WO2005085143A1 - Procede de traitement des boues d'epuration par combustion en lit fluidise circulant - Google Patents
Procede de traitement des boues d'epuration par combustion en lit fluidise circulant Download PDFInfo
- Publication number
- WO2005085143A1 WO2005085143A1 PCT/CN2005/000058 CN2005000058W WO2005085143A1 WO 2005085143 A1 WO2005085143 A1 WO 2005085143A1 CN 2005000058 W CN2005000058 W CN 2005000058W WO 2005085143 A1 WO2005085143 A1 WO 2005085143A1
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- Prior art keywords
- sludge
- coal
- circulating fluidized
- combustion
- slurry
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Classifications
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G7/00—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
- F23G7/001—Incinerators or other apparatus for consuming industrial waste, e.g. chemicals for sludges or waste products from water treatment installations
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- 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
- F23G5/30—Incineration of waste; Incinerator constructions; Details, accessories or control therefor having a fluidised bed
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2201/00—Pretreatment
- F23G2201/70—Blending
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2203/00—Furnace arrangements
- F23G2203/50—Fluidised bed furnace
- F23G2203/501—Fluidised bed furnace with external recirculation of entrained bed material
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- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23G—CREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
- F23G2204/00—Supplementary heating arrangements
- F23G2204/10—Supplementary heating arrangements using auxiliary fuel
- F23G2204/101—Supplementary heating arrangements using auxiliary fuel solid fuel
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02E—REDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
- Y02E20/00—Combustion technologies with mitigation potential
- Y02E20/12—Heat utilisation in combustion or incineration of waste
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- Y—GENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
- Y02—TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
- Y02W—CLIMATE CHANGE MITIGATION TECHNOLOGIES RELATED TO WASTEWATER TREATMENT OR WASTE MANAGEMENT
- Y02W10/00—Technologies for wastewater treatment
- Y02W10/40—Valorisation of by-products of wastewater, sewage or sludge processing
Definitions
- the invention relates to a method for treating sewage and sludge, in particular to a method for treating sludge of a sewage treatment plant by a circulating fluidized combustion method, which is used for harmless treatment and comprehensive utilization of sludge produced by a municipal sewage treatment plant. . Background technique
- the present invention provides a method for treating sludge of a sewage treatment plant by a circulating fluidized combustion method, which can harmlessly treat and comprehensively utilize the sludge produced by a municipal sewage treatment plant, and is beneficial to environmental protection.
- the technical solution of the present invention to solve the technical problem and achieve the purpose of the present invention is to provide a method for treating sludge of a sewage treatment plant by using a circulating fluidized combustion method, including the following steps-a.
- a step of preparing sludge coal water slurry Pulverized coal and dispersant are added to the sludge of the sewage treatment plant, and the stabilizer is added after stirring to make sludge coal slurry;
- Sludge coal slurry clean combustion step that is, the produced sludge coal slurry is sent to a circulating fluidized bed boiler for clean combustion, wherein the furnace of the circulating fluidized bed boiler includes a fluidized medium including quartz sand and limestone .
- the weight parts of each component are: 10-20 parts of sludge, 50-60 parts of pulverized coal, Water is 20-25 parts, dispersant is 2-5 parts, and the diameter of pulverized coal particles is 50-150Mm.
- the sludge used in the sludge coal slurry preparation step is coal filter sludge
- the coal filter sludge is obtained by treating sewage from a sewage treatment plant It is formed by adsorption and filtration of coal powder and quick lime powder to filter out impurities in sewage.
- the sludge coal slurry clean combustion step of the method for treating sludge of a sewage treatment plant by the above-mentioned circulating fluidized combustion method further includes injecting the sludge coal slurry from the middle or top of the circulating fluidized bed boiler by using a screw pump. And the combustion temperature of the circulating fluidized bed boiler is preferably controlled at 850-950 ° C.
- the method further includes disposing unburned coal and garbage particles carried out by the hot flue gas at all stations.
- the combustion fluid outlet of the circulating fluidized bed boiler or the fly ash separator at the rear is separated and captured, and then sent back to the dense phase area of the combustion chamber for circulating combustion through a return device provided at the lower part of the separator.
- a method for treating sludge of a sewage treatment plant by using a circulating fluidized combustion method including the following steps-a.
- Sludge coal preparation step that is, adding granular sludge and dispersant in a ball mill
- the medium ball is milled into a mixed coal slurry with a particle size of 50-150 ⁇ m, and then a stabilizer is added to stir to make a sludge coal slurry;
- Sludge coal slurry clean combustion step that is, the produced sludge coal slurry is sent to a circulating fluidized bed boiler for clean combustion, wherein the furnace of the circulating fluidized bed boiler contains media materials including quartz sand and limestone .
- the sludge used in the sludge coal water slurry preparation step is coal filter sludge, which is obtained by transferring the coal filter sludge from the sewage treatment plant.
- the sewage is formed by adsorption and sedimentation filtration of coal powder and quicklime powder to filter out impurities in the sewage.
- the sludge coal slurry clean combustion step of the method for treating sludge of a sewage treatment plant by the above-mentioned circulating fluidized combustion method further includes injecting the sludge coal slurry from the middle or top of the circulating fluidized bed boiler by using a screw pump.
- the method further includes setting unburned coal and garbage particles carried out by the hot flue gas in the circulating stream
- the outlet of the combustion chamber of the fluidized bed boiler or the fly ash separator at the rear is separated and captured, and then returned to the dense phase area of the combustion chamber for circulating combustion through the return device provided at the lower part of the separator.
- the method according to the present invention prepares sludge from a sewage treatment plant into sludge coal paddles, and then transports them to a circulating fluidized bed boiler for combustion.
- the combustion efficiency is 98%.
- the combustible materials in the sludge coal slurry are converted into heat energy after being burned in the furnace, and other impurities are mixed in the fly ash and discharged during the combustion process.
- the flue gas of the circulating fluidized bed boiler contains burned fly ash, which is collected by electrostatic precipitator or bag dust collector5, and the dust removal rate can reach 99.9%, so that the smoke dust concentration in the flue gas is ⁇ 80mg / m 3 .
- S0 2 emission concentration in flue gas ⁇ 100 ⁇ ! ⁇ ! ⁇ , ⁇ emission concentration ⁇ . !!! ⁇ ! ⁇ ,
- the Lingerman blackness of the flue gas is ⁇ 1, which meets the national environmental protection requirements for the atmosphere, completely avoiding the environmental pollution caused by fly ash. . '
- Circulating fluidized bed boilers that burn sludge coal slurry can use hot water boilers, low pressure steam boilers or high and medium pressure steam boilers.
- the steam produced can be used for power generation, urban heating or cogeneration.
- the integration of sludge treatment, power generation or power supply can save a lot of energy and environmental protection costs.
- the fly ash produced in the combustion process contains silicate and CaS0 4 , which has comprehensive utilization value. Mainly can It has the following uses-a. It has gelling properties and is a substitute for slag and gypsum required for manufacturing cement. It lacks sufficient resources to supplement slag. It is a raw material for manufacturing cement, 50% each with cement clinker, and can be made into 325 # cement. , Fly ash with high CaS0 4 content can make special cement and expansion agent.
- Figure 1 is a process flow diagram of preparing sludge coal slurry using municipal sewage
- Figure 2 is a process flow diagram of preparing sludge coal slurry using granular coal and sludge from a sewage treatment plant
- the figure shows the process flow for preparing sludge coal firewood using pulverized coal and sewage treatment plant sludge.
- Figure is a process flow diagram of the above-mentioned sludge coal slurry using a circulating fluidized bed combustion to generate steam and hot water.
- the present invention provides a method for treating sludge of a sewage treatment plant by using a circulating fluidized combustion method, including the following steps: a. Sludge coal slurry preparation step, that is, adding pulverized coal to the sludge from the sewage treatment plant And dispersant, after stirring, the stabilizer is added to make sludge coal slurry; b. Sludge coal slurry clean combustion step, that is, the produced sludge coal slurry is sent to a circulating fluidized bed boiler for clean combustion In the furnace of the circulating fluidized bed boiler, there is a fluidized medium composed of quartz sand and limestone.
- the methods for preparing sludge coal can be divided into two types: the use of sewage to prepare sludge coal firewood and the use of sludge from sewage treatment plants to prepare sludge coal.
- pulverized coal, coal-based activated carbon, and quicklime powder are added to the filter tank as a filter material, and a multi-stage filter tank can be constructed according to the needs of the amount of sewage treatment.
- Pulverized coal and quicklime powder have strong adsorption and flocculation properties.
- the coal powder and coal absorbed in the filter are In the activated carbon and raw rock powder filter layer, the remaining part and a small amount of fine coal powder are glued. The form of the body exists in the filtered water, which flows into the sedimentation tank.
- Flocculation produces a sedimentation effect, allowing the remaining impurities in the sewage to settle together with the pulverized coal.
- the supernatant water from the upper part of the sedimentation tank flows into the treatment tank.
- the solid-liquid ratio of the coal slurry in the lower part of the sedimentation tank can reach 30% to 40%.
- the pulverized coal, coal-based activated carbon, and quicklime powder filter materials in the filter tank are saturated to form coal filter sludge after a period of use. At this time, the water content of the coal filter sludge can reach 30% -40%.
- the saturated coal filter mud in the filter tank is transported to the bottom-flow storage tank by a screw pump, and the bottom-flow storage tank is used as the secondary sedimentation tank.
- the supernatant water from the upper part of the underflow tank is discharged to the treatment tank, and the coal sludge from the lower part of the tank is transported by the screw pump to the pulping tank.
- the filter material in the filter tank contains a certain amount of calcium hydroxide, and it also plays a role in denitrifying, dephosphorizing, decoloring, and deodorizing the sewage while filtering. '
- the coal filter sludge sent to the pulping tank should be tested before each batch is added to check the water content, etc., and then a certain amount of pulverized coal is added in proportion so that the ratio of coal to water reaches 6.5-7: 3.5- About 3, add dispersant, start the stirrer on the top of the pulping tank, and stir.
- the stirrer rotates at 60 rpm, continuously stirs at normal temperature, then adds the stabilizer, and then shears and matures with a shear pump. , And then transported to the sludge coal paddle storage tank for storage.
- Dispersants and stabilizers are collectively called additives, and they can be named NDF coal water slurry additives developed by the Nanjing University Surface and Interface Chemical Engineering Technology Center.
- the water in the treatment pond is pumped to the original sewage treatment system of the sewage treatment plant, and then discharged or reused after meeting the treatment standards again.
- Each batch of sludge coal slurry must be subjected to a small test to determine the proportion or quantity of various ingredients.
- the sludge coal slurry in the sludge coal slurry storage tank is stirred for 1 to 2 hours per day as required to prevent hard sedimentation.
- the sludge in the sludge tank is pumped to the ball mill in proportion to the ball mill, and the municipal sewage in the sewage storage tank and the additives in the additive tank are sent to the ball mill in parts by weight, where: sludge 10-20 parts, 50-60 parts of pulverized coal, 20-25 parts of water, 2-5 parts of dispersant, mill the coal to a mixed coal slurry with a particle size of 50-150 ⁇ , and then use a screw pump Transfer to the pulping tank, stir and add stabilizer. Then, it is cut and matured by a shear pump to make sludge coal water slurry, which is then transported to a storage tank for storage.
- the dispersant and stabilizer are collectively referred to as additives.
- the NDF water coal additive developed by Nanjing University Surface and Interface Chemical Engineering Technology Center can be used.
- coal quality and sludge must be tested, and small tests must be performed to determine the proportion of coal, sludge, urban sewage, dispersant, and stabilizer.
- the sludge coal slurry in the slurry tank should be stirred daily. ⁇ 1-2 hours to prevent hard precipitation.
- the present invention has modified the circulating fluidized bed boiler 4. The process is shown in Figure 4.
- Traditional circulating fluidized bed boilers use dry pulverized coal as fuel.
- a screw conveyor is used at the bottom of the boiler to send the pulverized coal into the furnace.
- the circulating fluidized bed boiler 4 that burns coal water and coal is based on the traditional boiler design, and a sludge coal water slurry supply paddle is provided at the top or middle of the boiler. If the circulating fluidized bed tilting boiler 4 only uses sludge coal water slurry as fuel, the spiral coal feeding equipment will be eliminated. If the boiler uses coal and sludge coal water slurry, the spiral coal feeder system will be retained.
- the circulating fluidized bed boiler 4 that burns sludge coal-water slurry uses hot air flow ignition. After the diesel is atomized by the ignition gun, it is burned in the pre-combustion cylinder. The high-temperature flue gas generated enters the isostatic air chamber to be heated. The air in the air duct and the heated high-temperature air enter the fluidized bed through the gas distribution plate. When the bed material is heated above 450 ° C, a small amount of sludge, water and fuelwood is added to the circulating fluidized bed boiler, and the furnace temperature rises rapidly at this time. When the internal temperature of the circulating fluidized bed boiler 4 reaches 600 ° C, the slurry supply can be gradually increased.
- the furnace temperature quickly rises, and the sludge coal paddle has been burned normally. At this time, the oil supply is stopped, the pre-combustion chamber is shut off, and the ignition is completed. ; Increase the supply of sludge coal slurry, adjust the blower 3 and induced draft fan 7 to the air volume required for transport fi 1 .
- the circulating fluidized bed boiler 4 uses a high-level slurry supply.
- a high-level slurry supply For medium and large boilers with a power of 35 tons or more than 29MW, there are two or three paddle supply ports in the middle of the boiler to feed the sludge coal slurry into the furnace. Small and medium-sized boilers can also use the furnace top for slurry supply. This slurry supply method makes full use of the height of the boiler, accelerates the precipitation of water and volatile components in the sludge coal slurry, and is beneficial to combustion.
- the sludge coal slurry is sent from the slurry storage tank 1 to the circulating fluidized bed boiler 4 through the boiler slurry pump 2.
- the sludge coal slurry enters the circulating fluidized bed boiler through the fuel supply port and becomes drip-shaped.
- the drop-shaped sludge coal in the furnace is filled with the fluidized hot air flow in the furnace. Fine particles fall down in the furnace at a temperature of 850-950 ° F. In During the fall, the droplets are heated, decomposed, and start to burn before entering the fluidized bed composed of quartz sand and limestone. During the continued heating of the hot fluidized bed material, the precipitation of moisture and volatiles was quickly completed, and the fire was burned and the coke was burned.
- the fine particles of the granular sludge coal slurry further disintegrated are taken out of the dense phase zone by the hot flue gas, enter the suspension chamber and continue to burn.
- a fly ash separation and return device is provided at the exit or rear of the combustion chamber. The media material carried out by the hot flue gas and large unburned coal and garbage particles are separated and captured by the separator. The return device returns to the dense phase area of the combustion chamber for cyclic combustion, and its combustion efficiency reaches 98%.
- the particle size of the limestone (desulfurizing agent) added to the circulating fluidized bed boiler is selected from about 1 to 2 mm.
- the calcium / sulfur molar ratio is 1.5-2.5.
- the combustible materials in the sludge coal package are converted into heat energy after being burned in the furnace, and other impurities are mixed and discharged in the fly ash during the combustion process.
- the circulating fluidized bed boiler flue gas contains burned fly ash, which is collected by electrostatic precipitator or bag dust collector 5 with a dust removal rate of 99.9%, so that the concentration of smoke and dust in the flue gas is ⁇ 80mg / m 3 .
- the concentration of S0 2 emissions in the flue gas is ⁇ 100 mg / m 3
- the concentration of NOx emissions is 3 ⁇ 4 ⁇ 150 mg m 3
- the Lingerman blackness of the flue gas is ⁇ 1, which meets the national standards for atmospheric environmental protection.
- the smoke is evacuated from the chimney 6.
- the circulating fluidized bed boiler 4 can be a hot water boiler, a low pressure steam boiler or a high or medium pressure steam boiler.
- the produced steam can be used for power generation, urban heating or cogeneration.
- the integration of sludge treatment, power generation or power supply is formed, which saves a lot of energy and environmental protection costs.
- the fly ash collected by the dust collector 5 after the sludge coal slurry is combusted can be comprehensively utilized.
- the fly ash generated after the sludge coal slurry is cleanly burned by the circulating fluidized bed boiler 4 is collected by a dust collector, and is conveyed to a sealed ash bin 8 by a sealed conveying device. After reaching a certain number, it is transported away by a special transporter for fly ash. The environmental pollution caused by fly ash is completely avoided.
- fly ash contains silicate and CaS0 4 , which has comprehensive utilization value. It can be used for the following purposes:
- Fly ash is gelatinous. It is a substitute for slag and gypsum needed to make cement. It lacks sufficient slag resources. It is a raw material for making cement. It can be made into 325 # cement with 50% of cement clinker. CaS0 4 a high content of fly ash may produce special cement and bulking agent.
- Fly ash can be used to make fly ash pavement tiles, square tiles, grass planting tiles, roadside stones, etc.
- Fly ash can be used to make road and airport fly ash concrete.
- Application example 1 Take an urban sewage treatment plant as an example.
- the plant is located on the edge of the city.
- the sludge in the sewage mainly contains organic matter and phosphorus.
- the sewage is treated and comprehensively utilized by the circulating fluidized combustion method.
- the sludge water coal slurry was prepared by filtering sewage sludge and coal powder after the coal sewage and quicklime powder were adsorbed and settled in the municipal sewage, and the particle size of 50-150 mm was added to the filter tank.
- Coal powder and quicklime powder were used as filter materials.
- Flocculation produces a sedimentation effect, allowing the remaining impurities in the sewage to settle together with the pulverized coal.
- the supernatant water from the upper part of the sedimentation tank flows into the treatment tank.
- the moisture content of the coal filter sludge at the lower part of the sedimentation tank can reach 30% to 40%. It is transported to the bottom flow storage tank by the screw pump at the lower part of the sedimentation tank.
- the pulverized coal and quicklime filter materials in the filter tank are saturated after being used for a period of time to form coal sludge. At this time, the moisture content of the coal sludge can reach 30% -40%.
- the saturated coal filter sludge in the filter tank is transported to the underflow storage tank by a screw pump, and the underflow storage tank is used as a secondary sedimentation tank.
- the supernatant water from the upper part of the underflow tank is discharged into the treatment tank, and the coal sludge from the lower part of the tank is transported to the pulping tank by the screw pump.
- the filter material in the filter tank contains a certain amount of calcium hydroxide, and it also plays a role in denitrifying, dephosphorizing, decoloring, and deodorizing the sewage while filtering.
- the sludge coal paddles in the storage tank are stirred for 1 to 2 hours per day to prevent hard sedimentation.
- the circulating fluidized bed boiler with sludge coal combustion uses hot air flow ignition. After the diesel is atomized by the ignition gun, it is burned in the pre-combustion cylinder. The high-temperature flue gas generated enters the isobar chamber to heat the air in the air duct. The heated high-temperature air enters the fluidized bed through the gas distribution plate. When the bed material is heated above 450 ° C, a small amount of sludge coal is added to the circulating fluidized bed boiler, and the furnace temperature rises rapidly at this time. When the temperature in the circulating fluidized bed boiler reaches 600 ° C, the supply amount can be gradually increased. The furnace temperature quickly rises, and the sludge coal slurry has been burned normally. At this time, the oil supply is stopped and the pre-ignition is cut off. The ignition is completed in the chamber; the supply of sludge, coal and coal is increased, and the blower and induced draft fan are adjusted to the air volume required for operation.
- the sludge coal slurry enters the circulating fluidized bed boiler through the slurry supply port and becomes a drop shape.
- the drop sludge coal blade in the furnace is disturbed by the fluidized hot air flow in the furnace, and the drop sludge coal blade becomes smaller. Particles fall down in the furnace at a temperature of 850-950 ° F.
- the droplets are heated, decomposed, and start to burn before entering the fluidized bed of quartz sand and limestone.
- the precipitation of moisture, volatiles is quickly completed, and the fire burns and coke burns.
- the fine particles of the granular sludge coal slurry further disintegrated are taken out of the dense phase zone by the hot flue gas into the suspension chamber to continue burning.
- a fly ash separation and return device is provided at the exit or rear of the combustion chamber. The media material carried by the hot flue gas and large unburned coal and garbage particles are separated and captured by the separator. The return device returns to the dense phase area of the combustion chamber for cyclic combustion, and the combustion efficiency reaches 98%.
- the particle size of the limestone (desulfurizing agent) added to the circulating fluidized bed boiler is selected from about 1 to 2 mm.
- the molar ratio of calcium / sulfur is 1.5-2.5.
- the combustible substances in the sludge coal-water slurry are converted into heat energy after being burned in the furnace, and other impurities are mixed and discharged in the fly ash during the combustion process.
- the two boilers burn 21-25 tons of sludge coal slurry per hour, produce 150 tons of steam at a pressure of 3.9-3.5MPa per hour, and can generate electricity of about 20,000KW.
- the circulating fluidized bed boiler flue gas contains burned fly ash, which is collected by electrostatic precipitator or bag dust collector.
- the dust removal rate can reach: 99.9%, so that the concentration of smoke and dust in the flue gas is 50mg / m 3 .
- the emission concentration of SO 2 in the flue gas is 80 mg / m 3
- the emission concentration of NOx is 90 mg / m 3
- the Lingerman blackness of the flue gas is ⁇ 1.
- the plant Take the same urban sewage treatment plant as an example.
- the plant is located on the edge of the city.
- the sludge in the sewage mainly contains organic matter and phosphorus.
- the sludge in the sewage treatment process is treated and comprehensively used by the circulating fluidized combustion method.
- the slurry After adding a stabilizer, the slurry is cut and matured by a shear pump to make sludge coal slurry, which is transported by a screw pump to a storage tank for storage. And regularly stirring for 1 to 2 hours every day, the sludge coal slurry is pumped into a circulating fluidized bed sludge coal slurry steam boiler by a screw pump. Two boilers burn 21-25 tons of sludge coal slurry per hour, and produce per hour The pressure is 3.9—3.5MPa, 150 tons of steam, and can generate about 20,000KW.
- the flue gas after combustion is removed by an electrostatic precipitator. Exhaust after dust. The dust removal rate of the boiler, the emission concentration of harmful substances in the flue gas, and the blackness of the flue gas have all reached the national standard for environmental protection.
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- General Engineering & Computer Science (AREA)
- Water Supply & Treatment (AREA)
- Fluidized-Bed Combustion And Resonant Combustion (AREA)
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Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
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US10/592,045 US20080017086A1 (en) | 2004-03-10 | 2005-01-14 | Method for Treating Sludge of the Sewage Treatment Plants by Using Circulating Fluidized Bed Combustion |
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CN200410021357.4 | 2004-03-10 | ||
CNA2004100213574A CN1559939A (zh) | 2004-03-10 | 2004-03-10 | 循环流化燃烧法处理污水处理厂污泥的方法 |
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WO2005085143A1 true WO2005085143A1 (fr) | 2005-09-15 |
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CN1559939A (zh) | 2005-01-05 |
US20080017086A1 (en) | 2008-01-24 |
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