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Research article · 2025 · Full text

International Journal of Advanced Chemistry Research

Covalent immobilization of laccase on amino-functionalized magnetic nanoparticles for degradation of textile dye effluents

Oluwaseun AdeyemiChidinma Nkechi Okafor

Volume 7(4) · Pages 170–173 · DOI: 10.33545/26646781.2025.v7.i4c.568 ↗

Research areasEnzyme-mediated dye degradationEnzyme Catalysis and ImmobilizationAdsorption and biosorption for pollutant removal

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Abstract

Author-written

Laccase enzymes catalyze the oxidation of phenolic and non-phenolic aromatic compounds using molecular oxygen as the terminal electron acceptor, making them attractive biocatalysts for textile dye removal from wastewater. However, free laccase is expensive and unstable under industrial conditions, limiting practical deployment. This research immobilized Trametes versicolor laccase onto amino-functionalized Fe₃O₄ magnetic nanoparticles (MNPs) via glutaraldehyde cross-linking and evaluated the conjugate for degradation of three textile dyes: Reactive Black 5, Acid Orange 7, and Crystal Violet. Immobilization efficiency reached 82.4% with a protein loading of 47.3 mg/g MNPs. The immobilized enzyme showed broadened pH and temperature optima compared to free laccase, with the pH optimum shifting from 4.5 to 5.0 and the temperature optimum from 50 to 60 °C. Thermal half-life at 60 °C increased from 28 min (free) to 187 min (immobilized). Dye decolorization within 6 hours reached 94.7% for Reactive Black 5, 97.2% for Acid Orange 7, and 91.3% for Crystal Violet at 50 mg/L initial concentration. Magnetic recovery enabled reuse over 10 cycles with 68.7% residual activity retained after the tenth cycle. The immobilized laccase maintained 84.1% activity after seven cycles, meeting the 80% industrial benchmark for enzyme reuse.

Summary

Source-checked

Plain-language reading of the full paper, prepared with AI and checked against the text. Each point links to the authors' own words.

  1. Why it matters

    • The textile industry in Nigeria produces approximately 200 million liters of dye-contaminated wastewater every day, but most factories lack biological treatment systems before discharging it. View evidence ↗

      Why it matters

      The textile industry in Nigeria produces approximately 200 million liters of dye-contaminated wastewater every day, but most factories lack biological treatment systems before discharging it.

      In the paper's own words

      “Nigeria’s textile industry, concentrated in Ondo, Lagos, and Kano states, generates an estimated 200 million liters of dye-laden wastewater daily, with fewer than 15% of factories operating any form of biological treatment before discharge into rivers and streams”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • Azo compounds, which make up 70% of global dye production, are difficult to treat with standard methods and can be carcinogenic or mutagenic. View evidence ↗

      Why it matters

      Azo compounds, which make up 70% of global dye production, are difficult to treat with standard methods and can be carcinogenic or mutagenic.

      In the paper's own words

      “Synthetic dyes — particularly azo compounds that constitute 70% of global dye production — are resistant to conventional biological and chemical treatment, persist in aquatic environments, and several are classified as carcinogenic or mutagenic”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
    • While laccase enzymes are effective biocatalysts, their industrial use is limited by high costs, instability in real effluent conditions, and the inability to recover free enzymes. View evidence ↗

      Why it matters

      While laccase enzymes are effective biocatalysts, their industrial use is limited by high costs, instability in real effluent conditions, and the inability to recover free enzymes.

      In the paper's own words

      “The main barrier to industrial adoption is cost: free laccase is denatured by the temperature, pH, and chemical conditions of real effluents, and cannot be recovered for reuse”

      Page 1

      Found in: Introduction

      Read it in the full textOpen PDF at page 1 ↗
  2. The question

    • The study aimed to optimize the immobilization of Trametes versicolor laccase on amino-functionalized magnetic nanoparticles (amino-MNPs) and test its ability to degrade three types of textile dyes. View evidence ↗

      The question

      The study aimed to optimize the immobilization of Trametes versicolor laccase on amino-functionalized magnetic nanoparticles (amino-MNPs) and test its ability to degrade three types of textile dyes.

      In the paper's own words

      “This research optimized the immobilization of commercial T. versicolor laccase on amino-MNPs, characterized the resulting biocatalyst, and evaluated its performance for degrading three structurally diverse textile dyes representative of those found in Nigerian industrial effluents”

      Page 2

      Found in: Introduction

      Read it in the full textOpen PDF at page 2 ↗
  3. What they did

    • Magnetic nanoparticles were created using alkaline co-precipitation of iron (II) and iron (III) chlorides in deoxygenated water at 80 °C. View evidence ↗

      What they did

      Magnetic nanoparticles were created using alkaline co-precipitation of iron (II) and iron (III) chlorides in deoxygenated water at 80 °C.

      In the paper's own words

      “Magnetic nanoparticles were synthesized by alkaline co-precipitation: FeCl₂·4H₂O (2.0 g) and FeCl₃·6H₂O (5.2 g) were dissolved in 100 mL deoxygenated water at 80 °C, and NH₄OH was added dropwise under nitrogen with vigorous stirring until pH 10.”

      Page 2

      Found in: Materials

      Read it in the full textOpen PDF at page 2 ↗
    • Laccase was covalently immobilized by activating 100 mg of amino-MNPs with 2.5% glutaraldehyde for 2 hours, followed by incubation with a 10 mg/mL laccase solution for 12 hours at 4 °C. View evidence ↗

      What they did

      Laccase was covalently immobilized by activating 100 mg of amino-MNPs with 2.5% glutaraldehyde for 2 hours, followed by incubation with a 10 mg/mL laccase solution for 12 hours at 4 °C.

      In the paper's own words

      “Amino-MNPs (100 mg) were Activated by incubation with 2.5% glutaraldehyde in phosphate buffer (pH 7.0) for 2 h at room temperature. After magnetic washing (3×), activated MNPs were mixed with laccase solution (10 mg/mL in 50 mM citrate-phosphate buffer, pH 5.0) and incubated at 4 °C for 12 h with gentle agitation.”

      Page 2

      Found in: Methods

      Read it in the full textOpen PDF at page 2 ↗
    • Dye degradation was tested using 50 mg/L concentrations of dyes with 50 mg of enzyme at 40 °C for 6 hours. View evidence ↗

      What they did

      Dye degradation was tested using 50 mg/L concentrations of dyes with 50 mg of enzyme at 40 °C for 6 hours.

      In the paper's own words

      “Dye decolorization experiments used 50 mg/L dye solutions in 50 mM citrate-phosphate buffer (pH 5.0) with 50 mg immobilized enzyme preparation (or equivalent free enzyme activity) at 40 °C and 150 rpm for 6 h.”

      Page 2

      Found in: Methods

      Read it in the full textOpen PDF at page 2 ↗
  4. What they found

    • The immobilization process achieved an efficiency of 82.4%, resulting in a protein loading of 47.3 mg per gram of magnetic nanoparticles. View evidence ↗

      What they found

      The immobilization process achieved an efficiency of 82.4%, resulting in a protein loading of 47.3 mg per gram of magnetic nanoparticles.

      In the paper's own words

      “Immobilization efficiency reached 82.4% with a protein loading of 47.3 mg/g MNPs.”

      Page 1

      Found in: Discussion

      Read it in the full textOpen PDF at page 1 ↗
    • Immobilization shifted the pH optimum from 4.5 to 5.0 and increased the temperature optimum from 50 °C to 60 °C. View evidence ↗

      What they found

      Immobilization shifted the pH optimum from 4.5 to 5.0 and increased the temperature optimum from 50 °C to 60 °C.

      In the paper's own words

      “pH optimum | 4.5 | 5.0”

      Page 2

      “Temperature optimum (°C) | 50 | 60”

      Page 2

      Found in: Table 1

      Read it in the full textOpen PDF at page 2 ↗
    • The thermal stability improved significantly, with the half-life at 60 °C increasing from 28 minutes for free laccase to 187 minutes for the immobilized form. View evidence ↗

      What they found

      The thermal stability improved significantly, with the half-life at 60 °C increasing from 28 minutes for free laccase to 187 minutes for the immobilized form.

      In the paper's own words

      “Thermal half-life at 60 °C (min) | 28 | 187”

      Page 2

      Found in: Table 1

      Read it in the full textOpen PDF at page 2 ↗
    • The biocatalyst could be reused over multiple cycles, retaining 84.1% activity after 7 cycles and 68.7% after 10 cycles. View evidence ↗

      What they found

      The biocatalyst could be reused over multiple cycles, retaining 84.1% activity after 7 cycles and 68.7% after 10 cycles.

      In the paper's own words

      “The immobilized enzyme retained 84.1% of initial activity after 7 cycles and 68.7% after 10 cycles.”

      Page 3

      Found in: Fig 1:

      Read it in the full textOpen PDF at page 3 ↗
    • The estimated cost of treatment is $0.15 per cubic meter of effluent, which is cheaper than Fenton treatment ($0.20-0.50/m³) and ozonation ($0.80-1.20/m³). View evidence ↗

      What they found

      The estimated cost of treatment is $0.15 per cubic meter of effluent, which is cheaper than Fenton treatment ($0.20-0.50/m³) and ozonation ($0.80-1.20/m³).

      In the paper's own words

      “the effective enzyme consumption is 6.8 mg protein per gram of dye degraded, translating to roughly $0.15/m³ of treated effluent at current laccase prices. This is competitive with Fenton treatment ($0.20-0.50/m³) and significantly cheaper than ozonation ($0.80-1.20/m³)”

      Page 4

      Found in: Discussion

      Read it in the full textOpen PDF at page 4 ↗
  5. What it means

    • The authors conclude that the immobilized laccase system is economically viable and competitive with chemical treatments because it maintains over 80% activity for at least 7 reuse cycles. View evidence ↗

      What it means

      The authors conclude that the immobilized laccase system is economically viable and competitive with chemical treatments because it maintains over 80% activity for at least 7 reuse cycles.

      In the paper's own words

      “Magnetic recovery enabled at least 7 reuse cycles above the 80% activity threshold, making the system economically competitive with conventional chemical treatment methods for Nigerian textile wastewater.”

      Page 4

      Found in: Conclusion

      Read it in the full textOpen PDF at page 4 ↗
    • A primary limitation of this method is the 6-hour treatment time, which is slower than the 1-2 hours required for chemical oxidation. View evidence ↗

      What it means

      A primary limitation of this method is the 6-hour treatment time, which is slower than the 1-2 hours required for chemical oxidation.

      In the paper's own words

      “The main limitation is the 6-hour treatment time, which is longer than the 1-2 hours typical for chemical oxidation.”

      Page 4

      Found in: Discussion

      Read it in the full textOpen PDF at page 4 ↗

Visual summary

3 visuals

Illustrations explain the paper; charts are replotted from the paper's own table values.

AI-generated illustration
AI-generated conceptual illustration (amino-functionalized magnetic nanoparticles and laccase enzyme). It explains the idea and does not show study data.↗ Enlarge
Enzyme Immobilization Process
AI-generated conceptual illustration (amino-functionalized magnetic nanoparticles and laccase enzyme). It explains the idea and does not show study data.

AI-generated conceptual illustration (amino-functionalized magnetic nanoparticles and laccase enzyme). It explains the idea and does not show study data.

Open full-size image ↗

Enzyme Immobilization Process

AI-generated conceptual illustration (amino-functionalized magnetic nanoparticles and laccase enzyme). It explains the idea and does not show study data.

View source evidence ↗
Replotted from source data
Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.↗ Enlarge
Thermal half-life at 60 °C (min): Free Laccase vs Immobilized
Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

Open full-size image ↗

Thermal half-life at 60 °C (min): Free Laccase vs Immobilized

Replotted from Table 1 (page 2) of the original paper. Every bar is the paper's own table value.

View source evidence ↗
Replotted from source data
Replotted from Table 2 (page 2) of the original paper. Every bar is the paper's own table value.↗ Enlarge
Free (%) and Immob.(%): Reactive Black 5 vs Acid Orange 7 vs Crystal Violet
Replotted from Table 2 (page 2) of the original paper. Every bar is the paper's own table value.

Replotted from Table 2 (page 2) of the original paper. Every bar is the paper's own table value.

Open full-size image ↗

Free (%) and Immob.(%): Reactive Black 5 vs Acid Orange 7 vs Crystal Violet

Replotted from Table 2 (page 2) of the original paper. Every bar is the paper's own table value.

View source evidence ↗

Figures & tables

From the original paper
Comparison of free and immobilized laccase properties.Table 1Page 2Decolorization efficiency of three textile dyes by free and immobilized laccase after 6 hours.Table 2Page 2Effect of pH on the relative activity of free and immobilized laccase using ABTS as substrate at 25 °C.Figure 1Page 3Operational stability of immobilized laccase over 10 consecutive decolorization cycles with Reactive Black 5 (50 mg/L). Dashed lineFigure 2Page 3
FULL TEXT Original article · reflowed for reading

Introduction

Nigeria's textile industry, concentrated in Ondo, Lagos, and Kano states, generates an estimated 200 million liters of dye-laden wastewater daily, with fewer than 15% of factories operating any form of biological treatment before discharge into rivers and streams [1] . Synthetic dyesparticularly azo compounds that constitute 70% of global dye production are resistant to conventional biological and chemical treatment, persist in aquatic environments, and several are classified as carcinogenic or mutagenic [2] . Advanced oxidation processes using Fenton chemistry or ozone can degrade these dyes but require expensive reagents and generate toxic intermediates [3] . Laccases (EC 1.10.3.2) are multicopper oxidases produced by white-rot fungi that catalyze single-electron oxidation of aromatic substrates coupled with four-electron reduction of O₂ to water. Their broad substrate specificity and use of oxygen rather than hydrogen peroxide as oxidant makes them environmentally benign biocatalysts for dye degradation [4] . The main barrier to industrial adoption is cost: free laccase is denatured by the temperature, pH, and chemical conditions of real effluents, and cannot be recovered for reuse [5] . Immobilization onto solid supports addresses both problems simultaneously. Covalent attachment through bifunctional cross-linkers like glutaraldehyde rigidifies the enzyme's tertiary structure, conferring thermal and chemical stability, while the support enables physical recovery [6] . Magnetic nanoparticles are ideal supports because they combine high surface area (facilitating high enzyme loading) with effortless recovery using an external magnetno centrifugation or filtration required [7] . Amino-functionalized MNPs provide primary amine groups that react with glutaraldehyde to form Schiff bases, creating a molecular spacer between the nanoparticle surface and the enzyme that preserves active site accessibility [8] . This research optimized the immobilization of commercial T. versicolor laccase on amino-MNPs, characterized the resulting biocatalyst, and evaluated its performance for degrading three structurally diverse textile dyes representative of those found in Nigerian industrial effluents [9] .

Reagents and Chemicals

Laccase from Trametes versicolor (lyophilized powder, ≥10 U/mg, Sigma-Aldrich), 2, 2′-azino-bis (3ethylbenzothiazoline-6-sulphonic acid) (ABTS, ≥98%), glutaraldehyde (25% aqueous solution), 3aminopropyltriethoxysilane (APTES, 99%), iron (II) chloride tetrahydrate, iron (III) chloride hexahydrate, and ammonium hydroxide (28-30%) were from Sigma-Aldrich. Reactive Black 5 (RB5, CI 20505), Acid Orange 7 (AO7, CI 15510), and Crystal Violet (CV, CI 42555) were obtained from Alfa Aesar. Bradford reagent was used for protein quantification with bovine serum albumin standards [10] .

Materials and Methods

Materials and Methods

Materials

Research was conducted at Federal University of Technology Akure, Akure, Ondo State, Nigeria, from March to October 2023. No ethical approval was required. Magnetic nanoparticles were synthesized by alkaline coprecipitation: FeCl₂•4H₂O (2.0 g) and FeCl₃•6H₂O (5.2 g) were dissolved in 100 mL deoxygenated water at 80 °C, and NH₄OH was added dropwise under nitrogen with vigorous stirring until pH 10. The black precipitate was collected magnetically, washed to neutral pH, and dried at 60 °C. Surface functionalization used APTES (2 mL in 50 mL ethanol, 12 h reflux). TEM (JEOL 1010) and XRD (Bruker D8) confirmed crystalline Fe₃O₄ with ~15 nm particle diameter [11] .

Methods

Immobilization procedure: Amino-MNPs (100 mg) were Activated by incubation with 2.5% glutaraldehyde in phosphate buffer (pH 7.0) for 2 h at room temperature. After magnetic washing (3×), activated MNPs were mixed with laccase solution (10 mg/mL in 50 mM citrate-phosphate buffer, pH 5.0) and incubated at 4 °C for 12 h with gentle agitation. The immobilized enzyme was magnetically collected, washed with buffer to remove unbound protein, and stored at 4 °C. Immobilization efficiency was calculated from protein mass balance using the Bradford assay [12] . Laccase activity was measured using ABTS oxidation (1 mM in 50 mM sodium acetate buffer, pH 4.5) monitored at 420 nm (ε = 36,000 M⁻¹cm⁻¹). One unit of activity was defined as the amount of enzyme oxidizing 1 μmol ABTS per minute at 25 °C. PH profiles were determined over pH 2.5-7.5 using citrate-phosphate buffers, and temperature profiles from 20 to 80 °C. Thermal stability was assessed by incubating enzyme at 60 °C and measuring residual activity at intervals over 4 h [13] . Dye decolorization experiments used 50 mg/L dye solutions in 50 mM citrate-phosphate buffer (pH 5.0) with 50 mg immobilized enzyme preparation (or equivalent free enzyme activity) at 40 °C and 150 rpm for 6 h. Decolorization was quantified spectrophotometrically at each dye's maximum absorbance wavelength (RB5: 597 nm; AO7: 484 nm; CV: 590 nm). Reusability was tested over 10 consecutive cycles with the same batch of immobilized enzyme, magnetically recovering the biocatalyst between cycles and adding fresh dye solution each time [14] .

Instrumentation

UV-Vis measurements used a Shimadzu UV-1900i spectrophotometer with temperature-controlled cuvette holder. Magnetic separation employed a NdFeB permanent magnet (1.2 T surface field). Protein quantification used a BioRad SmartSpec Plus spectrophotometer at 595 nm. TEM samples were prepared by depositing dilute MNP suspensions on carbon-coated copper grids. XRD operated at 40 kV/40 mA with Cu Kα radiation (2θ range 20-70°). FTIR (PerkinElmer Spectrum Two, ATR) confirmed successful surface functionalization and enzyme attachment. Immobilization shifted the pH optimum from 4.5 to 5.0, a well-documented effect attributed to the microenvironment created by amino groups on the MNP surface, which produces a local pH higher than the bulk solution. This shift is advantageous for treating real textile effluents, which typically have pH values of 5-8 [4] . The temperature optimum increased from 50 °C to 60 °C, reflecting the structural rigidity imparted by multipoint covalent attachment. The Kₘ increase from 0.18 to 0.27 mM indicates slightly reduced substrate affinity, consistent with partial diffusional limitation and possible steric restriction at the active site entrance due to the glutaraldehyde tether. However, the 6.7-fold increase in thermal half-life at 60 °C (28 to 187 min) and doubled storage stability (41% to 83% after 30 days) more than compensate for this modest kinetic penalty [6] . Immobilized laccase outperformed the free enzyme for all three dyes, despite its lower Vₘₐₓ value. The apparent contradiction is explained by the immobilized enzyme's superior operational stability during the 6-hour reaction: free laccase loses activity progressively at 40 °C and the slightly Acidic pH, while the immobilized form maintains catalytic function throughout. Acid Orange 7 was the most efficiently degraded (97.2%), consistent with monoazo dyes being more readily oxidized than the diazo structure of Reactive Black 5 or the triphenylmethane scaffold of Crystal Violet [15] .

Results

Results

Fig 1:

Effect of pH on the relative activity of free and immobilized laccase using ABTS as substrate at 25 °C. Reusability data showed a gradual decline in activity over 10 cycles. The immobilized enzyme retained 84.1% of initial activity after 7 cycles and 68.7% after 10 cycles. The decline reflects a combination of enzyme inactivation during each 6-hour reaction, mechanical damage to some nanoparticles during magnetic recovery, and accumulation of dye degradation products on the MNP surface that block substrate access. Between cycles 1-7, the biocatalyst remained above the 80% activity threshold commonly accepted as the minimum for industrial enzyme reuse, making this system economically viable for at least 7 batch treatments before replacement [16] . FTIR spectra provided molecular evidence for successful immobilization. The amino-MNPs showed characteristic peaks at 3380 cm⁻¹ (N-H stretching), 1625 cm⁻¹ (N-H bending), and 1030 cm⁻¹ (Si-O-Si from APTES). After glutaraldehyde activation, a new peak at 1720 cm⁻¹ (C=O stretching of aldehyde) appeared. Following laccase conjugation, the amide I band at 1648 cm⁻¹ and amide II band at 1538 cm⁻¹ confirmed protein attachment, while the aldehyde peak diminished, indicating Schiff base formation between aldehyde and enzyme amine groups [8] . XRD patterns of the immobilized preparation retained all characteristic Fe₃O₄ diffraction peaks (2θ = 30.1°, 35.5°, 43.1°, 57.0°, 62.6°) with no significant peak broadening, confirming that the surface modification and immobilization process did not alter the crystalline magnetic core structure. Kinetic analysis of dye decolorization revealed that the reaction followed pseudo-first-order kinetics for all three dyes. Rate constants were 0.48 h⁻¹ for Acid Orange 7, 0.39 h⁻¹ for Reactive Black 5, and 0.34 h⁻¹ for Crystal Violet. The faster degradation of monoazo AO7 compared to diazo RB5 correlates with the number of azo bonds requiring oxidative cleavage. Crystal Violet's slower rate despite its single chromophore center reflects the steric demand of its three dimethylaminophenyl groups, which hinder approach to the enzyme's T1 copper site. These kinetic differences have practical implications for reactor design, suggesting that mixed-dye effluents might benefit from staged treatment with longer residence times allocated to recalcitrant dyes [15] .

Discussion

The 82.4% immobilization efficiency achieved here is among the highest reported for laccase on magnetic supports, where typical values range from 50-80% [7] . The optimization of glutaraldehyde concentration was critical: below 1.5%, insufficient cross-linking left most enzyme weakly adsorbed rather than covalently attached, while above 3%, intermolecular cross-linking between enzyme molecules created multilayer protein aggregates with poor catalytic activity due to blocked active sites. The optimal 2.5% glutaraldehyde provided the right balance of covalent anchoring without excessive cross-linking [8] . The 94.7% decolorization of Reactive Black 5 is particularly notable because this diazo dye is among the most recalcitrant commercial dyes. Its structure contains two azo bonds flanked by sulfonated naphthalene groups that resist oxidation. Laccase attacks the hydroxyl-substituted naphthalene moiety, generating radical intermediates that undergo further non-enzymatic reactions leading to azo bond cleavage and chromophore destruction [15] . The complete degradation pathway likely produces sulfonated aminonaphthalenes as primary products, which are less colored and less toxic than the parent dye, though a full ecotoxicity assessment of the treated effluent would be necessary before discharge [17] . Compared to physicochemical treatment methods, the immobilized laccase system offers several advantages: operation at near-ambient temperature (40 °C vs >100 °C for Fenton), neutral pH (5.0 vs pH 2-3 for Fenton), no requirement for H₂O₂ or UV light, and no sludge generation. The main limitation is the 6-hour treatment time, which is longer than the 1-2 hours typical for chemical oxidation. For a factory producing 100 m³/day of dye effluent, this could be addressed through continuous flow in a packed-bed reactor containing the magnetic biocatalyst retained by an external magnetic field [18] . The enzyme cost calculation is favorable: at a protein loading of 47.3 mg/g MNPs and 7 reuse cycles, the effective enzyme consumption is 6.8 mg protein per gram of dye degraded, translating to roughly $0.15/m³ of treated effluent at current laccase prices. This is competitive with Fenton treatment ($0.20-0.50/m³) and significantly cheaper than ozonation ($0.80-1.20/m³) [19] .

Conclusion

Laccase from Trametes versicolor was successfully immobilized on amino-functionalized Fe₃O₄ magnetic nanoparticles with 82.4% efficiency and 47.3 mg/g protein loading. The immobilized enzyme showed enhanced thermal stability (6.7-fold increase in half-life at 60 °C), broadened pH optimum favorable for real effluent conditions, and superior dye decolorization performance (91.3-97.2% removal for three structurally diverse textile dyes). Magnetic recovery enabled at least 7 reuse cycles above the 80% activity threshold, making the system economically competitive with conventional chemical treatment methods for Nigerian textile wastewater.

Figures and tables from the paper

Table 1. Comparison of free and immobilized laccase properties.
PropertyFree LaccaseImmobilized
pH optimum4.55.0
Temperature optimum (°C)5060
Kₘ for ABTS (mM)0.180.27
Vₘₐₓ (U/mg protein)12.49.7
Thermal half-life at 60 °C (min)28187
Storage stability (30 d, 4 °C)41% residual83% residual

Table text extracted from the original PDF; superscript letters are shown inline. The original table image is below.

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Comparison of free and immobilized laccase properties.↗ Enlarge
Table 1
Comparison of free and immobilized laccase properties.

Comparison of free and immobilized laccase properties.

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Original paper tableSource PDF · page 2 ↗
Table 2. Decolorization efficiency of three textile dyes by free and immobilized laccase after 6 hours.
DyeTypeλmax (nm)Free (%)Immob.(%)
Reactive Black 5Diazo59787.394.7
Acid Orange 7Monoazo48491.897.2
Crystal VioletTriphenyl59082.191.3

Table text extracted from the original PDF; superscript letters are shown inline. The original table image is below.

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Decolorization efficiency of three textile dyes by free and immobilized laccase after 6 hours.↗ Enlarge
Table 2
Decolorization efficiency of three textile dyes by free and immobilized laccase after 6 hours.

Decolorization efficiency of three textile dyes by free and immobilized laccase after 6 hours.

Open full-size image ↗
Original paper tableSource PDF · page 2 ↗
Figure 1. Effect of pH on the relative activity of free and immobilized laccase using ABTS as substrate at 25 °C.
Effect of pH on the relative activity of free and immobilized laccase using ABTS as substrate at 25 °C.↗ Enlarge
Figure 1
Effect of pH on the relative activity of free and immobilized laccase using ABTS as substrate at 25 °C.

Effect of pH on the relative activity of free and immobilized laccase using ABTS as substrate at 25 °C.

Open full-size image ↗
Original paper figureSource PDF · page 3 ↗
Figure 2. Operational stability of immobilized laccase over 10 consecutive decolorization cycles with Reactive Black 5 (50 mg/L). Dashed line
Operational stability of immobilized laccase over 10 consecutive decolorization cycles with Reactive Black 5 (50 mg/L). Dashed line↗ Enlarge
Figure 2
Operational stability of immobilized laccase over 10 consecutive decolorization cycles with Reactive Black 5 (50 mg/L). Dashed line

Operational stability of immobilized laccase over 10 consecutive decolorization cycles with Reactive Black 5 (50 mg/L). Dashed line

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Original paper figureSource PDF · page 3 ↗

References

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