Rotary Batch And Cullet Preheater System And Method
20230038523 · 2023-02-09
Inventors
Cpc classification
Y02P40/50
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
F27D2013/007
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F28F5/02
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F28D7/1669
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F27D17/004
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
F28D2021/0045
MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
International classification
Abstract
Method of producing molten glass and system therefor, including providing a glass melting furnace configured to melt a glass sample, the glass sample including glass batch material including soda ash, or cullet or post-consumer cullet, or any combination of batch material, cullet and post-consumer cullet. The method includes introducing glass sample into a chamber of a rotary drum heat exchanger having at least one heat exchange tube; introducing the exhaust gas into the tube; causing a transfer of heat from the exhaust gas in the tube to the glass sample in the chamber to volatilize any organic impurities in the glass sample, heat the glass sample and evaporate water from the glass sample to dry it, the evaporated water forming water vapor in the chamber; contacting the dried sample with the water vapor; and discharging the dried sample from the rotary drum heat exchanger and introducing it into the furnace.
Claims
1. A method of producing molten glass, comprising: providing a glass melting furnace configured to melt, by burning fossil fuel, glass sample, the glass sample comprising glass batch material comprising soda ash, or cullet or post-consumer cullet, or any combination of batch material comprising soda ash, cullet and post-consumer cullet, said melting producing exhaust gas; introducing glass sample into a chamber of a rotary drum heat exchanger having at least one heat exchange tube; introducing said exhaust gas into said at least one heat exchange tube; causing a transfer of heat from said exhaust gas in said at least one heat exchange tube to said glass sample in said chamber to volatilize any organic impurities in said glass sample, heat said glass sample and evaporate water from said glass sample to dry said glass sample, said evaporated water forming water vapor in said chamber; and discharging the dried glass sample from said rotary drum heat exchanger and introducing it into said glass melting furnace.
2. The method of claim 1, further comprising combining said water vapor and any volatized organic impurities with said exhaust gas.
3. The method of claim 1, wherein said dried glass sample is contacted with said water vapor causing said soda ash in said glass sample to form sodium carbonate monohydrate.
4. The method of claim 3, wherein said transfer of heat from said exhaust gas to said glass sample is sufficient to dehydrate said sodium carbonate monohydrate.
5. The method of claim 3, wherein said transfer of heat raises the temperature of said glass sample to above 109° C.
6. The method of claim 1, wherein said glass sample comprises cullet, post-consumer cullet, or both, and wherein said method further comprising crushing said cullet and/or post-consumer cullet prior to its introduction into said chamber.
7. The method of claim 6, wherein said glass sample is crushed so that its largest dimension does not exceed 25 mm.
8. The method of claim 7, wherein there are a plurality of spaced heat exchange tubes in said rotary drum heat exchanger, and wherein the spacing between said plurality of tubes is less than 75 mm.
9. The method of claim 6, wherein said glass sample is crushed so that its largest dimension does not exceed 15 mm.
10. The method of claim 9, wherein there are a plurality of spaced heat exchange tubes in said rotary drum heat exchanger, and wherein the spacing between said plurality of tubes is less than 30 mm.
11. The method of claim 1, further comprising extracting a portion of gas in said chamber and mixing it with said exhaust gas.
12. The method of claim 1, further comprising combining said water vapor and any volatized organic impurities with the combustion space of said glass melting furnace.
13. The method of claim 1, wherein said glass batch material comprises cullet.
14. The method of claim 1, wherein said glass batch material comprises post-consumer recycle cullet.
15. The method of claim 1, further comprising a regenerative heat exchanger for preheating combustion aid and further comprising combining said water vapor and any volatized organic impurities with said exhaust gas before it enters the regenerative heat exchanger.
16. The method of claim 2, wherein at least a portion of the volatilized organic impurities are oxidized after mixing with said exhaust gas.
17. A system for melting glass, comprising: a glass melting furnace configured to melt, by burning fossil fuel, glass sample, the glass sample comprising glass batch material comprising soda ash, or cullet or post-consumer cullet, or any combination of batch material comprising soda ash, cullet and post-consumer cullet, said melting producing exhaust gas; a rotary drum heat exchanger having a chamber containing said glass sample and at least one heat exchange tube in said chamber having a gas outlet, said at least one heat exchange tube being in fluid communication with said exhaust gas so as to transfer heat from said exhaust gas in said at least one heat exchange tube to said glass sample in said chamber to volatilize any organic impurities in said glass sample, heat said glass sample and evaporate water from said glass sample to dry said glass sample, said evaporated water forming water vapor in said chamber, said chamber being in communication with said glass melting furnace for introduction of the dried glass sample into said glass melting furnace; and a controller in communication with (a) a temperature sensor configured to sense the temperature of said exhaust gas and with a valve positioned to regulate the amount of gas from said gas outlet of said at least one heat exchange tube that is combined with said exhaust gas prior to said exhaust gas being introduced into said at least one heat exchange tube, said controller configured to actuate said valve in response to said sensed temperature; and with (b) a flow volume sensor positioned to sense the flow volume of said exhaust gas prior to said exhaust gas being introduced into said at least one heat exchange tube, and with a driving force for driving the flow of said gas from said gas outlet of said at least one heat exchange tube, said controller configured to control the speed of said driving force in response to the sensed flow volume.
18. The system of claim 17, wherein said driving force comprises a fan with a variable speed motor, and wherein said controller controls the speed of said motor.
19. The system of claim 17, wherein said controller receives a pre-determined temperature set point and actuates said valve such that said sensed temperature reaches said pre-determined set point.
Description
BRIEF DESCRIPTION OF THE DRAWINGS
[0085] The above and other aspects of the present invention will now be described in further detail, by way of example only, with reference to the accompanying drawings, in which:
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DETAILED DESCRIPTION
[0097] Embodiments disclosed herein concern themselves with the manufacture of soda-lime glass, the most common glass type manufactured. At a glass factory, a variety of raw materials are mixed and then melted in the furnace. The principal ingredients in the manufacture of soda-lime glass are silica sand (SiO.sub.2), limestone (calcium carbonate, CaCO.sub.3), and soda ash (sodium carbonate, Na.sub.2CO.sub.3). In addition, a variety of minor ingredients can be added to promote special properties, including sodium sulfate (Na.sub.2SO.sub.4), carbon (C), gypsum (CaSO.sub.4), aluminum oxide (Al.sub.2O.sub.3), selenium (Se), cerium, cobalt oxide, and others.
[0098] Most glass manufacturing operations assure that batch includes about 3-4% water when introduced to the furnace. If water is not naturally occurring as a contaminant in the raw materials, glass manufacturing operations will add water to the batch. Water in the batch will reduce dusting during material handling and prevent segregation of the various batch constituents during handling and charging of the furnace.
[0099] Soda ash will typically comprise 15% to 18% of the total batch mass, with ranges as wide as 12% to 20%. Soda ash is water soluble, hygroscopic, and will form a variety of hydrated forms when contacted with water. When soda ash is mixed with the water some of the soda ash dissolves into the liquid water.
[0100] When sodium carbonate anhydrous (SCA) is contacted with water, various hydrates can be formed, specifically sodium carbonate monohydrate (SCM), Na.sub.2CO.sub.3.H.sub.2O, sodium carbonate heptahydrate (SCH), Na.sub.2CO.sub.3.7H.sub.2O, and sodium carbonate decahydrate (SCD), Na.sub.2CO.sub.3.10H.sub.2O. When initially contacted with water at room temperature, SCA will dissolve into the water to its saturation concentration of about 32 g/100 ml. This dissolution is exothermic and heats batch material, normally to temperature above 40° C.
[0101] When subsequently heated, as in a batch and cullet preheater, the water will be evaporated and leave behind the SCA solute as a residue. Embodiments disclosed herein take advantage of several features regarding soda ash/water physicochemical properties, including some or all of the following: [0102] 1) Soda ash readily dissolves into water. Saturation concentration is between 31 and 34.5 g/100 ml depending upon temperature. The dissolution process is exothermic. [0103] 2) Sodium carbonate is hygroscopic. When anhydrous sodium carbonate is exposed to air at temperature above 34.5° C. and with relative humidity greater than 72%, water vapor will be reacted with the sodium carbonate to form sodium carbonate monohydrate. This process is exothermic. [0104] 3) Sodium carbonate monohydrate (SCM) is a stable solid between temperatures of 34.5° C. and 109° C. [0105] 4) SCM thermally decomposes to sodium carbonate and water vapor at temperature above 109° C. The water does not go through a liquid phase. This process is endothermic. [0106] 5) SCM contains 85.48% Na.sub.2CO.sub.3 and 14.52% H.sub.2O by weight.
[0107] Taking batch with 18% soda ash as an example, stoichiometric conversion of all the soda ash to SCM would consume batch water of 3.1%. Thus, if this batch were made with 4% water, residual water after SCM conversion would be 0.9%.
[0108] As discovered by Slade, U.S. Pat. No. 3,545,988, dry batch which has been treated by exposure to atmospheres with high humidity will transform SCA into SCM as a coating on the silica sand grains. The resulting treated batch exhibits substantially less dust generation during handling processes and in the furnace than untreated batch.
[0109] As discovered by Delling, U.S. Pat. No. 5,759,507, light soda ash which has been hydrated to form sodium carbonate monohydrate will exhibit improved handling properties, such as increased density and elimination of fine particles that lead to dusting while handling. He further finds that such SCM maintains its improved handling properties even after the SCM had been dehydrated by heating to temperature above 109°C.
[0110] The present inventor has made the discovery that batch which has been treated as described above also exhibits more rapid melting in the glass furnace than untreated batch. It is postulated that the SCM coating on the silica sand grains improves the rate of fluxing action for melting of the silica. Soda ash melts at lower temperature than silica, and molten soda ash will serve as flux to melt the silica at lower temperature than pure silica will melt.
[0111] Where the glass sample comprises post-consumer recycled cullet, organic fumes and aerosols will be released upon heating the sample in the chamber. In some embodiments, these components may be oxidized such as by combining them with glass furnace exhaust gases that are at a temperature effective for oxidizing them. This combined stream may be used as the inlet gases 35 to the indirect heat exchanger.
[0112] A preferred embodiment is now described with reference to
[0113] With reference to
[0114] An embodiment of the rotating or rotatable drum chamber 19 is depicted alone in
[0115] Returning to
[0116] As infeed material is fed into the chamber and free falls at 18, the top level 45 of moving bed 20 rises until material spills over at 43 into the outlet cylinder 26. It travels along the bottom of outlet cylinder 26 until it drops off at 44 the end of the cylinder. In steady state, the amount of material exiting the device at 44 will equal the amount of material infeed 18 and the position or height of top level 45 will remain constant. To promote material flow along the axis of the device, the axis may be tilted to horizontal, for example at an angle of 4 degrees. Typically, this tilt may be between 1 and 5 degrees.
[0117] As infeed material at initial temperature (e.g., ambient temperature or 20° C., for example) is heated in the device, the heat input first provides for sensible heating of the wet material, up to temperature 100° C. After the wet material is heated to 100° C., additional heat input is used for the latent heat of water evaporation and water vapor is created inside drum chamber 19. As operation of the process continues, water vapor is continually formed inside of the drum chamber, building pressure inside. Discharge plenum 48 in communication with the drum chamber 19 serves to collect the discharged material mixture 44 and direct it to hopper 49 such as through chute 65. This plenum 48 may be sealed to discharge cylinder 26 and to hopper 49 to prevent air infiltration or leakage out of water vapor. The pressure generated by creation of water vapor causes water vapor 46 (or steam) to be vented from the port 47 of plenum 48.
[0118] After the water is evaporated from the moving bed material 20 in drum chamber 19, heat transferred from flowing hot gases 35 will provide sensible heat to the material 20 and the temperature of material 20 will increase. As the temperature of material 20 increases, impurities from the Post-Consumer Recycle cullet, if present, in the material will volatilize, creating organic fumes and aerosols. The organic fumes and aerosols will accumulate inside drum chamber 19 and be vented at 46 along with water vapor out of port 47. If material 20 is heated to greater than about 300° C., virtually all the organic impurities in the Post-Consumer Recycle cullet will be volatilized into organic fumes and aerosols and the heated material mixture 50 fed into the furnace will be essentially free of organic impurities.
[0119] Water vapor and any organic fumes and aerosols formed as described above occupy the drum chamber 19. Some small amounts of air may inadvertently infiltrate into chamber 19 but the resulting atmosphere in 19 will in general have high relative humidity. If the relative humidity is greater than 72% then water vapor will react with the SCA in the batch to form SCM. The reaction is exothermic and provides additional heat to the material mixture 20. Depending on the balance between amounts of SCA and water in the batch, most if not all the liquid water can be converted to SCM in the device and all the SCA can be converted to SCM.
[0120] As described earlier, this recrystallization of SCA to SCM has at least two significant benefits to the glass furnace process: [0121] 1. Subsequent handling of the batch will exhibit significantly reduced dust generation. [0122] 2. Subsequent melting of the batch will require shorter melting time and reduced melting energy.
[0123] As the material mixture travels farther downstream in the drum chamber 19, its temperature increases further. When the temperature exceeds 109° C. the SCM will begin to dehydrate, releasing the water molecule to form SCA and water vapor. This water vapor may be vented 46 out of the device through the discharge plenum port 47. The advantageous material properties from recrystallization to SCM will be maintained, even after the SCM is dehydrated.
[0124] The heated mixture material 50 in hopper 49 is fed into the furnace 52 (
[0125] In the embodiment of
[0126] Organic fumes and aerosols carried in water vapor 46 should not be discharged directly into the plant nor to atmosphere because they would result in air pollution, noxious odor and health hazard. Normally, these would be treated in a conventional air pollution control device, such as a scrubber, before being discharged to atmosphere. Instead, they may be vented from the indirect heat exchanger 14, conveyed such as inside a pipe 71, and introduced at 56 into the flue channel 55. Fan 62 may be used to provide the motive force to convey the water vapor with organic fumes and aerosols through the pipe or the like. In flue channel 55, they are blended with furnace exhaust gases 53 to form blended gases 57. The mass flow rate of water vapor with organic fumes and aerosols is typically less than 10% of the mass flow rate of exhaust gases 53 from the furnace. Exhaust gases 53 are typically at temperature 1350° C.-1450° C. Blended gases 57 are at high temperature, usually greater than about 1200° C. At this temperature and with oxygen content of 2%, the organic fumes and aerosols will be oxidized to form CO.sub.2 and water vapor. Care should be taken to prevent infiltration of tramp air into the injected gases 56. Too much tramp air would decrease the temperature of blended gases 57. If this temperature were to drop below 800° C., the oxidation of organic fumes and aerosols would be poor.
[0127] In the alternate embodiment of
[0128] Blended gases 57 travel through flue channel 55. A majority of the blended gases are drawn at 58 out of the flue channel and become the inlet gases 35 to the indirect heat exchanger 14. Heat exchanger 14 outlet gases 41 are introduced at 59 back into the flue channel 55. Fan 60 may be used to provide the motive force to draw gases 58 from the flue channel and pass them through the heat exchanger 14. Fan 60 may also be used to provide the motive force to introduce gases 59 back into the flue channel. In practice, nearly all (e.g., about 60 to about 100%, more preferably about 80 to about 95%) the furnace exhaust gases are drawn 58 out of the flue channel and directed to the heat exchanger. In this scenario, the maximum heat recovery from exhaust gases 53 is achieved. Furnace exhaust gases are finally discharged 61 to atmosphere.
[0129] For an oxyfuel fired glass furnace, temperature of discharge gases 61 must normally be above 320° C. These exhaust gases contain a large amount of water vapor (greater than 50%) as well as sodium sulfate (Na.sub.2SO.sub.4) solid particulate matter and SO.sub.3 gas as pollutants. At temperature below 320° C. the sodium sulfate (Na.sub.2SO.sub.4) solid particulate matter will react with SO.sub.3 gas and water vapor to form liquid sodium bisulfate (NaHSO.sub.4). This liquid substance will foul any downstream dust filtration equipment.
[0130] It is desired to preheat the batch and cullet mixture to as high a temperature as possible to achieve maximum benefit to the glass melting process. The present inventor has discovered that temperature greater than 520° C. can cause the material mixture to begin to fuse together. Preferably this is then set as a high limit on material preheat temperature.
[0131] Material mixture throughput in the heat exchanger 14 will be determined by the speed of screw auger 17. This may be controlled to maintain a supply of material 50 in hopper 49. In some embodiments, hopper 49 may be mounted on one or more load cells 68 or the like to measure the weight of its contents (
[0132] For an oxyfuel furnace, Qg is defined as the sensible heat contained in the exhaust gases 53 between their temperature at port 54 and 320° C. Equipment such as the flue channel, ducting, rotary heat exchanger and fan may be insulated to minimize heat losses, but there will always be parasitic heat losses, Qp from the equipment. The total heat available for preheating the batch and cullet mixture is Qa, where:
Qa=Qg−Qp
[0133] This available heat can be used for sensible heating of the batch and cullet mixture and latent and sensible heat for evaporation and heating of the water contained in the material. For typical oxyfuel fired glass furnaces, if all the available heat, Qa, were to be used for batch and cullet preheating, the batch and cullet mixture could be heated to a temperature between 450° C. and 500° C. Exact calculation depends on the detail design of the furnace, equipment, and flue channel. The conclusion can be made that usually there is not enough heat available to preheat the batch and cullet mixture up to the material high limit of 520° C. From the perspective of heat availability, the optimum design of a system will be obtained when the discharged exhaust gases 61 are at 320° C., that is when all the heat available in the exhaust gases has been transferred to the batch and cullet.
[0134] The temperature 70 of outlet 50 material mixture (
[0135] Since the mechanical design will be determined in advance by the designer and the material throughput will be determined by the furnace operation, only the gas 35 flow volume 73 and temperature 69 can be varied and controlled in real time. The heat transfer rate from gas to material will increase as both the temperature 69 and volume 73 are increased. As temperature 69 increases the temperature difference between gas and material increases, thus increasing the heat transfer rate. As flow 73 increases, the gas flow velocity inside tubes 23 increases. As velocity increases, the heat transfer rate from the flowing gases to the tube wall increases.
[0136] The temperature 69 will have a high limit as imposed by material sticking to the tube 23 wall. Therefore, the system operation will be optimum when temperature 69 is at this limit. Practical experience is that this limit will be between 600 and 650° C.
[0137] As flow 73 increases, the flow of gases 58 drawn from the flue also increase. Eventually flow of gases 58 will reach a critical point where they equal the flow of gases 57 in the flue. If flow 73 is increased further, gases 58 will be comprised of all of 57 plus some of the gases 59 being returned to the flue. These gases 59 will actually flow upward 81 in the flue, resulting in many deleterious effects, most importantly loss of furnace pressure control. At this critical point, the temperature of gases 58 will decrease and 69 will also decrease. The operator will learn from experience what the maximum flow 73 will be before this critical point is reached. Set point of 73 will then be a safe margin below the critical point.
[0138] A unique exhaust gas handling arrangement may be used and permits independent control of these two parameters to achieve controlled operation of the system, including: [0139] Valve 66 which allows a portion of outlet gas 41 flow from the heat exchange tube(s) in the drum chamber 19 to be blended with gases 58 withdrawn from the flue channel. It may be provided with an actuator (not shown) to allow the valve position to be adjusted and controlled automatically. The valve also may be controlled manually. The proportion of each blended gas stream will determine the inlet gas temperature Tgi 69. For example, 31300 Nm.sup.3/h of extracted gases 58 at temperature of 1200° C. would combine with 65900 Nm.sup.3/h of recycled gases 76 at temperature 400° C. to produce 97300 Nm.sup.3/h of mixture 35 at temperature of 650° C. inlet to the heat exchanger 14. [0140] A driving force such as fan 60 which may be provided with a motor 72 with variable speed drive, allowing the flow rate of the fan to be adjusted and controlled. [0141] Exhaust gas 35 flow rate 90 will be measured by flow measurement device 73, such as a pitot tube. [0142] Temperature of inlet gases may be measured directly such as by a thermocouple 69. [0143] Temperature of outlet gases 41 may be measured by thermocouple 80. [0144] Temperature of material outlet may be measured directly by thermocouple 70.
[0145] The control system may include two control loops, as shown in
If discharge gas temperature 80 drops too low, the heat exchanger 14 is transferring too much heat to the material. As described previously, exhaust gas temperature 61 must not be lower than 320° C. If this happens, the inlet gas temperature 69 set point will be decreased so lower material preheat temperatures 70 are achieved. The operator may increment inlet gas temperature 69 lower until the 320° C. temperature low limit of 61 is achieved. This may be carried out manually or automatically with the controller.
[0148] In the alternate embodiment shown in
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[0151] The maximum material throughput of rotary heat exchanger 14 is determined by the amount of heat transfer surface area afforded by the tubes 23. If the rotating drum 19 configurations of
[0152] An alternative embodiment is shown in
[0153] In the alternate embodiment of
[0154] From the flue channel 55, exhaust gases 78 flow into the regenerator 77 where they are cooled by heat exchange to the combustion air (not shown). Exhaust gases 79 leaving the regenerator are typically at temperature of 500° to 550° C. In this embodiment, the exhaust gases 58 are comprised of the regenerator outlet gases 79. These are drawn through the heat exchanger 14 by fan 60 and returned to the exhaust gas handling channel 59 where they comprise the exhaust gases discharged to atmosphere 61. In this configuration, the temperature 69 and flow rate 73 of gases inlet to the heat exchanger 14 will be determined by the operation of the furnace 52 and regenerator 77,
[0155] In this embodiment, the organic fumes and aerosols carried in water vapor 46 may be vented from the indirect heat exchanger 14, conveyed such as inside a pipe 71, and introduced at 56 into the flue channel 55. Fan 62 may be used to provide the motive force to convey the water vapor with organic fumes and aerosols through the pipe or the like. In flue channel 55, they are blended with furnace exhaust gases 53 to form blended gases 57. The mass flow rate of water vapor with organic fumes and aerosols is typically less than 10% the mass flow rate of exhaust gases 53 from the furnace. Exhaust gases 53 are typically at temperature 1350° C.-1450° C. At this temperature and with oxygen content of 2%, the organic fumes and aerosols will be oxidized to form CO.sub.2 and water vapor.
EXAMPLE
[0156] Typical system operation is described below.
[0157] A rotary heat exchanger with rotating chamber is fitted with 204 tubes. Tubes are 60 mm diameter and 3650 mm long. Distance between adjacent tubes is typically 30 mm. Such a device presents 142 square meters of heat transfer area associated with the tubes. The rotary heat exchanger is inclined at an angle of 3° to the horizontal to facilitate batch movement. The chamber rotates at 5 rotations per minute. The rotating chamber is enclosed by a fixed casing with exhaust gas inlet at one end and an exhaust gas outlet at the other end.
[0158] 4500 kg/h of wet batch (with 3% moisture) at temperature 20° C. and 4500 kg/h of wet post-consumer recycle (PCR) cullet (with 3% moisture) is blended to form a mixture and delivered to a storage hopper. The PCR cullet contains 1% organic impurities, equivalent to 45 kg/h. The mixture is fed out of the storage hopper and passed through a crusher where the maximum size piece is reduced to less than 15 mm.
[0159] The mixture is then fed into the chamber by a screw feeder.
[0160] The mixture is heated in the rotary heat exchanger and then fed into the glass melting furnace. The glass melting furnace is of oxy-fuel design, where 1190 Nm/h of 95% pure oxygen is blended with 540 Nm.sup.3/h of natural gas in the furnace combustion space and burned to generate heat for the melting process. 2435 Nm.sup.3/h of furnace gases at 1400° C. are exhausted from the furnace into the flue channel at temperature.
[0161] 270 kg/h of water vapor and 45 kg/h of volatilized organic matter are generated inside the rotating chamber and are vented out through a port. These comprise 390 Nm.sup.3/h of vented gases at 300° C. and are directed to the top of flue channel where they are mixed with the furnace exhaust gases. After mixing, the combined gas flow is 2825 Nm.sup.3/h at 1270° C. Because the furnace exhaust gases contain 2% oxygen, the combined temperature of 1270° C. is sufficient to oxidize 100% of the organic matter into CO.sub.2 and H.sub.2O. This prevents any discharge of organic material to atmosphere.
[0162] Further down the flue channel, 2825 Nm.sup.3/h of combined gases at 1270° C. are extracted and then blended with 3050 Nm.sup.3/h of outlet gases from the rotary heat exchanger to produce 5075 Nm.sup.3/h of blended inlet gases at 650° C. to the rotary heat exchanger. The 5075 Nm.sup.3/h of rotary heat exchanger outlet gases are drawn through the heat exchanger by a fan. The inlet duct to the heat exchanger is equipped with a flow measurement device. The fan speed is controlled via a PID control loop to maintain inlet gas flow volume at 5075 Nm.sup.3/h. The gases discharged from the fan are divided into two portions as controlled by valves in the ducting. The inlet duct to the heat exchanger is equipped with a temperature sensor, this temperature being used by a PID control loop driving the position of the aforementioned valves so the necessary quantity of fan outlet gases is directed to be combined with the 2825 Nm.sup.3/h of exhaust gases drawn from the flue to obtain blended temperature of 650° C., in this case the returned gases will be 3050 Nm.sup.3/h flow volume. The remaining portion of fan outlet gases, 2025 Nm.sup.3/h at 350° C., are returned to the flue channel downstream of the extraction point and are ultimately discharged to atmosphere.
[0163] Such a system will heat the batch and cullet up to a temperature of 425° C. and reduce the furnace natural gas and oxygen consumption by 22%. Specifically, the same furnace operating without the rotary heat exchanger would consume 692 Nm/h of natural gas and 1525 Nm/h of oxygen.