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. 2024 Jan 2;57(1):106-119.
doi: 10.1021/acs.accounts.3c00581. Epub 2023 Dec 20.

Selective Oxidation Using In Situ-Generated Hydrogen Peroxide

Affiliations

Selective Oxidation Using In Situ-Generated Hydrogen Peroxide

Richard J Lewis et al. Acc Chem Res. .

Abstract

ConspectusHydrogen peroxide (H2O2) for industrial applications is manufactured through an indirect process that relies on the sequential reduction and reoxidation of quinone carriers. While highly effective, production is typically centralized and entails numerous energy-intensive concentration steps. Furthermore, the overhydrogenation of the quinone necessitates periodic replacement, leading to incomplete atom efficiency. These factors, in addition to the presence of propriety stabilizing agents and concerns associated with their separation from product streams, have driven interest in alternative technologies for chemical upgrading. The decoupling of oxidative transformations from commercially synthesized H2O2 may offer significant economic savings and a reduction in greenhouse gas emissions for several industrially relevant processes. Indeed, the production and utilization of the oxidant in situ, from the elements, would represent a positive step toward a more sustainable chemical synthesis sector, offering the potential for total atom efficiency, while avoiding the drawbacks associated with current industrial routes, which are inherently linked to commercial H2O2 production. Such interest is perhaps now more pertinent than ever given the rapidly improving viability of green hydrogen production.The application of in situ-generated H2O2 has been a long-standing goal in feedstock valorization, with perhaps the most significant interest placed on propylene epoxidation. Until very recently a viable in situ alternative to current industrial oxidative processes has been lacking, with prior approaches typically hindered by low rates of conversion or poor selectivity toward desired products, often resulting from competitive hydrogenation reactions. Based on over 20 years of research, which has led to the development of catalysts for the direct synthesis of H2O2 that offer high synthesis rates and >99% H2 utilization, we have recently turned our attention to a range of oxidative transformations where H2O2 is generated and utilized in situ. Indeed, we have recently demonstrated that it is possible to rival state-of-the-art industrial processes through in situ H2O2 synthesis, establishing the potential for significant process intensification and considerable decarbonization of the chemical synthesis sector.We have further established the potential of an in situ route to both bulk and fine chemical synthesis through a chemo-catalytic/enzymatic one-pot approach, where H2O2 is synthesized over heterogeneous surfaces and subsequently utilized by a class of unspecific peroxygenase enzymes for C-H bond functionalization. Strikingly, through careful control of the chemo-catalyst, it is possible to ensure that competitive, nonenzymatic pathways are inhibited while also avoiding the regiospecific and selectivity concerns associated with current energy-intensive industrial processes, with further cost savings associated with the operation of the chemo-enzymatic approach at near-ambient temperatures and pressures. Beyond traditional applications of chemo-catalysis, the efficacy of in situ-generated H2O2 (and associated oxygen-based radical species) for the remediation of environmental pollutants has also been a major interest of our laboratory, with such technology offering considerable improvements over conventional disinfection processes.We hope that this Account, which highlights the key contributions of our laboratory to the field over recent years, demonstrates the chemistries that may be unlocked and improved upon via in situ H2O2 synthesis and it inspires broader interest from the scientific community.

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Conflict of interest statement

The authors declare no competing financial interest.

Figures

Figure 1
Figure 1
Simplified reaction scheme for the ammoximation of cyclohexanone via in situ H2O2 synthesis. Note that a wide conditions gap exists between the H2O2 direct synthesis and ketone ammoximation reactions, with the former favored by subambient temperatures and acidic conditions while the latter requires elevated reaction temperatures and basic conditions.
Figure 2
Figure 2
Ketone ammoximation via in situ H2O2 synthesis. (A) Catalytic activity of a 0.66% AuPd/TiO2 catalyst, used in conjunction with TS-1, toward the in situ ammoximation of a range of ketones. (B) Comparison of catalyst support on the activity of AuPd nanoalloys toward the in situ ammoximation of cyclohexanone. Note that with the exception of the TS-1 catalyst, all other formulations were used in conjunction with TS-1 (0.075 g). (C) Effect of the Au:Pd ratio on the catalytic activity of 0.66% PdAu/TS-1 catalysts toward the in situ ammoximation of cyclohexanone. (D) Catalytic activity of 0.66% PdX/TS-1 catalysts toward the in situ ammoximation of cyclohexanone. Note that Pd:X = 1:1 (w/w). Reaction conditions (A, B): Cyclohexanone (2 mmol), NH4HCO3 (4 mmol), 5% H2/N2 (420 psi), 25% O2/N2 (160 psi), catalyst (0.075 g), t-BuOH (5.9 g), H2O (7.5 g), reaction time 3 h, reaction temperature 80 °C, stirring speed 800 rpm. Reaction conditions (C, D): Same as above, but the reaction time is 6 h.
Figure 3
Figure 3
Industrial viability of the in situ approach to cyclohexanone ammoximation. (A) Cyclohexanone ammoximation via in situ H2O2 synthesis under industrially relevant conditions. (B) Techno-economic analysis comparison of the current commercial and in situ approaches to cyclohexanone ammoximation. Reaction conditions (A): Cyclohexanone (19 wt %): NH3 (aq) (1:1 (mol/mol)), 3.6% H2, 6.4% O2, 90% N2 (580 psi, 20 mL min–1), 0.33% Au 0.33% Pd/TS-1(acetate-O + R):Al2O3 (4:1) (catalyst mass = 0.42 g), t-BuOH: H2O (9:1 (v/v), 0.005–0.10 mL min–1), residence time 75 min at 0.01 mL min–1 liquid flow rate and 150 min at 0.005 mL min–1 liquid flow rate, reaction temperature 80 °C. Note 1: The catalyst was reduced (2 h, 200 °C, H2) following an initial oxidative heat treatment (16 h, 110 °C, static air). Note 2: Reaction conditions between 0 and 1.4 h: As above with liquid flow of 0.1 mL min–1 (purple background). Note 3: Reaction conditions between 1.4 and 12.3 h: As above with liquid flow of 0.01 mL min–1 (green background). Note 4: Reaction conditions between 12.3 and 16 h: As above with liquid flow of 0.005 mL min–1 (orange background). Note 5: The reader is directed to our original work for a complete techno-economic analysis.
Figure 4
Figure 4
Proposed reaction scheme for the oxidation of benzyl alcohol via in situ H2O2 synthesis.
Figure 5
Figure 5
Benzyl alcohol oxidation via in situ H2O2 synthesis. (A) Comparative performance of in situ H2O2 synthesis toward the oxidation of benzyl alcohol using a 1% Pd/TiO2 catalyst. (B) Comparison of the catalytic activity of 1% Pd/TiO2, 1% PdAu/TiO2, and 1% PdFe/TiO2 catalysts over sequential reactions. (C) Effect of reaction solvent on the performance of a 5% AuPd/TiO2 catalyst. (D) Experimental (black) and simulated (red) EPR spectra of DMPO-radical adducts formed during the oxidation reaction. Reactions were conducted in the presence of DMPO and (i) 1% Pd/TiO2 (0.083 h), (ii) 1% Pd/TiO2 (0.5 h), (iii) 1% PdAu/TiO2 (0.083 h), (iv) 1% PdAu/TiO2 (0.5 h), (v) 1% PdFe/TiO2 (0.083 h), and (vi) 1% PdFe/TiO2 (0.5 h). Reaction conditions: Catalyst (0.01 g), benzyl alcohol (1.04 g, 9.62 mmol), solvent (7.1 g), 5% H2/CO2 (420 psi), 25% O2/CO2 (160 psi), 0.5 h, 50 °C, 1200 rpm. Note 1: In A, the concentration of commercial H2O2 used is comparable to that produced if all H2 in a standard in situ reaction is converted to H2O2. H2O2 was not continually introduced into the reactor. N2 in parentheses is indicative of a gaseous atmosphere (580 psi). For experiments carried out using H2 or O2 only, a gaseous mixture of 5%H2/CO2 (420 psi) or 25%O2/CO2 (160 psi) was used, with the total pressure being maintained at 580 psi using N2. Note 2: In A–D, the solvent used was MeOH.
Figure 6
Figure 6
Proposed reaction pathways associated with the chemo-catalytic/enzymatic valorization of cyclohexane via in situ H2O2 synthesis.
Figure 7
Figure 7
Chemo/enzymatic C–H bond oxidation, via in situ H2O2synthesis. (A) Comparison of the chemo-catalytic/enzymatic system (where H2O2 is synthesized over a 5% AuPd/TiO2 catalyst) with the coenzymatic approach using glucose oxidase (GOx, 0.2 UmLRM–1) and 200 mM glucose under an oxidative atmosphere (air, 6 psi). (B) Product selectivity as a function of catalyst formulation when used in conjunction with PaDa-I. (C) Chemo-catalytic and (D) enzymatic overoxidation of cyclohexanol. Reaction conditions: Catalyst (0.001 g), substrate (10 mM), PaDa-I (15 U mLRM–1), phosphate buffer (100 mM, 10 mL, pH 6.0), using a gas mixture of 80% H2/air H2 (23 psi) and air (6 psi), X h, 20 °C, 250 rpm. Note 1: In B–D, the catalyst formulation is 1% PdX/TiO2 (Pd:X = 1:1 (w/w)).
Figure 8
Figure 8
Sources of enzyme deactivation in the chemo-enzymatic approach to cyclohexane oxidation. (A) Effect of key reaction parameters and (B) homogeneous metal species on enzyme deactivation, as determined by ABTS assay. ABTS assay reaction conditions for (A) and (B): 100 μL of the reaction solution was added to 900 μL of ABTS solution (100 mM sodium citrate–phosphate buffer, pH 4.4 with 0.3 mM ABTS and 2 mM H2O2), and substrate conversion was followed by measuring the absorption at 418 nm (ε 418 = 36 000 M–1 cm–1) at 30 °C. Note for A: In the case of the blank experiment, the UPO was stirred under ambient conditions and the pressure of the buffer only. In the case of the cyclohexanol experiment, the concentration of cyclohexanol was equivalent to that present at 30% conversion of cyclohexane. The blank cyclohexane oxidation reaction conditions for (B): Metal salt ((5.1–9.4) × 10–9 M), cyclohexane (10 mM), PaDa (15 U mLRM–1), and phosphate buffer (100 mM, 10 mL, pH 6.0), using a gas mixture of 80% H2 (23 psi) in air (6 psi), 2 h, 250 rpm.
Figure 9
Figure 9
Bioremediation via in situ H2O2 synthesis. (A) Proposed reaction scheme for the in situ remediation of E. coli. K12 JM109 by reactive oxygen species generated over AuPd surfaces, summarizing our observations of catalytic performance and O-centered radical speciation. (B) Comparison of microbicidal activity using aqueous NaOCl, preformed H2O2, and in situ-synthesized H2O2. Reaction conditions: Catalyst (0.12 g), 2% H2, 20% O2, 78% N2, (145 psi, 42 mL min–1), reaction solution (H2O and E. coli K12 JM109 (2 × 108 c.f.u. mL–1) 0.2 mL min–1 liquid flow), 0.5 h, 2 °C.
Figure 10
Figure 10
Oxidative degradation of phenol via in situ H2O2 synthesis. Comparison of catalytic activity using Pd-based catalysts (A) 1% Pd/TiO2, (B) 0.25% Pd-0.27% Fe/TiO2, and (C) 0.5% Pd/3% Fe-ZSM-5. (D) Performance of the 0.5% Pd/3% Fe-ZSM-5 catalyst over sequential reactions. Reaction conditions: Catalyst (0.01 g), phenol (1000 ppm, 8.5 g), 5% H2/CO2 (420 psi), 25% O2/CO2 (160 psi), 2 h, 30 °C, 2 h.
Figure 11
Figure 11
(A) Efficacy of the 0.5% Pd/3% Fe-ZSM-5 catalyst toward the oxidative degradation of phenol via in situ H2O2 synthesis as a function of the catalyst:phenol ratio. (B) Comparative performance of in situ H2O2 synthesis toward phenol degradation over a 0.5% Pd/0.5% Fe-ZSM-5 catalyst (0.0 1 g). Reaction conditions: Catalyst (X g), phenol (1000 ppm, 8.5 g), 5% H2/CO2 (420 psi), 25% O2/CO2 (160 psi), 2 h, 30 °C, 2 h. Note: In B, the concentration of commercial H2O2 used is comparable to that produced if all H2 in a standard in situ reaction is converted to H2O2. H2O2 was not continually introduced into the reactor. N2 in parentheses is indicative of the gaseous atmosphere (580 psi). For experiments carried out using H2 or O2 only, a gaseous mixture of 5% H2/CO2 (420 psi) or 25% O2/CO2 (160 psi) was used, with the balance consisting of N2.

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