EP0451648B1 - Opposed fired rotary kiln - Google Patents
Opposed fired rotary kiln Download PDFInfo
- Publication number
- EP0451648B1 EP0451648B1 EP91105063A EP91105063A EP0451648B1 EP 0451648 B1 EP0451648 B1 EP 0451648B1 EP 91105063 A EP91105063 A EP 91105063A EP 91105063 A EP91105063 A EP 91105063A EP 0451648 B1 EP0451648 B1 EP 0451648B1
- Authority
- EP
- European Patent Office
- Prior art keywords
- oxidant
- cylindrical body
- rotatable cylindrical
- flue
- injected
- 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 - Lifetime
Links
- 239000007800 oxidant agent Substances 0.000 claims description 108
- 230000001590 oxidative effect Effects 0.000 claims description 103
- 238000002485 combustion reaction Methods 0.000 claims description 62
- 239000007789 gas Substances 0.000 claims description 44
- 238000002347 injection Methods 0.000 claims description 41
- 239000007924 injection Substances 0.000 claims description 41
- 238000000034 method Methods 0.000 claims description 35
- 239000002699 waste material Substances 0.000 claims description 29
- 239000000446 fuel Substances 0.000 claims description 26
- 239000000463 material Substances 0.000 claims description 22
- QVGXLLKOCUKJST-UHFFFAOYSA-N atomic oxygen Chemical compound [O] QVGXLLKOCUKJST-UHFFFAOYSA-N 0.000 claims description 13
- 239000001301 oxygen Substances 0.000 claims description 13
- 229910052760 oxygen Inorganic materials 0.000 claims description 13
- XLYOFNOQVPJJNP-UHFFFAOYSA-N water Substances O XLYOFNOQVPJJNP-UHFFFAOYSA-N 0.000 claims description 7
- MYMOFIZGZYHOMD-UHFFFAOYSA-N Dioxygen Chemical compound O=O MYMOFIZGZYHOMD-UHFFFAOYSA-N 0.000 claims description 6
- UGFAIRIUMAVXCW-UHFFFAOYSA-N Carbon monoxide Chemical compound [O+]#[C-] UGFAIRIUMAVXCW-UHFFFAOYSA-N 0.000 claims description 4
- 239000003546 flue gas Substances 0.000 claims description 4
- 238000001035 drying Methods 0.000 description 10
- MWUXSHHQAYIFBG-UHFFFAOYSA-N nitrogen oxide Inorganic materials O=[N] MWUXSHHQAYIFBG-UHFFFAOYSA-N 0.000 description 9
- 239000003570 air Substances 0.000 description 7
- 239000002920 hazardous waste Substances 0.000 description 6
- VNWKTOKETHGBQD-UHFFFAOYSA-N methane Chemical compound C VNWKTOKETHGBQD-UHFFFAOYSA-N 0.000 description 6
- 230000006378 damage Effects 0.000 description 5
- 239000012530 fluid Substances 0.000 description 5
- 238000010304 firing Methods 0.000 description 3
- 239000003517 fume Substances 0.000 description 3
- 231100001261 hazardous Toxicity 0.000 description 3
- 239000003345 natural gas Substances 0.000 description 3
- 238000011017 operating method Methods 0.000 description 3
- 239000002689 soil Substances 0.000 description 3
- IJGRMHOSHXDMSA-UHFFFAOYSA-N Atomic nitrogen Chemical compound N#N IJGRMHOSHXDMSA-UHFFFAOYSA-N 0.000 description 2
- ATUOYWHBWRKTHZ-UHFFFAOYSA-N Propane Chemical compound CCC ATUOYWHBWRKTHZ-UHFFFAOYSA-N 0.000 description 2
- 230000015572 biosynthetic process Effects 0.000 description 2
- 239000004568 cement Substances 0.000 description 2
- 239000000919 ceramic Substances 0.000 description 2
- 239000000571 coke Substances 0.000 description 2
- 239000000567 combustion gas Substances 0.000 description 2
- 239000000470 constituent Substances 0.000 description 2
- 230000002349 favourable effect Effects 0.000 description 2
- 239000010808 liquid waste Substances 0.000 description 2
- 239000000203 mixture Substances 0.000 description 2
- 238000012545 processing Methods 0.000 description 2
- 239000000126 substance Substances 0.000 description 2
- 238000012546 transfer Methods 0.000 description 2
- 239000003039 volatile agent Substances 0.000 description 2
- 238000004056 waste incineration Methods 0.000 description 2
- 230000001154 acute effect Effects 0.000 description 1
- 238000003915 air pollution Methods 0.000 description 1
- 239000012080 ambient air Substances 0.000 description 1
- 238000001354 calcination Methods 0.000 description 1
- 238000006243 chemical reaction Methods 0.000 description 1
- 238000004891 communication Methods 0.000 description 1
- 238000000354 decomposition reaction Methods 0.000 description 1
- 238000013461 design Methods 0.000 description 1
- 238000001784 detoxification Methods 0.000 description 1
- 238000010494 dissociation reaction Methods 0.000 description 1
- 230000005593 dissociations Effects 0.000 description 1
- 230000000694 effects Effects 0.000 description 1
- 239000000295 fuel oil Substances 0.000 description 1
- 238000010438 heat treatment Methods 0.000 description 1
- 239000011344 liquid material Substances 0.000 description 1
- 238000002156 mixing Methods 0.000 description 1
- 229910052757 nitrogen Inorganic materials 0.000 description 1
- 238000013021 overheating Methods 0.000 description 1
- 231100000614 poison Toxicity 0.000 description 1
- 239000001294 propane Substances 0.000 description 1
- 238000000197 pyrolysis Methods 0.000 description 1
- 238000011084 recovery Methods 0.000 description 1
- 239000007787 solid Substances 0.000 description 1
- 239000011343 solid material Substances 0.000 description 1
- 239000002910 solid waste Substances 0.000 description 1
- 239000003440 toxic substance Substances 0.000 description 1
Images
Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F27—FURNACES; KILNS; OVENS; RETORTS
- F27B—FURNACES, KILNS, OVENS, OR RETORTS IN GENERAL; OPEN SINTERING OR LIKE APPARATUS
- F27B7/00—Rotary-drum furnaces, i.e. horizontal or slightly inclined
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/20—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having rotating or oscillating drums
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C9/00—Combustion apparatus characterised by arrangements for returning combustion products or flue gases to the combustion chamber
- F23C9/006—Combustion apparatus characterised by arrangements for returning combustion products or flue gases to the combustion chamber the recirculation taking place in the combustion chamber
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G5/00—Incineration of waste; Incinerator constructions; Details, accessories or control therefor
- F23G5/08—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating
- F23G5/12—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having supplementary heating using gaseous or liquid fuel
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F27—FURNACES; KILNS; OVENS; RETORTS
- F27B—FURNACES, KILNS, OVENS, OR RETORTS IN GENERAL; OPEN SINTERING OR LIKE APPARATUS
- F27B7/00—Rotary-drum furnaces, i.e. horizontal or slightly inclined
- F27B7/20—Details, accessories, or equipment peculiar to rotary-drum furnaces
- F27B7/34—Arrangements of heating devices
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C2202/00—Fluegas recirculation
- F23C2202/40—Inducing local whirls around flame
Definitions
- This invention relates generally to rotary kilns and is particularly useful with mobile rotary kilns.
- a rotary kiln is a refractory-lined cylindrical vessel commonly used, for example, in the incineration of waste, in the calcining of cement, coke or other materials, in the firing of ceramic, and in many other uses.
- the waste is provided into the kiln and is combusted while passing through the kiln by the combustion fuel and oxidant which is injected into the rotary kiln at one end of the kiln.
- the injection of the fuel and oxidant into the kiln may be either concurrent with the flow of waste or other material through the kiln, or it may be countercurrent to the flow of waste or other material through the kiln.
- Gases from within the kiln are removed through a flue located at one end of the kiln. After the waste has passed through the kiln, ash from the combusted waste is removed from the kiln.
- the throughput of material, such as waste, through the kiln is limited by the quantity of furnace gases generated within the kiln by the injected fuel and oxidant, and by the combusting volatiles if volatiles are present, and also by the rate at which heat can be transferred to wet material or to other heat sinks by the furnace gases.
- a rotary kiln comprising:
- Another aspect of this invention comprises: A method for operating a rotary kiln comprising:
- cylindrical means tubular, generally but not necessarily having a circular radial cross-section.
- waste means any material intended for partial or total combustion within a combustion zone.
- burner means a device through which both oxidant and combustible matter are provided into a combustion zone either separately or as a mixture.
- the term "lance” means a device through which either oxidant or combustible matter but not both is provided into a combustion zone.
- recirculation ratio means the ratio of the mass flowrate of material recirculated back toward the periphery of a jet to the mass flowrate of the total fluid injected into a combustion zone.
- combustion means a substance that will burn under combustion zone conditions.
- incombustible means a substance that will not burn under combustion zone conditions.
- volatile means a material which will pass into the vapor state under combustion zone conditions such as, for example, the vapor materials resulting from drying, or from the decomposition or thermal dissociation of solid or liquid materials.
- equivalent diameter means that diameter of a single circular orifice which would provide the same total area as the sum of the areas of a multi-orifice injection means.
- Figure 1 is a schematic representation of one embodiment of the invention carried out in conjunction with waste incineration within a countercurrent kiln.
- Figure 2 is a schematic representation of another embodiment of the invention carried out in conjunction with waste incineration within a concurrent kiln.
- Figure 3 is a schematic representation of another embodiment of the invention illustrating the invention carried out with a plug flow zone.
- Figure 4 is an illustration of a single orifice oxidant injection means for injecting oxidant with a high momentum into a kiln at the flue end.
- Figure 5 is an illustration of a multi-orifice oxidant injection means for injecting oxidant with a high momentum into a kiln at the flue end.
- Figure 7 is an illustration of a means to react fuel and oxidant in a recessed cavity prior to injection into the kiln.
- the invention enables a significant increase in rotary kiln throughput by maintaining a desirable temperature profile throughout the kiln. This reduces large temperature gradients through the kiln reducing the need for a high temperature in one part of the kiln in order to provide heat to another part of the kiln. In addition the need for auxiliary fuel combustion to provide heat to a drying zone within the kiln is reduced. Thus throughput limitations caused by localized hot temperatures or flue gas flowrates are relaxed.
- rotary kiln 1 having a rotatable cylindrical body 2, and nonrotatable walls 3 and 4 at each axial end of the rotatable cylindrical body to define a combustion zone 5.
- the kiln has a length to diameter ratio exceeding 4 but less than 8.
- Flue 6 is positioned at one axial end of rotatable cylindrical body 2. Although shown in Figure 1 as having a horizontal orientation, the flue may have a vertical or any other suitable orientation.
- a first oxidant injection means such as first burner 7 is positioned within nonrotatable wall 4 opposite the end having flue 6. First burner 7 is oriented to inject fuel and oxidant into combustion zone 5 within rotatable cylindrical body 2 in a direction toward the flue end.
- Second oxidant injection means such as second burner 8 is positioned within nonrotatable wall 3 at the flue end and is oriented to inject fuel and oxidant into combustion zone 5 in a direction toward the end opposite the flue end.
- either or both of the first and second oxidant injection means may be a lance, such as lance 12. In such a case only oxidant is provided into the combustion zone from a lance.
- the second oxidant injection means which injects oxidant into the kiln in the direction away from the flue end is adapted to inject the oxidant with a momentum sufficient to pass through the kiln a length equal to at least two times the internal diameter of, and preferably at least 50 percent of the length of, the rotatable cylindrical body.
- One means of accomplishing this high momentum is by the injection of the oxidant through a restricted orifice having a diameter, or multiple orifices having an equivalent diameter, not exceeding 1/30 of the kiln internal diameter and preferably not exceeding 1/100 of the kiln internal diameter.
- the restricted orifice imparts a high velocity to the oxidant as defined by Bernoulli's equation, and the high velocity causes the momentum to increase since momentum is the product of mass and velocity.
- Another means of accomplishing high momentum is by increasing the mass of the second oxidant. However, this is not preferable because this simultaneously increases the mass and the momentum of the gas flowing toward the flue end.
- Figures 4, 5 and 6 illustrate such second oxidant injection means.
- a single orifice nozzle having a restricted diameter for the injection of oxidant there is illustrated a single orifice nozzle having a restricted diameter for the injection of oxidant.
- Figure 5 illustrates a multiple orifice nozzle having an equivalent diameter of the defined restriction to enable the attainment of the required high momentum.
- Figure 6 illustrates a burner wherein oxidant and fuel may be injected through concentric tubes to produce oxidizing gas. Oxidant may be fed through the center tube and fuel may be fed through the outer annular passage or vice versa.
- the center tube may be fitted with a single or a multiple orifice nozzle.
- oxidant and some fuel can react and expand within a cavity recessed within the kiln wall.
- the cavity provides a restriction so that the hot combustion products at near the adiabatic flame temperature of the mixture leave the cavity at a high velocity.
- the cavity would have a diameter at the point of communication with the kiln of less than 1/10 of the kiln internal diameter.
- feed such as waste 9, comprising volatile material is provided into combustion zone 5, such as through ram feeder 10, to form a bed which flows through the combustion zone.
- Other feeds which be used with this invention include cement, coke, ceramic and other materials which include a volatile component such as water.
- the method of this invention will be described in detail with waste as the feed which may include volatile combustible and volatile incombustible matter.
- Waste may be liquid and/or solid waste such as is defined in the Resource Conservation Recovery Act (RCRA) or the Toxic Substances Control Act (TSCA).
- the waste passes sequentially through a drying zone 13 wherein it is dried of volatile incombustible matter such as water and some of the lighter volatile combustible matter, a pyrolysis zone 14 wherein additional combustible matter is volatized out, and a char burnout zone 15 wherein the residual solids are combusted.
- Resulting ash is removed from combustion zone 5 through ash removal door 11.
- ash removal door 11 As is appreciated by one skilled in the art, there is not a clear demarcation between these zones.
- the arrows indicate the volatization of incombustible and combustible matter in zones 13 and 14 respectively.
- Fuel and oxidant are injected through burner 7 into combustion zone 5 wherein they are combusted to provide heat to the combustion zone to carry out the drying, pyrolyzing and burning of the waste discussed above.
- the oxidant may be air, technically pure oxygen having an oxygen concentration greater than 99.5 percent, or oxygen-enriched air having an oxygen concentration of at least 25 percent and preferably greater than 30 percent.
- the fuel may be any suitable fluid fuel such as natural gas, propane, fuel oil, or liquid waste.
- Fuel and oxidant are injected into combustion zone 5 through second burner 8 and can be defined the same as the fuel and oxidant injected through first burner 7.
- the fuel and oxidant injected through burner 8 is injected having a momentum at least equal to, and preferably greater than 200 percent of, the momentum of the gas flowing toward the flue end.
- the gas flowing toward the flue end may include fuel and oxidant injected through the first burner and the combustion products thereof, water vapor, combustion products from the material injected through the second burner, and combustion products from the combustion of volatized combustible material.
- momentum is equal to the mass times the velocity of the fluid.
- the combustion reaction stream injected through burner 8 penetrates a significant distance into combustion zone 5, preferably at least two kiln diameters. Heat released from the combustion of the fuel and oxidant injected into combustion zone 5 through burner 8 serves to provide heat for the aforedescribed drying, pyrolyzing and burning of the waste.
- the arrangement of the invention wherein burners fire opposed to one another causes the temperature within the combustion zone to be much more uniform than with conventional rotary kiln arrangements because the two injected combustion streams tend to cause each other to recirculate through the combustion zone as indicated by the reversing flow arrows 16 in Figure 1, although only the recirculation of the gas flowing from the flue end is necessary for the successful operation of the invention.
- the high momentum of the flue end combustion stream causes enhanced recirculation as shown by arrows 17. In this way temperature gradients within the kiln are better controlled so throughput limitations based on heat transfer rate considerations or flue gas flowrate considerations are relaxed.
- the high momentum flame may be manipulated to enhance local radiative and convective heat transfer to the load when desired.
- either or both of the oxidant streams injected through oxidant injection means 7 and 8 are injected at a high velocity so as to provide a recirculation of gases within the combustion zone, preferably to provide a recirculation ratio exceeding 4.
- the oxidant stream velocity exceeds 150 feet per second. In this way the temperature uniformity within combustion zone 5 is enhanced. This is particularly the case for the oxidant stream injected through first burner 7 so that, as illustrated in Figure 1, the gases do not merely pass through combustion zone 5, but rather recirculate one or more times within combustion zone 5 so as to enhance mixing and combustion efficiency within combustion zone 5 and thus further enhance temperature uniformity within each of the two recirculation zones at the two parts of the combustion zone.
- the injection end of the second oxidant injection means located at the flue end protrudes a distance into the combustion zone as illustrated in Figure 3 rather than having its injection end flush with the wall within which it is positioned as is illustrated in Figures 1 and 2.
- the numerals in Figure 3 correspond to those of Figure 1 for the common elements.
- a plug flow zone is establish immediately before the flue.
- the gas velocity is reduced due to the lack of recirculation flow. Therefore, air-borne particulates have the opportunity to settle down from the gas stream. Also the gas is allowed to cool down somewhat, resulting in reduced gas velocity.
- the protrusion can be as long as practical and typically is about one kiln diameter.
- a countercurrent kiln it may be desirable to inject additional oxidant, such as technically pure oxygen, into the combustion zone at the flue end in order to carry out further combustion in the drying zone.
- additional oxidant such as technically pure oxygen
- the additional oxidant may be injected through burner 8 or through lance 12 depending on which is used as the second oxidant injection means.
- the invention enables the kiln operator to operate the combustion zone of the rotary kiln with two separate combustion control zones at each end of the kiln.
- the combustion control zone at each end of the kiln may be operated with pyrolytic (fuel-rich) or oxidating (oxygen-rich) conditions thus adding flexibility to the kiln design and to the combustion process control.
- the combustion control zone at the flue end of a countercurrent rotary kiln can be run in the pyrolytic mode so that combustible gases released from the waste are recirculated and entrained into the high momentum stream from the flue end burner thus consuming the oxidant.
- Residue char in the combustion control zone at the other end of the kiln can be exposed to oxidating conditions to complete the burnout.
- the use of oxygen enrichment serves to decrease the momentum of the gases flowing toward the flue thus enabling easier flue end injection into the kiln, and also serves to decrease the volumetric flowrate of gases flowing through the flue thus increasing throughput. Accordingly the lower the percentage of inert nitrogen introduced into the combustion zone with the oxidant, the more advantageous will be the operation of the method of this invention. Thus, to achieve maximum throughput, the most preferred oxidant is technically pure oxygen, air inleakage notwithstanding.
- Figure 2 illustrates the rotary kiln and operating method of this invention carried out with the incineration of waste in a concurrent kiln.
- flue 20 is located at the end opposite the end at which waste is provided into the kiln.
- First oxidant injection means such as a lance or burner 21 is positioned within nonrotatable wall 3 at the end opposite the flue end and second oxidant injection means such as a lance or burner 22 is positioned within nonrotatable wall 4 at the flue end.
- Oxidant injection means 21 and 22 inject oxidant toward the wall opposite from where they are positioned.
- the invention enables the operation of a rotary kiln with improved control by enabling independent or separate adjustment of the oxidant and fluid fuel injected at the flue end and at the end opposite the flue end. This is particularly advantageous when these two oxidants have differing oxygen concentrations, e.g. air and technically pure oxygen.
- determine means any way of arriving at a value including measuring, calculating or estimating the value.
- the flowrate may then be compared with a predetermined desired flowrate and the flowrate ratio of the oxidants may then be adjusted, i.e. changed, so that the determined flowrate changes in the direction toward the desired flowrate. Because of the high momentum of the oxidant injected at the flue end which passes significant gas flow away from the flue into the kiln, as opposed to prior art processes, changes in flue gas flowrate can be accomplished with changes in the flowrate ratio of the injected oxidants while being able to maintain a desirable temperature profile and furnace atmosphere.
- any operating parameter may be determined, compared with a predetermined desired value for that parameter, and the total flowrate and the flowrate ratio of the oxidants may be adjusted so that the determined value of the parameter changes in the direction toward the desired value for that parameter.
- this advantageous control based on changing the total flowrate and the ratio of the oxidants is due to the high momentum of the flue end injected oxidant which doesn't merely affect the proximity of the flue end as in conventional processes, but rather has a marked effect on the gas flow pattern within the kiln.
- a significant advantage of the invention is the ability to independently control temperature or heat release and atmosphere at each end of the kiln while simultaneously controlling gas flowrate or pressure in the kiln.
- a scaled-down cold flow model of a rotary kiln similar to that illustrated in Figure 3 was employed.
- the kiln model had a length of 3.5 feet and an L/D ratio of 7.
- the momentum of the flow from the burner ranged between 100 to 500 percent of the momentum of the gases flowing toward the flue.
- the flow from the flue end jet penetrated up to 63.3 percent of the length of the kiln. Recirculation gas flow within the kiln flue end was vigorous.
- a countercurrent rotary kiln similar to that illustrated in Figure 3 is employed having a length of 45 feet and an internal diameter of 6.5 feet.
- Oxygen at a flowrate of 4092 lb/hr and natural gas at a flowrate of 1066 lb/hr, having a heat value of 22,991 BTU/lb, are injected at a high momentum into the kiln at the flue end through a burner extending 5 feet into the kiln.
- Air at a flowrate of 11,000 lb/hr and natural gas at a flowrate of 613 lb/hr are injected into the kiln through a burner at the end opposite the flue end.
- the kiln is operated at negative pressure and ambient air leaks into the kiln at a flowrate of 5500 lb/hr.
- Soil comprising hazardous waste and having a water content of 15 percent but no heating value is passed into the kiln at the flue end at the rate of 25 tons per hour.
- Ash is removed from the kiln at a temperature of 900°F at a flowrate of 42,494 lb/hr and gas is passed out of the kiln through the flue at the rate of 29,777 lb/hr (30,630 actual cubic feed per minute) at a temperature of 1600°F and having an oxygen concentration of 3.1 percent.
- the maximum soil processing rate is only 16 tons per hour while meeting the required ash temperature of 900°F.
- the flame is shortened and the combustion gas temperature gradient is significantly increased so that, at an increased throughput, the soil does not undergo sufficient residence time at the elevated temperature to undergo a detoxification reaction.
Landscapes
- Engineering & Computer Science (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Chemical & Material Sciences (AREA)
- Combustion & Propulsion (AREA)
- Incineration Of Waste (AREA)
- Muffle Furnaces And Rotary Kilns (AREA)
- Treatment Of Fiber Materials (AREA)
- Thermotherapy And Cooling Therapy Devices (AREA)
- Soy Sauces And Products Related Thereto (AREA)
Description
- This invention relates generally to rotary kilns and is particularly useful with mobile rotary kilns.
- A rotary kiln is a refractory-lined cylindrical vessel commonly used, for example, in the incineration of waste, in the calcining of cement, coke or other materials, in the firing of ceramic, and in many other uses. In the incineration of waste, the waste is provided into the kiln and is combusted while passing through the kiln by the combustion fuel and oxidant which is injected into the rotary kiln at one end of the kiln. The injection of the fuel and oxidant into the kiln may be either concurrent with the flow of waste or other material through the kiln, or it may be countercurrent to the flow of waste or other material through the kiln. Gases from within the kiln are removed through a flue located at one end of the kiln. After the waste has passed through the kiln, ash from the combusted waste is removed from the kiln.
- In a countercurrent kiln the hot combustion gases and excess air are carried through the kiln first volatizing combustibles from the waste. These combustibles are combusted generating additional heat flowing countercurrently to the flowing waste which further dries the waste. It is imperative that the furnace gases contain sufficient mass to absorb the heat release without overheating which can cause refractory damage to the kiln or kinetically favor the generation of nitrogen oxides (NOx). Accordingly the throughput of material, such as waste, through the kiln is limited by the quantity of furnace gases generated within the kiln by the injected fuel and oxidant, and by the combusting volatiles if volatiles are present, and also by the rate at which heat can be transferred to wet material or to other heat sinks by the furnace gases.
- In a concurrent kiln another problem arises in that the heat released from volatile combustibles is passing away from the wet material heat sink. An auxiliary burner is generally required to provide extra heat to the drying zone to dry the material so as to enable volatization of the volatile combustibles. This increases the volumetric flowrate of the gases passing out the flue increasing particulate carryover and burden on the air pollution devices thus limiting the throughput through the kiln.
- The mismatch of heat source and heat sink which creates throughput limitations for both countercurrent and concurrent rotary kilns is more severe for long rotary kilns, such as kilns having a length to diameter (L/D) ratio exceeding 4.
- A recent use for rotary kilns which has been gaining wide acceptance has been in the incineration of hazardous waste. A particularly advantageous rotary kiln for this application is a mobile or transportable rotary kiln which can be transported to the hazardous waste site and then removed when the hazardous waste site has been cleaned. Unfortunately a mobile rotary kiln is by necessity smaller than a stationary rotary kiln in order to enable transportability. Thus the throughput limitations discussed above are even more acute in the case of a mobile rotary kiln.
- Accordingly it is an object of this invention to provide a rotary kiln having increased throughput over conventional rotary kilns without causing high potential for refractory damage or creating conditions highly favorable for NOx formation.
- It is another object of this invention to provide a method for operating a rotary kiln so as to increase throughput over that obtainable with conventional rotary kiln operating methods without causing high potential for refractory damage or creating conditions highly favorable for NOx formation.
- The above and other objects which will become apparent to one skilled in the art upon a reading of this disclosure are attained by the present invention one aspect of which is:
A rotary kiln comprising: - (A) a rotatable cylindrical body having an internal diameter;
- (B) a nonrotatable wall at each end of the rotatable cylindrical body;
- (C) flue means at one end of the rotatable cylindrical body;
- (D) a first oxidant injection means positioned within the nonrotatable wall at the end opposite to the flue end, said first oxidant injection means oriented to inject oxidant into the rotatable cylindrical body toward the flue end; and
- (E) a second oxidant injection means positioned within the nonrotatable wall at the flue end, said second oxidant injection means oriented to inject oxidant into the rotatable cylindrical body toward the end opposite the flue end and adapted to inject the oxidant with a momentum sufficient to pass through a length equal to at least two times the internal diameter of the rotatable cylindrical body.
- Another aspect of this invention comprises:
A method for operating a rotary kiln comprising: - (A) providing feed comprising volatile material into a rotatable cylindrical body;
- (B) removing gas from the rotatable cylindrical body through a flue at one end of the rotatable cylindrical body;
- (C) injecting oxidant into the rotatable cylindrical body at the end opposite the flue end in the direction of the flue end to create a flow of gas toward the flue end;
- (D) injecting oxidant into the rotatable cylindrical body at the flue end in the direction of the end opposite the flue end having a momentum at least equal to that of gas flowing toward the flue end; and
- (E) volatizing material from the feed within the rotatable cylindrical body.
- As used herein the term "cylindrical" means tubular, generally but not necessarily having a circular radial cross-section.
- As used herein, the term "waste" means any material intended for partial or total combustion within a combustion zone.
- As used herein the term "burner" means a device through which both oxidant and combustible matter are provided into a combustion zone either separately or as a mixture.
- As used herein the term "lance" means a device through which either oxidant or combustible matter but not both is provided into a combustion zone.
- As used herein the term "recirculation ratio" means the ratio of the mass flowrate of material recirculated back toward the periphery of a jet to the mass flowrate of the total fluid injected into a combustion zone.
- As used herein the term "combustible" means a substance that will burn under combustion zone conditions.
- As used herein the term "incombustible" means a substance that will not burn under combustion zone conditions.
- As used herein the term "volatile" means a material which will pass into the vapor state under combustion zone conditions such as, for example, the vapor materials resulting from drying, or from the decomposition or thermal dissociation of solid or liquid materials.
- As used herein the term "equivalent diameter" means that diameter of a single circular orifice which would provide the same total area as the sum of the areas of a multi-orifice injection means.
- Figure 1 is a schematic representation of one embodiment of the invention carried out in conjunction with waste incineration within a countercurrent kiln.
- Figure 2 is a schematic representation of another embodiment of the invention carried out in conjunction with waste incineration within a concurrent kiln.
- Figure 3 is a schematic representation of another embodiment of the invention illustrating the invention carried out with a plug flow zone.
- Figure 4 is an illustration of a single orifice oxidant injection means for injecting oxidant with a high momentum into a kiln at the flue end.
- Figure 5 is an illustration of a multi-orifice oxidant injection means for injecting oxidant with a high momentum into a kiln at the flue end.
- Figure 6 is an illustration of a burner which may be used in the practice of this invention.
- Figure 7 is an illustration of a means to react fuel and oxidant in a recessed cavity prior to injection into the kiln.
- The invention enables a significant increase in rotary kiln throughput by maintaining a desirable temperature profile throughout the kiln. This reduces large temperature gradients through the kiln reducing the need for a high temperature in one part of the kiln in order to provide heat to another part of the kiln. In addition the need for auxiliary fuel combustion to provide heat to a drying zone within the kiln is reduced. Thus throughput limitations caused by localized hot temperatures or flue gas flowrates are relaxed.
- The invention will be described in detail with reference to the Drawings.
- Referring now to Figure 1, there is illustrated
rotary kiln 1 having a rotatablecylindrical body 2, andnonrotatable walls 3 and 4 at each axial end of the rotatable cylindrical body to define acombustion zone 5. Preferably the kiln has a length to diameter ratio exceeding 4 but less than 8. -
Flue 6 is positioned at one axial end of rotatablecylindrical body 2. Although shown in Figure 1 as having a horizontal orientation, the flue may have a vertical or any other suitable orientation. A first oxidant injection means such as first burner 7 is positioned within nonrotatable wall 4 opposite theend having flue 6. First burner 7 is oriented to inject fuel and oxidant intocombustion zone 5 within rotatablecylindrical body 2 in a direction toward the flue end. Second oxidant injection means such assecond burner 8 is positioned withinnonrotatable wall 3 at the flue end and is oriented to inject fuel and oxidant intocombustion zone 5 in a direction toward the end opposite the flue end. Alternatively either or both of the first and second oxidant injection means may be a lance, such as lance 12. In such a case only oxidant is provided into the combustion zone from a lance. - The second oxidant injection means which injects oxidant into the kiln in the direction away from the flue end is adapted to inject the oxidant with a momentum sufficient to pass through the kiln a length equal to at least two times the internal diameter of, and preferably at least 50 percent of the length of, the rotatable cylindrical body. One means of accomplishing this high momentum is by the injection of the oxidant through a restricted orifice having a diameter, or multiple orifices having an equivalent diameter, not exceeding 1/30 of the kiln internal diameter and preferably not exceeding 1/100 of the kiln internal diameter. The restricted orifice imparts a high velocity to the oxidant as defined by Bernoulli's equation, and the high velocity causes the momentum to increase since momentum is the product of mass and velocity. Another means of accomplishing high momentum is by increasing the mass of the second oxidant. However, this is not preferable because this simultaneously increases the mass and the momentum of the gas flowing toward the flue end.
- Figures 4, 5 and 6 illustrate such second oxidant injection means. Referring to Figure 4 there is illustrated a single orifice nozzle having a restricted diameter for the injection of oxidant. Figure 5 illustrates a multiple orifice nozzle having an equivalent diameter of the defined restriction to enable the attainment of the required high momentum. Figure 6 illustrates a burner wherein oxidant and fuel may be injected through concentric tubes to produce oxidizing gas. Oxidant may be fed through the center tube and fuel may be fed through the outer annular passage or vice versa. The center tube may be fitted with a single or a multiple orifice nozzle.
- In anther embodient illustrated in Figure 7, one can cause oxidant and some fuel to react and expand within a cavity recessed within the kiln wall. The cavity provides a restriction so that the hot combustion products at near the adiabatic flame temperature of the mixture leave the cavity at a high velocity. In this case the cavity would have a diameter at the point of communication with the kiln of less than 1/10 of the kiln internal diameter.
- In operation, feed, such as
waste 9, comprising volatile material is provided intocombustion zone 5, such as throughram feeder 10, to form a bed which flows through the combustion zone. Other feeds which be used with this invention include cement, coke, ceramic and other materials which include a volatile component such as water. The method of this invention will be described in detail with waste as the feed which may include volatile combustible and volatile incombustible matter. Waste may be liquid and/or solid waste such as is defined in the Resource Conservation Recovery Act (RCRA) or the Toxic Substances Control Act (TSCA). The waste passes sequentially through a dryingzone 13 wherein it is dried of volatile incombustible matter such as water and some of the lighter volatile combustible matter, apyrolysis zone 14 wherein additional combustible matter is volatized out, and achar burnout zone 15 wherein the residual solids are combusted. Resulting ash is removed fromcombustion zone 5 through ash removal door 11. As is appreciated by one skilled in the art, there is not a clear demarcation between these zones. In Figure 1 the arrows indicate the volatization of incombustible and combustible matter inzones - Fuel and oxidant are injected through burner 7 into
combustion zone 5 wherein they are combusted to provide heat to the combustion zone to carry out the drying, pyrolyzing and burning of the waste discussed above. The oxidant may be air, technically pure oxygen having an oxygen concentration greater than 99.5 percent, or oxygen-enriched air having an oxygen concentration of at least 25 percent and preferably greater than 30 percent. The fuel may be any suitable fluid fuel such as natural gas, propane, fuel oil, or liquid waste. - The combustion of the fuel and oxidant injected into
combustion zone 5 through first burner 7, and the combustion of the volatile combustibles evaporated from the waste, create a flow of gas toward the flue end. Gas is removed fromcombustion zone 5 throughflue 6. - Fuel and oxidant are injected into
combustion zone 5 throughsecond burner 8 and can be defined the same as the fuel and oxidant injected through first burner 7. The fuel and oxidant injected throughburner 8 is injected having a momentum at least equal to, and preferably greater than 200 percent of, the momentum of the gas flowing toward the flue end. The gas flowing toward the flue end may include fuel and oxidant injected through the first burner and the combustion products thereof, water vapor, combustion products from the material injected through the second burner, and combustion products from the combustion of volatized combustible material. As is known, momentum is equal to the mass times the velocity of the fluid. In this way the combustion reaction stream injected throughburner 8 penetrates a significant distance intocombustion zone 5, preferably at least two kiln diameters. Heat released from the combustion of the fuel and oxidant injected intocombustion zone 5 throughburner 8 serves to provide heat for the aforedescribed drying, pyrolyzing and burning of the waste. - The arrangement of the invention wherein burners fire opposed to one another causes the temperature within the combustion zone to be much more uniform than with conventional rotary kiln arrangements because the two injected combustion streams tend to cause each other to recirculate through the combustion zone as indicated by the reversing
flow arrows 16 in Figure 1, although only the recirculation of the gas flowing from the flue end is necessary for the successful operation of the invention. Furthermore, the high momentum of the flue end combustion stream causes enhanced recirculation as shown byarrows 17. In this way temperature gradients within the kiln are better controlled so throughput limitations based on heat transfer rate considerations or flue gas flowrate considerations are relaxed. In addition, the high momentum flame may be manipulated to enhance local radiative and convective heat transfer to the load when desired. - In a preferred operating method either or both of the oxidant streams injected through oxidant injection means 7 and 8 are injected at a high velocity so as to provide a recirculation of gases within the combustion zone, preferably to provide a recirculation ratio exceeding 4. Preferably the oxidant stream velocity exceeds 150 feet per second. In this way the temperature uniformity within
combustion zone 5 is enhanced. This is particularly the case for the oxidant stream injected through first burner 7 so that, as illustrated in Figure 1, the gases do not merely pass throughcombustion zone 5, but rather recirculate one or more times withincombustion zone 5 so as to enhance mixing and combustion efficiency withincombustion zone 5 and thus further enhance temperature uniformity within each of the two recirculation zones at the two parts of the combustion zone. - In an alternative arrangement, the injection end of the second oxidant injection means located at the flue end protrudes a distance into the combustion zone as illustrated in Figure 3 rather than having its injection end flush with the wall within which it is positioned as is illustrated in Figures 1 and 2. The numerals in Figure 3 correspond to those of Figure 1 for the common elements. In this way a plug flow zone is establish immediately before the flue. In a plug flow zone there is very little backmixing or recirculation of gases. In the more quiescent plug flow region, the gas velocity is reduced due to the lack of recirculation flow. Therefore, air-borne particulates have the opportunity to settle down from the gas stream. Also the gas is allowed to cool down somewhat, resulting in reduced gas velocity. The protrusion can be as long as practical and typically is about one kiln diameter.
- In a countercurrent kiln it may be desirable to inject additional oxidant, such as technically pure oxygen, into the combustion zone at the flue end in order to carry out further combustion in the drying zone. This is particularly the case where a large amount of combustibles are volatized from the feed and are carried into the drying zone by the flowing gases resulting in pyrolytic or fuel-rich conditions in the drying zone. The additional oxidant may be injected through
burner 8 or through lance 12 depending on which is used as the second oxidant injection means. - The invention enables the kiln operator to operate the combustion zone of the rotary kiln with two separate combustion control zones at each end of the kiln. In addition to stoichiometric operation, the combustion control zone at each end of the kiln may be operated with pyrolytic (fuel-rich) or oxidating (oxygen-rich) conditions thus adding flexibility to the kiln design and to the combustion process control. For example, especially with the processing of high-BTU waste, the combustion control zone at the flue end of a countercurrent rotary kiln can be run in the pyrolytic mode so that combustible gases released from the waste are recirculated and entrained into the high momentum stream from the flue end burner thus consuming the oxidant. Residue char in the combustion control zone at the other end of the kiln can be exposed to oxidating conditions to complete the burnout.
- In the method of this invention the use of oxygen enrichment serves to decrease the momentum of the gases flowing toward the flue thus enabling easier flue end injection into the kiln, and also serves to decrease the volumetric flowrate of gases flowing through the flue thus increasing throughput. Accordingly the lower the percentage of inert nitrogen introduced into the combustion zone with the oxidant, the more advantageous will be the operation of the method of this invention. Thus, to achieve maximum throughput, the most preferred oxidant is technically pure oxygen, air inleakage notwithstanding.
- Figure 2 illustrates the rotary kiln and operating method of this invention carried out with the incineration of waste in a concurrent kiln. The numerals in Figure 2 correspond to those of Figure 1 for the common elements. In the embodiment illustrated in Figure 2,
flue 20 is located at the end opposite the end at which waste is provided into the kiln. First oxidant injection means such as a lance orburner 21 is positioned withinnonrotatable wall 3 at the end opposite the flue end and second oxidant injection means such as a lance orburner 22 is positioned within nonrotatable wall 4 at the flue end. Oxidant injection means 21 and 22 inject oxidant toward the wall opposite from where they are positioned. The operation of the rotary kiln illustrated in Figure 2 is similar to that of the kiln illustrated in Figure 1 except that the flow of gases toward the flue end is concurrent with, not countercurrent to, the flow of waste sequentially through the drying, pyrolyzing and char burning zones. - In a conventional rotary kiln used to incinerate hazardous waste, hazardous fumes released from the waste may not always pass through the flame region of the combustion zone. For a conventional countercurrent rotary kiln the fumes may not even be exposed to a high temperature within the kiln. Accordingly conventional incineration systems employing rotary kilns depend in great measure on a secondary combustion chamber for the destruction of hazardous constituents. However with the system of this invention wherein opposed fired burners cause extensive gas recirculation within the combustion zone, fumes volatized from the waste pass several times through the flame region thus increasing the destruction efficiency of the hazardous constituents. This may, in some cases, eliminate the need for a secondary combustion chamber in the incineration of hazardous waste.
- The invention enables the operation of a rotary kiln with improved control by enabling independent or separate adjustment of the oxidant and fluid fuel injected at the flue end and at the end opposite the flue end. This is particularly advantageous when these two oxidants have differing oxygen concentrations, e.g. air and technically pure oxygen.
- For example, one may determine the volumetric flowrate of the gas being removed through the flue. As used herein the term "determine" means any way of arriving at a value including measuring, calculating or estimating the value. The flowrate may then be compared with a predetermined desired flowrate and the flowrate ratio of the oxidants may then be adjusted, i.e. changed, so that the determined flowrate changes in the direction toward the desired flowrate. Because of the high momentum of the oxidant injected at the flue end which passes significant gas flow away from the flue into the kiln, as opposed to prior art processes, changes in flue gas flowrate can be accomplished with changes in the flowrate ratio of the injected oxidants while being able to maintain a desirable temperature profile and furnace atmosphere.
- In another example, one may determine the pressure within the rotatable cylindrical body. Typically when waste is being incinerated the pressure within the kiln is desired to be a negative pressure. The determined pressure may then be compared with a predetermined desired pressure and the flowrate ratio of the oxidants may then be adjusted so that the determined pressure changes in the direction of the desired pressure while maintaining a desirable temperature profile and furnace atmosphere.
- In another method for improving the control of the operation of the rotary kiln, one may determine the heat demand at both the flue end zone and at the end zone opposite the flue end and adjust the flow of one or both of the oxidants and fluid fuel, if necessary, to accommodate the heat demands simultaneously.
- As can be seen any operating parameter may be determined, compared with a predetermined desired value for that parameter, and the total flowrate and the flowrate ratio of the oxidants may be adjusted so that the determined value of the parameter changes in the direction toward the desired value for that parameter. As indicated earlier this advantageous control based on changing the total flowrate and the ratio of the oxidants is due to the high momentum of the flue end injected oxidant which doesn't merely affect the proximity of the flue end as in conventional processes, but rather has a marked effect on the gas flow pattern within the kiln. A significant advantage of the invention is the ability to independently control temperature or heat release and atmosphere at each end of the kiln while simultaneously controlling gas flowrate or pressure in the kiln.
- Temperature within the kiln may also be controlled or moderated by the injection of water, especially as an atomized stream, into the kiln.
- The following examples are provided for illustrative purposes and are not intended to limiting.
- A scaled-down cold flow model of a rotary kiln similar to that illustrated in Figure 3 was employed. The kiln model had a length of 3.5 feet and an L/D ratio of 7. A nozzle injected gas toward the flue end at a volumetric flowrate of 7380 cubic feet per hour (CFH) and a burner fired away from the flue end with a high velocity jet injected at a volumetric flowrate of up to 670 CFH wherein the initial velocity of the jet was about 1000 feet per second. The momentum of the flow from the burner ranged between 100 to 500 percent of the momentum of the gases flowing toward the flue. The flow from the flue end jet penetrated up to 63.3 percent of the length of the kiln. Recirculation gas flow within the kiln flue end was vigorous.
- A countercurrent rotary kiln similar to that illustrated in Figure 3 is employed having a length of 45 feet and an internal diameter of 6.5 feet. Oxygen at a flowrate of 4092 lb/hr and natural gas at a flowrate of 1066 lb/hr, having a heat value of 22,991 BTU/lb, are injected at a high momentum into the kiln at the flue end through a burner extending 5 feet into the kiln. Air at a flowrate of 11,000 lb/hr and natural gas at a flowrate of 613 lb/hr are injected into the kiln through a burner at the end opposite the flue end. The kiln is operated at negative pressure and ambient air leaks into the kiln at a flowrate of 5500 lb/hr. Soil comprising hazardous waste and having a water content of 15 percent but no heating value is passed into the kiln at the flue end at the rate of 25 tons per hour. Ash is removed from the kiln at a temperature of 900°F at a flowrate of 42,494 lb/hr and gas is passed out of the kiln through the flue at the rate of 29,777 lb/hr (30,630 actual cubic feed per minute) at a temperature of 1600°F and having an oxygen concentration of 3.1 percent.
- With the air fired burner firing alone, the maximum soil processing rate is only 16 tons per hour while meeting the required ash temperature of 900°F. Moreover with oxygen enrichment at the discharge end and without the oxygen burner firing toward the discharge end, the flame is shortened and the combustion gas temperature gradient is significantly increased so that, at an increased throughput, the soil does not undergo sufficient residence time at the elevated temperature to undergo a detoxification reaction.
Claims (40)
- A method for operating a rotary kiln comprising:(A) providing feed comprising volatile material into a rotatable cylindrical body;(B) removing gas from the rotatable cylindrical body through a flue at one end of the rotatable cylindrical body;(C) injecting oxidant into the rotatable cylindrical body at the end opposite the flue end in the direction of the flue end to create a flow of gas toward the flue end;(D) injecting oxidant into the rotatable cylindrical body at the flue end in the direction of the end opposite the flue end having a momentum at least equal to that of gas flowing toward the flue end; and(E) volatizing material from the feed within the rotatable cylindrical body.
- The method of claim 1 wherein feed is provided into the rotatable cylindrical body at the same end as that where gas is removed through the flue.
- The method of claim 1 wherein feed is provided into the rotatable cylindrical body at the end opposite to the end where gas is removed through the flue.
- The method of claim 1 wherein the oxidant injected in step (D) penetrates into the rotatable cylindrical body a distance at least equal to two diameters of the rotatable cylindrical body.
- The method of claim 1 wherein the feed is waste comprising combustible material.
- The method of claim 5 additionally comprising combusting volatized combustible material from the waste within the rotatable cylindrical body.
- The method of claim 5 wherein the feed comprises water as a volatile material.
- The method of claim 1 wherein at least one of the oxidant injected into the rotatable cylindrical body in steps (C) and (D) is technically pure oxygen.
- The method of claim 1 wherein at least one of the oxidant injected into the rotatable cylindrical body in steps (C) and (D) is oxygen-enriched air having an oxygen concentration of at least 25 percent.
- The method of claim 1 wherein the oxidant injected into the rotatable cylindrical in step (C) is air and the oxidant injected into the rotatable cylindrical body in step (D) is technically pure oxygen.
- The method of claim 1 wherein the oxidant injected into the rotatable cylindrical body in step (D) is injected flush with a wall at that end.
- The method of claim 1 wherein the oxidant injected into the rotatable cylindrical body in step (D) is injected extending from a wall at that end.
- The method of claim 1 wherein fuel is injected with the oxidant in step (C).
- The method of claim 1 wherein fuel is injected with the oxidant in step (D).
- The method of claim 1 wherein combustion is carried out at at least one of the flue end and the end opposite the flue end under pyrolytic conditions.
- The method of claim 1 wherein combustion is carried out at at least one of the flue end and the end opposite the flue end under oxidating conditions.
- The method of claim 1 wherein combustion is carried out at the flue end under pyrolytic conditions and combustion is carried out at the end opposite the flue end under oxidating conditions.
- The method of claim 1 further comprising determining the volumetric flowrate of the gas being removed through the flue, comparing the determined flowrate with a predetermined desired flowrate, and adjusting the volumetric flowrate ratio of the oxidant injected in step (C) and the oxidant injected in step (D) so that the flue gas volumetric flowrate changes toward the desired flowrate.
- The method of claim 1 further comprising determining the pressure within the rotatable cylindrical body, comparing the determined pressure with a predetermined desired pressure, and adjusting the volumetric flowrate ratio of the oxidant injected in step (C) and the oxidant injected in step (D) so that the pressure within the rotatable cylindrical body changes toward the desired pressure.
- The method of claim 1 further comprising determining the heat demand at the flue end and also at the end opposite the flue end, and adjusting the flow of at least one of the oxidant injected in step (C) and the oxidant injected in step (D) to accommodate the determined heat demands.
- The method of claim 1 wherein the oxidant injected in step (C) and the oxidant injected in step (D) have different oxygen concentrations.
- The method of claim 1 further comprising determining the value of an operating parameter, comparing the determined value with a predetermined desired value for that parameter, and adjusting the volumetric flowrate ratio of the oxidant injected in step (C) and the oxidant injected in step (D) so that the determined value changes toward the desired value.
- The method of claim 1 further comprising independently controlling the temperature and atmosphere at each end of the rotatable cylindrical body while simultaneously controlling the gas flowrate into the rotatable cylindrical body.
- The method of claim 1 wherein the oxidant injected into the rotatable cylindrical body in step (D) is introduced into a cavity recessed from the wall at that end and thereafter passed from the cavity into the rotatable cylindrical body.
- The method of claim 24 wherein some oxidant combusts with fuel within the cavity.
- The method of claim 1 wherein the oxident injected in step (D) is oxidizing gas generated from a burner.
- The method of claim 1 further comprising injecting water into the rotatable cylindrical body.
- A rotary kiln comprising:(A) a rotatable cylindrical body having an internal diameter;(B) a nonrotatable wall at each end of the rotatable cylindrical body;(C) flue means at one end of the rotatable cylindrical body;(D) a first oxidant injection means positioned within the nonrotatable wall at the end opposite to the flue end, said first oxidant injection means oriented to inject oxidant into the rotatable cylindrical body toward the flue end; and(E) a second oxidant injection means positioned within the nonrotatable wall at the flue end, said second oxidant injection means oriented to inject oxidant into the rotatable cylindrical body toward the end opposite the flue end and adapted to inject the oxidant with a momentum sufficient to pass through a length equal to at least two times the internal diameter of the cylindrical body.
- The rotary kiln of claim 28 wherein the rotatable cylindrical body has a length to diameter ratio exceeding 4.
- The rotary kiln of claim 28 additionally comprising means to provide feed into the kiln at the end where the flue means is located.
- The rotary kiln of claim 28 additionally comprising means to provide feed into the kiln at the end opposite to the end where the flue means is located.
- The rotary kiln of claim 28 wherein the rotary kiln is a mobile rotary kiln.
- The rotary kiln of claim 28 wherein the second oxidant injection means has its injection end flush with the nonrotatable wall within which it is positioned.
- The rotary kiln of claim 28 wherein the injection end of the second oxidant injection means extends beyond the nonrotatable wall within which the second oxidant injection means is positioned.
- The rotary kiln of claim 28 wherein at least one of the first oxidant injection means and the second oxidant injection means is a burner.
- The rotary kiln of claim 28 wherein at least one of the first oxidant injection means and the second oxidant injection means is a lance.
- The rotary kiln of claim 28 wherein the second oxidant injection means comprises a restricted orifice having a diameter, or a plurality of orifices having an equivalent diameter not exceeding 1/30 of the internal diameter of the rotatable cylindrical body.
- The rotary kiln of claim 28 wherein the second oxidant injection means comprises a cavity within the nonrotatable wall which communicates with the rotatable cylindrical body.
- The rotary kiln of claim 38 wherein the cavity has a restricted diameter at the point where it communicates with the rotatable cylindrical body.
- The rotary kiln of claim 39 wherein the restricted diameter is less than 1/10 of the internal diameter of the rotatable cylindrical body.
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US50090690A | 1990-03-29 | 1990-03-29 | |
US500906 | 1990-03-29 |
Publications (3)
Publication Number | Publication Date |
---|---|
EP0451648A2 EP0451648A2 (en) | 1991-10-16 |
EP0451648A3 EP0451648A3 (en) | 1992-05-13 |
EP0451648B1 true EP0451648B1 (en) | 1993-05-05 |
Family
ID=23991420
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
EP91105063A Expired - Lifetime EP0451648B1 (en) | 1990-03-29 | 1991-03-28 | Opposed fired rotary kiln |
Country Status (7)
Country | Link |
---|---|
EP (1) | EP0451648B1 (en) |
JP (1) | JPH04225783A (en) |
KR (1) | KR960010601B1 (en) |
BR (1) | BR9101206A (en) |
CA (1) | CA2039317C (en) |
DE (1) | DE69100074T2 (en) |
ES (1) | ES2040605T3 (en) |
Cited By (1)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP2208935A1 (en) * | 2009-01-15 | 2010-07-21 | Siemens Aktiengesellschaft | Combustion chamber and gas turbine |
Families Citing this family (15)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US5186617A (en) * | 1991-11-06 | 1993-02-16 | Praxair Technology, Inc. | Recirculation and plug flow combustion method |
GB9125423D0 (en) * | 1991-11-29 | 1992-01-29 | Kyffin Robin A | Heat treatment of expansible materials to form lightweight aggregate |
DK0614452T3 (en) * | 1991-11-29 | 1996-08-19 | Robin Anthony Kyffin | Heat treatment of an inflatable material to produce a light aggregate |
US5203859A (en) * | 1992-04-22 | 1993-04-20 | Institute Of Gas Technology | Oxygen-enriched combustion method |
EP0653590B2 (en) * | 1993-11-17 | 2003-10-29 | Praxair Technology, Inc. | Method for deeply staged combustion |
FR2733303B1 (en) * | 1995-04-19 | 1997-05-30 | Gaz De France | WASTE BOILER-INCINERATOR AND METHOD FOR OPERATING A WASTE BOILER-INCINERATOR |
KR100339484B1 (en) * | 1999-08-06 | 2002-05-31 | 장기종 | Rotary kiln incineration system |
ITRM20040324A1 (en) * | 2004-06-30 | 2004-09-30 | Ct Sviluppo Materiali Spa | APPARATUS FOR WASTE DISPOSAL. |
DE102006023677A1 (en) * | 2006-05-19 | 2007-11-22 | Polysius Ag | Plant and process for the production of cement clinker |
DE102006028770B4 (en) * | 2006-06-23 | 2008-04-30 | Basf Coatings Ag | Incinerator for liquid and solid residues and processes |
JP5876264B2 (en) * | 2011-10-07 | 2016-03-02 | 株式会社アクトリー | Waste treatment equipment |
DE102012002548A1 (en) | 2012-02-09 | 2013-08-14 | Linde Aktiengesellschaft | Firing a rotary kiln |
EP2626628B1 (en) | 2012-02-09 | 2014-04-09 | Linde Aktiengesellschaft | Firing of an industrial furnace and associated burner |
DE102013017943A1 (en) * | 2013-10-29 | 2015-04-30 | Linde Aktiengesellschaft | Method for operating a rotary drum furnace |
EP3037765A1 (en) | 2014-12-26 | 2016-06-29 | L'Air Liquide Société Anonyme pour l'Etude et l'Exploitation des Procédés Georges Claude | Direct-fired inclined counterflow rotary kilns and use thereof |
Family Cites Families (6)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
JPS5141271A (en) * | 1974-09-24 | 1976-04-07 | Daburyuu Baakusu Paa | Ekitai gasujo oyobi peesutojohatsubutsunoshokyakuho narabini sochi |
DE2549076A1 (en) * | 1975-11-03 | 1977-05-12 | Kraftanlagen Ag | Solid and liquid waste combustion system - has rotary main combustion chamber and after burner chamber surrounding a mixer tube |
US4245571A (en) * | 1978-04-05 | 1981-01-20 | T R Systems, Inc. | Thermal reductor system and method for recovering valuable metals from waste |
US4863371A (en) * | 1988-06-03 | 1989-09-05 | Union Carbide Corporation | Low NOx high efficiency combustion process |
JPH0210017A (en) * | 1988-06-29 | 1990-01-12 | Mitsubishi Heavy Ind Ltd | Refuse incinerator |
US4957050A (en) * | 1989-09-05 | 1990-09-18 | Union Carbide Corporation | Combustion process having improved temperature distribution |
-
1991
- 1991-03-26 BR BR919101206A patent/BR9101206A/en not_active IP Right Cessation
- 1991-03-28 EP EP91105063A patent/EP0451648B1/en not_active Expired - Lifetime
- 1991-03-28 DE DE9191105063T patent/DE69100074T2/en not_active Expired - Fee Related
- 1991-03-28 KR KR1019910004841A patent/KR960010601B1/en not_active IP Right Cessation
- 1991-03-28 ES ES199191105063T patent/ES2040605T3/en not_active Expired - Lifetime
- 1991-03-28 JP JP3087369A patent/JPH04225783A/en active Pending
- 1991-03-28 CA CA002039317A patent/CA2039317C/en not_active Expired - Fee Related
Cited By (2)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
EP2208935A1 (en) * | 2009-01-15 | 2010-07-21 | Siemens Aktiengesellschaft | Combustion chamber and gas turbine |
WO2010081578A1 (en) * | 2009-01-15 | 2010-07-22 | Siemens Aktiengesellschaft | Combustion chamber and gas turbine |
Also Published As
Publication number | Publication date |
---|---|
JPH04225783A (en) | 1992-08-14 |
DE69100074D1 (en) | 1993-06-09 |
KR910017153A (en) | 1991-11-05 |
EP0451648A3 (en) | 1992-05-13 |
ES2040605T3 (en) | 1993-10-16 |
DE69100074T2 (en) | 1993-08-12 |
KR960010601B1 (en) | 1996-08-06 |
CA2039317C (en) | 1995-01-17 |
BR9101206A (en) | 1991-11-05 |
EP0451648A2 (en) | 1991-10-16 |
Similar Documents
Publication | Publication Date | Title |
---|---|---|
EP0451648B1 (en) | Opposed fired rotary kiln | |
US4861262A (en) | Method and apparatus for waste disposal | |
US5123364A (en) | Method and apparatus for co-processing hazardous wastes | |
US5102330A (en) | Opposed fired rotary kiln | |
US5105747A (en) | Process and apparatus for reducing pollutant emissions in flue gases | |
EP0541105B1 (en) | Recirculation and plug flow combustion method | |
USRE34298E (en) | Method for waste disposal | |
CA2222819C (en) | Method and device for producing and utilizing gas from waste materials | |
US5000102A (en) | Method for combusting wet waste | |
US5553554A (en) | Waste disposal and energy recovery system and method | |
CN102449394A (en) | Nox suppression techniques for a rotary kiln | |
US5372497A (en) | Process and apparatus for igniting a burner in an inert atmosphere | |
US5213492A (en) | Combustion method for simultaneous control of nitrogen oxides and products of incomplete combustion | |
KR101133434B1 (en) | Low pollutant emission combustion using high-temperature fgr | |
US5242295A (en) | Combustion method for simultaneous control of nitrogen oxides and products of incomplete combustion | |
JP4015026B2 (en) | Advanced NOx reduction method for boilers | |
EP0499184B1 (en) | Combustion method for simultaneous control of nitrogen oxides and products of incomplete combustion | |
CA1333973C (en) | Method and apparatus for waste disposal | |
JPH0510514A (en) | Incineration method of refuse and apparatus therefor | |
AU621059B2 (en) | A method and apparatus for waste disposal | |
RU2052726C1 (en) | Waste gas afterburning device | |
JP2004085027A (en) | Operation method for waste incinerator using dried sludge and dried sludge thermal decomposition device |
Legal Events
Date | Code | Title | Description |
---|---|---|---|
PUAI | Public reference made under article 153(3) epc to a published international application that has entered the european phase |
Free format text: ORIGINAL CODE: 0009012 |
|
AK | Designated contracting states |
Kind code of ref document: A2 Designated state(s): BE DE ES FR IT |
|
PUAL | Search report despatched |
Free format text: ORIGINAL CODE: 0009013 |
|
AK | Designated contracting states |
Kind code of ref document: A3 Designated state(s): BE DE ES FR IT |
|
17P | Request for examination filed |
Effective date: 19920527 |
|
17Q | First examination report despatched |
Effective date: 19920810 |
|
ITF | It: translation for a ep patent filed | ||
GRAA | (expected) grant |
Free format text: ORIGINAL CODE: 0009210 |
|
RAP1 | Party data changed (applicant data changed or rights of an application transferred) |
Owner name: PRAXAIR TECHNOLOGY, INC. |
|
AK | Designated contracting states |
Kind code of ref document: B1 Designated state(s): BE DE ES FR IT |
|
REF | Corresponds to: |
Ref document number: 69100074 Country of ref document: DE Date of ref document: 19930609 |
|
ET | Fr: translation filed | ||
REG | Reference to a national code |
Ref country code: ES Ref legal event code: FG2A Ref document number: 2040605 Country of ref document: ES Kind code of ref document: T3 |
|
PLBE | No opposition filed within time limit |
Free format text: ORIGINAL CODE: 0009261 |
|
STAA | Information on the status of an ep patent application or granted ep patent |
Free format text: STATUS: NO OPPOSITION FILED WITHIN TIME LIMIT |
|
26N | No opposition filed | ||
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: FR Payment date: 19990302 Year of fee payment: 9 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: DE Payment date: 19990305 Year of fee payment: 9 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: BE Payment date: 19990323 Year of fee payment: 9 |
|
PGFP | Annual fee paid to national office [announced via postgrant information from national office to epo] |
Ref country code: ES Payment date: 19990324 Year of fee payment: 9 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: ES Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 20000329 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: BE Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 20000331 |
|
BERE | Be: lapsed |
Owner name: PRAXAIR TECHNOLOGY INC. Effective date: 20000331 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: FR Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 20001130 |
|
REG | Reference to a national code |
Ref country code: FR Ref legal event code: ST |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: DE Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES Effective date: 20010103 |
|
REG | Reference to a national code |
Ref country code: ES Ref legal event code: FD2A Effective date: 20010910 |
|
PG25 | Lapsed in a contracting state [announced via postgrant information from national office to epo] |
Ref country code: IT Free format text: LAPSE BECAUSE OF NON-PAYMENT OF DUE FEES;WARNING: LAPSES OF ITALIAN PATENTS WITH EFFECTIVE DATE BEFORE 2007 MAY HAVE OCCURRED AT ANY TIME BEFORE 2007. THE CORRECT EFFECTIVE DATE MAY BE DIFFERENT FROM THE ONE RECORDED. Effective date: 20050328 |