CA1048234A - Emission control system and method - Google Patents
Emission control system and methodInfo
- Publication number
- CA1048234A CA1048234A CA75217484A CA217484A CA1048234A CA 1048234 A CA1048234 A CA 1048234A CA 75217484 A CA75217484 A CA 75217484A CA 217484 A CA217484 A CA 217484A CA 1048234 A CA1048234 A CA 1048234A
- Authority
- CA
- Canada
- Prior art keywords
- catalyst
- gaseous effluent
- flow
- effluent
- heating
- 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.)
- Expired
Links
- 238000000034 method Methods 0.000 title abstract description 9
- 238000013022 venting Methods 0.000 claims abstract description 5
- 239000003054 catalyst Substances 0.000 claims description 50
- 238000010438 heat treatment Methods 0.000 claims description 35
- 238000001035 drying Methods 0.000 claims description 14
- 238000009792 diffusion process Methods 0.000 claims description 13
- 239000011368 organic material Substances 0.000 claims description 11
- 230000003213 activating effect Effects 0.000 claims description 7
- 239000002245 particle Substances 0.000 claims description 6
- 238000011144 upstream manufacturing Methods 0.000 claims description 6
- 238000004140 cleaning Methods 0.000 claims description 3
- 238000004891 communication Methods 0.000 claims description 3
- 239000012530 fluid Substances 0.000 claims description 3
- 238000009833 condensation Methods 0.000 claims description 2
- 230000005494 condensation Effects 0.000 claims description 2
- 230000003405 preventing effect Effects 0.000 claims description 2
- 238000001914 filtration Methods 0.000 claims 1
- 239000007787 solid Substances 0.000 claims 1
- 230000003197 catalytic effect Effects 0.000 abstract description 3
- 230000003647 oxidation Effects 0.000 abstract description 2
- 238000007254 oxidation reaction Methods 0.000 abstract description 2
- 239000007789 gas Substances 0.000 description 39
- 239000002023 wood Substances 0.000 description 13
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Chemical compound O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 description 6
- RSWGJHLUYNHPMX-UHFFFAOYSA-N Abietic-Saeure Natural products C12CCC(C(C)C)=CC2=CCC2C1(C)CCCC2(C)C(O)=O RSWGJHLUYNHPMX-UHFFFAOYSA-N 0.000 description 5
- 239000000463 material Substances 0.000 description 5
- BASFCYQUMIYNBI-UHFFFAOYSA-N platinum Chemical compound [Pt] BASFCYQUMIYNBI-UHFFFAOYSA-N 0.000 description 5
- KHPCPRHQVVSZAH-HUOMCSJISA-N Rosin Natural products O(C/C=C/c1ccccc1)[C@H]1[C@H](O)[C@@H](O)[C@@H](O)[C@@H](CO)O1 KHPCPRHQVVSZAH-HUOMCSJISA-N 0.000 description 3
- 229920002522 Wood fibre Polymers 0.000 description 3
- 239000006227 byproduct Substances 0.000 description 3
- 239000003344 environmental pollutant Substances 0.000 description 3
- 231100000719 pollutant Toxicity 0.000 description 3
- KHPCPRHQVVSZAH-UHFFFAOYSA-N trans-cinnamyl beta-D-glucopyranoside Natural products OC1C(O)C(O)C(CO)OC1OCC=CC1=CC=CC=C1 KHPCPRHQVVSZAH-UHFFFAOYSA-N 0.000 description 3
- 239000002025 wood fiber Substances 0.000 description 3
- BTXXTMOWISPQSJ-UHFFFAOYSA-N 4,4,4-trifluorobutan-2-one Chemical compound CC(=O)CC(F)(F)F BTXXTMOWISPQSJ-UHFFFAOYSA-N 0.000 description 2
- BQACOLQNOUYJCE-FYZZASKESA-N Abietic acid Natural products CC(C)C1=CC2=CC[C@]3(C)[C@](C)(CCC[C@@]3(C)C(=O)O)[C@H]2CC1 BQACOLQNOUYJCE-FYZZASKESA-N 0.000 description 2
- QGZKDVFQNNGYKY-UHFFFAOYSA-N Ammonia Chemical compound N QGZKDVFQNNGYKY-UHFFFAOYSA-N 0.000 description 2
- CBENFWSGALASAD-UHFFFAOYSA-N Ozone Chemical compound [O-][O+]=O CBENFWSGALASAD-UHFFFAOYSA-N 0.000 description 2
- 238000009835 boiling Methods 0.000 description 2
- 229910052729 chemical element Inorganic materials 0.000 description 2
- 238000006243 chemical reaction Methods 0.000 description 2
- 229910052739 hydrogen Inorganic materials 0.000 description 2
- 239000001257 hydrogen Substances 0.000 description 2
- 238000012423 maintenance Methods 0.000 description 2
- 229910052751 metal Inorganic materials 0.000 description 2
- 239000002184 metal Substances 0.000 description 2
- 229910052697 platinum Inorganic materials 0.000 description 2
- 230000008569 process Effects 0.000 description 2
- 239000000047 product Substances 0.000 description 2
- 230000005855 radiation Effects 0.000 description 2
- 230000009257 reactivity Effects 0.000 description 2
- 150000003505 terpenes Chemical class 0.000 description 2
- 235000007586 terpenes Nutrition 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- NLZUEZXRPGMBCV-UHFFFAOYSA-N Butylhydroxytoluene Chemical compound CC1=CC(C(C)(C)C)=C(O)C(C(C)(C)C)=C1 NLZUEZXRPGMBCV-UHFFFAOYSA-N 0.000 description 1
- OKTJSMMVPCPJKN-UHFFFAOYSA-N Carbon Chemical compound [C] OKTJSMMVPCPJKN-UHFFFAOYSA-N 0.000 description 1
- UFHFLCQGNIYNRP-UHFFFAOYSA-N Hydrogen Chemical compound [H][H] UFHFLCQGNIYNRP-UHFFFAOYSA-N 0.000 description 1
- 229910052782 aluminium Inorganic materials 0.000 description 1
- XAGFODPZIPBFFR-UHFFFAOYSA-N aluminium Chemical compound [Al] XAGFODPZIPBFFR-UHFFFAOYSA-N 0.000 description 1
- 229910021529 ammonia Inorganic materials 0.000 description 1
- 230000008901 benefit Effects 0.000 description 1
- 229910052799 carbon Inorganic materials 0.000 description 1
- 239000000969 carrier Substances 0.000 description 1
- 239000000919 ceramic Substances 0.000 description 1
- 229940000425 combination drug Drugs 0.000 description 1
- 238000010276 construction Methods 0.000 description 1
- 230000001276 controlling effect Effects 0.000 description 1
- 230000001419 dependent effect Effects 0.000 description 1
- 230000008021 deposition Effects 0.000 description 1
- 235000014113 dietary fatty acids Nutrition 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000000194 fatty acid Substances 0.000 description 1
- 229930195729 fatty acid Natural products 0.000 description 1
- 150000004665 fatty acids Chemical class 0.000 description 1
- 239000000835 fiber Substances 0.000 description 1
- 239000012634 fragment Substances 0.000 description 1
- 150000002431 hydrogen Chemical class 0.000 description 1
- 238000009413 insulation Methods 0.000 description 1
- 239000000395 magnesium oxide Substances 0.000 description 1
- CPLXHLVBOLITMK-UHFFFAOYSA-N magnesium oxide Inorganic materials [Mg]=O CPLXHLVBOLITMK-UHFFFAOYSA-N 0.000 description 1
- AXZKOIWUVFPNLO-UHFFFAOYSA-N magnesium;oxygen(2-) Chemical compound [O-2].[Mg+2] AXZKOIWUVFPNLO-UHFFFAOYSA-N 0.000 description 1
- 238000012986 modification Methods 0.000 description 1
- 230000004048 modification Effects 0.000 description 1
- TWNQGVIAIRXVLR-UHFFFAOYSA-N oxo(oxoalumanyloxy)alumane Chemical compound O=[Al]O[Al]=O TWNQGVIAIRXVLR-UHFFFAOYSA-N 0.000 description 1
- 239000013618 particulate matter Substances 0.000 description 1
- 239000011120 plywood Substances 0.000 description 1
- 239000011819 refractory material Substances 0.000 description 1
- 230000000087 stabilizing effect Effects 0.000 description 1
Classifications
-
- 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
Landscapes
- Drying Of Solid Materials (AREA)
Abstract
EMISSION CONTROL SYSTEM AND METHOD
ABSTRACT
An emission control system and a method of treating a gaseous effluent is disclosed. The system s particularly suited for treating gaseous effluents from a veneer dryer prior to venting to the atmosphere.
The system comprises means for temperature adjustment, flow control, and catalytic oxidation of the effluent.
ABSTRACT
An emission control system and a method of treating a gaseous effluent is disclosed. The system s particularly suited for treating gaseous effluents from a veneer dryer prior to venting to the atmosphere.
The system comprises means for temperature adjustment, flow control, and catalytic oxidation of the effluent.
Description
3~ :
BACKGROUND OF THE INVENTION
It is common practice to dry wood fibers, wood veneer, and plywood in ovenis utilizing either heated air or steam flow as the drying means.
In typical steam dryer operations, the alr flow can vary from about 5,000 to 10,000 SCFM. The `~ drying causes large volumes of water vapor to be e~pelled from the wood and 9 together with the water9 there are expelled organic materîals such as ~osin--~ type ma~erials and terpenes. Such organic materials are not only vented to the atmosphere where they causP
a substantial pollution problem but, in additi~n, the higher boiling fractions thereof, such as abietic acid, condense on the walls and exit of the smokestack or 3~ reo~JrJ~n~g the dryer ~u~,~u~ extended maintenance~because such buildup is a potential fire hazard.
- Attemp~s to overcome this prob~em by the use :
of higher drying temperatures to degrade the organic materials or keep them from condensing have not been en~irely successful due to the fact that such higher temperatures cause an undesirable darkening of the wood : .
or wood fibers. In addition, apparatus and method for handling the large amount of effluent gas from such dryers are no~ satisfactory in that they soon oul and themselves require extensive and repeated maintenance.
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; _ _MARY OF TIIE rNv~NTIoN-An improved system and method have now been developed which a~e capable of substantially reducing the pollutant content i.e cleaning, large volumes of effluent gas from wood dryers and without either extensive fouling or rosin buildup.
Briefly stated, the present invention comprises an emission control system for treating the gaseous effluent from a drying apparatus prior to venting said gaseous effluent from said apparatus to the atmosphere.
Accordingly, the present invention relates to a~ emission control system for cleaning substantially the entire flow of gaseous effluent from an apparatus for drying wood-type products prior to venting said gas~ous effluent ~rom said dr~ing appara-tus to the atmosphere, said system comprising, in in-line com-bination and in fluid flow communication, an inlet, first means for heating said gaseous effluent to a temperature pre-venting condensation of organic materials entrained in said effluent, a diffusion chamber for adjusting t~e 10w of said heated gaseous effluent so that it assumes su~stantially a uniform flow across the area of its path of travel~ a catalyst ` - zonP including at least two spaced apart catalyst beds both operating at temperatures sufficient to oxidize the organic materials present in said gaseous effluent,sec~nd heatin~
reans including an array of heating elements disposed in the upstream path of said flow and adjacent to a face of each .. ',' ` ' ~ .
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catalyst in said catalyst beds, refl.ective means disposed in the region o:E said heating el~ments of said array for directing radiant energy to said face o~ each catalyst for heating said ca-talyst and said gaseous effluent thereby to main-tain said gaseous effluent in an elevated noncombusted gaseous state through said catalyst zone, means connecting said heating means in an electric circuit, and a stack having an output emitting said gaseous.e~fluent in a cleaned condition to the atmosphere.
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BR:rE'F DESCE~_:[ON ~ . I ' L Dl;/:~ILNLS
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FIG. 1 is an elevational view o~ one form of the invention, portions thereof having been broken away to ; illustrate a damper and catalys-t bed;
; . FIG. 2 is an elevational view of an al-ternate f~rm - of the invention;
FIG. 3 is an elevational view of a further form o~
. ~ . the invention;
FIG. 4 is an elevational view of a form of the inven~
ti.on wherein a single stack accommodates at least a pair of dryers;
FIG. 5 is an elevational view of yet a further form of the invention including heating means and activating gas inlet means upstream of the effluent inlet;
FIG. 6 is an elevational view, partly in section, of - a preferred form of the invention;
FIG. 7, located on the same sheet as FIG.5, is an : elevational view, partly in section, of a pair of catalyst ;; beds having a heating source adjacent to the leading face i 20 of each bed;
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FIG. 8, located on the same sheet as FIG. 6, is an eleva-tional view of the form of FIG.6 in axial alignment; and, FIG. g~ also located on the ~ame Sheet as FIG.6, is a 9ection as seeh along the line 9-9 ]n FIG. 8 .. :
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3~
_~TAIL~D DESCRIP'ilION
Wllile the instant invention is suitable for use with any of the presen~ly used drying ovens and pro-cedures, it has particular application to and will be described in connection with wood veneer drying.
Referring to all oE the drawing figures, there are shown in fragment~ry form, the insulated roo~s and/ or walls 10, 20, 30... and 70 of a drying oven ada~ted for drying wood veneer. The oven can be any of those conventionally used to dry such product. The structure and operation of such dryers is well known in the art and~ since the dryer itself forms no part of the present invention other than in the combination with the system as the source of the emission to be controlled, will not be described in detail.
Wood, having a water content from about 40 to about 60 percent by as~is weight, is drie~ utili~ing steam or gas-fired drying means to heat air which is then forced through the dryer to dry the wood, As limited a quantity of air .: ~
as possible is used in order to minimize the amount of air that has to be heated as ~ell as to limit the amount of gas that is expelled through thP stack leaving the dryer.
~ypically, the air flow ~ill be, as previvusly noted~ in the range of about 5,000 to , -4-, ,;. .
:. .
about 10,000 SCFM. The air in leaving the dr~er will contain about 20 percent by volume vapor comprising essentially water, rosin fatty acids, and terpenes that are extracted from the wood. Based on wood containing from about 40 to 60 percent by weight water and subject to treatment with the noted air:~:flow, there will be exhausted from the dryer anywhere from about 5-15 pounds per hour of organic materials.
The temperature of a veneer dryer effluent gas can vary widely, but typically is about 300 to 375F.
In present dryer practice, as has been noted, such water and orgnic materials are simply vented through ~:
the stack with the consequent problems noted of air ~ a~/~*o~
~o~uticn and dryers and stack fouling and accompanying fire hazard.
In accordance with the present invention, the emission control system 12 of a first embodiment is dispo-sed to receive the emission from the dryer at an outlet 11 (see FIG. 1)~ The system 12 generally comprises a diffusion chamber 13, catalyst treatment zone 14, and :
stack 15 *~in fluid flow communication so that exhaust or effluent gas from the dryer will pass therethrough in the sequence noted.
It may be desired to incorporate combustor means .
16, preferably a burner, for heating the effluent gas prior to its entry into diffusion chamber 13. A blower 17 is located between catalyst zone 14 and stack 15 to '' :
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maintain flow conditions during operation. For optimum operation, it is also desirable to have gas flow control means such as a damper 18 placed at the inlet to the treatment system 12.
Means for separating entrained particulate matter, as for example, filter (not shown) may be incorporalted within to span the conduit 19 within the region of ~he inlet thereb~ to isolate the downstream components ~f the system including the burner 16 from entrained parti-culate ma~ter of gross size. Thusg in drying certain wood materials, such as fibers, veneer or flakes, large gross particles may, on occasion, be entrained in the drying air stream and otherwise carried into the system 12 where they collect on the catalyst in catalyst zone 14 and impair the efficiency thereof. A preferred example of such separating means is a filter preferably formed of any one of the commercially available porous ceramic types. With such fi~ters, application of heat and/or flame can be used to burn off any wood particles trapped thereon as discussed below. This form of filter is suitable for use in each of the embodiments hereof.
However, there may be used to equal advantage different types of particle entrapment means such as a metal screenO
The function of burner 16 in the present inven-tion is to adjust the temperature of the effluent gas ~L~ 3~
stream to that temperature at which the organic compoundstherein will be most effectively catalytically oxidized in the subsequent catalyst zone 14. As has been pre-viously noted, most of the difficulty with fouling comes from the condensable high boiling rosin material such as abietic acid. By raising the heat of the effluent gas stream, such materials will be brought ~o a temperature at which they will remain in gaseous form. Further, by ~-raising the heat of the effluent gas stream to such tempe-rature it is best converted by the catalyst which then operates more effectivety to ~xidize the organic material to harmless byproducts which then can be safely vented to the atmosphere. The temperature range most suitable for the platinum catalyst hereinafter described is about 450 to 525F. The b~rner 16 can also be used to consume the wood particles entering the system past damper 18 or that are trapped on the filter. Such burning of particles trapped on the filter eliminates the need to shut down the system to clean the filter.
Diffusion chamber 13 preferably is utilized to adjust the flow of effluent gas so that it assumes a substantially uniform flow across the area of its path of travel. This insures that the effluent gas will be evenly spread across the catalyst zone.
Catalyst zone 14, preferably comprises a series of catalyst containing means, or beds 45. In the FIGo 1 ~-' ~L~4~
embodiment each of the beds are in close proximity one to the other. The catalyst is preEerably ~ commercially available platinum metal sol coated on a carrier of expanded aluminum oxide or aluminum sllicate. Such a *
carrier is sold under the trade name "Torvex". It will be evident that other known catalysts and/or carriers can be used in gas permeable means which will function to oxidize the organic materials in the effluent gas to harmless and non-polIuting byproducts. The size of each catalys~ zone, the depth thereof, number of beds~ and the like are dependent upon the degree of pollutants in the effluent stream as well as the volume of air handled in the par~icular dryer. This can be readily calculated, and for a dryer having an air flow of 10,000 SCFM with wood fibers having the characteristics noted previously~ the ., catalyst zone itself will be approximately 4 feet by 4 - C~ r A t ~
feet in cross~section and cont~in~ng a number of beds.
It~is also preferred to have a blower 17 above ' the catalyst to insure that all gaseous effluent in the dryer passes through the system 12 of the present inven-tion and is treated prior to being passed through stack 15.
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In the ~igures, while the stacks illustrated have been shown as Venturi types the instant invention is - effective with any stack configuration. The purpose of the preferred Venturi type stack is to minimize the s'~' ~ ~a J~ ~na~k .
9 ~
stack steam plume. Since the heated off gas can contain some 20 percent moisture, a pl-ume could result, under certain atmospheric conditions, if Venturi flaring or some similar control device where not utilized to vent the cleaned gas to the atmosphere.
While the foregoing description has been mainly of the invention as illustrated in FIG. 1, it is equally applicable to the embodiments depicted in FIGS. 2-5 and for the most part to the preferr~d embodiment of FIGS. 6~9.
It will be evident that FIGS. 2-5 embodiments utilize the same components in the assembly as described in connec-tion with FIG. 1, but illustrate various alternatives in associating the assembly with a wood-'dryer. Thus, FI&. 2 depicts a side mounting with the damper and diffusion chamber in the dryer; FIG. 3 illustrates a top mounting -with the burner, damper, and diffusion chamber in the ~-dryer; FIG. 4 illustrates a single stack for venting -effluent gas from two dryers; and FIG. 5 illustrates a mounting on the roof of the dryer with the burner, damper, and diffusion chamber being outside of the dryer.
In the embodiment shown in FIG. 4, the stack is preferably separated from each of the blowers by a short conduit 41, each containing a flow control valve 42. Should only one dryer be in use, the valve in the conduit 41 of the other dryer can be closed to permit the assembly of the operating dryer to work most effectively.
3,Q~BZ3~
The embodiment depicted in FIG. 5 includes a heating element 51 and an inlet for activating gas 52, 53 The heating element Sl preferably is în the form of a coil mounted on the inside wall at the inlet to the system. The source of heat may be by exchange of heat from circulating flulds such as steam, hot water, and the like. Alternatively, the heating element can be an electric coil. The heating element 51 functions to raise the temperature of the effluent gas at the inlet to prevent deposition of pollutants from the gas stream.
The heating element may operate in conjunction with the burner 16.
The activating gas from a source (not shown) is introduced to the system through inlet conduit 52 and nozzle 53 although it should be evident that any struc-ture for introducing gas into the assembly is suitable.
The conduit for supply of gas from the source, such PS
a tank, may include the conventional valve structure for control purposes. The inlet is positioned upstream of the diffusion chamber so that any gas introduced likewise will be substantially uniformly spread across the path of flow of the effluent gas into the catalyst zone. As used herein, the term "activating as" refers t1 D 1l 0 Y~
to gases such as dhydrogen, carbon ~ #~e-, ammonia and ozone which ac~ to increase the speed of oxi~ation~
The hydrogen, for example~ in amounts as low as 1 percent~
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can be periodically inj ected into the effluent gas, The hydrogen will react with the prcferred platinum catalyst thereby raising the temperature of the catalyst surface to a temperature of about 75 to 100F. above ~hat o the effluent gas, which temperature differential gives an increased catalyst reactivity. With a similar quantity of gas such as ozone, there is more rapid oxi- ;
dation in the effluent gas stream which results in increased catalyst reactivity. Thus, the activating gases can act directly on the catalyst or the effluent gas.
Turning our attention now to what are considered ., ~ , .
the preferred embodim~nts of the invention, i.e~, FIGS. 6-9, there is illustrated a system 120 for controll ing the emission from a dryer. The emission control ; system 120 of FIG. 6 is enclosed within an elbow shaped ,- ,.
;~- conduit mounted on the roof 60 of the dryerg and includes ":
~ structure whose construction and operation, unless spe-..
cified otherwise, duplicates that of the previously des-. :-, cribed embodiments. Effluent from the dryer passes into the system at the outlet 11 of the dryer under control of a damper Preferably, the dryer effluent will be haated to or maintained at dryer temperature by a ,.
s heating element 51 disposed at the outlet 11.
A diffusion chamber is disposed to receive the , 7 flow of ~effluent and to pass the ef~luent to the oatalyst under substantially laminar flow conditions across the ` ~ 11 : , .~
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conduit~ For the sahe of simplicity only a single of what may be multiple of beds 45 of catalyst is illustra-ted in FIGo 6.
Heating means 122 is disposed in the direction of effluent flow just before the catalyst. The heating means preferably is formed by a multiplicity of electr;c heating elements which extend across the conduit in spaced parallel relation (see FIG. 9). Each heating element is formed by a metal sleeve or sheath 124 which surrounds a resistance member. Suitable refractory material 126, such as magnesium oxide, is compacted around the resistance member by conven~ional procedures to provide a stabilizing medium for purposes of insulation. At least the sheath or the so-called "cold pin" attached to both ends of the resistance member extends through opposite sides of the conduit. Each of the heating elements is ~; connected in parallel in an electric circuit. A cover 128 received on the conduit encloses the area of connec-tion. It will be readily evident that other heating means can be utilized so long as they are capable of adjusting the temperature of the catalyst to that desired.
The heating elements provide direct radiant heat transfer to the upstream face o~ the bed 45 of catalyst. The catalyst described above is considered capable of absorbing some 90 to 95 percent of the radiant heat energy. To this end, the heating elements are ': 1 . , . , . - . - .
dlsposed within rather close proximity to the ace. It has been found that this spacing may range from about 2 to about 8 inches from the face. Preferably~ the spacing of the heating elements will be about 2 to 4 inches.
A plurality of reflecting members 130 for re-ducing convection losses are positioned within the conduit on the upstream side of the heating elements. Each member may be of semi-circular, parabolic, or of pther ' similar structure for directing the radiation toward ` the face of the catalyst. Suitably, the members will be formed of material to provide a reflective surface.
;~ As may now have been appreciated the embodiments of FIGS. 6-9 operate without resort to the~ ~ 16 of, for example, the FIG. 1 embodiment. To this end, it has been found that the radiation from the heating ele-ments also heats the stream moving toward the catalyst : .:
by convection.
The radiant energy transferred to the catalyst face, to heat the face to a temperature of from about 150F. above ambient effluent ternperature may be provided in the preferred embodiment by a grid of heating elements located on about 3 inch centers across a generally square conduit for a flow of 5000 SCFM. The conduit may be about 28 inches in both dimensions. The total power -~ input may be approximately 60kw.
cata l-y~l c The~ 4~}~ activity has been found to .
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increase significantly through use of the heating ele-ments as described. The enhancement is in a substantiaL
doubling of the reaction rate for each 20F. rise in catalyst temperature over its normal temperature, as long as the reaction is not mass transfer limited.
The embodiment of FIG. 8 illustrating a stra-Lght-through conduit otherwise duplicates that of FIG. 6 in s~ructure and operation.
FIG. 7 illustrates an alternative make-up of the catalyst whereby a second!bed 20 of catalyst is uti-lized for purposes of~oxidation of the dryer effluent.
A grid of heating elements 122 is disposed adjacent to each bed in a manner and for the purposes as previously described.
A blower, as illustrated in FIG. 8, is utilized with each of the embodiments of FIGS. 6-9 to pull the :"
gases through the stackO
In a specific example of the process, 0.1 inch Douglas Fir heart strips were dried in a veneer oven at the rate of 7,794 square feet per one hour (3/8 inch basis).
The temperature of the dryer exhaust effluent gas was 354F. and the temperature at the catalyst face ;~
was 513F.
At the inlet to the catalytic unit, the effluent particulate concen~ration was 0.272 grains ~Iscf, the . . - .. .
emission rate was 7.04 pouncls per hour, the flow rate was 3021 DSCMF, and the moisture content was 14~6 percent by volume.
The cleaned effluent exhausted from the catalytic 0 0~3 unit had a particulate concentration of ~ 3 grains/scf, an emission rate of 1.73 pounds per hour, a flow rate of 3816 DSCFM, 13.5 percent moisture by voluoe and zero s~ack flow opaci~y.
While the process of the instant invention is largely evident from the above descrlption~ it comprises passing the e~fluent gas into a diffusion chamber to obtain as best as possible substantially uniform flow across the area of its confined path of travel and then passin~ the gas into a catalyst zone. In its preferred embodiment, the effluent gas is heated to a temperature above that at which the organic materials contained therein will condense and the surface of the catalyst is heated by a closely disposed source of radiant heat.
In this manner and by these means substantially all of the organic materials contained in the flow are cata- -lytically oxidized to innocuous byproducts.
While the present invention has been described .~
; ~ in~ connection with a preferred embodiment, it is not intended to limit the inverltion to the particular form set forth, but, on the contrary, i~ is in~ended to cover - such alternatives, modifications and equivalents as may ;~ 15 .,.
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be included within the spirit and scope of the inven-. tion as defined by the appended claims.
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BACKGROUND OF THE INVENTION
It is common practice to dry wood fibers, wood veneer, and plywood in ovenis utilizing either heated air or steam flow as the drying means.
In typical steam dryer operations, the alr flow can vary from about 5,000 to 10,000 SCFM. The `~ drying causes large volumes of water vapor to be e~pelled from the wood and 9 together with the water9 there are expelled organic materîals such as ~osin--~ type ma~erials and terpenes. Such organic materials are not only vented to the atmosphere where they causP
a substantial pollution problem but, in additi~n, the higher boiling fractions thereof, such as abietic acid, condense on the walls and exit of the smokestack or 3~ reo~JrJ~n~g the dryer ~u~,~u~ extended maintenance~because such buildup is a potential fire hazard.
- Attemp~s to overcome this prob~em by the use :
of higher drying temperatures to degrade the organic materials or keep them from condensing have not been en~irely successful due to the fact that such higher temperatures cause an undesirable darkening of the wood : .
or wood fibers. In addition, apparatus and method for handling the large amount of effluent gas from such dryers are no~ satisfactory in that they soon oul and themselves require extensive and repeated maintenance.
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; _ _MARY OF TIIE rNv~NTIoN-An improved system and method have now been developed which a~e capable of substantially reducing the pollutant content i.e cleaning, large volumes of effluent gas from wood dryers and without either extensive fouling or rosin buildup.
Briefly stated, the present invention comprises an emission control system for treating the gaseous effluent from a drying apparatus prior to venting said gaseous effluent from said apparatus to the atmosphere.
Accordingly, the present invention relates to a~ emission control system for cleaning substantially the entire flow of gaseous effluent from an apparatus for drying wood-type products prior to venting said gas~ous effluent ~rom said dr~ing appara-tus to the atmosphere, said system comprising, in in-line com-bination and in fluid flow communication, an inlet, first means for heating said gaseous effluent to a temperature pre-venting condensation of organic materials entrained in said effluent, a diffusion chamber for adjusting t~e 10w of said heated gaseous effluent so that it assumes su~stantially a uniform flow across the area of its path of travel~ a catalyst ` - zonP including at least two spaced apart catalyst beds both operating at temperatures sufficient to oxidize the organic materials present in said gaseous effluent,sec~nd heatin~
reans including an array of heating elements disposed in the upstream path of said flow and adjacent to a face of each .. ',' ` ' ~ .
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catalyst in said catalyst beds, refl.ective means disposed in the region o:E said heating el~ments of said array for directing radiant energy to said face o~ each catalyst for heating said ca-talyst and said gaseous effluent thereby to main-tain said gaseous effluent in an elevated noncombusted gaseous state through said catalyst zone, means connecting said heating means in an electric circuit, and a stack having an output emitting said gaseous.e~fluent in a cleaned condition to the atmosphere.
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BR:rE'F DESCE~_:[ON ~ . I ' L Dl;/:~ILNLS
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FIG. 1 is an elevational view o~ one form of the invention, portions thereof having been broken away to ; illustrate a damper and catalys-t bed;
; . FIG. 2 is an elevational view of an al-ternate f~rm - of the invention;
FIG. 3 is an elevational view of a further form o~
. ~ . the invention;
FIG. 4 is an elevational view of a form of the inven~
ti.on wherein a single stack accommodates at least a pair of dryers;
FIG. 5 is an elevational view of yet a further form of the invention including heating means and activating gas inlet means upstream of the effluent inlet;
FIG. 6 is an elevational view, partly in section, of - a preferred form of the invention;
FIG. 7, located on the same sheet as FIG.5, is an : elevational view, partly in section, of a pair of catalyst ;; beds having a heating source adjacent to the leading face i 20 of each bed;
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FIG. 8, located on the same sheet as FIG. 6, is an eleva-tional view of the form of FIG.6 in axial alignment; and, FIG. g~ also located on the ~ame Sheet as FIG.6, is a 9ection as seeh along the line 9-9 ]n FIG. 8 .. :
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3~
_~TAIL~D DESCRIP'ilION
Wllile the instant invention is suitable for use with any of the presen~ly used drying ovens and pro-cedures, it has particular application to and will be described in connection with wood veneer drying.
Referring to all oE the drawing figures, there are shown in fragment~ry form, the insulated roo~s and/ or walls 10, 20, 30... and 70 of a drying oven ada~ted for drying wood veneer. The oven can be any of those conventionally used to dry such product. The structure and operation of such dryers is well known in the art and~ since the dryer itself forms no part of the present invention other than in the combination with the system as the source of the emission to be controlled, will not be described in detail.
Wood, having a water content from about 40 to about 60 percent by as~is weight, is drie~ utili~ing steam or gas-fired drying means to heat air which is then forced through the dryer to dry the wood, As limited a quantity of air .: ~
as possible is used in order to minimize the amount of air that has to be heated as ~ell as to limit the amount of gas that is expelled through thP stack leaving the dryer.
~ypically, the air flow ~ill be, as previvusly noted~ in the range of about 5,000 to , -4-, ,;. .
:. .
about 10,000 SCFM. The air in leaving the dr~er will contain about 20 percent by volume vapor comprising essentially water, rosin fatty acids, and terpenes that are extracted from the wood. Based on wood containing from about 40 to 60 percent by weight water and subject to treatment with the noted air:~:flow, there will be exhausted from the dryer anywhere from about 5-15 pounds per hour of organic materials.
The temperature of a veneer dryer effluent gas can vary widely, but typically is about 300 to 375F.
In present dryer practice, as has been noted, such water and orgnic materials are simply vented through ~:
the stack with the consequent problems noted of air ~ a~/~*o~
~o~uticn and dryers and stack fouling and accompanying fire hazard.
In accordance with the present invention, the emission control system 12 of a first embodiment is dispo-sed to receive the emission from the dryer at an outlet 11 (see FIG. 1)~ The system 12 generally comprises a diffusion chamber 13, catalyst treatment zone 14, and :
stack 15 *~in fluid flow communication so that exhaust or effluent gas from the dryer will pass therethrough in the sequence noted.
It may be desired to incorporate combustor means .
16, preferably a burner, for heating the effluent gas prior to its entry into diffusion chamber 13. A blower 17 is located between catalyst zone 14 and stack 15 to '' :
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maintain flow conditions during operation. For optimum operation, it is also desirable to have gas flow control means such as a damper 18 placed at the inlet to the treatment system 12.
Means for separating entrained particulate matter, as for example, filter (not shown) may be incorporalted within to span the conduit 19 within the region of ~he inlet thereb~ to isolate the downstream components ~f the system including the burner 16 from entrained parti-culate ma~ter of gross size. Thusg in drying certain wood materials, such as fibers, veneer or flakes, large gross particles may, on occasion, be entrained in the drying air stream and otherwise carried into the system 12 where they collect on the catalyst in catalyst zone 14 and impair the efficiency thereof. A preferred example of such separating means is a filter preferably formed of any one of the commercially available porous ceramic types. With such fi~ters, application of heat and/or flame can be used to burn off any wood particles trapped thereon as discussed below. This form of filter is suitable for use in each of the embodiments hereof.
However, there may be used to equal advantage different types of particle entrapment means such as a metal screenO
The function of burner 16 in the present inven-tion is to adjust the temperature of the effluent gas ~L~ 3~
stream to that temperature at which the organic compoundstherein will be most effectively catalytically oxidized in the subsequent catalyst zone 14. As has been pre-viously noted, most of the difficulty with fouling comes from the condensable high boiling rosin material such as abietic acid. By raising the heat of the effluent gas stream, such materials will be brought ~o a temperature at which they will remain in gaseous form. Further, by ~-raising the heat of the effluent gas stream to such tempe-rature it is best converted by the catalyst which then operates more effectivety to ~xidize the organic material to harmless byproducts which then can be safely vented to the atmosphere. The temperature range most suitable for the platinum catalyst hereinafter described is about 450 to 525F. The b~rner 16 can also be used to consume the wood particles entering the system past damper 18 or that are trapped on the filter. Such burning of particles trapped on the filter eliminates the need to shut down the system to clean the filter.
Diffusion chamber 13 preferably is utilized to adjust the flow of effluent gas so that it assumes a substantially uniform flow across the area of its path of travel. This insures that the effluent gas will be evenly spread across the catalyst zone.
Catalyst zone 14, preferably comprises a series of catalyst containing means, or beds 45. In the FIGo 1 ~-' ~L~4~
embodiment each of the beds are in close proximity one to the other. The catalyst is preEerably ~ commercially available platinum metal sol coated on a carrier of expanded aluminum oxide or aluminum sllicate. Such a *
carrier is sold under the trade name "Torvex". It will be evident that other known catalysts and/or carriers can be used in gas permeable means which will function to oxidize the organic materials in the effluent gas to harmless and non-polIuting byproducts. The size of each catalys~ zone, the depth thereof, number of beds~ and the like are dependent upon the degree of pollutants in the effluent stream as well as the volume of air handled in the par~icular dryer. This can be readily calculated, and for a dryer having an air flow of 10,000 SCFM with wood fibers having the characteristics noted previously~ the ., catalyst zone itself will be approximately 4 feet by 4 - C~ r A t ~
feet in cross~section and cont~in~ng a number of beds.
It~is also preferred to have a blower 17 above ' the catalyst to insure that all gaseous effluent in the dryer passes through the system 12 of the present inven-tion and is treated prior to being passed through stack 15.
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In the ~igures, while the stacks illustrated have been shown as Venturi types the instant invention is - effective with any stack configuration. The purpose of the preferred Venturi type stack is to minimize the s'~' ~ ~a J~ ~na~k .
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stack steam plume. Since the heated off gas can contain some 20 percent moisture, a pl-ume could result, under certain atmospheric conditions, if Venturi flaring or some similar control device where not utilized to vent the cleaned gas to the atmosphere.
While the foregoing description has been mainly of the invention as illustrated in FIG. 1, it is equally applicable to the embodiments depicted in FIGS. 2-5 and for the most part to the preferr~d embodiment of FIGS. 6~9.
It will be evident that FIGS. 2-5 embodiments utilize the same components in the assembly as described in connec-tion with FIG. 1, but illustrate various alternatives in associating the assembly with a wood-'dryer. Thus, FI&. 2 depicts a side mounting with the damper and diffusion chamber in the dryer; FIG. 3 illustrates a top mounting -with the burner, damper, and diffusion chamber in the ~-dryer; FIG. 4 illustrates a single stack for venting -effluent gas from two dryers; and FIG. 5 illustrates a mounting on the roof of the dryer with the burner, damper, and diffusion chamber being outside of the dryer.
In the embodiment shown in FIG. 4, the stack is preferably separated from each of the blowers by a short conduit 41, each containing a flow control valve 42. Should only one dryer be in use, the valve in the conduit 41 of the other dryer can be closed to permit the assembly of the operating dryer to work most effectively.
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The embodiment depicted in FIG. 5 includes a heating element 51 and an inlet for activating gas 52, 53 The heating element Sl preferably is în the form of a coil mounted on the inside wall at the inlet to the system. The source of heat may be by exchange of heat from circulating flulds such as steam, hot water, and the like. Alternatively, the heating element can be an electric coil. The heating element 51 functions to raise the temperature of the effluent gas at the inlet to prevent deposition of pollutants from the gas stream.
The heating element may operate in conjunction with the burner 16.
The activating gas from a source (not shown) is introduced to the system through inlet conduit 52 and nozzle 53 although it should be evident that any struc-ture for introducing gas into the assembly is suitable.
The conduit for supply of gas from the source, such PS
a tank, may include the conventional valve structure for control purposes. The inlet is positioned upstream of the diffusion chamber so that any gas introduced likewise will be substantially uniformly spread across the path of flow of the effluent gas into the catalyst zone. As used herein, the term "activating as" refers t1 D 1l 0 Y~
to gases such as dhydrogen, carbon ~ #~e-, ammonia and ozone which ac~ to increase the speed of oxi~ation~
The hydrogen, for example~ in amounts as low as 1 percent~
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can be periodically inj ected into the effluent gas, The hydrogen will react with the prcferred platinum catalyst thereby raising the temperature of the catalyst surface to a temperature of about 75 to 100F. above ~hat o the effluent gas, which temperature differential gives an increased catalyst reactivity. With a similar quantity of gas such as ozone, there is more rapid oxi- ;
dation in the effluent gas stream which results in increased catalyst reactivity. Thus, the activating gases can act directly on the catalyst or the effluent gas.
Turning our attention now to what are considered ., ~ , .
the preferred embodim~nts of the invention, i.e~, FIGS. 6-9, there is illustrated a system 120 for controll ing the emission from a dryer. The emission control ; system 120 of FIG. 6 is enclosed within an elbow shaped ,- ,.
;~- conduit mounted on the roof 60 of the dryerg and includes ":
~ structure whose construction and operation, unless spe-..
cified otherwise, duplicates that of the previously des-. :-, cribed embodiments. Effluent from the dryer passes into the system at the outlet 11 of the dryer under control of a damper Preferably, the dryer effluent will be haated to or maintained at dryer temperature by a ,.
s heating element 51 disposed at the outlet 11.
A diffusion chamber is disposed to receive the , 7 flow of ~effluent and to pass the ef~luent to the oatalyst under substantially laminar flow conditions across the ` ~ 11 : , .~
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conduit~ For the sahe of simplicity only a single of what may be multiple of beds 45 of catalyst is illustra-ted in FIGo 6.
Heating means 122 is disposed in the direction of effluent flow just before the catalyst. The heating means preferably is formed by a multiplicity of electr;c heating elements which extend across the conduit in spaced parallel relation (see FIG. 9). Each heating element is formed by a metal sleeve or sheath 124 which surrounds a resistance member. Suitable refractory material 126, such as magnesium oxide, is compacted around the resistance member by conven~ional procedures to provide a stabilizing medium for purposes of insulation. At least the sheath or the so-called "cold pin" attached to both ends of the resistance member extends through opposite sides of the conduit. Each of the heating elements is ~; connected in parallel in an electric circuit. A cover 128 received on the conduit encloses the area of connec-tion. It will be readily evident that other heating means can be utilized so long as they are capable of adjusting the temperature of the catalyst to that desired.
The heating elements provide direct radiant heat transfer to the upstream face o~ the bed 45 of catalyst. The catalyst described above is considered capable of absorbing some 90 to 95 percent of the radiant heat energy. To this end, the heating elements are ': 1 . , . , . - . - .
dlsposed within rather close proximity to the ace. It has been found that this spacing may range from about 2 to about 8 inches from the face. Preferably~ the spacing of the heating elements will be about 2 to 4 inches.
A plurality of reflecting members 130 for re-ducing convection losses are positioned within the conduit on the upstream side of the heating elements. Each member may be of semi-circular, parabolic, or of pther ' similar structure for directing the radiation toward ` the face of the catalyst. Suitably, the members will be formed of material to provide a reflective surface.
;~ As may now have been appreciated the embodiments of FIGS. 6-9 operate without resort to the~ ~ 16 of, for example, the FIG. 1 embodiment. To this end, it has been found that the radiation from the heating ele-ments also heats the stream moving toward the catalyst : .:
by convection.
The radiant energy transferred to the catalyst face, to heat the face to a temperature of from about 150F. above ambient effluent ternperature may be provided in the preferred embodiment by a grid of heating elements located on about 3 inch centers across a generally square conduit for a flow of 5000 SCFM. The conduit may be about 28 inches in both dimensions. The total power -~ input may be approximately 60kw.
cata l-y~l c The~ 4~}~ activity has been found to .
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increase significantly through use of the heating ele-ments as described. The enhancement is in a substantiaL
doubling of the reaction rate for each 20F. rise in catalyst temperature over its normal temperature, as long as the reaction is not mass transfer limited.
The embodiment of FIG. 8 illustrating a stra-Lght-through conduit otherwise duplicates that of FIG. 6 in s~ructure and operation.
FIG. 7 illustrates an alternative make-up of the catalyst whereby a second!bed 20 of catalyst is uti-lized for purposes of~oxidation of the dryer effluent.
A grid of heating elements 122 is disposed adjacent to each bed in a manner and for the purposes as previously described.
A blower, as illustrated in FIG. 8, is utilized with each of the embodiments of FIGS. 6-9 to pull the :"
gases through the stackO
In a specific example of the process, 0.1 inch Douglas Fir heart strips were dried in a veneer oven at the rate of 7,794 square feet per one hour (3/8 inch basis).
The temperature of the dryer exhaust effluent gas was 354F. and the temperature at the catalyst face ;~
was 513F.
At the inlet to the catalytic unit, the effluent particulate concen~ration was 0.272 grains ~Iscf, the . . - .. .
emission rate was 7.04 pouncls per hour, the flow rate was 3021 DSCMF, and the moisture content was 14~6 percent by volume.
The cleaned effluent exhausted from the catalytic 0 0~3 unit had a particulate concentration of ~ 3 grains/scf, an emission rate of 1.73 pounds per hour, a flow rate of 3816 DSCFM, 13.5 percent moisture by voluoe and zero s~ack flow opaci~y.
While the process of the instant invention is largely evident from the above descrlption~ it comprises passing the e~fluent gas into a diffusion chamber to obtain as best as possible substantially uniform flow across the area of its confined path of travel and then passin~ the gas into a catalyst zone. In its preferred embodiment, the effluent gas is heated to a temperature above that at which the organic materials contained therein will condense and the surface of the catalyst is heated by a closely disposed source of radiant heat.
In this manner and by these means substantially all of the organic materials contained in the flow are cata- -lytically oxidized to innocuous byproducts.
While the present invention has been described .~
; ~ in~ connection with a preferred embodiment, it is not intended to limit the inverltion to the particular form set forth, but, on the contrary, i~ is in~ended to cover - such alternatives, modifications and equivalents as may ;~ 15 .,.
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be included within the spirit and scope of the inven-. tion as defined by the appended claims.
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Claims (5)
1. An emission control system for cleaning substantially the entire flow of gaseous effluent from an apparatus for drying wood-type products prior to venting said gaseous effluent from said drying apparatus to the atmosphere, said system comprising, in in-line combination and in fluid flow communication, an inlet, first means for heating said gaseous effluent to a temperature preventing condensation of organic materials entrained in said effluent, a diffusion chamber for adjusting the flow of said heated gaseous effluent so that it assumes substantially a uniform flow across the area of its path of travel, a catalyst zone including at least two spaced apart catalyst beds both operating at temperatures sufficient to oxidize the organic materials present in said gaseous effluent, second heating means including an array of heating elements disposed in the upstream path of said flow and adjacent to a face of each catalyst in said catalyst beds, reflective means disposed in the region of said heating elements of said array for directing radiant energy to said face of each catalyst for heating said catalyst and said gaseous effluent thereby to maintain said gaseous effluent in an elevated noncombusted gaseous state through said catalyst zone, means connecting said heating means in an electric circuit, and a stack having an output emitting said gaseous effluent in a cleaned condition to the atmosphere.
2. The system of Claim 1, including means for maintaining the flow of said gaseous effluent to said catalyst zone.
3. The system of Claim 1, wherein said reflective means are supported to partially surround each of said heating elements for directing radiant energy to said face of said catalyst bed.
4. The system of Claim 1, including means for introducing an activating gas into said flow of gaseous effluent, said introducing means communicating said activating gas between said inlet and said diffusion chamber.
5. The system of Claim 1, including filter means interposed between the inlet and the diffusion chamber for filtering solid particles from said gaseous effluent.
Applications Claiming Priority (2)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| US43378374A | 1974-01-16 | 1974-01-16 | |
| US05/513,453 US3941493A (en) | 1973-10-11 | 1974-10-09 | Device for mounting spherical piston-rod ends of barrel-type hydraulic machine |
Publications (1)
| Publication Number | Publication Date |
|---|---|
| CA1048234A true CA1048234A (en) | 1979-02-13 |
Family
ID=27029971
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CA75217484A Expired CA1048234A (en) | 1974-01-16 | 1975-01-07 | Emission control system and method |
Country Status (1)
| Country | Link |
|---|---|
| CA (1) | CA1048234A (en) |
-
1975
- 1975-01-07 CA CA75217484A patent/CA1048234A/en not_active Expired
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