Solid Acid Catalysts for Hock Cleavage of Hydroperoxides: Comparison
Please note this is a comparison between Version 2 by Bruce Ren and Version 1 by Matthias Eisenacher.

The oxidation of cumene and following cleavage of cumene hydroperoxide (CHP) with sulfuric acid (Hock rearrangement) is still, by far, the dominant synthetic route to produce phenol. In 2020, the global phenol market reached a value of 23.3 billion US$ with a projected compound annual growth rate of 3.4% for 2020–2025. From ecological and economical viewpoints, the key step of this process is the cleavage of CHP. One sought-after way to likewise reduce energy consumption and waste production of the process is to substitute sulfuric acid with heterogeneous catalysts. Different types of zeolites, silicon-based clays, heteropoly acids, and ion exchange resins have been investigated and tested in various studies. For every type of these solid acid catalysts, several materials were found that show high yield and selectivity to phenol.

  • Hock cleavage
  • heterogeneous catalysis
  • cumene hydroperoxide

1. Introduction

The cumene process is the worldwide most used process for producing oxygenated hydrocarbons such as phenol and acetone from petrochemical feedstocks [1]. Even though one-step routes via oxidation of benzene with oxygen, hydrogen peroxide, or nitrous oxide to produce phenol were developed [2,3[2][3][4][5][6][7][8][9],4,5,6,7,8,9], with 12.7 × 106 t/an over 97% of the worldwide produced phenol and 7.8 × 106 t/a of acetone the cumene process is still the by far most used process today [1,10][1][10]. It was discovered and developed almost parallel in the UDSSR and in Germany. In the years 1943–1946, UDRIS and SERGEEV developed a method for the synthesis of phenol and acetone by acid decomposition of cumene hydroperoxide (CHP), in 1944 Hock and Lang published a three-step route from benzene and propylene to cumene via alkylation and following autoxidation to CHP, that is cleaved to phenol and acetone by acid decomposition (Figure 1) [11,12,13][11][12][13].
Figure 1. Cumene process.
The decomposition named ‘Hock rearrangement’ is a Brønsted or Lewis acid catalyzed cleavage of a hydroperoxide, resulting in an alcohol and carbonyl compound, in case of the cumene process from CHP to phenol and acetone [14]. The Hock rearrangement has a high impact on the entire cumene consumption rate of the whole phenol plant and determines the safety level of the cumene process. CHP releases a lot of heat when decomposed (−252 kJ/mol) and is an explosive chemical, resulting in a high hazard potential that has caused numerous incidents, which cause loss of life, damage to facilities, and subsequent production stops. Therefore, it is vital to understand the behavior of hydroperoxides and achieve a high selectivity in the cleavage step [15,16,17,18][15][16][17][18].
The most commonly used catalyst for the cleavage of CHP is sulfuric acid [1], which unfortunately has intrinsic disadvantages: alongside the corrosive problem it is mandatory to add a neutralization agent after the decomposition step to prevent side reactions and remove the aggressive acid before rectification. The accruing salts within the occurring aqueous phase have to be removed to prevent the evaporator of the rectification columns from fouling and plugging [19]. This recovery and reutilization have a negative impact on the overall costs of the process.

2. Solid Acid Catalysts

After the commercialization in Europe and the USA after World War II, different other homogeneous catalysts have been investigated [38[20][21][22][23][24][25][26],39,40,41,42,43,44], but none of them demonstrated superior performance to sulfuric acid regarding catalytic and cost efficiency. To eliminate the persisting issues with sulfuric acid as corrosive and homogeneous catalyst, different approaches to substitute the homogeneous catalyst with a solid catalyst have been explored in the past 20 years.

2.1. Mineral Acid-Treated Clays

Smectite clay minerals [45][27] are layer aluminosilicates with a broad variety of properties which are beneficial for catalyzing an organic reaction, and especially montmorillonites are used as acid catalyst [39][21]. Therefore, the acidity and surface area of this smectites are often modified by different methods. Furthermore, they can be altered by impregnation with metal salts or intercalation of heteropolyacids (HPA) or Lewis acids [46][28]. One method to modify clays is the treatment with inorganic acids such as hydrochloric acid and sulfuric acid. That results in a leaching of Al3+ and creates therefore mesopores in the clay structure, contributing to a higher surface area. In addition, interlamellar cations are replaced with protons of the applied acid. Furthermore, the leaching of Al3+ results in a decrease of strong Brønsted acid sites, but the overall concentration of weak Brønsted acid sites and the population of Lewis acid sites increases [47,48,49][29][30][31]. Bentonite treated with hydrochloric acid of different concentrations show a significant difference in Brønsted acid sites and according performance in a reaction system with CHP [50][32]. Treatment with low concentrated hydrochloric acid seems to increase the activity of the catalyst as more Brønsted acid sites are created, but treatment with highly concentrated acids leads to an elution of strong Brønsted acid sites. As strong Brønsted acid sites are required for the decomposition of CHP [51][33], the elutriation due to higher concentrated acids results in a deactivation.
Knifton and Sandserson used acid treated montmorillonites clays with different acidity, ranging from 10–16 mg KOH/g, in batch and continuous experiments. The former showed a yield of 98 mol % for the clays with high acidity. The experiments in a continuous plug-flow reactor revealed that acid treated montmorillonites clays are capable of performing for at least 1000 h in continuous conditions. The reaction parameters were set between 60 to 80 °C, 6 to 65 bar and a LHSV from 1 to 10 Lh−1. Although the reactor was cooled, the temperature profile in the reactor raised up to 25 °C with LHSV 1 and 45 °C at LHSV 10. With a set temperature of 80 °C this leads to a drop of the phenol yield to 94% and shows the significant problem with heat removal operating this highly exothermic reaction in a fixed bed reactor [52][34]. Han et al. activated montmorillonite powder with 30 wt % sulfuric acid and used cordierite as support. The loading of montmorillonite on the support varied between 13.0 wt % and 38.5 wt %. Phenol yields ranged from about 65% with 19.5 wt % montmorillonite loading and 75% with 38.5 wt % montmorillonite loading at 60 °C and about 85% phenol yield with 19.5 wt % montmorillonite loading and 95% with 38.5 wt % montmorillonite loading at a reaction temperature of 90 °C. The highest selectivity was achieved at 60 °C with >99%, slightly dropping to about 99.5% at 90 °C. In their experiments HAN et al. also used a plug-flow reactor and found the optimum WHSV at 90 h−1. Overall, the optimal parameters with montmorillonite on cordierite wherewith a loading of 32.5 wt % acid per clay, reaction temperature of 80 °C, WHSV of 90 h−1, and mass ratio of CHP to acetone of 1:3 [53][35].

2.2. Heteropoly Acids (HPA) on Supports

Heteropolyacids (HPAs) are complex proton acids which are formed by condensation of transition metal oxoacids. The octahedral structure is built by heteroatoms (group I–VII possible) connected to a transition metal (addenda atoms, mostly Mo, W, and V) via oxygen atoms. The most researched HPAs are those with the Keggin structure, as these HPAs are simply prepared and show the highest Brønsted acidity [54,55,56,57,58,59][36][37][38][39][40][41]. Immobilized on supports like clays or titania, the downsides that normally occur if used as homogeneous catalyst plus the low surface area can be eluded. Experiments with dodecatungstophosphoric acid (DTP) and similar HPAs with Keggin structure show phenol yields up to 99 mol % at quantitative conversion of CHP if impregnated on a montmorillonite clay, even with high feed rates like LHSV at 10 h−1 [52][34]. To achieve a high stability of the HPAs in solution and to enhance the surface area and thermal stability, protons can be partial substituted with Cs+-Ions. The modified salts of HPAs und montmorillonite clays show high stability and reusability with high conversion rates of CHP [18].

2.3. Zeolites

During the last three decades, zeolites have become more and more relevant catalysts as they are cheap, readily available, and—due to their strong acidity—capable of phasing-out several mineral acids. Zeolites are shape-selective, often improving the processes yield and selectivity, and consequentially products quality. For the cleavage of CHP in the cumene process, several types of zeolites have been tested, including X-, USY-, Beta-, and ZSM-5-type zeolites [51,60,61,62,63,64,65,66][33][42][43][44][45][46][47][48]. Zeolites are mostly used in a fixed bed reactor and the reaction parameters strongly depend on the used zeolite. Beta and ZSM-5 zeolites and corresponding metallosilicates containing trivalent elements in the framework (B, Fe, Ga) are active at room-temperature and a reaction time of 5 min are enough for 100% conversion of CHP [51][33]. The selectivity to phenol varies from 86% to 92%, with a slightly better selectivity if Beta zeolites are used. Over 10 h under fixed-bed conditions the H-Al-Beta zeolite can hold the conversion rate of 100%, but the selectivity towards phenol decreases from 95% to 90%. ZSM-12, NCL-1, ZSM-22, EU-1, MCM-22, and ZSM 48 need elevated temperatures (40–60 °C) to reach high conversion rates [51][33]. With medium-pore unidimensional zeolites like ZSM-22 and ZSM-48 the CHP conversion is significantly lower than over ZSM 5 or Beta zeolites, 65% for ZSM-22, and 45% for ZSM-48. This can be explained with diffusion restrictions due to the channel system of these zeolites. The performance of unidimensional zeolites with larger pores and thus better accessible channel system (ZSM-12, NCL-1, and MCM-22) show 85–90% conversion. The selectivity is only slightly inferior to ZSM-5 and Beta zeolites. KUMAR showed that lowering the particle size of ZSM-5 crystals from 90 nm to nanocrystals with a particle size of 18.3 nm results in a rise in CHP conversion from 60.1% to 94% [66][48] due to lower diffusion restrictions and therefore an enhanced accessibility to the acid sites. Besides good accessibility of the catalytic active sites of the catalyst, the conversion of CHP strongly depends on the number and strength of Brønsted acid sites of the zeolites [51,65][33][47]. The lack or only small amount of acid sites in molecular sieves like AIPO-5 and SAPO 5 results in low conversions of 10% for the aluminophosphate and 25% for the silico-aluminophosphate, respectively [51,67,68][33][49][50]. The maximum number of protonic sites is equal to the number of framework aluminum atoms [69[51][52],70], but the strength of the acid site is higher if isolated by Si in next nearest neighbor (NNN)-positions. The strength of the protic sites is therefore inversely proportional to the Al content [65,69,71][47][51][53]. For ultra-stable Y zeolites in H-form (HUSY) an additional property has been found: partially dealuminated HUSY can mediate reactions only expectable to occur in superacids. The protonation inside the zeolite pores follow a certain mechanism, resulting in high kinetic acidity. Over HUSY with Si/Al ratios of 15–40 CHP converts up to 100% with good selectivity (0.1% w/w HUSY, 60 °C, 20 min reaction time). The high hydrophilicity of the HUSY zeolite require to be activated at 500 °C. That pre-activation diminishes poisoning by water, preventing loss of activity over several runs [66,72,73,74][48][54][55][56].

2.4. Ion Exchange Resins

Another class that can be used as catalysts for CHP cleavage is ion exchange resins. The resins used consist of a macroporous polystyrene backbone and sulfonic acid groups as ion-exchange groups. Ye et al. used AMBERLYST 35WET and AMBERLYST 35DRY with the polystyrene-backbone cross-linked with divinylbenzene [74][56]. Huang et al. selected a resin entitled TH-02 with additional not otherwise specified functional groups to obtain higher exchange capacity and large internal pores [75][57]. The larger internal pores result from less crosslinking, making the resins mechanically less stable. Therefore, Huang et al. used a special reactor consisting of a riser, a main reactor, a liquid–solid separator and a loop, called TPCFB reactor [75][57]. At a WHSV of 30 h−1 the conversion of CHP varies between 99.5% at 60 °C and 100% at 90 °C and higher. The selectivity is >99.9% at 60 °C and drops slightly to 97% at 98 °C. YE et al. used a lab-scale RD column to test the AMBERLYST 35 resins for the decomposition of CHP. Their experiments showed that a dry resin has superior catalytic activity. This is explained by the negative influence of the high water content on the intermediate dehydration step in the CHP decomposition [74][56].
The different catalysts and their performance regarding the decomposition of CHP are listed in Table 1.
Table 1. Catalytic decomposition of cumene hydroperoxide over various catalysts.
Catalyst Si/Al Ratio Reaction Time/min Reaction Temperature/°C Conversion of CHP/% Y (phenol)/% S (phenol)/%
Clays            
K1051 n/a 30 50 100 n/a n/a
K1051 with ZnCl2 n/a 30 50 80 n/a n/a
K1051 with FeCl3 n/a 30 50 92 n/a n/a
K1051 with CeCl3 n/a 30 50 100 n/a n/a
K1051 with LaCl3 n/a 30 50 95 n/a n/a
K1018 n/a 30 40 99 n/a n/a
Grade F2452 n/a 120 57–80 100 98 98
Grade F11352 n/a 120 57–80 100 95 95
Grade F1352 n/a 120 57–80 100 99 99
Grade F6252 n/a 120 57–80 76 37 49
Acidic montmorillonite53 n/a 90 90 n/a 95 n/a
HPA on supports            
12-tungstophosphoric acid52 n/a 120 57–80 100 99 n/a
12-molybdophosphoric acid52 n/a 120 57–80 100 99 n/a
12-tungstosilicic acid52 n/a 120 57–80 100 99 n/a
12-molybdosilicic acid52 n/a 120 57–80 100 99 n/a
Cs2.5H0.5PW12O40 on K1018 n/a 30 40 99   n/a
Zeolites            
H-[Al]-Beta65 14 5 25 100 88 88
H-[Ga]-Beta65 20 5 25 100 92 92
H-[Fe]-Beta65 22 5 25 100 91 91
H-[B]-Beta65 30 5 25 100 92 92
H-[Al]-ZSM-565 30 5 25 100 86 86
H-[Ga]-ZSM-565 35 5 25 100 89 89
H-[Fe]-ZSM-565 30 5 25 100 88 88
H-Mordenite65 7 5 25 100 87 87
H-Y65 2.5 10 40 96 82 85
H-[Al]-ZSM-1265 40 30 40 95 78 82
H-[Al]-NCL-165 40 15 40 85 71 84
H-[Al]-ZSM-2265 60 15 40 65 57 88
H-[Al]-MCM-2265 30 15 40 90 78 87
H-[Al]-ZSM-4865 50 60 60 45 36 80
H-[Al]-EU-165 50 30 60 80 71 89
H-SAPO-565 n/a 60 60 10 9 88
H-AlPO-565 n/a 60 60 25 22 86
H-[Al]-Betac65 14 60 60 99 94 95
ZSM-5-0NC70 n/a 25 50 60 n/a n/a
ZSM-5-30NC70 n/a 25 50 94 n/a n/a
HUSY66 2.5 10 60 32 n/a n/a
HUSY66 15 10 60 90 n/a n/a
HUSY66 40 10 60 85 n/a n/a
HY66 n/a 20 60 10 n/a n/a
Beta66 n/a 600 20 89 n/a n/a

References

  1. Weber, M.M.; Weber, M.M.; Weber, V. Phenol; Wiley-VCH Verlag GmbH & Co. KgaA: Weinheim, Germany, 2020; pp. 4–7.
  2. Sheldon, R.A. Homogeneous and Heterogeneous Catalytic Oxidations with Peroxide Reagents. Org. Peroxygen Chem. 1993, 164, 21–43.
  3. Alekar, N.A.; Indira, V.; Halligudi, S.B.; Srinivas, D.; Gopinathan, S.; Gopinathan, C. Kinetics and Mechanism of Selective Hydroxylation of Benzene Catalysed by Vanadium Substituted Heteropolymolybdates. J. Mol. Catal. A Chem. 2000, 164, 181–189.
  4. Lee, C.W.; Lee, W.J.; Park, Y.K.; Park, S.E. Catalytic Hydroxylation of Benzene over Vanadium-Containing Molecular Sieves. Catal. Today 2000, 61, 137–141.
  5. Olah, G.A.; Ohnishi, R. Oxyfunctionalization of Hydrocarbons. 8. Electrophilic Hydroxylation of Benzene, Alkylbenzenes, and Halobenzenes with Hydrogen Peroxide in Superacids. J. Org. Chem. 1978, 43, 865–867.
  6. Kuznetsova, N.I.; Kuznetsova, L.I.; Kirillova, N.V.; Pokrovskii, L.M.; Detusheva, L.G. Oxidation of Cyclohexene and α Pinene with O2—H2 Mixture. Russ. Chem. Bull. 2003, 52, 1544–1551.
  7. Niwa, S.I.; Eswaramoorthy, M.; Nair, J.; Raj, A.; Itoh, N.; Shoji, H.; Namba, T.; Mizukami, F. A One-Step Conversion of Benzene to Phenol with a Palladium Membrane. Science 2002, 295, 105–107.
  8. Sobolev, V.I.; Dubkov, K.A.; Paukshtis, E.A.; Piratko, L.V.; Rodkin, M.A.; Kharitonov, A.S.; Panov, G.I. On the Role of Brønsted Acidity in the Oxidation of Benzene to Phenol by Nitrous Oxide. Appl. Catal. A Gen. 1996, 141, 185–192.
  9. Dubkov, K.A.; Sobolev, V.I.; Talsi, E.P.; Rodkin, M.A.; Watkins, N.H.; Shteinman, A.A.; Panov, G.I. Kinetic Isotope Effects and Mechanism of Biomimetic Oxidation of Methane and Benzene on FeZSM-5 Zeolite. J. Mol. Catal. A Chem. 1997, 123, 155–161.
  10. Zakoshansky, V. Phenol Process Celebrates Its 60th Anniversary: The Role of Chemical Principles in Technological Breakthroughs. Russ. J. Gen. Chem. 2009, 79, 2267–2271.
  11. Morachevskii, A.G.; Nemtsov, M.S. Vospominaniya i Razmyshleniya (Zapiski Khimika) (Recollections and Reflection (Chemist’s Memoirs)). Russ. J. Appl. Chem. 2007, 80, 511–512.
  12. Hock, H.; Lang, S. Autoxydation von Koblenwasserstoffen: Über Peroxyde von Benzol-Derivaten. Eur. J. Inorg. Chem. 1944, 77, 257–263.
  13. Udris, R.J.; Sergeyev, P.G.; Kruzhalov, B.D. Sposob Polucheniya Gidroperekisejj Alkilirovannykh-Proizvodnykh Benzola Ili Alicikloaromaticheskikh Uglevodorodov. USSR Patent 106,666, 7 January 1947.
  14. Yaremenko, I.A.; Vil’, V.A.; Demchuk, D.V.; Terent’ev, A.O. Rearrangements of Organic Peroxides and Related Processes. Beilstein J. Org. Chem. 2016, 12, 1647–1748.
  15. Duh, Y.S.; Kao, C.S.; Hwang, H.H.; Lee, W.W.L. Thermal Decomposition Kinetics of Cumene Hydroperoxide. Process Saf. Environ. Prot. 1998, 76, 271–276.
  16. Tsai, H.F.; Guo, S.J.; Wu, S.H. Fire and Thermal Hazard Analyses of Industrial Zeolite Catalysis for Phenol Production. Adv. Mater. Res. 2012, 560–561, 161–166.
  17. The 100 Largest Losses 1972–2011; Marsh & McLennan: New York, NY, USA, 2011; pp. 1–42.
  18. Yadav, G.D.; Asthana, N.S. Selective Decomposition of Cumene Hydroperoxide into Phenol and Acetone by a Novel Cesium Substituted Heteropolyacid on Clay. Appl. Catal. A Gen. 2003, 244, 341–357.
  19. Schmidt, R.J. Industrial Catalytic Processes—Phenol Production. Appl. Catal. A Gen. 2005, 280, 89–103.
  20. Sheldon, R.A.; van Doorn, J.A. Observation by PMR Spectroscopy of the Intermediate Alkoxycarbonium Ions in the Acid-Catalysed Decomposition of Organic Hydroperoxides. Tetrahedron Lett. 1973, 14, 1021–1022.
  21. Barton, D.H.R.; Delanghe, N.C. New Catalysts for the Conversion of Cumene Hydroperoxide into Phenol. Tetrahedron Lett. 1997, 38, 73–78.
  22. Kharasch, M.S.; Fono, A.; Nudenberg, W. The Chemistry Of Hydroperoxides I. The Acid-Catalyzed Decomposition of α,α-Dimethylbenzyl (α-Cumyl) Hydroperxoide. J. Org. Chem. 1950, 15, 748–752.
  23. Seubold, F.H.; Vaughan, W.E. Acid-Catalyzed Decomposition of Cumene Hydroperoxide. J. Am. Chem. Soc. 1953, 75, 3790–3792.
  24. Turner, J.O. The Acid-Catalyzed Decomposition of Aliphatic Hydroperoxides: Reactions in the Presence of Alcohols. Tetrahedron Lett. 1971, 12, 887–890.
  25. Deno, N.C.; Billups, W.E.; Kramer, K.E.; Lastomirsky, R.R. The Rearrangement of Aliphatic Primary, Secondary, and Tertiary Alkyl Hydroperoxides in Strong Acid. J. Org. Chem. 1970, 35, 3080–3082.
  26. Hock, H.; Kropf, H. Autoxydation von Kohlenwasserstoffen Und Die Cumol-Phenol-Synthese. Angew. Chem. 1957, 69, 313–321.
  27. Pinnavaia, T.J. Intercalated Clay Catalysts. Science 1983, 220, 365–371.
  28. Varma, R.S. Clay and Clay-Supported Reagents in Organic Synthesis. Tetrahedron 2002, 58, 1235–1255.
  29. Theocharis, C.R.; S’Jacob, K.J.; Gray, A.C. Enhancement of Lewis Acidity in Layer Aluminosilicates. Treatment with Acetic Acid. J. Chem. Soc. Faraday Trans. 1 Phys. Chem. Condens. Phases 1988, 84, 1509–1515.
  30. Cativiela, C.; Fraile, J.M.; Garcia, J.I.; Mayoral, J.A.; Figueras, F.; De Menorval, L.C.; Alonso, P.J. Factors Influencing the K10 Montmorillonite-Catalyzed Diels-Alder Reaction between Methyl Acrylate and Cyclopentadiene. J. Catal. 1992, 137, 394–407.
  31. Rhodes, C.N.; Brown, D.R. Surface Properties and Porosities of Silica and Acid-Treated Montmorillonite Catalyst Supports: Influence on Activities of Supported ZnCl2 Alkylation Catalysts. J. Chem. Soc. Faraday Trans. 1993, 89, 1387–1391.
  32. Selvin, R.; Hsu, H.L.; Aneesh, P.; Chen, S.H.; Hung, L.H. Preparation of Acid-Modified Bentonite for Selective Decomposition of Cumene Hydroperoxide into Phenol and Acetone. React. Kinet. Mech. Catal. 2010, 100, 197–204.
  33. Sasidharan, M.; Kumar, R. Zeolite-Catalysed Selective Decomposition of Cumene Hydroperoxide into Phenol and Acetone. J. Chem. Res.-Part S 1997, 2, 52–53.
  34. Knifton, J.F.; Sanderson, J.R. Phenol/Acetone Cogeneration via Solid Acid Catalysis. Appl. Catal. A Gen. 1997, 161, 199–211.
  35. Han, L.; Wang, Y.; Zhang, J.; Lei, Z.; Huang, C.; Chen, B. Acidic Montmorillonite/Cordierite Monolithic Catalysts for Cleavage of Cumene Hydroperoxide. Chin. J. Chem. Eng. 2014, 22, 854–860.
  36. Pope, M.T. Heteropoly and Isopoly Oxometalates; Springer: Berlin/Heidelberg, Germany, 1993.
  37. Izumi, Y.; Urabe, K.; Onaka, M. Zeolites, Calys and Heteropoly Acids; VSH Publishers Inc.: London, UK, 1992.
  38. Okuhara, T.; Mizuno, N.; Misono, M. Catalytic Chemistry of Heteropoly Compounds. Adv. Catal. 1996, 41, 113–252.
  39. Misono, M.; Nojiri, N. Recent Progress in Catalytic Technology in Japan. Appl. Catal. 1990, 64, 1–30.
  40. Corma, A. Inorganic Solid Acids and Their Use in Acid-Catalyzed Hydrocarbon Reactions. Chem. Rev. 1995, 95, 559–614.
  41. Kozhevnikov, I.V. Heteropoly Acids as Catalysts for Fine Chemicals Synthesis; Woodhead Publishing Ltd.: Sawston, UK, 2005; Volume 6.
  42. Chang, C.D.; Pelrine, P.P. Mobil Oil Corporation Production of Phenol. U.S. Patent 4490565A, 25 December 1984.
  43. Romano, U.; Clerici, M.G.; Bellussi, G.; Buonomo, F. Catalyst for the Selective Decomposition of Cumene Hydroperoxide. U.S. Patent 47543573A, 10 May 1988.
  44. Romano, U.; Clerici, M.G.; Bellussi, G.; Buonomo, F. Catalyst for the Selective Decompostion of Cumene Hydroperoxide and Process Using it. U.S. Patent 4849387A, 18 July 1989.
  45. Xu, R.; Pang, W.; Yu, J.; Huo, Q.; Chen, J. Chemistry of Zeolites and Related Porous Materials; Wiley: Hoboken, NJ, USA, 2007.
  46. Cejka, J.; Corma, A.; Zones, S. Zeolites and Catalysis; Wiley: Hoboken, NJ, USA, 2010.
  47. Koltunov, K.Y.; Sobolev, V.I. Efficient Cleavage of Cumene Hydroperoxide over HUSY Zeolites: The Role of Brønsted Acidity. Appl. Catal. A Gen. 2008, 336, 29–34.
  48. Kumar, K.P.; Selvin, R.; Kumari, P.; Roselin, L.S.; Arul, N.S.; Bououdina, M. Selective Decomposition of Cumene Hydroperoxide into Phenol and Acetone over Nanocrystalline ZSM-5. Int. J. Mater. Eng. Innov. 2010, 1, 417–425.
  49. Hedge, S.G.; Ratnasamy, P.; Kustov, L.M.; Kazansky, V.B. Acidity and Catalytic Activity of SAPO-5 and AlPO-5 Molecular Sieves. Zeolites 1988, 8, 137–141.
  50. Chaudhary, V.R.; Singh, A.P.; Kumar, R. Acidity and Sorbate Shape Selectivity of H-ZSM-22, H-ZSM-48, and H-ZSM-50 Zeolites. J. Catal. 1991, 129, 293–296.
  51. Guisnet, M.; Gilson, J.-P. Zeolites for Cleaner Technologies; Imperial College Press: London, UK, 2002.
  52. Louis, B.; Walspurger, S.; Sommer, J. Quantitative Determination of Brönsted Acid Sites on Zeolites: A New Approach towards the Chemical Composition of Zeolites. Catal. Lett. 2004, 93, 81–84.
  53. Koltunov, K.Y.; Walspurger, S.; Sommer, J. Superelectrophilic Activation of Polyfunctional Organic Compounds Using Zeolites and Other Solid Acids. Chem. Commun. 2004, 15, 1754.
  54. Koltunov, K.Y.; Walspurger, S.; Sommer, J. Cyclization of 1-Phenyl-2-Propen-1-Ones into 1-Indanones Using H-Zeolite and Other Solid Acids. The Role of Mono- and Dicationic Intermediates. Tetrahedron Lett. 2005, 46, 8391–8393.
  55. Koltunov, K.Y.; Walspurger, S.; Sommer, J. Selective, C,C-Double Bond Reduction of α,β-Unsaturated Carbonyl Compounds with Cyclohexane Using Zeolites. J. Mol. Catal. A Chem. 2006, 245, 231–234.
  56. Ye, J.; Li, J.; Sha, Y.; Xu, Y.; Zhou, D. Novel Reactive Distillation Process for Phenol Production with a Dry Cation Exchange Resin as the Catalyst. Ind. Eng. Chem. Res. 2014, 53, 12614–12621.
  57. Huang, D.; Han, M.; Wang, J.; Jin, Y. Catalytic Decomposition Process of Cumene Hydroperoxide Using Sulfonic Resins as Catalyst. Chem. Eng. J. 2002, 88, 215–223.
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