyme free beads where also conducted.

Effect of Temperature and pH on the Enzyme Stability
Thermostability tests of the free and entrapped laccases were carried out by incubating the enzyme at different temperatures, ranging from 4 °C to 80 °C, using 100 mM citrate-phosphate (pH 6). Furthermore, the stability at different pH was analyzed, incubating the enzyme preparations in different 100 mM citrate-phosphate buffer solutions (pH 2-9) at room temperature.
In both studies, the sample was left under assay conditions for 120 min; next, the residual activity was measured using ABTS as the substrate for the reaction at pH 6. Assays were carried out in triplicate on 2 mL microtubes containing 0.5 mL of buffer. Re-

Reactive Blue 2 Decolorization Assays
The Rb-2 decolorization by galactomannan entrapped laccase was conducted in conical tubes containing 5.0 mL of 0.5 mM Rb-2 (dissolved in 100 mM citrate-phosphate, pH 6) and 3 beads of entrapped laccase (0.39 mU mg −1 of catalyst). A simultaneous experiment with equal activity units of free laccase and the same reaction conditions was performed. Samples were incubated on an orbital shaker at 250 rpm and 37 • C. A sample (200 µL) was taken every 20 min and analyzed spectrophotometrically at λ max = 610 nm. The extent of decolorization was expressed in terms of a percentage calculated as follows: where A 0 is the initial absorbance and A t is the absorbance of test sample. All samples were analyzed in triplicate.
To determine the possible adsorption of Rb-2 on galactomannan beads, control experiments with galactomannan enzyme free beads where also conducted.

Effect of Temperature and pH on the Enzyme Stability
Thermostability tests of the free and entrapped laccases were carried out by incubating the enzyme at different temperatures, ranging from 4 • C to 80 • C, using 100 mM citratephosphate (pH 6). Furthermore, the stability at different pH was analyzed, incubating the enzyme preparations in different 100 mM citrate-phosphate buffer solutions (pH 2-9) at room temperature.
In both studies, the sample was left under assay conditions for 120 min; next, the residual activity was measured using ABTS as the substrate for the reaction at pH 6. Assays were carried out in triplicate on 2 mL microtubes containing 0.5 mL of buffer. Residual activity was calculated considering the maximum activity as 100%. For activity tests, the entrapped laccase was recovered by draining the beads, while the free enzyme was conveniently diluted in 100 mM citrate-phosphate buffer at pH 6.

Reusability Capacity of Entrapped Laccase
The reusability test was evaluated in batch. A bead of entrapped laccase with an initial activity of 0.39 mU mg −1 of catalyst and 0.5 mL of 0.5 mM Rb-2 (dissolved in 100 mM citrate-phosphate, pH 6) were placed in 2 mL microtubes. Tubes were incubated on an orbital shaker (250 rpm) at 37 • C for 30 min. Samples were taken at the beginning and after the incubation time to determine the decolorization (%). After one cycle of decolorization, the liquid was withdrawn, and 0.5 mL of fresh Rb-2 solution was added to initiate a new cycle. A total of 7-batch cycles were evaluated. Decolorization was reported as the percentage of dye elimination in every batch test. Dye decolorization in the first cycle was considered as 100%.

Isolation, Screening, and Identification of Laccase-Producing Microorganism
A total of 33 strains were isolated from soil samples from El Tamuín, San Luis Potosí, Mexico. These were screened in a selective medium containing lignin as the sole carbon source. After 14 days, 4 strains had grown, and only the strain HP3 generated a brown halo around the colony, indicating laccase production ( Figure S2).
The PCR amplification of the ITS region (476 bp) of HP3 and phylogenetic analysis ( Figure 2) revealed that the most closely related fungal strain was Gliomastix murorum sp. JCKQF8 (sequence ID: KT968540.1), with 99.58% identity. Ten sequences were selected to make the phylogenetic tree based on, the identity percentage, the score, and the query cover.
sidual activity was calculated considering the maximum activity as 100%. For activity tests, the entrapped laccase was recovered by draining the beads, while the free enzyme was conveniently diluted in 100 mM citrate-phosphate buffer at pH 6.

Reusability Capacity of Entrapped Laccase
The reusability test was evaluated in batch. A bead of entrapped laccase with an initial activity of 0.39 mU mg −1 of catalyst and 0.5 mL of 0.5 mM Rb-2 (dissolved in 100 mM citrate-phosphate, pH 6) were placed in 2 mL microtubes. Tubes were incubated on an orbital shaker (250 rpm) at 37 °C for 30 min. Samples were taken at the beginning and after the incubation time to determine the decolorization (%). After one cycle of decolorization, the liquid was withdrawn, and 0.5 mL of fresh Rb-2 solution was added to initiate a new cycle. A total of 7-batch cycles were evaluated. Decolorization was reported as the percentage of dye elimination in every batch test. Dye decolorization in the first cycle was considered as 100%.

Isolation, Screening, and Identification of Laccase-Producing Microorganism
A total of 33 strains were isolated from soil samples from El Tamuín, San Luis Potosí, Mexico. These were screened in a selective medium containing lignin as the sole carbon source. After 14 days, 4 strains had grown, and only the strain HP3 generated a brown halo around the colony, indicating laccase production ( Figure S2).
The PCR amplification of the ITS region (476 bp) of HP3 and phylogenetic analysis ( Figure 2) revealed that the most closely related fungal strain was Gliomastix murorum sp. JCKQF8 (sequence ID: KT968540.1), with 99.58% identity. Ten sequences were selected to make the phylogenetic tree based on, the identity percentage, the score, and the query cover. G. murorum is a type of saprophyte belonging to the order Hypocreales, which are related to the Dothideales, Magnaporthales, Capnodiales, and Leotiomycetes as ascomycetous fungi responsible for the degradation of lignocellulosic materials in forest litter and soil G. murorum is a type of saprophyte belonging to the order Hypocreales, which are related to the Dothideales, Magnaporthales, Capnodiales, and Leotiomycetes as ascomycetous fungi responsible for the degradation of lignocellulosic materials in forest litter and soil [36]. To our knowledge, no laccase activity has been reported in this genus; furthermore, there are few ascomycete laccases reported in the literature, and most of the laccases that have been studied in depth come from the division Basidiomycetes [18].

Laccase Production
Gliomastix murorum sp. HP3 was grown in agave bagasse-based medium to produce laccase. The same profile was observed between enzyme production and cell biomass, the maximum enzyme activity was reached at 72 h of culture (1798.6 U L −1 ) (Figure 3). This phenomenon was similar to laccases produced by white-rot fungi grown in natural substrates, such as agricultural residues in submerged fermentation [37,38]. However, Myasoedova et al. [39] observed that the maximum production of laccase activity in Hypocreal ascomycetes occurs between three and seven days when they are grown in a mineral medium with a complex carbon source (grain crops or potato).
Sustainability 2021, x, x FOR PEER REVIEW 6 of 13 [36]. To our knowledge, no laccase activity has been reported in this genus; furthermore, there are few ascomycete laccases reported in the literature, and most of the laccases that have been studied in depth come from the division Basidiomycetes [18].

Laccase Production
Gliomastix murorum sp. HP3 was grown in agave bagasse-based medium to produce laccase. The same profile was observed between enzyme production and cell biomass, the maximum enzyme activity was reached at 72 h of culture (1798.6 U L −1 ) (Figure 3). This phenomenon was similar to laccases produced by white-rot fungi grown in natural substrates, such as agricultural residues in submerged fermentation [37,38]. However, Myasoedova et al. [39] observed that the maximum production of laccase activity in Hypocreal ascomycetes occurs between three and seven days when they are grown in a mineral medium with a complex carbon source (grain crops or potato). On the other hand, it can be observed that both the production of laccase and the growth of the strain decline at the time the reducing sugars are exhausted; this can be solved through a fed batch fermentative strategy, which takes into account both the catabolic repression by glucose, as well as the maintenance of the culture [40].

Kinetic Parameters of Free and Entrapped Laccase
The kinetic parameters of the free and immobilized enzyme were determined for the oxidation of 2,2' azino bis (3 ethylbenzthiazoline-6-sulfonic acid) (ABTS) and Reactive Blue 2 (Rb-2) decolorization. Kinetics were performed using a range of substrate concentrations, and the results obtained are shown in Table 1. Both free and entrapped laccase showed a higher affinity for Rb-2 than for ABTS, while Vmax was higher in the oxidation of ABTS for entrapped enzyme. The results suggest that the immobilization of laccases in galactomannan beads does not modify the nature of the enzyme; however, the lower catalytic rate can be attributed to diffusion phenomena within the hydrogel, causing low accessibility of the substrate to the active sites [24]. Gliomastix murorum sp. HP3-free laccase presented greater affinity for ATBS than entrapped laccase; similar results were found for Thielavia sp. ascomycete and Trametes pubescens laccase-free [20,24,41]. Nevertheless, Vmax for ABTS substrate in entrapped laccase was 2.5 times higher than free laccase, and the opposite was true for Rb-2 substrate; Vmax of 5.67 for free laccase and 1.19 for entrapped laccase, respectively. On the other hand, it can be observed that both the production of laccase and the growth of the strain decline at the time the reducing sugars are exhausted; this can be solved through a fed batch fermentative strategy, which takes into account both the catabolic repression by glucose, as well as the maintenance of the culture [40].

Kinetic Parameters of Free and Entrapped Laccase
The kinetic parameters of the free and immobilized enzyme were determined for the oxidation of 2,2 azino bis (3 ethylbenzthiazoline-6-sulfonic acid) (ABTS) and Reactive Blue 2 (Rb-2) decolorization. Kinetics were performed using a range of substrate concentrations, and the results obtained are shown in Table 1. Both free and entrapped laccase showed a higher affinity for Rb-2 than for ABTS, while V max was higher in the oxidation of ABTS for entrapped enzyme. The results suggest that the immobilization of laccases in galactomannan beads does not modify the nature of the enzyme; however, the lower catalytic rate can be attributed to diffusion phenomena within the hydrogel, causing low accessibility of the substrate to the active sites [24]. Gliomastix murorum sp. HP3-free laccase presented greater affinity for ATBS than entrapped laccase; similar results were found for Thielavia sp. ascomycete and Trametes pubescens laccase-free [20,24,41]. Nevertheless, V max for ABTS substrate in entrapped laccase was 2.5 times higher than free laccase, and the opposite was true for Rb-2 substrate; V max of 5.67 for free laccase and 1.19 for entrapped laccase, respectively.

Evaluation of Laccase in Reactive Blue 2 Decolorization
The effectiveness of free and entrapped laccase in Rb-2 decolorization is shown in Figure 4. Rb-2 was 82% decolorized after 2 h of treatment with entrapped laccase; as expected, the treatment with the free enzyme reached 100% at the same time.

Temperature and pH Effects on the Stability of Free and Entrapped Laccase
The effect of temperature (4-80 °C) on free and entrapped laccases was evaluated (Figure 5a). The temperature effect on laccase stability was different from the free and entrapped enzyme. For free laccase, residual activity decreased near 55% after 20 °C and kept decreasing as the temperature increased, while for entrapped laccase, residual activity remained ˃95% until 40 °C and decreased ˂50% after 50 °C. These results show an increase in the thermal stability of the enzyme when galactomannan is used. Biopolymer use confers additional resistance and a protective microenvironment matrix.
The effect of pH (2-9) on stability of free and entrapped laccases was evaluated (Figure 5b). Entrapped laccase presented higher residual activity (23.75 ± 11.25) to acidic pH (2)(3)(4)(5). Similar residual activity was maintained for free and entrapped laccase to alkaline pH (6-9). Lassouane et al. [41] found high stability under acidic conditions (pH 3-6) in crosslinked-entrapped laccase in Ca-alginate beads, and more than 80% of its initial activity was retained. Results suggest that galactomannan hydrogel protects enzyme against acidic pH.  The use of galactomannan for enzyme entrapment has not been reported before. Different hydrogels for enzyme immobilization have been used. Bayramoglu et al. [15] immobilized laccase (Trametes versicolor) in poly hydroxyethyl methacrylate-co-vinylene carbonate p (HEMMA-co-VC) microbeads with acetosyringone as mediator, finding 43% Cibacron Blue 3GA degradation in a 2 h contact period. Ma et al. [24] found 77.49% removal of the dye Acid Black 172 through laccase (Trametes pubescens) immobilized by genipinactivated chitosan beads after 96 h of incubation. Zheng et al. [28] studied Acid Black 172 dye, finding 68.84% decolorization efficiency after a 48 h reaction by laccase (Trametes pubescens) immobilized in chitosan beads using glutaraldehyde as crosslinker; both studies used 50 mg L −1 as the initial dye concentration. Likewise, polyacrylamide-alginate cryogel was used for laccase (Trametes versicolor) immobilization in the elimination of different dyes, and results showed a >75% removal after 5 h (50 mg L −1 dye initial concentration) [29].

Time (min)
On the other hand, synthetic mediators are usually applied to improve dye oxidation; however, they are toxic compounds and their application increases dye treatment costs [19]. Gliomatix murorum sp. HP3 laccase does not require the addition of mediators to obtain high dye decolorization. In this work, more than 60% decolorization of Rb-2 (0.5 mM initial concentration) was achieved in the first 20 min when free laccase was used, while Othman et al. [42] observed a 29.29% decolorization of Rb-2 (0.12 mM initial concentration) after 35 min reaction using a laccase extract of the Basidiomycete Agaricus bisporus CU13, adding HBT 1 mM as mediator.
These results highlight the potential applications that laccase derived from Gliomatix murorum sp. HP3 entrapped in galactomannan beads has for dye removal over other hydrogel matrices, with the additional benefit of not requiring the addition of mediators.

Temperature and pH Effects on the Stability of Free and Entrapped Laccase
The effect of temperature (4-80 • C) on free and entrapped laccases was evaluated (Figure 5a). The temperature effect on laccase stability was different from the free and entrapped enzyme. For free laccase, residual activity decreased near 55% after 20 • C and kept decreasing as the temperature increased, while for entrapped laccase, residual activity remained >95% until 40 • C and decreased <50% after 50 • C. These results show an increase in the thermal stability of the enzyme when galactoatches of 30 min were analyzed. Residual activimannan is used. Biopolymer use confers additional resistance and a protective microenvironment matrix.

Reusability of Entrapped Laccase
The capacity of reusability of immobilized laccase is one of the most important indicators in industrial enzymatic applications (for reducing the cost) [41]. Therefore, it is necessary to investigate the feasibility of reusing the biocatalyst immobilized on different substrates [28,43]. Laccases entrapped in galactomannan beads have not been studied before. In this work, seven successive batches of 30 min were analyzed. Residual activity The effect of pH (2-9) on stability of free and entrapped laccases was evaluated (Figure 5b). Entrapped laccase presented higher residual activity (23.75 ± 11.25) to acidic pH (2)(3)(4)(5). Similar residual activity was maintained for free and entrapped laccase to alkaline pH (6)(7)(8)(9). Lassouane et al. [41] found high stability under acidic conditions (pH 3-6) in crosslinked-entrapped laccase in Ca-alginate beads, and more than 80% of its initial activity was retained. Results suggest that galactomannan hydrogel protects enzyme against acidic pH.

Reusability of Entrapped Laccase
The capacity of reusability of immobilized laccase is one of the most important indicators in industrial enzymatic applications (for reducing the cost) [41]. Therefore, it is necessary to investigate the feasibility of reusing the biocatalyst immobilized on different substrates [28,43]. Laccases entrapped in galactomannan beads have not been studied before. In this work, seven successive batches of 30 min were analyzed. Residual activity was >90% after four cycles and >80% after six cycles ( Figure 6). It is worth noting that, at 30 min of reaction, 20% decolorization was achieved and, to reach an 80% level, 120 min are needed; the difference in operation time could affect the loss of activity, lowering the reusability.
Sustainability 2021, x, x FOR PEER REVIEW 10 of 13 Figure 6. Effect of reuse on the activity of entrapped laccase. The assays were performed with 0.39 mU mg −1 of laccase at 37 °C, pH 6, under orbital shaking (250 rpm). After one cycle of decolorization, the liquid was withdrawn, and a fresh Rb-2 solution (0.5 mM, pH 6) was added to initiate a new cycle.
Results obtained from the reuse test of laccase entrapped in galactomannans are similar to those reported by Zheng et al. [28], who used chitosan to immobilize the laccase of Trametes pubescens, with a residual activity ˃60% after six cycles. Alginate is another widely used hydrogel for the entrapment of enzymes in the removal of dyes and other compounds. Reda et al. [43] found that the relative activity of the enzyme immobilized in alginate retains approximately 65% of activity after the seventh cycle. Daàssi et al. [25] detected that, after the fourth cycle, the discoloration values were >70% in laccase immobilized in Ca-alginate beads. It is worth mentioning that combinations of different matrices have been made to increase the reuse of immobilized enzymes. Some studies report the combination of graphene oxide in alginate to degrade different compounds, finding decolorizations >75%, with reuse between four and six cycles [36,44]. The decrease in enzyme activity could be attributed to the inactivation and loss of enzyme molecules during each cycle [28]. Furthermore, the environment of the solution could induce some conformational changes in the enzyme during continuous reprocessing, which would cause a decrease in the performance of catalytic activity [45].
The results suggest that the use of galactomannans for laccase entrapment implies excellent operational stability and good reusability. Results obtained from the reuse test of laccase entrapped in galactomannans are similar to those reported by Zheng et al. [28], who used chitosan to immobilize the laccase of Trametes pubescens, with a residual activity >60% after six cycles. Alginate is another widely used hydrogel for the entrapment of enzymes in the removal of dyes and other compounds. Reda et al. [43] found that the relative activity of the enzyme immobilized in alginate retains approximately 65% of activity after the seventh cycle. Daàssi et al. [25] detected that, after the fourth cycle, the discoloration values were >70% in laccase immobilized in Ca-alginate beads. It is worth mentioning that combinations of different matrices have been made to increase the reuse of immobilized enzymes. Some studies report the combination of graphene oxide in alginate to degrade different compounds, finding decolorizations >75%, with reuse between four and six cycles [36,44]. The decrease in enzyme activity could be attributed to the inactivation and loss of enzyme molecules during each cycle [28]. Furthermore, the environment of the solution could induce some conformational changes in the enzyme during continuous reprocessing, which would cause a decrease in the performance of catalytic activity [45].

Reusability (batches)
The results suggest that the use of galactomannans for laccase entrapment implies excellent operational stability and good reusability.

Conclusions
The laccase produced by ascomycetes Gliomastix murorum sp. HP3 exhibits a greater affinity for Reactive Blue 2 (Rb-2) decolorization, an anthraquinoid dye of significant toxicity, than by 2,2 azino bis (3 ethylbenzthiazoline-6-sulfonic acid) (ABTS), which is the conventional substrate for laccases. In addition, the catalytic rate is similar to that reported for other laccases that require the addition of redox mediators. The galactomannans matrix generated for the entrapment of laccases conferred enzyme stability against temperature and pH. The use of biopolymer allowed the enzyme to be reused for up six cycles, maintaining 82% in Rb-2 decolorization activity. Using hydrogels based on galactomannans for enzymatic trapping is a viable alternative which offers the advantage of obtaining dye beads that could be stored under ambient conditions. Supplementary Materials: The following are available online at https://www.mdpi.com/article/ 10.3390/su13169019/s1, Figure S1: Pareto analysis plot of effect of A inductor, B substrate and C nitrogen, on yield of enzyme production, Figure S2: Main effects plot: inductor (agave and cane), substrate (glucose and starch) and nitrogen (potassium nitrate and urea) for enzyme production yield, Figure S3: Interaction plot: Inductor and substrate (upper left), inductor and nitrogen (lower left) and substrate and nitrogen (lower right) on enzyme production yield, Figure S4: Response surface showing the interaction between three parameters and extracellular laccase production, Table S1: Experimental multifactorial design for screening of medium components for Gliomastix murorum (strain HP3) laccase production, Table S2: Response surface design.