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Article

Iron Porphyrin as a Cytochrome P450 Model for the Degradation of Dye

by
Dan-Dan Ren
1,2,†,
Xiaoyan Lu
2,*,†,
Li-Ping Zhou
2,
Huanghongjun Tian
2,
Shuang Wang
2,
Lu-Fang Ma
1,2,* and
Dong-Sheng Li
1
1
College of Materials and Chemical Engineering, China Three Gorges University, Yichang 443002, China
2
Henan Key Laboratory of Function-Oriented Porous Materials, College of Chemistry and Chemical Engineering, Luoyang Normal University, Luoyang 471934, China
*
Authors to whom correspondence should be addressed.
†
These authors contributed equally to this work.
Molecules 2022, 27(22), 7948; https://doi.org/10.3390/molecules27227948
Submission received: 9 October 2022 / Revised: 13 November 2022 / Accepted: 14 November 2022 / Published: 17 November 2022
(This article belongs to the Special Issue Applications of Metal Complexes)
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Versions Notes

Abstract

:
Organic dyes are widely used in the textile, biological, medical and other fields. However, a serious environmental problem has appeared because of the presence of organic dyes in industrial aqueous effluents. Thus, the efficient treatment of organic dyes in industrial wastewaters is currently in real demand. The current study investigated the oxidative degradation of the organic dye gentian violet by meso-tetra(carboxyphenyl) porphyriniron(III), [FeIII(TCPP)] as a cytochrome P450 model and iodosylbenzene (PhIO) as an oxidant at room temperature. The degradation reaction was monitored by UV–vis absorption spectroscopy via the observation of UV–vis spectral changes of the gentian violet. The results showed that the efficiency of catalyzed degradation reached more than 90% in 1 h, indicating the remarkable oxidative degradation capacity of the [FeIII(TCPP)]/PhIO system, which provided an efficient approach for the treatment of dyeing wastewater.

1. Introduction

As is well known, dyes are widely used in the papermaking, textile, food, cosmetics and other industries [1,2]. With the increase in material and cultural needs, the dye industry continues to develop and grow. About 300–400 million tons of industrial waste are discharged into rivers every year [3,4]. These persistent organic dyes found in industrial aqueous effluents can accumulate in the body after entering the human system and result in serious health problems in the cardiovascular, endocrine, nervous and immune systems, which may even be passed to the next generation. Among the various dyes, triphenylmethane dyes, for example gentian violet, are the largest and most versatile, and they play a predominant role in human and veterinary medicine and the textile processing industry [5]. However, gentian violet is difficult to degrade and can remain in the environment for a long period. It is toxic to aquatic and terrestrial life, and it is considered a mitotic poisoning agent and a potent clastogene [6]. Thus, the efficient treatment of gentian violet in industrial wastewaters is currently in real demand [7].
In the past few decades, people have invested a lot of energy into the treatment of dye-containing effluents [8,9,10,11,12,13,14,15,16]. Various methods to degrade dyes, including chemical [17,18], physical [19,20,21,22] and biological [23,24] methods, have been developed and widely applied for the degradation of organic dyes. However, these traditional methods have certain limitations. For example, air-bubbling visible-light photocatalytic degradation can eliminate pollutants in wastewater under mild conditions [25,26,27]. However, due to the small active area of photocatalysts, insufficient light absorption and instantaneous electron hole separation, the photocatalytic degradation activity of this method is reduced. In addition, adsorption is the most common technology used to remove pollution from textile, printing and dyeing industrial wastewater [28,29], but the adsorption capacity of this method is generally low, and new adsorbents are still being developed. Another example is the microbial treatment of printing and dyeing wastewater, which is considered to be an economical and feasible method without secondary pollution, yet biodegradation has the disadvantages of it being unstable and time-consuming. Thus, it is urgent and necessary to develop new methods to degrade dye-containing wastewater.
Enzymes are among the most sophisticated catalysts due to their unparalleled catalytic specificity and efficiency. For example, cytochrome P450 is able to catalyze a variety of oxidation reactions, including the oxygenation of aromatics, hydroxylation of C–H bonds and epoxidation of double bonds at room temperature and atmospheric pressure [30]. However, due to their high cost, highly restricted catalytic conditions and fragile nature, the practical applications of enzymes have been hindered. To overcome these problems of enzymes for practical applications, biomimetic systems have subsequently emerged as an effective approach to synthesize highly efficient biomimetic catalysts via mimicking certain key features of enzymes [31,32].
Metalloporphyrins, as a representative model of cytochrome P450, have been extensively studied, in which a number of metalloporphyrins have been used to catalyze the degradation of dyes [33,34,35,36,37,38,39,40,41]. For example, manganese porphyrins, manganese tetra-(p-carboxylphenyl) porphyrin (MnP(COOH)4) and manganese tetra-(p-methylpyridium) porphyrin [Mn(TMPyP)], among others, have been used to catalyze the decolorization of azo dyes with H2O2 as an oxidant in the presence of imidazole in aqueous solution and in nonaqueous solvents [40,41,42]. Meyer and coworkers investigated the oxidative degradation of dyes by meso-tetrakis(1-methylpyridinium-4-yl)porphyrinatomanganese(III), [MnIII(tmpyp)], in aqueous solution, which showed that it is an efficient catalysts for the oxidation of various substrates, and high-oxidation-state oxomanganese(IV) and oxomanganese(V) intermediates have been proposed to play a significant role in these reactions [39,43,44,45,46,47,48,49,50,51]. Very recently, Meyer and coworkers also reported an iron porphyrin, meso-tetrakis(1-methylpyridinium-4-yl)prophyrinatoiron(III) ([FeIII(tmpyp)]) as an efficient catalyst to degrade azo dyes using meta-chloroperoxy benzoic acid (m-CPBA) as an oxidant in aqueous solution at room temperature [52]. They found that the dye degradation rate was determined by the concentrations of [FeIII(tmpyp)], m-CPBA, dye and surfactants and the pH value of the solution, and they suggested that [FeIII(tmpyp)] is transformed into a high-valent iron(IV)-oxo porphyrin π-cation radical species [FeIV(O)(tmpyp+•)], referred to as compound I (Cpd-I), within 20–30 ms followed by the formation of relatively stable [FeIV(O)(tmpyp)], referred to as compound II (Cpd-II) by spectral analyses and kinetic data. However, very limited ironporphyrins used as cytochrome P450 models have been reported to catalyze the oxidative degradation of dyes [35,36,38,42].
The ironporphyrin, 5,10,15,20-tetra(4-carboxyphenyl)porphyrinato iron(III) chloride, [FeIII(TCPP)], as a cytochrome P450 model, has been reported to be grafted in metal–organic frameworks, which have been widely applied in the fields of photodynamic therapy, signal probing, photocatalytic degradation, the photocatalytic reduction of carbon dioxide and the selective reduction of nitrogen to ammonia [53,54,55,56,57,58]. However, the degradation of dyes by [FeIII(TCPP)] has rarely been studied [52,59]. Herein, we investigated [FeIII(TCPP)] as a cytochrome P450 model for the oxidative degradation of a selected dye, gentian violet, employing iodosylbenzene (PhIO) as the oxidant (Figure 1) in methanol at 30 ℃. The degradation reaction of gentian violet was monitored by UV–vis absorption spectroscopy via the observation of UV–vis spectral changes in the gentian violet. The [FeIII(TCPP)]/PhIO system gave a remarkable oxidative degradation of gentian violet.

2. Materials and Methods

2.1. Materials and Instruments

All reagents and solvents were commercially purchased and used without further purification. Dichloromethane (DCM), methanol and sodium hydroxide (NaOH) were obtained from Damao Chemical Reagent Factory), Tianjin, China. Ethyl ether (Luoyang Chemical Reagent Factory, Luoyang, China), gen-tian violet (Tianjin Guangfu Fine Chemical Research Institute, Tianjin, China) and 5,10,15,20-tetra(4-carboxyphenyl)porphyrinato iron(III) chloride ([FeIII(TCPP)] (Bide Pharmatech Ltd., Shanghai, China) were used as provided. (Diacetoxyiodo)benzene (PhI(OAc)2) and 3-Chloroperoxybenzoic acid (m-CPBA) were provided by Shanghai Macklin Biochemical Co., Ltd., Shanghai, China. The water used in all experiments was distilled water. UV–vis absorption spectra were recorded on a Hitachi U-3010 spectrometer.

2.2. Preparation of Iodosylbenzene (PhIO)

Iodosylbenzene (PhIO) was prepared by a previously reported method [60]. A total of 8 g of (diacetoxyiodo)benzene (PhI(OAc)2) was weighed and placed in a 250 mL beaker and wrapped in tin foil for light protection. A total of 4.5 g of sodium hydroxide (NaOH) was weighed in a 50 mL beaker and dissolved with 30 mL H2O. The NaOH solution was slowly added to the beaker containing the solution of PhI(OAc)2 within 0.5 h, which was then stirred vigorously at room temperature for 1 h. Then, 20 mL H2O was added and continuously stirred for 1.5 h. The resulting solution was then filtered and washed with water until the pH value of filtrate reached 7, and then the precipitate was washed with dichloromethane and ethyl ether, respectively, dried and kept in a refrigerator for further use. Its purity was periodically controlled by iodometric titration [61].

2.3. Determination of Concentration of Gentian Violet

The concentration of gentian violet in the resulting solution was determined by a UV–vis spectrophotometer with a quartz cuvette (path length = 10 mm) in the wavelength range of 200–800 nm. The UV–vis spectrum of 0.05 mM gentian violet in MeOH exhibited a distinct absorption band at 578 nm (λmax) with an absorbance of 1.022 (Figure 2a), and its extinction coefficient (ε) was then calculated to be 20,440 M−1 cm−1 using Beer’s law, A = εc, where A is the absorbance at 578 nm and c is the concentration of gentian violet. Thus, the concentration of gentian violet in the reaction solution could be determined from the absorption band at λmax = 578 nm following Beer’s law. The UV–vis spectrum of the [FeIII(TCPP)] in MeOH showed a distinct absorption band at 414 nm (Figure 2b), which did not have an influence on the absorption band of gentian violet at 578 nm.

2.4. Degradation of Gentian Violet

The stock solution of gentian violet with a concentration of 10 mM and [FeIII(TCPP)] with a concentration of 0.315 mM in MeOH were prepared, which were kept for further use. It should be noted that the stock solution of PhIO (10 mM) was reconfigured with each use.

2.4.1. General Procedure for the Effect of PhIO Concentration on Degradation of Gentian Violet

In a typical experiment, 160 μL of the stock solution of [FeIII(TCPP)] and 50 μL of the stock solution of gentian violet were put in 10 mL of MeOH to give a final concentration of 0.005 mM [FeIII(TCPP)] and 0.05 mM gentian violet. Then, 1 equiv, 2 equiv, 3 equiv, 4 equiv and 5 equiv of PhIO (relative to gentian violet, same as below) were added into the solution, respectively. The reaction mixture was stirred in a water bath at 303 K for 2.5 h. After that, the concentration of gentian violet in the resulting solution was determined by an ultraviolet–visible (UV–vis) spectrophotometer. Control experiments using [FeIII(TCPP)] or PhIO alone in gentian violet solution were performed in parallel. Reactions were performed at least in triplicate, and the data reported represent the average of these reactions.

2.4.2. General Procedure for the Effect of Reaction Time on Degradation of Gentian Violet

In a typical experiment, 240 μL of the stock solution of [FeIII(TCPP)] and 75 μL of the stock solution of gentian violet were put in 15 mL of MeOH, and then 1–5 equiv of PhIO were added into this solution, respectively. Then, the reaction mixture was stirred in a water bath at 303 K. A total of 2 mL of each solution was taken at 0.5 h, 1 h, 1.5 h, 2 h and 2.5 h, respectively, to measure the UV–vis spectra. Reactions were performed at least in triplicate, and the data reported represent the average of these reactions.

3. Results and Discussion

The UV–vis spectra of the gentian violet and [FeIII(TCPP)] in MeOH exhibited a distinct absorption band at 578 nm and 414 nm, respectively, which indicated that their absorption peaks had no effect on each other. Thus, using UV–vis spectroscopy to monitor the concentration changes in the gentian violet was a suitable method. The degradation of the gentian violet was examined at fixed concentrations of catalyst [FeIII(TCPP)] and gentian violet dye in MeOH at 303 K using m-CPBA and PhIO as the oxidant, respectively, at preliminary experiments. No spectral change was observed when using 5 equiv of m-CPBA and reacting for 2.5 h. However, the color of the reaction solution changed from purple to colorless when using 5 equiv of PhIO and reacting for 2.5 h (Figure 3). Therefore, herein, PhIO and [FeIII(TCPP)] were employed as the oxidant and catalyst, respectively, for the degradation of the gentian violet.
The effect of PhIO concentration on the degradation of the gentian violet was first studied at fixed concentrations of [FeIII(TCPP)] and gentian violet in the [FeIII(TCPP)]/PhIO system. A typical set of PhIO concentration-dependent spectral absorptions recorded for the [FeIII(TCPP)]-catalyzed degradation of gentian violet in MeOH at 303 K is shown in Figure 4. The absorbance band at 578 nm, which was due to the gentian violet, decreased when increasing the concentration of PhIO, and it provided a 98% degradation efficiency when adding 5 equiv of PhIO (Table 1). The absorbance at 414 nm, which was due to the [FeIII(TCPP)], exhibited almost no change (Supplementary Materials Figure S1), which indicated that the catalyst [FeIII(TCPP)] was stable during the degradation of the gentian violet. No spectral changes were observed in the absence of [FeIII(TCPP)] or PhIO (Supplementary Materials, Figure S2). The spectral measurements confirmed that the presence of both [FeIII(TCPP)] and PhIO was essential for the degradation of the gentian violet and a high concentration of PhIO was beneficial in improving the degradation efficiency.
The effect of the reaction time on the degradation of the gentian violet was further examined at fixed concentrations of [FeIII(TCPP)] and gentian violet in the [FeIII(TCPP)]/PhIO system, and the results are presented in Figure 5, Table 2 and Figures S3–S6 in the Supplementary Materials. As shown in Figure 5 and Table 2, when using 1 equiv of PhIO, the degradation rate was the slowest and the degradation efficiency of gentian violet was the lowest compared with that of 2–5 equiv of PhIO. The degradation efficiency was basically unchanged after 2 h due to the insufficient amount of oxidant. When using 2 equiv and 3 equiv oxidants, although the corresponding degradation efficiency of gentian violet increased, the degradation rates were slow, and the degradation efficiency was only 65% and 79% after reacting for 2.5 h, respectively. When 4 equiv oxidant was used, with the increase in the reaction time, the degradation efficiency of gentian violet increased to 90%, but it remained almost unchanged after 2 h. When using 5 equiv oxidant, the degradation efficiency of gentian violet reached 75% within 0.5 h and 94% within 1 h, showing a remarkable degradation of gentian violet. The degradation products of the gentian violet produced by the [FeIII(TCPP)]/PhIO system after color removal were detected by GC-MS (Supplementary Materials, Figure S7). However, only iodobenzene (PhI) with a molecular weight of 204 was shown in the GC-MS results, which came from the reduction of PhIO. No product of the gentian violet was observed, which may have been due to the formation of high-boiling-point products, which could not be detected by GC-MS.
The above experimental results are summarized in Figure 6, which indicated that with the increase in PhIO concentration and reaction time, the degradation efficiency of gentian violet increased, and it was up to more than 90% within 1 h when using 5 equiv of PhIO, showing a high catalytic degradation efficiency of the [FeIII(TCPP)]/PhIO system. Generally, the iron(IV)-oxo porphyrin π-cation radical species [FeIV(O)(porph+•)] was proposed as the active species, which plays a major role in the catalytic oxidation process of iron porphyrin. Kong et al. proposed that an iron(IV)-oxo porphyrin π-cation radical, generated from the heterolytic cleavage of the O-O bond in H2O2 catalyzed by hemin, may play a major role in dye degradation [62]. Meyer et al. investigated the oxidative degradation of azo dyes by [FeIII(tmpyp)] and m-CPBA in aqueous solution at room temperature and suggested that [FeIV(O)(tmpyp+•)] was capable of oxidatively breaking down the naphthalene core of azo dyes [52]. Thus, based on the previously suggested mechanisms [52,62] and the data obtained from the various experiments described above in the [FeIII(TCPP)]/PhIO system, it was assumed that the reaction between [FeIII(TCPP)] and PhIO generated a transient intermediate [FeIV(O)(TCPP+•)], which rapidly interacted with gentian violet to make the gentian violet degrade and regenerate the catalyst [FeIII(TCPP)].

4. Conclusions

Various methods have been developed and widely applied for the degradation of gentian violet. However, these traditional methods have certain limitations. The traditional physical method is inefficient for eliminating dyes, especially from dilute solutions. The photo-oxidation method is relatively expensive and not appropriate for the treatment of large flows. Microbial treatment is considered to be an economical and feasible method without secondary pollution, yet biodegradation has the disadvantages of being unstable and time-consuming. Metalloporphyrins, as a representative model of cytochrome P450, have unparalleled catalytic specificity and efficiency, and they can be used as a catalyst to overcome the disadvantages of the above methods used to degrade dyes. In this work, a ferric porphyrin complex, [FeIII(TCPP)], as a cytochrome P450 model, was investigated for its potential to degrade dyes, where [FeIII(TCPP)] in combination with an oxidant, PhIO, was used for the degradation of the dye gentian violet. UV–vis absorption spectroscopy was used to monitor the concentration changes in the gentian violet via its UV–vis spectral changes. The [FeIII(TCPP)]/PhIO system provided a high catalytic degradation efficiency, where the degradation efficiency reached more than 90% in 1 h when using 5 equiv of PhIO at 303 K. Thus, as a cytochrome P450 model, iron porphyrins can play a great role in the degradation of dyes, which provides an efficient approach for the treatment of dye-containing wastewater.

Supplementary Materials

The following supporting information can be downloaded at: https://www.mdpi.com/article/10.3390/molecules27227948/s1, Figure S1: UV-visible absorption spectra of [FeIII(TCPP)] (blue line), the mixture of gentian violet and [FeIII(TCPP)] (red line), and the solution after the degradation of crystal violet by the [FeIII(TCPP)]/PhIO system (pink line); Figure S2: UV-visible absorption spectra of gentian violet (0.05 mM, blue line); the mixture of gentian violet (0.05 mM) and [FeIII(TCPP)] (red line); the solution of gentian violet (0.05 mM) and PhIO (5 equiv) after stirring 2.5 h (pink line); and the solution of gentian violet (0.05 mM) and PhIO (5 equiv) in the presence of [FeIII(TCPP)] after stirring 2.5 h (cyan line); Figure S3: UV−vis spectral change observed in the degradation of gentian violet by various concentrations of PhIO. Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; PhIO 0, 1, 2, 3, 4, 5 equiv; solvent MeOH; 303 K; reaction time 0.5 h; Figure S4: UV−vis spectral change observed in the degradation of gentian violet by various concentrations of PhIO. Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; PhIO 0, 1, 2, 3, 4, 5 equiv; solvent MeOH; 303 K; reaction time 1 h; Figure S5: UV−vis spectral change observed in the degradation of gentian violet by various concentrations of PhIO. Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; PhIO 0, 1, 2, 3, 4, 5 equiv; solvent MeOH; 303 K; reaction time 1.5 h; Figure S6: UV−vis spectral change observed in the degradation of gentian violet by various concentrations of PhIO. Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; PhIO 0, 1, 2, 3, 4, 5 equiv; solvent MeOH; 303 K; reaction time 2 h; Figure S7: GC-MS analysis of the degradation products of crystal violet degraded by the [FeIII(TCPP)]/PhIO system after color removal. (a) Gas chromatogram; (b) mass spectra for the peak with RT value of 5.028 min.

Author Contributions

Conceptualization, X.L.; synthesis and purification of oxidants, D.-D.R. and H.T.; study of the degradation of the dye, D.-D.R., L.-P.Z. and H.T.; formal analysis, X.L. and S.W.; writing—original draft preparation, X.L. and D.-D.R.; writing—review and editing, L.-F.M. and D.-S.L. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Natural Science Foundation of China (Grants 22102068 and 22105093) and Key Scientific Research Projects of Higher Education of He’nan Province (Grants 22A150016 and 22A150049).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Conflicts of Interest

The authors declare no conflict of interest.

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Molecules 27 07948 g001 550
Figure 1. Structures of the catalyst [FeIII(TCPP)], the dye gentian violet and the oxidant iodosylbenzene (PhIO) used in this study.
Figure 1. Structures of the catalyst [FeIII(TCPP)], the dye gentian violet and the oxidant iodosylbenzene (PhIO) used in this study.
Molecules 27 07948 g001
Molecules 27 07948 g002 550
Figure 2. UV–vis spectra of gentian violet (a) and [FeIII(TCPP)] in MeOH (b).
Figure 2. UV–vis spectra of gentian violet (a) and [FeIII(TCPP)] in MeOH (b).
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Molecules 27 07948 g003 550
Figure 3. UV–vis spectral change in gentian violet before degradation (black line) and after degradation (blue line). Conditions: gentian violet 0.05 mM, [FeIII(TCPP)] 0.005 mM, PhIO 5 equiv, solvent MeOH, 303 K and reaction time 2.5 h.
Figure 3. UV–vis spectral change in gentian violet before degradation (black line) and after degradation (blue line). Conditions: gentian violet 0.05 mM, [FeIII(TCPP)] 0.005 mM, PhIO 5 equiv, solvent MeOH, 303 K and reaction time 2.5 h.
Molecules 27 07948 g003
Molecules 27 07948 g004 550
Figure 4. UV–vis spectral change observed in the degradation of gentian violet by various concentrations of PhIO. Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; PhIO 0, 1, 2, 3, 4, 5 equiv; solvent MeOH; 303 K and reaction time 2.5 h.
Figure 4. UV–vis spectral change observed in the degradation of gentian violet by various concentrations of PhIO. Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; PhIO 0, 1, 2, 3, 4, 5 equiv; solvent MeOH; 303 K and reaction time 2.5 h.
Molecules 27 07948 g004
Molecules 27 07948 g005 550
Figure 5. Effect of reaction time on the [FeIII(TCPP)]-catalyzed degradation of gentian violet by 1 equiv (a), 2 equiv (b), 3 equiv (c), 4 equiv (d) and 5 equiv (e) of PhIO. Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; solvent MeOH and 303 K.
Figure 5. Effect of reaction time on the [FeIII(TCPP)]-catalyzed degradation of gentian violet by 1 equiv (a), 2 equiv (b), 3 equiv (c), 4 equiv (d) and 5 equiv (e) of PhIO. Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; solvent MeOH and 303 K.
Molecules 27 07948 g005
Molecules 27 07948 g006 550
Figure 6. Degradation efficiency for the [FeIII(TCPP)]-catalyzed degradation of gentian violet by various concentrations of PhIO under various reaction times. Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; solvent MeOH and 303 K.
Figure 6. Degradation efficiency for the [FeIII(TCPP)]-catalyzed degradation of gentian violet by various concentrations of PhIO under various reaction times. Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; solvent MeOH and 303 K.
Molecules 27 07948 g006
Table
Table 1. [FeIII(TCPP)]-catalyzed degradation1 of gentian violet by PhIO.
Table 1. [FeIII(TCPP)]-catalyzed degradation1 of gentian violet by PhIO.
CatalystPhIO (equiv)Degradation Efficiency (%)
[FeIII(TCPP)]-0
-50
[FeIII(TCPP)]127
[FeIII(TCPP)]265
[FeIII(TCPP)]379
[FeIII(TCPP)]490
[FeIII(TCPP)]598
1 Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; PhIO 0, 1, 2, 3, 4, 5 equiv; solvent MeOH; 303 K and reaction time 2.5 h.
Table
Table 2. [FeIII(TCPP)]-catalyzed degradation 1 of gentian violet by various concentrations of PhIO under various reaction times.
Table 2. [FeIII(TCPP)]-catalyzed degradation 1 of gentian violet by various concentrations of PhIO under various reaction times.
Time
(h)		Degradation Efficiency (%)
PhIO
1 equiv		PhIO
2 equiv		PhIO
3 equiv		PhIO
4 equiv		PhIO
5 equiv
0.5 938426175
1.0 1854607294
1.5 2160698294
2.0 2763748996
2.5 2765799098
1 Conditions: gentian violet 0.05 mM; [FeIII(TCPP)] 0.005 mM; PhIO; solvent MeOH and 303 K.
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Ren, D.-D.; Lu, X.; Zhou, L.-P.; Tian, H.; Wang, S.; Ma, L.-F.; Li, D.-S. Iron Porphyrin as a Cytochrome P450 Model for the Degradation of Dye. Molecules 2022, 27, 7948. https://doi.org/10.3390/molecules27227948

AMA Style

Ren D-D, Lu X, Zhou L-P, Tian H, Wang S, Ma L-F, Li D-S. Iron Porphyrin as a Cytochrome P450 Model for the Degradation of Dye. Molecules. 2022; 27(22):7948. https://doi.org/10.3390/molecules27227948

Chicago/Turabian Style

Ren, Dan-Dan, Xiaoyan Lu, Li-Ping Zhou, Huanghongjun Tian, Shuang Wang, Lu-Fang Ma, and Dong-Sheng Li. 2022. "Iron Porphyrin as a Cytochrome P450 Model for the Degradation of Dye" Molecules 27, no. 22: 7948. https://doi.org/10.3390/molecules27227948

APA Style

Ren, D. -D., Lu, X., Zhou, L. -P., Tian, H., Wang, S., Ma, L. -F., & Li, D. -S. (2022). Iron Porphyrin as a Cytochrome P450 Model for the Degradation of Dye. Molecules, 27(22), 7948. https://doi.org/10.3390/molecules27227948

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