EP1523466A1 - Decomposition of cumene oxidation product - Google Patents

Decomposition of cumene oxidation product

Info

Publication number
EP1523466A1
EP1523466A1 EP02761128A EP02761128A EP1523466A1 EP 1523466 A1 EP1523466 A1 EP 1523466A1 EP 02761128 A EP02761128 A EP 02761128A EP 02761128 A EP02761128 A EP 02761128A EP 1523466 A1 EP1523466 A1 EP 1523466A1
Authority
EP
European Patent Office
Prior art keywords
acetone
reactor
reaction mixture
chp
decomposition
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Withdrawn
Application number
EP02761128A
Other languages
German (de)
English (en)
French (fr)
Inventor
Bernard K. Marshall, Jr.
Anthony J. Decaria
Richard R. Hertzog
Stylianos Sifniades
William B. Fisher
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Sunoco Inc R&M
Original Assignee
Sunoco Inc R&M
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Sunoco Inc R&M filed Critical Sunoco Inc R&M
Publication of EP1523466A1 publication Critical patent/EP1523466A1/en
Withdrawn legal-status Critical Current

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C1/00Preparation of hydrocarbons from one or more compounds, none of them being a hydrocarbon
    • C07C1/20Preparation of hydrocarbons from one or more compounds, none of them being a hydrocarbon starting from organic compounds containing only oxygen atoms as heteroatoms
    • C07C1/24Preparation of hydrocarbons from one or more compounds, none of them being a hydrocarbon starting from organic compounds containing only oxygen atoms as heteroatoms by elimination of water
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C37/00Preparation of compounds having hydroxy or O-metal groups bound to a carbon atom of a six-membered aromatic ring
    • C07C37/08Preparation of compounds having hydroxy or O-metal groups bound to a carbon atom of a six-membered aromatic ring by decomposition of hydroperoxides, e.g. cumene hydroperoxide
    • CCHEMISTRY; METALLURGY
    • C07ORGANIC CHEMISTRY
    • C07CACYCLIC OR CARBOCYCLIC COMPOUNDS
    • C07C45/00Preparation of compounds having >C = O groups bound only to carbon or hydrogen atoms; Preparation of chelates of such compounds
    • C07C45/51Preparation of compounds having >C = O groups bound only to carbon or hydrogen atoms; Preparation of chelates of such compounds by pyrolysis, rearrangement or decomposition
    • C07C45/53Preparation of compounds having >C = O groups bound only to carbon or hydrogen atoms; Preparation of chelates of such compounds by pyrolysis, rearrangement or decomposition of hydroperoxides

Definitions

  • This invention relates to a process for the preparation of phenol wherein relatively high yields of alpha-methylstyrene (AMS), a useful by-product, are obtained.
  • AMS alpha-methylstyrene
  • Phenol is manufactured via air oxidation of cumene to cumene hydroperoxide
  • CHP decomposition is a very exothermic reaction which is normally carried out on a commercial scale in continuous stirred or back-mixed reactors. In such reactors only a small fraction of CHP remains at any given time and the reaction medium consists essentially of the products of decomposition of CHP, i.e., phenol and acetone, plus any solvent (e.g., cumene) and other materials added with CHP to the reactor.
  • solvent e.g., cumene
  • DMPC dimethyl phenyl carbinol
  • acetophenone acetophenone
  • DMPC dehydrates to AMS, a useful by-product.
  • Very high yields of AMS can be obtained from pure DMPC, e.g., 98 percent yield upon dehydration over acidic silica at 300°C.
  • the AMS yield is normally about 50-60 mol percent of the DMPC.
  • Main by-products are AMS dimers and cumylphenol which have no commercial value. Formation of cumylphenol also reduces the phenol yield.
  • G. G. Joris U.S. Patent 2,757,209, teaches that the amount of AMS dimers and cumylphenol formed can be substantially reduced by carrying out the reaction in two stages, hi the first stage CHP is decomposed in a stirred or back-mixed reactor in the presence of small amounts of sulfur dioxide as catalyst and water as catalyst moderator.
  • Preferred conditions are: temperature 45-65°C sulfur dioxide 50-500 ppm, water 2-5 weight percent. Under these conditions the CHP concentration in the reaction mixture withdrawn from the reactor is less than 5 percent but more than 1 percent by weight.
  • the mixture withdrawn from the first reactor is heated in a second reactor, optionally with additional catalyst, in order to decompose residual CHP and to effect the dehydration of DMPC to AMS.
  • This second reactor is either a batch reactor, or a continuous plug-flow reactor. Preferred conditions are: temperature 110-120°C, reaction time 5-15 minutes. Care must be taken to stop the high temperature reaction once AMS formation is completed so as to minimize dimerization of AMS or the reaction of AMS with phenol to form by-products.
  • the present invention is concerned with the decomposition of cumene oxidation product in high yield to phenol, acetone and AMS, and particularly with the means of effecting such decomposition in a relatively stable and economical manner.
  • acetone By adding acetone to the cumene oxidation product reaction mixture, in addition to acetone normally produced by the decomposition of CHP, relatively high yields of AMS are obtained even with residual CHP as low as 0.2 weight percent.
  • the additional acetone may most conveniently be obtained by adiabatic flash evaporation of crude product downstream of the process. In this way the heat content of the crude product is utilized to produce the recycle acetone and energy savings are achieved.
  • the additional acetone may also be obtained by refluxing an overhead vapor produced in the first stage reactor or series of reactors. The acetone obtained in these manners may also contain significant amounts of water.
  • An embodiment of the present invention includes a process for decomposing a cumene oxidation product mixture containing CHP and DMPC to produce phenol, acetone and AMS with enhanced safety of operation and reduced by-product formation which comprises the steps: [0010] (a) mixing the cumene oxidation product in a first reactor (e.g. a stirred or back- mixed reactor) with an acid catalyst, with 10 to 100 percent acetone relative to the amount of acetone produced during the reaction and with an effective amount of water, at an average temperature between about 50°C and about 90°C for a time sufficient to lower the average CHP concentration of the reactor to between about 0.2 and about 3.0 weight percent and wherein a portion of DMPC is converted to DCP; then
  • a first reactor e.g. a stirred or back- mixed reactor
  • an acid catalyst e.g. a stirred or back- mixed reactor
  • step (b) reacting the reaction mixture from step (a) at a temperature between about 120 and 150°C under plug-flow conditions for a time sufficient to decompose substantially all residual CHP and at least 90% of DCP formed in step (a).
  • the product from step (b) is submitted to adiabatic flash evaporation, recovering an acetone-rich distillate which is recycled to step (a) to provide said acetone.
  • an acetone rich vapor from the cumene oxidation product reaction mixture from step (a) is condensed at a condenser or heat exchanger to provide said acetone.
  • the effective amount of water is an amount up to about 10 wt% of the reaction mixture. In a preferred process, the effective amount of water is up to about 4 wt% of the reaction mixture
  • step (a) additionally comprises reacting the reaction mixture having an average CHP concentration of between about 0.2 and about 3.0 weight percent at between 50°C and about 90°C under plug-flow conditions for a time sufficient to produce a reaction mixture having a CHP concentration no greater than about 0.4 weight percent.
  • the invention includes a method for controlling variables in the reactor or series of reactors to eliminate or dampen fluctuations in the process operating conditions. These variables include residence time, temperature, acetone and water content. In one embodiment, automated controls are implemented for residence time and the first reactor content.
  • the method includes: providing an excess amount of acetone in the reaction mixture in the first reactor; monitoring the content of an acetone addition stream; adjusting the feed rate of at least one of said inlet streams to offset fluctuations in the content of said acetone stream; and controlling the residence time of the first reactor.
  • the method mcludes reacting the reaction mixture in a first reactor (or series of reactors) to decompose the CHP in the cumene oxidation product to phenol and acetone, and convert the DMPC in the cumene oxidation product to DCP, and in a second reactor, having plug flow conditions and elevated temperatures relative to the first reactor, convert the DCP formed in the first reactor into AMS and water.
  • the method includes adding excess acetone to the reaction mixture from about 10 to 100% excess acetone relative to the amount of acetone produced during the decomposition reaction, and optionally, water in an adjustable feed stream.
  • the embodiment also includes monitoring the content of the acetone added to the reaction mixture, and adjusting the amount of water added to the reaction mixture based on the content of the acetone in order to maintain a substantially constant amount of water and acetone in the first reactor or series of reactors.
  • the acetone solution is provided by recycling acetone within the phenol plant, e.g. by recovering the acetone solution from a crude product stream following the decomposition of DCP to AMS or other effluent stream.
  • an acetone solution is recovered and recycled from an effluent stream to the first reactor.
  • the average temperature in the first reactor (or series of reactors) is between about 50°C and 90°C and said average temperature in the plug-flow reactor for dehydrating the DCP is greater than said average temperature in the first reactor, provided that the second average temperature does not exceed 150°C.
  • acetone is obtained by refluxing an acetone rich vapor in the first stage reactor or series of reactors
  • the step of refluxing the acetone includes cooling the acetone rich vapor into an acetone containing mixture, collecting the acetone containing mixture in a vessel, and returning the acetone containing mixture to the cumene oxidation product reaction mixture
  • the method includes automatically adjusting the amount of additional water added to the reaction mixture to dampen fluctuations in the mass composition of water in the recycle acetone added to the reaction mixture from the down-stream distillation area. This recycle acetone is added such that the amount of excess acetone is established and maintained in the reaction mixture at a substantially constant amount between about 10% to 100% acetone above the amount of acetone produced during the decomposition reaction.
  • the level of reaction mixture in a first stage cleavage reactor or series of reactors is allowed to fluctuate in order to control the residence time in the reactor or series of reactors.
  • the method includes controlling the concentration of CHP and DCP in the reaction mixture and controlling the residence time in the reactors.
  • the standard deviation of the rise in temperature following acid addition to a slipstream, referred to herein as d(T) is less than 1.5. In one embodiment, this standard deviation is reduced to less than about 0.5.
  • FIG. 1 shows a schematic arrangement of first example of equipment useful in practicing the process of this invention which includes a recycle acetone stream.
  • FIG. 2 provides AMS yield versus CHP concentration in the stirred reactor for 60 percent, 40 percent, and no acetone recycle.
  • FIG. 3 depicts a simplified schematic diagram of a second example of the equipment used in practicing the process of the invention, including both a recycle acetone stream and a reflux acetone stream.
  • the method and process of the invention comprises the following steps.
  • cumene oxidation product is mixed with an acid catalyst, with acetone and optionally with a small quantity of water in a first cleavage or decomposition reactor, typically a stirred or back-mixed reactor, and is held for a sufficient time to reduce the average CHP content of the reactor to between about 0.2 and about 3.0 wt percent.
  • step (a) the effluent from step (a), is reacted at an elevated temperature, preferably between about 120 and 150°C for a sufficient time in a plug-flow reactor to complete the decomposition to phenol, acetone and AMS.
  • the acetone is collected from the effluent from step (b), preferably by submitting the effluent to an evaporation step, more preferably an adiabatic flash evaporation, to produce an acetone-rich distillate. This distillate is then recycled to the reactor of step (a). It may be preferred that in step (a), the effluent from the first reactor is also held in a plug-flow reactor for a sufficient time to reduce the CHP content to below 0.4 weight percent before proceeding with step (b). In these embodiments, the decomposition or cleavage of CHP to phenol and acetone takes place in a series of reactors, e.g. stirred reactors, back-mixed reactors, or plug flow reactors, isothermal or at differing temperatures relative to the first reactor in the series.
  • a series of reactors e.g. stirred reactors, back-mixed reactors, or plug flow reactors
  • the acid catalyst used in the process is selected from the group comprising sulfur dioxide, strong inorganic acids such as sulfuric, perchloric and the like, strong organic acids such as toluene sulfonic acid, and Lewis acids such as boron trifluoride or aluminum chloride.
  • Typical acid catalyst levels are between 30 and 500 ppm (0.003-0.050 weight percent) of the reaction mass.
  • Preferred catalysts include sulfuric acid and sulfur dioxide. It is believed that the acetone, or acetone and water solution, reduce the strength of the acidic catalyst and moderate the reaction, either by dilution/phase separation, as a Lewis base, or both. However, no assertion of or reliance upon these theories is made herein as underlying the improved reaction specificity.
  • the acetone used in the process may come from any convenient source, and may contain varying amounts of water.
  • a preferred source is the acetone already produced in phenol producing plants, e.g. from the adiabatic flash-evaporation of the effluent from step (b). Additionally, flash evaporation of this effluent cools the flash residue. Since this effluent stream must normally be cooled before neutralization of the acid catalyst, the cooling caused by flash evaporation also reduces cooling expenditures that would be otherwise required in the production process.
  • Additional sources for recycled acetone produced in phenol plants includes the acetone rich vapor from the overhead of the first reactor (or series of reactors) for decomposing CHP, or acetone obtained in distillation or waste streams.
  • Evaporation of the reaction mixture helps cool the reaction and control the reactor temperature. Given and the relatively high volatility of acetone, the vapor typically contains a relatively high concentration of acetone and may be condensed and returned to the reaction mixture. [0029] It is recognized that these exemplar sources may be used to increase the amount of acetone in the reaction mixture above that produced by the reaction itself, and may save energy that would be otherwise required to cool the reaction mixture or evaporate the added acetone. It is also recognized that these sources may be used alone or in combination. [0030] The amount of acetone added to the reaction mixture is from about 10 percent to about 100 percent of the amount produced during the reaction.
  • the recycled acetone corresponds from about 3 to about 30 weight percent of the oxidation product. Amounts less than 10 percent of that produced during the reaction have no significant beneficial effect on the reaction. Amounts higher than 100 percent are economically unattractive.
  • Water is also normally produced during the process in the dehydration and condensation reactions of DMPC. Additional amounts of water are introduced with the recycled acetone, especially if it is obtained by flash evaporation of the product of the second stage decomposition, plug-flow reactor. Acetone thus produced may contain from about 1 to about 5 weight percent of water.
  • the water produced in the reaction and that introduced with the acetone is sufficient to moderate the activity of the acid catalyst.
  • small additional amounts of water may be added to further moderate the activity of the catalyst, and most preferably in a controlled amount to offset fluctuations in the amount of water introduced with the acetone. This is accomplished by monitoring the content of the acetone stream, and adjusting the feed rate of the water stream accordingly to maintain a substantially constant addition of water and acetone to the reaction mixture in the first reactor or series of reactors.
  • the total amount of added water should not exceed about 4 weight percent of the reaction mixture. Too much water may cause the catalyst to become less active and slow down the reaction.
  • the average temperature in step (a) is from about 50°C to about 90°C.
  • the temperature may be maintained either by means of heat exchangers or by means of evaporative cooling. In the latter case the pressure of the reactor may be substantially below atmospheric so that the desired temperature may be achieved.
  • acetone may preferably be obtained by condensing this vapor into an acetone rich solution and returning it to the reaction mixture.
  • the residence time is from about 5 minutes to 2 hours. It will be appreciated that the operational objective is to maintain the average CHP concentration in the first reactor from between about 0.2 weight percent to about 3 wt percent. This can be achieved by an almost infinite variety of reaction conditions within the limits herein prescribed keeping in mind the following:
  • step (a) is carried out in a well-stirred reactor, both the temperature and the
  • CHP concentration at various points of the reactor vary little from their respective average values. In such a reactor it is sufficient to monitor these quantities at only one point. If, however, a back-mixed reactor is employed, there will exist gradients of temperature and CHP concentration the magnitude of which will depend on the reactor geometry and recirculation ratio. In such a reactor the average temperature and CHP concentration are defined as the temperature and concentration that would result if the reactor contents were to be instantly homogenized. To estimate the averages it may be necessary to monitor the temperature and the CHP concentration in more than one point. Monitoring CHP is essential to the success of this process. To achieve a stable and safe operation it is preferable to have on-line analysis for CHP.
  • step (b) This can be accomplished, for example, by means of an automatic hydroperoxide titrator, or by measuring the temperature rise in a slip-stream off the reactor circulated over a strongly acidic ion exchange resin as taught in Japanese Patent 7,446,278 to Mitsui, or by any other means.
  • U.S. 4,358,618 teaches that before completing the reaction in step (b), it is desirable to ensure that the CHP content of the reaction mixture is below 0.4, weight percent. This is so, because heating CHP at the relatively high temperatures of step (b) causes a small increase in the formation of by-products.
  • step (a) Further CHP decomposition is accomplished in step (a) by optional steps (d) which normally employs a tube with residence time of up to a few minutes, hi the process of the present invention the CHP content of the effluent from step (a) may be below 0.4 weight percent. In that case step (d) is not needed. Even at high CHP levels, step (d) may be omitted as a separate piece of equipment because CHP largely decomposes during the heatup period in the heat exchanger which is part of step (b) and which may fulfill the function of step (d).
  • Step (a) is performed in back-mixed reactor 1 at between 50°C and 90°C under conditions establishing a residence time of 5 - 120 minutes.
  • Technical CHP, acetone, acid catalyst and water are introduced to the reactor through inlets 2, 3, 4, 5 respectively.
  • the desired temperature is maintained by means of circulation through cooler 6. Due to the strong exothermicity of CHP decomposition, the minimum residence time in reactor 1, which includes time spent in cooler 6, is determined by the design of the cooler and the nature of cooling fluid. A practical lower limit of approximately 5 minutes is imposed if the coolant is water.
  • Lower residence may be achieved if a refrigeration system is employed.
  • the upper limit of residence time depends on the temperature, the acid content, the acetone content and the water content of the reaction mixture. A residence time of approximately 120 minutes may be considered as the upper limit. Preferred residence time is between 10 and 60 minutes.
  • step (d) of the reaction may be carried out in tube 7 which may have sufficient capacity to provide a residence time between 0.1 and 5 minutes.
  • the temperature in tube 7 is approximately the same as in 1. No means for cooling is provided, because the only significant reaction taking place in this step is decomposition of residual CHP which has already been reduced to 0.2 - 3 percent level in step (a).
  • step (b) is carried out, i.e. decomposition of DCP and dehydration of DMPC to AMP as well as complete decomposition of any residual CHP.
  • the temperature at the exit of pipe 9 is normally somewhat higher than that at the exit of heat exchanger 8 due to these reactions. Best AMS yields are obtained if the residence time in heater 8 is relatively short (e.g. under 30 seconds) compared to that in pipe 9 (at least 30 additional seconds), because in that way most of the residual DMPC and DCP decompose at the higher temperature regime which favors AMS formation.
  • Pipe 9 is fitted with sampling ports at the entrance 9A, at an intermediate point 9B and at the exit 9C, for monitoring DCP concentration.
  • step (c) the reaction product' is cooled by 10 - 60°C.
  • remedial measures e.g. increasing the reactor's residence time, increasing the acid concentration to above optimum levels, or even shutting down the reactor, thereby significantly reducing the plant's phenol, acetone, and AMS capacity.
  • the operator's remedial measures may also have only a delayed effect upon the reaction. Typical lag times between implementation and impact upon dT vary from between 1 to 30 minutes. Regardless, an excess or a lack of CHP will reduce the yield of AMS, phenol and acetone.
  • FIG. 3 depicts an apparatus according to the additional embodiment of the invention, including a stirred first stage cleavage reactor, a condenser for returning acetone to the first stage reactor, and a second stage dehydration reactor, e.g. a plug flow reactor.
  • a stirred first stage cleavage reactor for returning acetone to the first stage reactor
  • a second stage dehydration reactor e.g. a plug flow reactor.
  • the range of variability in AMS yield spanned from a low of about 63 mol percent to a high of about 83 mol percent over the course of a three year period for two reactors having a design as depicted in FIG. 3, but with a set reactor level and without residence time controls.
  • the sources for this variability were investigated, and found to be based primarily in fluctuations in the reaction mixture's content while in the first stage reactor.
  • Investigation of the process revealed high variability in d(T) value, in both short term d(T) values, e.g. variability in 1-3 minutes, and long term d(T) values, e.g.
  • the long term variability appeared to be caused by fluctuations in the residence time and water concentration in the reactor.
  • a reactant species e.g. CHP, DMPC, DCP, etc.
  • Control of the residence time was accomplished by allowing the liquid level of the first stage cleavage reactor (also referred to herein as the decomposer, or first reactor(s)) to fluctuate based upon the total feed rate to the reactor, albeit these fluctuations should of course be within the safety parameters of the individual reactor.
  • EXAMPLE 1 A cumene oxidation product that contained 81.6 weight percent CHP, 5.00 weight percent DMPC and 0.40 weight percent acetophenone, the balance being mostly cumene, was. pumped at the rate of 1.62g/min into a thermostated pyrex Morton flask equipped with magnetic stirring and an overflow device that maintained the volume of the reaction mixture at 30mL. Simultaneously, an acetone solution containing 0.86 weight percent AMS, 2.06 weight percent phenol, 5.83 weight percent cumene, 1.60 weight percent water and 0.0512 weight percent sulfuric acid was pumped into the reactor at the rate of 0.230 g/min.
  • the composition of the acetone solution, except for the acid content, corresponded to that of a flash distillate that could be obtained from the product of the reaction.
  • the acetone added was equivalent to approximately 40 percent of the acetone produced during the reaction.
  • the acid content was calculated to maintain 80 ppm in the reaction mixture.
  • the residence time in the reactor was 16 minutes and the temperature 80°C.
  • the stirred reactor effluent was pumped through a 1/8" stainless steel tube reactor immersed in a bath at 125°C.
  • the residence time in the tube was 1.6 minutes. After the two reactors had reached steady-state operation, samples were withdrawn for analysis as the exit of each reactor. Subsequently, the temperature of the bath in which the tube reactor was submerged was increased to 135°C and again to 145°C.
  • AMS 0 is the concentration of AMS in the charge and CE is the total carbinol
  • CE equivalent which is defined as the sum of all products that can be formed by reactions of DMPC.
  • the main components of CE are DMPC, AMS, DCP, AMS dimers and cumylphenol.
  • Table I Other examples using substantially the same cumene oxidation product but variable reaction conditions are summarized in Table I. Examples 7 through 11 utilized no added acetone and they are shown for comparison purposes. In example 12 the acetone added corresponded to 60 percent acetone recycle but the sulfuric acid was increased to .500 pm and the residence time to 20 minutes so that the residual concentration of CHP in the stirred reactor effluent was substantially zero. DCP was 0.55 weight percent.
  • the yield of AMS in the stirred reactor effluent was 62.6% and it increased to 68.1% after further reaction at* 125°C in a tube reactor. In some examples a post-reactor isothermal to the stirred reactor was also used. This was 1/8" stainless steel tube with residence time approximately 3 minutes.
  • the maximum yield of AMS obtained in these examples is plotted in FIG. 2 against the concentration of residual CHP in the stirred reactor. The lowest curve (open squares) represents examples with no recycled acetone. The middle curve (squares with an x) represents examples with 40 percent acetone recycle. The upper curve (solid squares) represents examples with 60 percent acetone recycle. It is clear from FIG.
  • FIG. 3 is a simplified schematic diagram of a decomposition of cumene oxidation product system 30.
  • the system includes a first reactor 32 operating with an adjustable reactor level; a condenser 40 and reflux acetone collection vessel 42; and a second reactor 46 for DCP dehydration having plug flow conditions and an elevated temperature, which produces decomposition product mixture stream 48.
  • First reactor 32 is a continuously stirred, tank reactor, and is fed by cumene oxidation product stream 34, recycle acetone stream 35, sulfuric acid feed stream 38, and water feed stream 36. Water is added in an amount of up to about 10% by weight of the reaction mixture.
  • Typical operating conditions for reactors of this design are depicted in Table 2 below, though these conditions can vary substantially from reactor to reactor depending on the processing plant's design and system tolerances. Otherwise, the reaction conditions in first reactor 32 are similar to those described in reference to FIG. 1.
  • first reactor 32 is a continuously stirred tank reactor having similar temperature, residence times and reaction mixture compositions as described in reactor 1, FIG. 1, although configured to operate using a boiling reaction mass.
  • An acetone overhead vapor produced in first reactor 32 is cooled by condenser 40 and collected in reflux collection vessel 42. The predominantly acetone mixture is then allowed to run back into the reaction mixture.
  • the reflux acetone collected contains 90-95% acetone, and 4 to 7% water, with the balance being organic reaction components of the reaction mixture.
  • the amount of CHP in the reaction mixture in reactor 32 is also monitored by online analysis of slipstream 50. In this example, slipstream 50 represents an extremely small amount of reaction mass.
  • the temperature of the reaction mixture is measured initially after it is withdrawn from the reactor through slipstream 50, an excess amount of acid catalyst is then added to the slipstream, preferably using a mixing "T" or small vessel (not shown).
  • the excess acid catalyst causes the exothermic decomposition of the residual CHP and the DCP present in the reaction mixture, causing a rise in temperature.
  • the value dT represents the difference in temperature of the slipstream before and after acid addition..
  • the system also included an automatic temperature alarm (not shown) set to initiate an automatic shutdown should the dT of reaction mixture exceed a maximum safe value.
  • the maximum safe value in the system used was 22 to 26 F, however, this value can be higher or lower in other systems depending on a number of factors, includmg the system's configuration, condition and age.
  • the reaction mixture is sent through pipe 42 to second reactor 46, with 10% of the reaction mixture being diverted to the acid feed mixing T to dilute the acid stream 38 prior to being fed to first reactor 32.
  • Second reactor 46 is maintained at an elevated temperature relative to first reactor
  • the acetone added to the reactor in recycle acetone stream 34 contains acetone recovered from effluent streams elsewhere in the phenol plant. Its content is monitored using automated online analysis, and the feed rate of the water addition stream is automatically adjusted to offset or dampen fluctuations in the content of the acetone stream.
  • the benefits of the present invention have been demonstrated comparison of the fluctuations in dT values in a test reactor before and after implementation of dampening controls and reactor level fluctuation. First, over a twenty day control test period without dampening controls and without residence time control, the dT value was seen to fluctuate abruptly from 6 to over 16 over both short and long term periods.
  • the average water feed rate increased slightly from 1.33, and to 1.49, while the residence time increased from 6.66 and to 6.99.
  • typically increasing water feed and increasing residence time are undertaken in response to a short term increase in dT, to cause a reduction in dT, and result in a corresponding reduction in AMS yield.
  • the increase in process stability ensured that the process was operated safely, but with an increase in the average dT from 10.66 to almost 12, with an expected corresponding increase in AMS yield.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Organic Low-Molecular-Weight Compounds And Preparation Thereof (AREA)
EP02761128A 2002-07-19 2002-07-19 Decomposition of cumene oxidation product Withdrawn EP1523466A1 (en)

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
PCT/US2002/022968 WO2004009522A1 (en) 2002-07-19 2002-07-19 Decomposition of cumene oxidation product

Publications (1)

Publication Number Publication Date
EP1523466A1 true EP1523466A1 (en) 2005-04-20

Family

ID=30769018

Family Applications (1)

Application Number Title Priority Date Filing Date
EP02761128A Withdrawn EP1523466A1 (en) 2002-07-19 2002-07-19 Decomposition of cumene oxidation product

Country Status (5)

Country Link
EP (1) EP1523466A1 (zh)
JP (1) JP2005533848A (zh)
CN (1) CN1639097A (zh)
AU (1) AU2002326413A1 (zh)
WO (1) WO2004009522A1 (zh)

Families Citing this family (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US7141700B1 (en) * 2005-08-19 2006-11-28 Uop Llc Decomposition of cumene hydroperoxide
US7141701B1 (en) * 2005-08-19 2006-11-28 Uop Llc Decomposition of cumene hydroperoxide
US20110306800A1 (en) * 2010-06-09 2011-12-15 Scott Roy Keenan Method for the decomposition of cumene hydroperoxide
EP2616423A1 (en) 2010-09-14 2013-07-24 Exxonmobil Chemical Patents Inc. Processes for producing phenol
US9469589B2 (en) 2011-06-30 2016-10-18 Exxonmobil Chemical Patents Inc. Process for producing phenol and/or cyclohexanone
WO2014209577A1 (en) * 2013-06-28 2014-12-31 Exxonmobil Chemical Patents Inc. Process for producing phenol and/or cyclohexanone
JP2017508857A (ja) * 2014-06-17 2017-03-30 ポリム テクノロジー コーポレーションPolym Technology Corporation 共役複素芳香環重合体を含む電気活性重合体溶液または塗膜を形成する組成物および方法、電気活性重合体溶液、電気活性塗膜を含むコンデンサ(キャパシタ)および帯電防止体、および固体電解質コンデンサとその製造方法
CN105669367B (zh) * 2016-03-10 2017-09-19 张殿豪 一种提高过氧化氢异丙苯分解收率的方法
WO2021257950A1 (en) * 2020-06-19 2021-12-23 Kellogg Brown & Root Llc Acetone recovery and purification
JP7464211B2 (ja) * 2020-12-21 2024-04-09 エルジー・ケム・リミテッド α-メチルスチレンの製造方法

Family Cites Families (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US20020040165A1 (en) * 1989-01-17 2002-04-04 Hertzog Richard R. Decomposition of cumene oxidation product
US5463136A (en) * 1994-12-22 1995-10-31 Shell Oil Company Cumene hydroperoxide cleavage process
JP3769050B2 (ja) * 1995-07-07 2006-04-19 三井化学株式会社 フェノールの製造方法

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
See references of WO2004009522A1 *

Also Published As

Publication number Publication date
AU2002326413A1 (en) 2004-02-09
WO2004009522A1 (en) 2004-01-29
JP2005533848A (ja) 2005-11-10
CN1639097A (zh) 2005-07-13

Similar Documents

Publication Publication Date Title
US7166752B2 (en) Decomposition of cumene oxidation product
EP0738698B1 (en) Process for decomposition of cumene hydroperoxide
US5430200A (en) Process for producing phenol from cumene
RU2108318C1 (ru) СПОСОБ ПОЛУЧЕНИЯ ФЕНОЛА, АЦЕТОНА И α МЕТИЛСТИРОЛА
RU2141938C1 (ru) Энергосберегающий и высокоселективный способ получения фенола и ацетона (процесс иф-96)
WO2004009522A1 (en) Decomposition of cumene oxidation product
US7141701B1 (en) Decomposition of cumene hydroperoxide
JP3769050B2 (ja) フェノールの製造方法
WO2007024572A2 (en) Decomposition of cumene hydroperoxide
EP1042264B1 (en) High selective method of phenol and acetone production
RU2142932C1 (ru) Высокоселективный способ получения фенола и ацетона (процесс фан-98)
US7312365B2 (en) Process for low temperature cleavage of an oxidation mixture comprising hydroperoxides
US5463136A (en) Cumene hydroperoxide cleavage process
US20020040165A1 (en) Decomposition of cumene oxidation product
JP2000178214A (ja) 酸触媒によるクメンヒドロペルオキシドの分解によるフェノ―ルおよびアセトンの製造方法
KR20050025356A (ko) 큐멘 산화 생성물의 분해
US6630608B2 (en) Process for preparing phenols
TW583167B (en) Decomposition of cumene oxidation product
US4297518A (en) Decomposition of cumene hydroperoxide with a homogeneous catalyst
US4210607A (en) Decomposition of cumene hydroperoxide using a stable nitrosonium or nitronium salt as the catalyst
US6444861B1 (en) Process for the cleavage of alkylaryl hydroperoxides
US2868828A (en) Method of removing lactonitrile from aqueous mixtures
JPH0597744A (ja) 晶析生成物から分離された母液の処理方法
MXPA00004379A (en) High selective method of phenol and acetone production

Legal Events

Date Code Title Description
PUAI Public reference made under article 153(3) epc to a published international application that has entered the european phase

Free format text: ORIGINAL CODE: 0009012

17P Request for examination filed

Effective date: 20041222

AK Designated contracting states

Kind code of ref document: A1

Designated state(s): AT BE BG CH CY CZ DE DK EE ES FI FR GB GR IE IT LI LU MC NL PT SE SK TR

AX Request for extension of the european patent

Extension state: AL LT LV MK RO SI

DAX Request for extension of the european patent (deleted)
17Q First examination report despatched

Effective date: 20060719

STAA Information on the status of an ep patent application or granted ep patent

Free format text: STATUS: THE APPLICATION IS DEEMED TO BE WITHDRAWN

18D Application deemed to be withdrawn

Effective date: 20061130