WO2000025901A1 - Process for low temperature removal of volatile organic compounds from industrial exhaust gas - Google Patents
Process for low temperature removal of volatile organic compounds from industrial exhaust gas Download PDFInfo
- Publication number
- WO2000025901A1 WO2000025901A1 PCT/US1999/019967 US9919967W WO0025901A1 WO 2000025901 A1 WO2000025901 A1 WO 2000025901A1 US 9919967 W US9919967 W US 9919967W WO 0025901 A1 WO0025901 A1 WO 0025901A1
- Authority
- WO
- WIPO (PCT)
- Prior art keywords
- catalyst
- bed
- gaseous stream
- percent
- organic compounds
- Prior art date
Links
Classifications
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/70—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
- B01J23/76—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
- B01J23/84—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with arsenic, antimony, bismuth, vanadium, niobium, tantalum, polonium, chromium, molybdenum, tungsten, manganese, technetium or rhenium
- B01J23/889—Manganese, technetium or rhenium
- B01J23/8892—Manganese
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D53/00—Separation of gases or vapours; Recovering vapours of volatile solvents from gases; Chemical or biological purification of waste gases, e.g. engine exhaust gases, smoke, fumes, flue gases, aerosols
- B01D53/34—Chemical or biological purification of waste gases
- B01D53/74—General processes for purification of waste gases; Apparatus or devices specially adapted therefor
- B01D53/86—Catalytic processes
- B01D53/8668—Removing organic compounds not provided for in B01D53/8603 - B01D53/8665
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J23/00—Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
- B01J23/002—Mixed oxides other than spinels, e.g. perovskite
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01D—SEPARATION
- B01D2257/00—Components to be removed
- B01D2257/70—Organic compounds not provided for in groups B01D2257/00 - B01D2257/602
- B01D2257/708—Volatile organic compounds V.O.C.'s
-
- B—PERFORMING OPERATIONS; TRANSPORTING
- B01—PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
- B01J—CHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
- B01J2523/00—Constitutive chemical elements of heterogeneous catalysts
-
- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02A—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
- Y02A50/00—TECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE in human health protection, e.g. against extreme weather
- Y02A50/20—Air quality improvement or preservation, e.g. vehicle emission control or emission reduction by using catalytic converters
Definitions
- This invention provides a method to substantially reduce the content of volatile organic compounds (VOCs) in industrial exhaust gas to enable the processes generating these gases to comply with increasingly stringent limits required by environmental control regulations.
- VOCs volatile organic compounds
- an adiabatic oxidation process may be suitable because the oxidation reaction heat is sufficient to keep the reactor temperature in an acceptable operating range. If the impurities concentration is lower than 0.05%, an isothermic process is needed which will require additional heat from a source outside the process. Such a process is described in U.S. patent 5,292,991 Cl. C07C 7/152, C07C 7/00, issued March 8, 1994.
- hydrocarbons and oxygen-containing organics are oxidized at 600°C over platinum-palladium catalyst modified with zirconium and titanium.
- the disadvantage of this process is the necessity to heat the gas stream to a high temperature and its use of noble metals as the catalyst.
- hopcalite-type catalysts containing active manganese dioxide and copper oxide
- hopcalite catalyst modified with yttrium, lithium , and lanthanum in an amount of from 3 to 15% provides practically complete hydrocarbons and oxygen-containing compounds conversion (starting concentration 400 - 2000 ppm) at 250 - 400°C.
- hopcalite is used as a generic term to identify at column 4, lines58 to 60, a copper/ manganese compound used in gas masks to convert carbon monoxide into carbon dioxide.
- Ozone Engineering uses "Hopcalite” as a trademark in its literature describing Hopcalite Catalyst- H Grade with a composition being a mixture of manganese dioxide and copper oxide. Lee et al.
- the process for reducing the level of volatile organic compounds in a gaseous stream of the present invention substantially eliminates this detrimental formation of nitrogen oxides by the purification processes of the prior art by preparing a bed of catalyst comprising manganese dioxide, copper oxide and potassium oxide and passing through the catalyst bed a gaseous stream containing volatile organic compounds at a temperature of from about 50 to about 150°C. whereby the level of volatile organic compounds in the gaseous stream is reduced by at least about 90 percent.
- the present process inimize or substantially eliminate the formation of nitrogen oxides, but also its low operating temperature range substantially reduces the energy consumption of process which in turn reduces the environmental impact of the process and favorably affects the economics of its operation.
- the process of the present invention can be equally effective in VOCs removal from gaseous streams at temperatures as high as about 200 to about 250°C.
- industrial exhaust gas is intended to be construed in its broadest sense and includes any gaseous stream containing VOCs regardless of the source of these streams.
- Typical industrial exhaust gases include, but are not limited to, fugitive emissions and gases from vents from chemical processes, polymerization processes, waste treatment operations, storage vessels, power plants, warehouses, distillation towers, separators, paint booths, laboratory hoods, pilot plants, degreasing operations, paint stripping operations, synthetic fiber production and spinning, petroleum cracking, ore refining, hydrocarbon processing, mechanical assembly operations, paper mills, cloth preparation, livestock enclosures and the like.
- ethers preferably ethers
- the industrial waste gas streams purified by the method of this invention include any streams in which VOCs occur at low levels, e.g., no more than about 1000 ppm, preferably from about 20 to about 500 ppm, more preferably from about 80 to about 400 ppm, still more preferably from about 150 to about 250 ppm and most preferably about 200 ppm.
- Industrial waste streams in which the method of this invention is preferably useful are waste streams from processes synthesizing organic compositions, more preferably waste streams from processes synthesizing oxygen-containing aromatic compounds and still more preferably waste streams from processes for synthesizing phenol.
- the current invention surprisingly increases the activity of a manganese containing catalyst, such as a hopcalite catalyst, in exhaust gas purification to remove a high percentage, e.g., at least about 90%, preferably at least about 93%, more preferably at least about 96% and still more preferably at least about 98% of the VOCs present at low levels in the industrial waste gas stream at substantially lower temperatures without NOX formation.
- a manganese containing catalyst such as a hopcalite catalyst
- the present invention purifies waste streams contaminated with hydrocarbons by removing a high percentage, e.g.,at least about 90%, preferably at least about 93%, more preferably at least about 96% and still more preferably at least about 98% of the hydrocarbon VOCs present at low levels in the industrial waste gas stream at substantially lower temperatures by the substantially complete conversion to more highly oxygenated organic compounds which, preferably, in turn, may be further oxidized to water and carbon dioxide.
- a preferred manganese oxide/ copper oxide catalyst which is a hopcalite type catalyst is commercially available from Carus Chemical Company under the trademark, CARULITE ® , grade numbers 100, 110, 150, 200 and 300. and has a composition of about the following, as published in the trade literature:
- catalyst useful in the present process have compositions within this range as follows:
- manganese-containing catalysts useful in the process of the present invention have been described as having an elemental manganese content of from about 37 - 39 % elemental manganese and an elemental copper content of about 9 - 11 % elemental copper.
- the efficient and effective removal of VOCs from gaseous streams at low temperatures without substantial formation of NOX and with low energy consumption is accomplished by adding to the manganese-containing catalyst potassium oxide in amount of from about 0.01 to about 5% by weight, preferably from about 0.02 to about 4% by weight, more preferably from about 0.04 to about 3% by weight and still more preferably from about 0.05 to about 2.0% by weight of the catalyst, passing a gas stream, containing VOCs, over the manganese-containing catalyst containing the potassium oxide, at a temperature of from about 50 to about 135°C, preferably from about 70 to about 135°C, more preferably from about 90 to about 130°C and still more preferably from about 100°C to about 130°C and at a space velocity of from about 2000 to about 15000 hN Potassium oxide can be added to the catalyst composition in a stage of paste preparation by a known method (RF patent 2,064,834, Cl B 01 J 23/889, B 01 J 37/04), or with the feed compounds, used in catalyst production.
- the space velocity of the gaseous stream is not critical to the practice of the process of the present invention so long as there is adequate contact with the catalyst bed which can be in the form of either a fixed bed or fluidized bed, it is preferred that the space velocity be within the range of from about 1000 to about 200001V 1 , more preferably from about 2000 to about 5000h- ⁇ .
- the catalyst can be employed in the present process without a support or supported.
- a preferred support is alumina.
- catalyst life is important to the practice of the invention.
- a gaseous stream either added to the waste stream or separately oxygen at a volume percent of from about 2% to about 21% (the level of oxygen present in air), more preferably from about 4% to about 21% and still more preferably about 5% to about 21%, and operating the purification process at least about 100°C, catalyst life can be extended.
- Atmospheric air is the most convenient source of oxygen. It is postulated that at a temperature of 100°C.
- the manganese monoxide is regenerated to the catalytically active species of manganese dioxide in the presence of the cupric oxide, the other essential component of the catalyst.
- the process of the present invention in the lower portion of the operating temperature range, i.e., from about 50°C. up to less than about 100°C, it is preferable to employ two catalyst beds in the practice of the present process, allowing one to be in use while the other is being regenerated.
- the present process at about 100°C. or above only one catalyst bed is required in view of the self-regeneration of the bed as described above. A second benefit of operating the present process at about 100°C.
- a glass reactor of 2.26 cm 2 cross-sectional area is filled with hopcalite catalyst, containing 0.05% potassium oxide.
- the catalyst particle size is from about 1 to about 3 mm.
- the catalyst bed depth is about 19 cm.
- the reactor is heated by an electric jacket to 95 ⁇ 1°C. Gas is fed as a stream at a rate through the reactor of about 461/h.
- the incoming gas composition is as follows
- the glass reactor, described in Example 1 is filled with 23 ml of hopcalite catalyst, containing 2.0% potassium oxide.
- the catalyst bed temperature is 130 ⁇ 1°C.
- the gas stream has the same composition as in Example 1 and passes through the reactor at a rate of 345 1/h, a space velocity of 15000 rv 1 .
- the total methanol amount passed through the catalyst bed in the reactor was 0.368 g.
- the methanol amount collected in the traps described in Example 1 was 0.00074 g, i.e., methanol conversion 99.8%.
- the methanol concentration in the gas stream was reduced from 200 ppm to 0.4 ppm.
- the glass reactor, described in Example 1 is filled with 23 ml of hopcalite catalyst, containing 0.5% potassium oxide.
- the catalyst bed temperature is 100 ⁇ 1°C.
- a gas stream of the same composition as in Example 1 passes through the reactor at rate of 1151/h, space velocity 5000 rv 1 .
- the total amount of methanol passed through the catalyst bed in the reactor was 0.123 g.
- the methanol amount collected in the traps described in Example 1 was 0.00012 g, conversion 99.9%.
- the methanol concentration in the gas stream was reduced from 200 ppm to 0.2 ppm.
- the glass reactor, described in Example 1, was filled with 23 ml of hopcalite catalyst, containing 0.05% potassium oxide.
- the catalyst bed temperature was 130 ⁇ 1°C.
- Example 1 except for 0.02% of ethanol instead of methanol, is passed through the reactor at a rate of 2301/h, space velocity 10000 hN In a period of 4-hours, the total ethanol amount passed through the catalyst bed in the reactor was 0.353 g. The ethanol amount collected in the traps described in Example 1 was 0.00106 g, conversion 99.7%. The ethanol concentration in the gas stream was reduced from 200 ppm to 0.6 ppm.
- Example 1 The glass reactor described in Example 1 was filled with 23 ml of hopcalite catalyst, containing 2.0% potassium oxide. Catalyst bed temperature was 95+1 °C.
- the gas stream had the same composition as indicated in Example 1, except for 0.02% of ethanol instead of methanol, and was passed through the reactor at a rate of 461/h, space velocity 2000 hN In a the traps described in Example 1 was 0.00099 g, conversion 98.6%.
- the ethanol concentration in the gas stream was reduced from 200 ppm to 2.8 ppm.
- hopcalite catalyst is added, containing 0.5% potassium oxide.
- the catalyst particle size is from about 1 to about 3 mm.
- the catalyst bed depth is about 19 cm.
- the reactor is heated by an electric jacket to 70 ⁇ 1°C. Gas is fed as a stream at a rate through the reactor of about 601/h.
- the incoming gas composition is as follows (vol.%): nitrogen 91.0, oxygen 6.0, water 3.0, methanol 0.02, cumene ⁇ 10 ppm.
- Space velocity is 2400 hNResidence time is 1.5 seconds.
- Pressure is about 1 atmosphere.
- the level of methanol is reduced by about 95% by volume.
- a glass reactor, as described in Example 1, is filled with 23 ml of manganese oxide-containing catalyst, containing 1.0% potassium oxide.
- the catalyst bed temperature is 110 ⁇ 1°C.
- a gas stream of the composition of Example 1, except that 0.02% (vol.) of acetaldehyde is present in place of the methanol, is passed through the reactor at a rate of 115 1/h and a space velocity of 5000 rv 1 . In a period of 4-hours, the total acetaldehyde amount passed through the catalyst bed is 0.169 g.
- the amount of acetaldehyde collected in traps is 0.00034 g, a reduction in acetaldehyde content of 99.8%.
- the acetaldehyde concentration in the gas stream is reduced from 200 ppm to 0.4 ppm.
Landscapes
- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Materials Engineering (AREA)
- Chemical Kinetics & Catalysis (AREA)
- Organic Chemistry (AREA)
- Environmental & Geological Engineering (AREA)
- Health & Medical Sciences (AREA)
- Biomedical Technology (AREA)
- Analytical Chemistry (AREA)
- General Chemical & Material Sciences (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Catalysts (AREA)
Abstract
An efficient and effective process substantially reduces volatile organic compounds in a gaseous stream without the formation of nitrogen oxides and with low energy consumption. The process uses a bed of catalyst comprising manganese dioxide, copper oxide and potassium oxide. The gaseous stream containing volatile organic compounds passes through the catalyst bed at a temperature of from about 50 to about 150 °C and reduces the level of volatile organic compounds in the gaseous stream by at least about 90 percent.
Description
PROCESS FOR LOW TEMPERATURE REMOVAL OF VOLATILE ORGANIC COMPOUNDS FROM INDUSTRIAL EXHAUST GAS
CROSS-REFERENCE TO RELATED APPLICATIONS
This application claims rights of priority under 35 U.S.C. § 119 from Russian Patent Application No. N 98119648, filed November 3, 1998.
FEDERALLY SPONSORED RESEARCH
Not applicable.
BACKGROUND OF THE INVENTION
This invention provides a method to substantially reduce the content of volatile organic compounds (VOCs) in industrial exhaust gas to enable the processes generating these gases to comply with increasingly stringent limits required by environmental control regulations.
The basis for choosing an appropriate exhaust gas purification method will depend on the level of the impurities, which must be removed. If the impurities concentration in the gas to be purified is as high as from about 0.5 to about 1.0 %, an adiabatic oxidation process may be suitable because the oxidation reaction heat is sufficient to keep the reactor temperature in an acceptable operating range. If the impurities concentration is lower than 0.05%, an isothermic process is needed which will require additional heat
from a source outside the process. Such a process is described in U.S. patent 5,292,991 Cl. C07C 7/152, C07C 7/00, issued March 8, 1994. According to this process, hydrocarbons and oxygen-containing organics are oxidized at 600°C over platinum-palladium catalyst modified with zirconium and titanium. The disadvantage of this process is the necessity to heat the gas stream to a high temperature and its use of noble metals as the catalyst.
There are known methods for oxidizing VOCs at low temperature (including room temperature) over the catalysts containing platinum, palladium, and other rare and precious metals in amount up to 22% (e.g. US patent 5,009,872, Cl. B 01 D, issued April 23, 1991). In this case complete methanol conversion was guaranteed. The disadvantage of this process is the extremely high catalyst cost.
Industrial exhaust gas purification from oxygen-containing organics and hydrocarbons over hopcalite-type catalysts, containing active manganese dioxide and copper oxide, are known too, as mentioned in U.S. patent 5,238,897 Cl. B 01 J 23/34, B 01 J 23/72, B 01 J 37/34, issued 24.08.1993, hopcalite catalyst modified with yttrium, lithium , and lanthanum in an amount of from 3 to 15% provides practically complete hydrocarbons and oxygen-containing compounds conversion (starting concentration 400 - 2000 ppm) at 250 - 400°C.
In U.S. patent 5,238,897 hopcalite is used as a generic term to identify at column 4, lines58 to 60, a copper/ manganese compound used in gas masks to convert carbon monoxide into carbon dioxide. However, Ozone Engineering uses "Hopcalite" as a trademark in its literature describing Hopcalite Catalyst- H Grade with a composition being a mixture of manganese dioxide and copper oxide. Lee et al. in Catalytic Oxidation of Carbon Monoxide at Low Temperature over Pd-Cu Loaded Porous Supports state with reference to low temperature oxidation of CO that a "catalyst known as Hopcalite is also
commercially available for similar use, which is a mixture of Sn02, Mnθ2, CuO and other oxides, but being prone to deactivation by the presence of water vapor."
The method closest to the method of removal of VOCs from industrial exhaust gas of the current invention is the process described in U.S. patent 4,238,460, Cl. B 01 D, issued December 9, 1980. According to this method, passing of aliphatic and aromatic hydrocarbons and products of their incomplete oxidation, containing 1 to 10 carbon atoms (and CO) in an amount of from 25 to 300 ppm over hopcalite catalyst at 140 - 540°C provides practically complete purification of exhaust gas from dangerous compounds. The disadvantage of this method is the necessity to heat the gas stream to a high temperature. This is especially disadvantageous if there is a large- volume of exhaust gas with high nitrogen concentration from which the well- known noxious by-products of nitrogen oxides (NOX) that are extremely detrimental to the environment.
SUMMARY OF THE INVENTION
The process for reducing the level of volatile organic compounds in a gaseous stream of the present invention substantially eliminates this detrimental formation of nitrogen oxides by the purification processes of the prior art by preparing a bed of catalyst comprising manganese dioxide, copper oxide and potassium oxide and passing through the catalyst bed a gaseous stream containing volatile organic compounds at a temperature of from about 50 to about 150°C. whereby the level of volatile organic compounds in the gaseous stream is reduced by at least about 90 percent. Not only does the present process π inimize or substantially eliminate the formation of nitrogen oxides, but also its low operating temperature range substantially reduces the energy consumption of process which in turn reduces the environmental impact of the process and favorably affects the
economics of its operation. When formation of NOX or energy efficiency is not an issue, the process of the present invention can be equally effective in VOCs removal from gaseous streams at temperatures as high as about 200 to about 250°C.
The term "industrial exhaust gas" is intended to be construed in its broadest sense and includes any gaseous stream containing VOCs regardless of the source of these streams. Typical industrial exhaust gases include, but are not limited to, fugitive emissions and gases from vents from chemical processes, polymerization processes, waste treatment operations, storage vessels, power plants, warehouses, distillation towers, separators, paint booths, laboratory hoods, pilot plants, degreasing operations, paint stripping operations, synthetic fiber production and spinning, petroleum cracking, ore refining, hydrocarbon processing, mechanical assembly operations, paper mills, cloth preparation, livestock enclosures and the like.
Although the present process is useful generally for the removal of any
VOCs, VOCs that are removed by the present process with particular efficiency include ethers, preferably ethers containing from two to eight carbons, more, preferably dimethylether, diethylether and methylethyl ether and still more preferably dimethyl ether, alcohols, preferably alcohols containing from one to four carbons, more preferably, ethanol and methanol, aldehydes, preferably aldehydes with from one to nine carbons, more preferably aldehydes with from one to seven carbons and still more preferably formaldehyde and acetaldehyde, ketones, preferably ketones with from three to nine carbons, more preferably ketones with from three to seven carbons and still more preferably acetone and methylethyl ketone and esters, preferably esters with from three to nine carbons, more preferably esters with from three to seven carbons and still more preferably ethyl acetate and propyl acetate.
The industrial waste gas streams purified by the method of this invention include any streams in which VOCs occur at low levels, e.g., no more than about 1000 ppm, preferably from about 20 to about 500 ppm, more preferably from about 80 to about 400 ppm, still more preferably from about 150 to about 250 ppm and most preferably about 200 ppm. Industrial waste streams in which the method of this invention is preferably useful are waste streams from processes synthesizing organic compositions, more preferably waste streams from processes synthesizing oxygen-containing aromatic compounds and still more preferably waste streams from processes for synthesizing phenol.
DESCRIPTION OF THE DRAWINGS
Not applicable.
DETAILED DESCRIPTION OF THE INVENTION
The current invention surprisingly increases the activity of a manganese containing catalyst, such as a hopcalite catalyst, in exhaust gas purification to remove a high percentage, e.g., at least about 90%, preferably at least about 93%, more preferably at least about 96% and still more preferably at least about 98% of the VOCs present at low levels in the industrial waste gas stream at substantially lower temperatures without NOX formation. In a preferred embodiment, the present invention purifies waste streams contaminated with hydrocarbons by removing a high percentage, e.g.,at least about 90%, preferably at least about 93%, more preferably at least about 96% and still more preferably at least about 98% of the hydrocarbon VOCs present at low levels in the industrial waste gas stream at substantially lower temperatures by the substantially complete conversion to more highly oxygenated organic compounds which, preferably, in turn, may be further oxidized to water and carbon dioxide.
A preferred manganese oxide/ copper oxide catalyst which is a hopcalite type catalyst is commercially available from Carus Chemical Company under the trademark, CARULITE®, grade numbers 100, 110, 150, 200 and 300. and has a composition of about the following, as published in the trade literature:
50 - 75% Mn02
10 - 40% CuO
10 - 20% Alumina binder (bentonite).
Some catalyst useful in the present process have compositions within this range as follows:
Mnθ2 CuO Aluminum oxide
54% 36% 10%
60 - 75% 11 - 14% 15 - 16%
Other manganese-containing catalysts useful in the process of the present invention have been described as having an elemental manganese content of from about 37 - 39 % elemental manganese and an elemental copper content of about 9 - 11 % elemental copper.
The efficient and effective removal of VOCs from gaseous streams at low temperatures without substantial formation of NOX and with low energy consumption is accomplished by adding to the manganese-containing catalyst potassium oxide in amount of from about 0.01 to about 5% by weight, preferably from about 0.02 to about 4% by weight, more preferably from about 0.04 to about 3% by weight and still more preferably from about 0.05 to about 2.0% by weight of the catalyst, passing a gas stream, containing VOCs, over the manganese-containing catalyst containing the potassium oxide, at a
temperature of from about 50 to about 135°C, preferably from about 70 to about 135°C, more preferably from about 90 to about 130°C and still more preferably from about 100°C to about 130°C and at a space velocity of from about 2000 to about 15000 hN Potassium oxide can be added to the catalyst composition in a stage of paste preparation by a known method (RF patent 2,064,834, Cl B 01 J 23/889, B 01 J 37/04), or with the feed compounds, used in catalyst production.
Although the space velocity of the gaseous stream is not critical to the practice of the process of the present invention so long as there is adequate contact with the catalyst bed which can be in the form of either a fixed bed or fluidized bed, it is preferred that the space velocity be within the range of from about 1000 to about 200001V1, more preferably from about 2000 to about 5000h-ι.
The catalyst can be employed in the present process without a support or supported. A preferred support is alumina.
In a preferred embodiment in which extended catalyst life is important to the practice of the invention, it has been found that by feeding to the catalyst bed a gaseous stream either added to the waste stream or separately oxygen at a volume percent of from about 2% to about 21% (the level of oxygen present in air), more preferably from about 4% to about 21% and still more preferably about 5% to about 21%, and operating the purification process at least about 100°C, catalyst life can be extended. Atmospheric air is the most convenient source of oxygen. It is postulated that at a temperature of 100°C. or greater, in the presence of the foregoing levels of oxygen the manganese monoxide is regenerated to the catalytically active species of manganese dioxide in the presence of the cupric oxide, the other essential component of the catalyst.
When operating the process of the present invention in the lower portion of the operating temperature range, i.e., from about 50°C. up to less than about 100°C, it is preferable to employ two catalyst beds in the practice of the present process, allowing one to be in use while the other is being regenerated. When operating the present process at about 100°C. or above, only one catalyst bed is required in view of the self-regeneration of the bed as described above. A second benefit of operating the present process at about 100°C. or above is the fact that at these operating temperatures any water present or formed in the removal of VOCs is present only as vapor. The water vapor rapidly exists the catalyst bed before it coats the active catalyst sites and deactivates the catalyst as taught in the prior art patent US 5,238,897.
The application of this invention is illustrated by the following examples but is not intended to be limited thereby. Percentages herein are expressed as weight percent unless expressly stated otherwise.
EXAMPLE 1
A glass reactor of 2.26 cm2 cross-sectional area is filled with hopcalite catalyst, containing 0.05% potassium oxide. The catalyst particle size is from about 1 to about 3 mm. The catalyst bed depth is about 19 cm. The reactor is heated by an electric jacket to 95±1°C. Gas is fed as a stream at a rate through the reactor of about 461/h. The incoming gas composition is as follows
(vol.%): nitrogen 91.0, oxygen 6.0, water as steam 3.0, methanol 0.02. Space velocity is 2000 h-1 and linear velocity is about 0.9 m/sec. Experiment time is 4 hours. Total methanol amount entering in the incoming gas and passing through the catalyst bed in the reactor is 0.049 g. The gas exiting the reactor then passes through an absorption system, which consists of four concurrent traps (absorbers) cooled with a dry ice/ acetone mixture (at a temperature of from -70 to -80°C). The first and last traps are empty. The second and third are filled with n-butanol. After the experiment finished, total methanol amount
found in traps is 0.00083 g, i.e. methanol conversion 98.3%. The methanol concentration in the gas stream is reduced from 200 ppm to 3.3 ppm.
EXAMPLE 2
The glass reactor, described in Example 1 is filled with 23 ml of hopcalite catalyst, containing 2.0% potassium oxide. The catalyst bed temperature is 130±1°C. The gas stream has the same composition as in Example 1 and passes through the reactor at a rate of 345 1/h, a space velocity of 15000 rv1. In a period of 4-hours, the total methanol amount passed through the catalyst bed in the reactor was 0.368 g. The methanol amount collected in the traps described in Example 1 was 0.00074 g, i.e., methanol conversion 99.8%. The methanol concentration in the gas stream was reduced from 200 ppm to 0.4 ppm.
EXAMPLE 3
The glass reactor, described in Example 1, is filled with 23 ml of hopcalite catalyst, containing 0.5% potassium oxide. The catalyst bed temperature is 100±1°C. A gas stream of the same composition as in Example 1 passes through the reactor at rate of 1151/h, space velocity 5000 rv1. In a period of 4-hours, the total amount of methanol passed through the catalyst bed in the reactor was 0.123 g. The methanol amount collected in the traps described in Example 1 was 0.00012 g, conversion 99.9%. The methanol concentration in the gas stream was reduced from 200 ppm to 0.2 ppm.
EXAMPLE 4
The glass reactor, described in Example 1, was filled with 23 ml of hopcalite catalyst, containing 0.05% potassium oxide. The catalyst bed temperature was 130±1°C. A gas stream of a composition as indicated in
Example 1, except for 0.02% of ethanol instead of methanol, is passed through
the reactor at a rate of 2301/h, space velocity 10000 hN In a period of 4-hours, the total ethanol amount passed through the catalyst bed in the reactor was 0.353 g. The ethanol amount collected in the traps described in Example 1 was 0.00106 g, conversion 99.7%. The ethanol concentration in the gas stream was reduced from 200 ppm to 0.6 ppm.
EXAMPLE 5
The glass reactor described in Example 1 was filled with 23 ml of hopcalite catalyst, containing 2.0% potassium oxide. Catalyst bed temperature was 95+1 °C. The gas stream had the same composition as indicated in Example 1, except for 0.02% of ethanol instead of methanol, and was passed through the reactor at a rate of 461/h, space velocity 2000 hN In a the traps described in Example 1 was 0.00099 g, conversion 98.6%. The ethanol concentration in the gas stream was reduced from 200 ppm to 2.8 ppm.
The data from Examples 1 through 5 are summarized in the table below:
EXAMPLE 6
To a glass reactor of 2.26 cm2 cross-sectional area, 26 milliliters of hopcalite catalyst is added, containing 0.5% potassium oxide. The catalyst particle size is from about 1 to about 3 mm. The catalyst bed depth is about 19 cm. The reactor is heated by an electric jacket to 50±1°C. Gas is fed as a stream at a rate through the reactor of about 601/h. The incoming gas composition is as follows (vol.%): nitrogen 91.0, oxygen 6.0, water 3.0, methanol 0.02, cumene <10 ppm. Space velocity is 2400 hNResidence time is 1.5 seconds. Pressure is about 1 atmosphere. The level of methanol is reduced by about 90% by volume.
EXAMPLE 7
To a glass reactor of 2.26 cm2 cross-sectional area, 26 milliliters of hopcalite catalyst is added, containing 0.5% potassium oxide. The catalyst particle size is from about 1 to about 3 mm. The catalyst bed depth is about 19 cm. The reactor is heated by an electric jacket to 70±1°C. Gas is fed as a stream at a rate through the reactor of about 601/h. The incoming gas composition is as follows (vol.%): nitrogen 91.0, oxygen 6.0, water 3.0, methanol 0.02, cumene <10 ppm. Space velocity is 2400 hNResidence time is 1.5 seconds. Pressure is about 1 atmosphere. The level of methanol is reduced by about 95% by volume.
COMPARATIVE EXAMPLE 1
Repeating the process substantially as described in Example 1 without the addition of potassium oxide and at each of the catalyst mid-bed temperatures as set forth below the percent removal of methanol is shown:
Catalyst Mid-Bed Percent Methanol
Temperature in °C. Removal
125 71
140 81
175 89
200 96
235 99
This illustrates that without the addition of potassium oxide, a temperature of over 175°C. is required if it is desired to remove at least 90% of the methanol.
COMPARATIVE EXAMPLE 2
Repeating the process substantially as described in Example 4 using CARULITE 150 bead type hopcalite catalyst without the addition of potassium oxide a catalyst temperature of 167°C is required to remove 95% of the ethanol.
COMPARATIVE EXAMPLE 3
Repeating the process substantially as described in Comparative Example 2 but substituting for the ethanol the VOCs set forth below, the catalyst mid-bed temperatures to remove 95% of the VOCs are set forth below,
Catalyst Mid-Bed Oxygen-Contai
Temperature in °C. Impurity
178 Propanol
186 Methylethyl Ke
181 Ethyl Acetate
200 Propyl Acetate
278 Heptane
222 Toluene
COMPARATIVE EXAMPLE 4
Repeating the process substantially as described in Example 4 using CARULITE 110TR bead type hopcalite catalyst without the addition of potassium oxide a catalyst temperature of 222°C is required to remove 95% of the ethanol.
COMPARATIVE EXAMPLE 5
Repeating the process substantially as described in Comparative Example 4 but substituting for the ethanol the VOCs set forth below, the catalyst mid-bed temperatures to remove 95% of the VOCs are set forth below,
Catalyst Mid-Bed Oxygen-Containing
Temperature in °C. Impurity
250 Propanol
<222 Methylethyl Ketone
250 Ethyl Acetate
222 Propyl Acetate
306 Heptane
333 Toluene
EXAMPLE 8
Repeating the process substantially as described in Example 3 but substituting in the gas stream an equal amount of acetone for the methanol, the level of acetone was reduced to 18 ppm, a reduction of 91%.
EXAMPLE 9
Repeating the process substantially as described in Example 3 but substituting an equal amount of methylethyl ketone for the methanol, the level of methylethyl ketone was reduced to 15 ppm, a reduction of 92.5%.
EXAMPLE 10
A glass reactor, as described in Example 1, is filled with 23 ml of manganese oxide-containing catalyst, containing 1.0% potassium oxide. The catalyst bed temperature is 110±1°C. A gas stream of the composition of Example 1, except that 0.02% (vol.) of acetaldehyde is present in place of the methanol, is passed through the reactor at a rate of 115 1/h and a space velocity of 5000 rv1. In a period of 4-hours, the total acetaldehyde amount passed through the catalyst bed is 0.169 g. The amount of acetaldehyde collected in traps is 0.00034 g, a reduction in acetaldehyde content of 99.8%. The acetaldehyde concentration in the gas stream is reduced from 200 ppm to 0.4 ppm.
Claims
1. A process for the reduction of volatile organic compounds in a gaseous stream comprising preparing a bed of catalyst comprising manganese dioxide, copper oxide and potassium oxide and passing through the catalyst bed a gaseous stream containing volatile organic compounds at a temperature of from about 50 to about 150°C whereby the level of volatile organic compounds in the gaseous stream is reduced by at least about 90 percent.
2. The process of claim 1 wherein the potassium oxide is present in an amount of from about 0.01 percent to about 5 percent by weight of the catalyst.
3. The process of claim 1 wherein the potassium oxide is present in an amount of from about 0.02 percent to about 4 percent by weight of the catalyst.
4. The process of claim 1 wherein the potassium oxide is present in an amount of from about 0.04 percent to about 3 percent by weight of the catalyst.
5. The process of claim 1 wherein the potassium oxide is present in an amount of from about 0.05 percent to about 2 percent by weight of the catalyst.
6. The process of claim 1 wherein the level of volatile organic compounds in the gaseous stream is reduced by at least about 95 percent.
7. The process of claim 1 wherein the temperature of the gaseous stream in the catalyst bed is from about 70 to about 135°C.
8. The process of claim 1 wherein the temperature of the gaseous stream in the catalyst bed is from about 90 to about 130°C.
9. The process of claim 1 wherein the temperature of the gaseous stream in the catalyst bed is from about 100 to about 130°C.
10. The process of claim 9 wherein the gaseous stream is an industrial exhaust gas.
11. The process of claim 10 wherein only a single catalyst bed is employed.
12. The process of claim 1 wherein the catayst is supported.
13. The process of claim 12 wherein the support is alumina.
14. The process of claim 1 wherein the catayst is unsupported.
15. The process of claim 1 wherein the catalyst bed is a fixed bed.
16. The process of claim 1 wherein the catalyst bed is a fluidized bed.
17. The process of claim 1 wherein the catalyst contains from about
50 to about 75% manganese dioxide.
18. The process of claim 17 wherein the catalyst is a hopcalite catalyst.
19. A process for the reduction of volatile organic compounds in a gaseous stream comprising preparing a bed of catalyst comprising a hopcalite catalyst containing from about 50 to about 75% manganese dioxide by weight of the catalyst and passing through the catalyst bed a gaseous stream containing volatile organic compounds at a temperature of from about 50 to about 250°C whereby the level of volatile organic compounds in the gaseous stream is reduced by at least about 90%.
20. A process for the reduction of methanol or ethanol in a gaseous stream comprising preparing a bed of catalyst comprising a hopcalite catalyst containing from about 50 to about 75% manganese dioxide and potassium oxide in an amount of from about 0.05 percent to about 2 percent by weight of the catalyst and passing through the catalyst bed a gaseous stream containing methanol or ethanol at a space velocity of from about 1000 to about 200001V1 at a temperature of from about 100 to about 130°C whereby the level of methanol or ethanol in the gaseous stream is reduced by at least about 90%.
Applications Claiming Priority (4)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
RU98119648A RU2140811C1 (en) | 1998-11-03 | 1998-11-03 | Method of cleaning of industrial gas effluents from organic oxygen-containing compounds |
RU98119648 | 1998-11-03 | ||
US27533499A | 1999-03-24 | 1999-03-24 | |
US09/275,334 | 1999-03-24 |
Publications (1)
Publication Number | Publication Date |
---|---|
WO2000025901A1 true WO2000025901A1 (en) | 2000-05-11 |
Family
ID=26653980
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
PCT/US1999/019967 WO2000025901A1 (en) | 1998-11-03 | 1999-08-31 | Process for low temperature removal of volatile organic compounds from industrial exhaust gas |
Country Status (1)
Country | Link |
---|---|
WO (1) | WO2000025901A1 (en) |
Cited By (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP1197259A1 (en) * | 2000-10-11 | 2002-04-17 | Süd Chemie Mt S.R.L. | Oxidation catalysts |
GB2442444A (en) * | 2006-10-06 | 2008-04-09 | Howard Paul Davis | A process for catalytically removing NOx from a gas stream |
WO2008068318A1 (en) * | 2006-12-07 | 2008-06-12 | Beko Technologies Gmbh | Purification apparatus for gases |
Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2640889A1 (en) * | 1988-12-26 | 1990-06-29 | Toulouse Inst Nat Polytech | Process and device for catalytic purification of the atmosphere of an enclosure for storing plants |
WO1993005879A1 (en) * | 1991-09-27 | 1993-04-01 | North Carolina Center For Scientific Research, Inc. | Catalyst prepared using irradiation |
EP0625368A1 (en) * | 1993-05-19 | 1994-11-23 | Japan Pionics Co., Ltd. | Process for cleaning harmful gas |
-
1999
- 1999-08-31 WO PCT/US1999/019967 patent/WO2000025901A1/en active Application Filing
Patent Citations (3)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
FR2640889A1 (en) * | 1988-12-26 | 1990-06-29 | Toulouse Inst Nat Polytech | Process and device for catalytic purification of the atmosphere of an enclosure for storing plants |
WO1993005879A1 (en) * | 1991-09-27 | 1993-04-01 | North Carolina Center For Scientific Research, Inc. | Catalyst prepared using irradiation |
EP0625368A1 (en) * | 1993-05-19 | 1994-11-23 | Japan Pionics Co., Ltd. | Process for cleaning harmful gas |
Cited By (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP1197259A1 (en) * | 2000-10-11 | 2002-04-17 | Süd Chemie Mt S.R.L. | Oxidation catalysts |
US6683021B2 (en) | 2000-10-11 | 2004-01-27 | Sud Chemie Mt. S.R.L. | Oxidation catalysts |
US6833125B2 (en) | 2000-10-11 | 2004-12-21 | Sud Chemie Mt. S.R.L. | Oxidation catalysts |
GB2442444A (en) * | 2006-10-06 | 2008-04-09 | Howard Paul Davis | A process for catalytically removing NOx from a gas stream |
WO2008068318A1 (en) * | 2006-12-07 | 2008-06-12 | Beko Technologies Gmbh | Purification apparatus for gases |
US8968664B2 (en) | 2006-12-07 | 2015-03-03 | Beko Technologies Gmbh | Purification apparatus for gases |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
US5895772A (en) | Catalyst having a zirconium oxide and/or cerium oxide support and containing gold and a transition metal oxide | |
EP1197259B1 (en) | Oxidation catalysts | |
US7700519B2 (en) | Catalyst for decomposing nitrous oxide and method for performing processes comprising formation of nitrous oxide | |
WO1993015824A1 (en) | A process for the conversion of n2o | |
KR100756109B1 (en) | Catalyst for the decomposition of ?2? in the ostwald process | |
CA2092265A1 (en) | Process for controlled n2o decomposition in an n20-containing gas stream | |
AU2968597A (en) | Oxidation catalyst | |
Shi et al. | Promotion effects of ZrO2 on the Pd/HZSM-5 catalyst for low-temperature catalytic combustion of methane | |
WO2000025901A1 (en) | Process for low temperature removal of volatile organic compounds from industrial exhaust gas | |
US20030124041A1 (en) | Process for removing nitrogen oxides from gases | |
WO2023026023A1 (en) | A method for the treatment of an exhaust gas and an hvac system | |
KR100544693B1 (en) | Catalytic Composition for Destroying Volatile Organic Compound and Carbon Monoxide and Method of Catalytic Conversion using the Same | |
KR20020032167A (en) | Catalyst for decomposition of toxic pollutants and producing process thereof | |
KR100407166B1 (en) | Oxidation catalysts and method for controlling co, voc, and halogenated organic | |
KR100537787B1 (en) | Catalysts and method for low temperature oxidation | |
KR100418717B1 (en) | CATALYSTS AND METHOD FOR SELECTIVE AND NON-SELECTIVE CATALYTIC REDUCTION DE-NOx TECHNOLOGY | |
KR100503227B1 (en) | Oxidation catalyst for remonal of chlorinated volatile organic compounds and method for preparing thereof | |
JP3538984B2 (en) | Decomposition method of chlorinated organic compounds | |
Lou et al. | Preparing copper/manganese catalyst by sol–gel process for catalytic incineration of VOCs | |
KR100651785B1 (en) | Oxidation catalyst for removing carbon monoxide and method of removing carbon monoxide using same | |
KR100487944B1 (en) | Catalyst for reducing sulfur dioxide and the method for eliminating sulfur dioxide thereby | |
KR100406360B1 (en) | A catalytic oxidizing method of chlorine-based volatile organic compounds | |
KR20020041346A (en) | Water and gas treatment for increasing activity and decreasing deactivation of catalyst | |
JPH0771614B2 (en) | Exhaust gas purification method | |
CN118179484A (en) | Application of manganese modified spherical cerium oxide catalyst in low-temperature catalytic hydrolysis of methyl mercaptan |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
AK | Designated states |
Kind code of ref document: A1 Designated state(s): BR CA CN IN JP KR MX RU SG |
|
AL | Designated countries for regional patents |
Kind code of ref document: A1 Designated state(s): AT BE CH CY DE DK ES FI FR GB GR IE IT LU MC NL PT SE |
|
121 | Ep: the epo has been informed by wipo that ep was designated in this application | ||
DFPE | Request for preliminary examination filed prior to expiration of 19th month from priority date (pct application filed before 20040101) | ||
122 | Ep: pct application non-entry in european phase |