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Wang, T. Textile Dye Biodecolorization by MnP. Encyclopedia. Available online: https://encyclopedia.pub/entry/12900 (accessed on 25 April 2024).
Wang T. Textile Dye Biodecolorization by MnP. Encyclopedia. Available at: https://encyclopedia.pub/entry/12900. Accessed April 25, 2024.
Wang, Tao. "Textile Dye Biodecolorization by MnP" Encyclopedia, https://encyclopedia.pub/entry/12900 (accessed April 25, 2024).
Wang, T. (2021, August 07). Textile Dye Biodecolorization by MnP. In Encyclopedia. https://encyclopedia.pub/entry/12900
Wang, Tao. "Textile Dye Biodecolorization by MnP." Encyclopedia. Web. 07 August, 2021.
Textile Dye Biodecolorization by MnP
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Manganese peroxidase (MnP) is an oxidoreductase with ligninolytic activity and is a promising biocatalyst for the biodegradation of hazardous environmental contaminants, and especially for dye wastewater decolorization.

manganese peroxidase biodecolorization dye wastewater immobilization recombinant enzyme

1. Introduction

The textile industry produces large quantities of wastewater containing different types of dyes used during the dyeing process, which cause great harm to the environment [1][2]. Many dyes and their intermediate metabolites have been identified as mutagenic, teratogenic, or carcinogenic, and represent serious health threats to living ecosystems [3].
At present, the treatment of dye wastewater mainly relies on physical or chemical management techniques, including chemical reduction, adsorption, ionizing radiation, precipitation, flocculation and flotation, membrane filtration, electric coagulation, electrochemical destruction, and ion exchange ozonation [4][5]. These technologies have obvious shortcomings such as the excessive use of chemicals, sludge production, expensive factory requirements or high operating expenses, low decolorization efficiencies, and the inability to handle large numbers of dyes with different structures, so they are not economically suitable for large-scale wastewater decolorization [6].
The current focus is to reduce toxicity and develop an efficient, economical, and green dye detoxification and decolorization technology. Compared with physical and chemical methods, biological methods offer beneficial and effective prospects due to their economical and environmentally friendly advantages, as well as being simple to use, safe, and efficient, with no secondary pollution [7][8]. Therefore, biotechnology is considered the best choice to degrade and remove these pollutants effectively. In the biotechnology field, enzyme biocatalysis is currently the main research area due to its broad application prospects [9][10].
Manganese peroxidases (EC 1.11.1.13; MnPs) are a family of heme-containing glycoproteins belonging to the oxidoreductase group. It was discovered in Phanerochaete chrysosporium and is also found in many bacteria and white-rot fungi (WRF) [11][12][13][14]. There are different MnPs in nature with differentiated properties. For example, long and short MnPs were reported in WRF associated with the presence/absence of the C-terminal tail extension, and these showed different catalytic and stability properties [15]. According to the residues of the Mn2+-binding site, three novel subfamilies of MnP were described in Agaricales including MnP-ESD (Glu/Ser/Asp Mn2+-oxidation site), MnP-DGD (Asp/Gly/Asp Mn2+-oxidation site), and MnP-DED (Asp/Glu/Asp Mn2+-oxidation site) [16]. However, the Mn2+-binding site is not the unique feature of MnPs, because versatile peroxidases (VPs), which evolved directly from MnPs, also possess such a site and can oxidize Mn2+ to Mn3+ [17].
For enzyme applications, MnPs can catalyze the peroxide-dependent degradation of a variety of toxic dye pollutants, phenolic compounds, antibiotics, and polycyclic aromatic hydrocarbons, so are promising biocatalysts for hazardous environmental contaminants biodegradation [18][19]. Moreover, the use of MnPs is suitable for dye wastewater decolorization as the process is simple and the enzyme can be recycled, thus reducing operating costs [20][21][22].

2. The Crystal Structure of MnPs

The crystal structure of an enzyme provides information on the catalytic mechanism and for potential in-depth design and transformation, and for realizing the green biotechnological use of enzymes [23][24][25].
The heme conformation of MnP is similar to that of lignin peroxidase (LiP) and is evolutionarily conserved [26]. In its resting-state form, MnP is a strongly helical protein containing a Fe3+ penta-coordinated structure with the porphyrin ring of the heme cofactor and a proximal histidine, with the sixth coordination position open for H2O2 [27].
To date, several crystal structures of MnP from different sources have been reported, and the highest-resolution crystal structures (~0.93Å) of MnP complexed with Mn2+ (Mn-MnP) are shown in Figure 1 [28]. The conserved Ca2+ ions are important for the stability of the protein [29]; these are indicated as gold yellow spheres and the position of the Mn2+ substrate is shown in violet. The active site is composed of three highly conserved amino acids (Glu35, Glu39, and Asp179) and one heme propionate. The Mn2+ substrate binds in the center of the active site, and the heme propionate (HEM) is located in the internal hydrophobic cavity of the enzyme. The spatial structure of HEM is further stabilized by four hydrogen bonds (green dashed line), two electrostatic interactions (orange dashed line), and some other weak interactions. The catalytic site of heme peroxidases is strongly conserved, with only minor variations occurring in the replacement of Phe with Trp in several enzymes such as ascorbate peroxidase and cytochrome c. The Asp–His pair (242 and 173, respectively) is also conserved.
Figure 1. The overall structure (A), active site structure (B,C), and interaction mode (D) of Mn–MnP refined at 0.93 Å resolution [28]. PDB ID: 3M5Q.

3. MnP Catalysis

At the beginning of the catalytic cycle, H2O2 or organic peroxide binds to the enzyme in resting state in ferric (Fe3+) form (Figure 2). This process releases one molecule of H2O and forms MnP–compound I (Fe4+-oxo-porphyrin radical complex), with two oxidation equivalents. This oxidizes Mn2+ to Mn3+, forming MnP–compound II (Fe4+-oxo-porphyrin complex). Immediately afterwards, the MnP–compound II combines with Mn2+ in a similar manner to generate Mn3+, releasing one molecule of H2O, and is reduced to the original state of ferric MnP, completing the catalytic cycle [30].
Figure 2. The MnP catalytic cycle [30].
The MnP catalytic cycle resembles that of other lignin and heme peroxidases in the presence of native Fe3+ enzymes and two reactive intermediates [31]. However, in contrast to other peroxidases, MnP preferentially uses Mn2+ as the substrate, converting it to the strong oxidation state of Mn3+ through a series of redox reactions [32].

4. Application of Unmodified MnPs in the Decolorization of Dye Wastewater

Table 1 contains a summary of recent studies on the breakdown and decolorization of textile-derived dye compounds by microbial MnPs.
Table 1. Recent applications of unmodified MnPs in dye decolorization.

Source

Types of Dyes

Initial Concentration of Dyes

Removal Rate

Time Cost

Reference

Microbial consortium SR

Crystal Violet

20 mg/L

63%

6 days

[20]

Cresol Red

100 mg/L

93%

CBB G250

100 mg/L

96%

Trametes pubescens strain i8

Acid Blue 158

50 μM

95%

24 h

[22]

Poly R-478

88%

Remazol Brilliant Violet 5R

76%

Direct Red 5B

66%

Indigo Carmine

64%

Methyl Green

50%

Cibacet Brilliant Blue BG

46%

Remazol Brilliant Blue Reactif

42%

Aspergillus terreus GS28

Direct Blue-1

100 mg/L

98.4%

168 h

[33]

Bjerkandera adusta strain CX-9

Acid Blue 158

50 μM

91%

12 h

[34]

Poly R-478

80%

Cibacet Brilliant Blue BG

77%

Remazol Brilliant Violet 5R

70%

Trametes sp.48424

Indigo Carmine

100 mg/L

94.6%

18 h

[35]

Remazol Brilliant Blue R

85.0%

Remazol Brilliant Violet 5R

88.4%

Methyl Green

93.1%

Microbial consortium ZSY

Metanil Yellow G

100 mg/L

93.39%

48 h

[36]

Microbial Consortium ZW1

Methanil Yellow G

100 mg/L

93.3%

16 h

[37]

Trichoderma harzianum

Alizarin Blue Black B

0.03%

92.34%

14 days

[38]

Phanerochaete chrysosporium CDBB 686

Congo Red

50 ppm

41.84%

36 h

[39]

Poly R-478

56.86%

Methyl Green

69.79%

Bjerkandera adusta CCBAS 930

Alizarin Blue Black B

0.01%

86.5%

20 days

[40]

Acid Blue 129

89.22%

Cerrena unicolor BBP6

Congo Red

100 mg/L

53.9%

12 h

[41]

Methyl Orange

77.6%

12 h

Remazol Brilliant Blue R

81.0%

5 h

Bromophenol Blue

62.2%

12 h

Crystal Violet

80.9%

12 h

Azure Blue

63.1%

24 h

Phanerochaete chrysosporium

Indigo Carmine

30 mg/L

90.18%

6 h

[42]

Trametes versicolor

Dye mixture

(Brilliant Blue FCF

and

Allura Red AC)

100 mg/L

80.45%

14 days

[43]

Irpex lacteus

86.04%

19 days

Bjerkandera adusta

82.83%

9 days

Ceriporia lacerata ZJSY

Congo Red

100 mg/L

90%

48 h

[44]

Bacillus cohnni RKS9

Congo Red

100 mg/L

99%

12 h

[45]

Schizophyllum commune IBL-06

Solar Brilliant Red 80

0.01%

100%

3 days

[46]

Irpex lacteus CD2

Remazol Brilliant Violet 5R

50 mg/L

92.8%

5 h

[47]

Remazol Brilliant Blue R

87.1%

5 h

Indigo Carmine

91.5%

5 h

Direct Red 5B

82.4%

36 h

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