WO2014150695A1 - Utilisation de chaleur résiduelle de four pour réduire la teneur en humidité de biosolides de classe a et d'autres combustibles de biomasse - Google Patents

Utilisation de chaleur résiduelle de four pour réduire la teneur en humidité de biosolides de classe a et d'autres combustibles de biomasse Download PDF

Info

Publication number
WO2014150695A1
WO2014150695A1 PCT/US2014/024007 US2014024007W WO2014150695A1 WO 2014150695 A1 WO2014150695 A1 WO 2014150695A1 US 2014024007 W US2014024007 W US 2014024007W WO 2014150695 A1 WO2014150695 A1 WO 2014150695A1
Authority
WO
WIPO (PCT)
Prior art keywords
biosolids
fuel
coal
coke
dried
Prior art date
Application number
PCT/US2014/024007
Other languages
English (en)
Inventor
Kent D. MARTIN
Jeremy LUCKIN
Nicholas H. PIVAR
Brian M. WHITTAKER
Original Assignee
Lehigh Cement Company Llc
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by Lehigh Cement Company Llc filed Critical Lehigh Cement Company Llc
Publication of WO2014150695A1 publication Critical patent/WO2014150695A1/fr

Links

Classifications

    • C—CHEMISTRY; METALLURGY
    • C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B7/00—Hydraulic cements
    • C04B7/36—Manufacture of hydraulic cements in general
    • C04B7/43—Heat treatment, e.g. precalcining, burning, melting; Cooling
    • C04B7/44—Burning; Melting
    • C04B7/4407—Treatment or selection of the fuel therefor, e.g. use of hazardous waste as secondary fuel ; Use of particular energy sources, e.g. waste hot gases from other processes
    • C—CHEMISTRY; METALLURGY
    • C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B7/00—Hydraulic cements
    • C04B7/36—Manufacture of hydraulic cements in general
    • C04B7/43—Heat treatment, e.g. precalcining, burning, melting; Cooling
    • C04B7/47—Cooling ; Waste heat management
    • C04B7/475—Cooling ; Waste heat management using the waste heat, e.g. of the cooled clinker, in an other way than by simple heat exchange in the cement production line, e.g. for generating steam
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L5/00—Solid fuels
    • C10L5/02—Solid fuels such as briquettes consisting mainly of carbonaceous materials of mineral or non-mineral origin
    • C10L5/04—Raw material of mineral origin to be used; Pretreatment thereof
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L5/00—Solid fuels
    • C10L5/02—Solid fuels such as briquettes consisting mainly of carbonaceous materials of mineral or non-mineral origin
    • C10L5/06—Methods of shaping, e.g. pelletizing or briquetting
    • C10L5/10—Methods of shaping, e.g. pelletizing or briquetting with the aid of binders, e.g. pretreated binders
    • C—CHEMISTRY; METALLURGY
    • C04—CEMENTS; CONCRETE; ARTIFICIAL STONE; CERAMICS; REFRACTORIES
    • C04B—LIME, MAGNESIA; SLAG; CEMENTS; COMPOSITIONS THEREOF, e.g. MORTARS, CONCRETE OR LIKE BUILDING MATERIALS; ARTIFICIAL STONE; CERAMICS; REFRACTORIES; TREATMENT OF NATURAL STONE
    • C04B2290/00—Organisational aspects of production methods, equipment or plants
    • C04B2290/20—Integrated combined plants or devices, e.g. combined foundry and concrete plant
    • C—CHEMISTRY; METALLURGY
    • C10—PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10L—FUELS NOT OTHERWISE PROVIDED FOR; NATURAL GAS; SYNTHETIC NATURAL GAS OBTAINED BY PROCESSES NOT COVERED BY SUBCLASSES C10G, C10K; LIQUEFIED PETROLEUM GAS; ADDING MATERIALS TO FUELS OR FIRES TO REDUCE SMOKE OR UNDESIRABLE DEPOSITS OR TO FACILITATE SOOT REMOVAL; FIRELIGHTERS
    • C10L5/00—Solid fuels
    • C10L5/40—Solid fuels essentially based on materials of non-mineral origin
    • C10L5/44—Solid fuels essentially based on materials of non-mineral origin on vegetable substances
    • C10L5/442—Wood or forestry waste
    • 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
    • Y02E50/00—Technologies for the production of fuel of non-fossil origin
    • Y02E50/30—Fuel from waste, e.g. synthetic alcohol or diesel
    • 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
    • Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P20/00—Technologies relating to chemical industry
    • Y02P20/10—Process efficiency
    • Y02P20/129—Energy recovery, e.g. by cogeneration, H2recovery or pressure recovery turbines
    • 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
    • Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00—Technologies relating to the processing of minerals
    • Y02P40/10—Production of cement, e.g. improving or optimising the production methods; Cement grinding
    • Y02P40/121—Energy efficiency measures, e.g. improving or optimising the production methods
    • 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
    • Y02P—CLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P40/00—Technologies relating to the processing of minerals
    • Y02P40/10—Production of cement, e.g. improving or optimising the production methods; Cement grinding
    • Y02P40/125—Fuels from renewable energy sources, e.g. waste or biomass

Definitions

  • the present invention pertains to using bio-solid materials as a fuel or fuel additive in a cement-making process.
  • the present invention pertains to drying biosolids containing Class A biosolids and/or other dried biomass fuels in a cement- making process and cement-making apparatus.
  • Cement-making processes are based upon the processing of limestone (CaC0 3 ) by heating to achieve a cement clinker that contains calcium oxide (CaO) chemically bound with other materials such as alumina, silica, and iron.
  • a Portland Cement manufacturing process the main raw ingredient, limestone, is prepared with or without smaller amounts of materials containing alumina, silica, and iron and ground to produce what is called a raw meal.
  • the meal is then conducted to a pyro-processing area, which may include preheaters and calciners to condition the raw meal for introduction into a rotary kiln where the intermediate product clinker is produced.
  • the main kiln and the preheaters and calciners of a clinker production system are conventionally heated with burners using fossil fuels.
  • Coal, coke, oil, or gas are generally mixed with preheated combustion air and ignited to provide the heat necessary to decarbonate and melt the raw meal to produce clinker.
  • the hot clinker is introduced into a clinker cooler, wherein large amounts of air are blown through the hot clinker to cool it. After sufficient cooling the clinker can be ground into a final product. In the grinding operation of the cooled clinker a small amount of gypsum may be added to produce the finished Portland Cement.
  • biosolid materials such as sewage sludge and other biomass fuels.
  • the qualities of raw biosolid materials available for use as alternate fuel sources vary considerably. Biomass materials have significant moisture content and are often processed to reduce moisture content prior to delivery to a cement manufacturing plant. Typical biosolid materials nevertheless require further processing of the material at the cement manufacturing site before they are suitable for use as a fuel in cement- making.
  • precautions must be taken in handling, storage, and treatment of the material to control odors and to eliminate the explosion hazards associated with the volatile materials that these materials produce, evolve, or emit.
  • U.S. Patent Pub. No. US 2005/0274293 Al describes a method and apparatus for drying wet biosolids using waste heat from clinker cooler or kiln exhaust gases in a cement-making process.
  • the wet biosolids are fed by a closed system into a drying operation to reduce their moisture content to about 10% by weight.
  • the high levels of volatile organic materials evolved from the wet biosolids treated according to the system described cannot be vented to the atmosphere, but are recovered in a closed system and fed to the combustion process of the cement-making system.
  • U.S. Patent Pub. No. US 2010/0032385 Al describes a cement-making apparatus that used calciner exhaust gases to dry high water-content organic waste such as sewage sludge.
  • Organic waste containing 40% or more by weight is contacted with combustion gas in a flash grinder.
  • the combustion gas exhausted from the grinder has a low oxygen content but a high concentration of volatile, combustible, and odoriferous compounds and must be returned to the calciner exhaust for deodorization treatment.
  • European Patent Applications No. 0 496 290 A2 and No. 0 664 330 Al describe power plants wherein wet sewage sludge is dried to less than 10% water content by indirect heating with exhaust steam from the power plant turbines or by direct heating with hot flue gas from the power plant furnace. The vapors and gases evolved during the drying of the sludge are recovered and fed into the furnace for combustion. The dried sludge may be mixed with coal, crushed, and further dried for use as fuel in the power plant.
  • Chinese Patent Application No. 101177331 A describes a method and device of treating sludge containing 70 to 95 % water using exhaust gases from a cement rotary kiln to treat and dry the sludge to 2 to 10% water content.
  • the exhaust gas produced in the drying process must be returned to the kiln exhaust gas system for further treatment before it can be vented to the atmosphere.
  • Class A biosolids are a manufactured product, produced by biological digestion of, for example, municipal sewage sludge.
  • the full requirements for sewage sludge to be classified as Class A biosolids are set forth in the U.S. Environmental Protection Agency regulations at 40 C.F.R. Part 503.
  • steps such as composting, pasteurization, drying, heat treatment, alkaline treatment, and the like, to a level that does not pose a risk of infectious disease transmission through casual contact or ingestion.
  • Class A materials are approved for application to land. Similar materials are currently available at home improvement centers as organic fertilizers under the names of Milorganite, Granulite, Vital Cycle, etc.
  • Class A biosolids are used as an alternate fuel in cement kiln systems to substitute for traditional fossil fuels such as coal, coke, natural gas, and oil.
  • the processing of, for example, sewage sludge to Class A biosolids can occur by various methods, including mechanical, chemical, biological, and thermal treatments.
  • Class A biosolids can have varying amounts of moisture content.
  • other biomass fuels are processed in various methods for preparation as a fuel, and not all methods include drying. Other treated biomass fuels will pose the same problem as Class A biosolids having varying amounts of moisture.
  • Class A biosolids and other biomass fuels will lower the potential calorific value (heating value) of these alternate fuels. If the moisture level is too high, Class A biosolids or other biomass fuels will not have a recuperative calorific (heating) value, because all of the heat available from burning these materials will be used to heat and evaporate the moisture contained within them Moreover, the moisture level where a material becomes heat neutral or negative will vary depending on the material composition, particularly its carbon and hydrogen content. Thus a need persists for a method and apparatus that can treat alternate fuel materials containing Class A biosolids or other biomass fuels for use in a cement-making process such that they contribute a positive heating value to the process while minimizing the environmental and safety hazards associated with the use of these biomass materials.
  • the present invention pertains to methods and apparatus for making a fuel or fuel additive for use in a cement-making process.
  • the raw materials for making the fuel or fuel additive are coal and/or coke and a dried biosolid material containing Class A biosolids and/or other biomass fuel.
  • the raw materials for the fuel or fuel additive are mixed, ground, and dried together, the drying being effected by contacting the mixed materials with hot exhaust gases exiting the clinker cooler or kiln of the cement-making process.
  • the fuel or fuel additive can either be stored for future use or incorporated directly into the combustion processes of the cement-making operation.
  • the present invention is a method of making a fuel or fuel additive, for use in a cement-making process, from raw coal and/or coke and dried biosolids containing Class A biosolids and/or other biomass fuel, by mixing the raw coal or coke and dried biosolids; grinding the coal or coke and the dried biosolids together to reduce the particle size and to increase the uniformity of the particle size of the mixture; drying the mixture with kiln or clinker cooler exhaust gases from the cement-making process to form the fuel or fuel additive; and venting the kiln or clinker cooler gases from the drying step to the atmosphere.
  • the present invention is a method for incorporating dried biosolids comprising Class A biosolids and/or other biomass materials for use as a fuel or fuel additive in a cement-making process, by collecting exhaust gases carrying waste heat from a kiln or a clinker cooler used in the cement-making process; transferring heat from the exhaust gases to the dried biosolids to reduce the total contained moisture content of the biosolids to 10% by weight or less; and burning the dried biosolids alone or with a fuel selected from the group consisting of coal, coke, and mixtures thereof in a burner used in the cement-making process.
  • the present invention is an apparatus for making a fuel or fuel additive for use in a cement-making process from raw coal and/or coke and dried biosolids containing Class A biosolids and/or other biomass fuel, including a cement-making apparatus comprising a main cement kiln and a clinker cooler, each producing exhaust gases carrying waste heat; a mixing apparatus for forming a mixture of the coal or coke and the dried biosolids; a drying and grinding apparatus for the mixture of coal or coke and dried biosolids, wherein the apparatus effects the transfer of the waste heat from the kiln or clinker cooler exhaust gases to the mixture of coal or coke and dried biosolids, forming the fuel or fuel additive; and a vent to exhaust the drying gases from the drying and grinding apparatus to the atmosphere after the mixture of coal or coke and dried biosolids is dried.
  • a cement-making apparatus comprising a main cement kiln and a clinker cooler, each producing exhaust gases carrying waste heat
  • a mixing apparatus for forming a mixture of the coal
  • the present invention is a cement-making apparatus, including a main cement kiln and a clinker cooler, each producing exhaust gases carrying waste heat; a means to form a fuel mixture containing coal and/or coke and dried biosolids comprising Class A biosolids and/or other biomass fuel; a means to grind the fuel mixture and to dry the fuel mixture by contact with the kiln and/or clinker cooler exhaust gases; and a means to vent the exhaust gases after to the atmosphere after contact with and drying of the fuel mixture.
  • Class A biosolids and other biomass fuels By introducing the Class A biosolids and other biomass fuels into the coal/coke drying and grinding system, waste heat from the kiln system can be used to dry these materials and create a higher calorific (heating) value fuel.
  • Class A biosolids and other biomass fuels can either be introduced with the raw coal/coke or by a separate introduction point to the coal/coke drying and grinding system . In addition to drying these materials, by processing Class A biosolids and other biomass fuels in the coal/coke drying and grinding system, these materials will be reduced in size to further improve their combustion.
  • FIG. 1 is a representation of a conventional cement making process.
  • FIG. 2 is a flow diagram of a process and apparatus according to an embodiment of the present invention.
  • FIG. 3 is a flow diagram of a process and apparatus according to another embodiment of the present invention .
  • FIG. 4 is a partial schematic of a process and apparatus according to yet another embodiment of the present invention.
  • This invention involves drying Class A biosolids and other treated biomass fuels containing moistu re using a coal/coke drying and grinding system, to increase their calorific (heating) value for use in the combustion operations of a cement-making system.
  • Waste heat from a kiln system can be obtained either from the combustion exhaust gases produced by combustion in the kiln system or cooling air used to cool the clinker exiting the kiln . These gases, which are normally cooled prior to being vented to atmosphere, are contacted with the Class A biosolids and other treated biomass fuels containing moisture in the coal/coke drying and grinding operation .
  • size reduction and equalization with the co-ground coal and/or coke will also occu r, improving the combustion characteristics of the Class A biosolids and other biomass fuels contained in the dried mixture.
  • Biosolids are the nutrient-rich organic materials resulting from the treatment of domestic sewage in a treatment facility. Biosolids differ from sewage sludge, in that biosolids are treated sewage sludge. Biosolids are carefu lly treated and monitored and must be used in accordance with regulatory requirements. Class A biosolids contain no detectible levels of pathogens. Class A biosolids that meet strict vector attraction reduction requ irements and low levels metals contents, only have to apply for permits to ensu re that these very tough standards have been met. In general, exceptional quality (Class A) biosolids used in small quantities by general public have no buffer requirements, crop type, crop harvesting or site access restrictions. When used in bulk, Class A biosolids are subject to buffer requirements, but not to crop harvesting restrictions. Representative standards for EPA Class A biosolids are shown in the following Table 1, alongside a selected state standard and a typical commercially-available material :
  • biomass fuels for use in the invention include but are not limited to seeds (corn, wheat, soy bean, etc.), paper sludge, saw dust, wood byproducts, or any other biomass material where reduction in moisture content and/or size will increase the materials' calorific value. These other biomass fuels are pretreated to a moisture content of about 10% by weight or less, consistent with the moisture level required for Class A biosolid status.
  • Paper pulp biosolids generally consist of organic based byproducts from paper manufacturing.
  • Paper manufacturing uses conventional sources of cellulose such as wood and flax.
  • Paper manufacturing also uses secondary sources of cellulose such as waste paper and waste cardboard.
  • the manufacturing process requires the grinding, particle size classification, heating, and blending of conventional and secondary sources of cellulose. These processes generate by-products that have various concentrations of water and organic components.
  • Industrial sludges for use in the present invention contain organic byproducts with liquid or solid hydro-carbon components.
  • Petroleum tanker sludge, oil soaked clay, oil soaked filter media, sediment from coal washing operations and wet flexi coke are examples of suitable industrial sludges.
  • Food processing sludges are generated from many process operations. These materials generally consist of grain and vegetable based products that are being ground, mixed and dosed to produce various food products. In other processes diatomaceous earth filter media often becomes saturated with the organic residues form mixing, batching, cooking and pasteurizing processes. These saturated filter media materials are suitable bio-solid sludges for the processes of the present invention.
  • Agricultural waste sludges consist of by-products from harvesting and processing crops. Materials such as stalks, seeds, shells, pits, skins, rinds, twigs, leaves, and bark with various concentrations of moisture are suitable for the process of the present invention.
  • the caloric heating value of these biomass materials can be increased by going through the inventive drying and grinding process.
  • a conventional cement manufacturing process uses large volumes of raw materials such as limestone and coal to produce Portland Cement.
  • the process consists of three main areas, raw meal preparation, pyro-processing, and finished grinding.
  • Limestone (CaC0 3 ) is generally the main raw ingredient. Smaller amounts of materials containing alumina, silica and iron are proportioned and ground with limestone to produce a raw meal.
  • a precisely controlled mixture of raw meal is then fed to the pyro-processing area.
  • the pyro-processing area burns large amounts of conventional fuel such as coal, oil and gas to generate the temperatures required to calcine the limestone and allow the new cement components to form.
  • An intermediate product called clinker is produced in the pyro-processing area. Clinker is cooled from high pyro-processing temperatures to ambient temperature.
  • a finished grinding process which incorporates a small percentage of gypsum into the clinker results in a Portland Cement product.
  • the apparatus 100 includes a preheating section 110 which can include a series of preheater stages 111, 112, 113, 114, and 115, which are interconnected with recovery conduits, e.g. 116, wherein the raw meal represented by arrow 117 introduced by a conduit 118 is gradually preheated for introduction into the main kiln 119 via a conduit 120.
  • a calciner 121 Downstream of the preheater section the process apparatus includes a calciner 121, which is fired with a burner 122 to begin the conversion of the limestone to clinker.
  • the calciner portion of the process can include a loop system 123 which includes a conduit 124 to introduce additional fuel into the loop system 123 whereby the fines from the calciner are recycled and eventually introduced into the main kiln 119.
  • Gases and fine particles exiting the preheater section 110 are sent to a cooling tower 125 for cooling of the gases and exhausting via a blower 126. Dust is removed in a dust collector 127.
  • Main kiln 119 includes a main burner 128 which is fired using a fuel such as coal or coke together with an oxygen-containing fluid such as air.
  • the preheated or pre-calcined meal enters the kiln at a first or entry end 129.
  • the clinker exits the kiln 119 and is deposited into a clinker cooler 131 where the clinker is cooled to a temperature of about 200° F.
  • the clinker represented by arrow 132 is conducted via a conduit for other delivery device 133 to the grinding operation.
  • the clinker cooler 131 includes a dust recovery system 134 so that dust can be recycled to the pyro-processing portion of the cement-making process.
  • a flow diagram 200 of a method and apparatus according to one embodiment of the present invention is shown incorporated into a cement-making process.
  • raw coal and/or coke 201 are mixed with dried biosolids containing Class A biosolids and/or other biomass fuels 202 upstream of, and are then fed into, a coal/coke drying and grinding system 203.
  • Waste heat 204 in the form of exhaust gases collected from the kiln and/or clinker cooler elements of the kiln system 205 are fed to the drying and grinding system 203, where they contact the mixture of coal and/or coke and dried biosolids to effect further drying thereof.
  • the finished fuel or fuel additive containing the mixed, ground, and dried coal and/or coke and dried biosolids 206 are fed into the kiln system 205 to be used as fuel in the cement-making process.
  • the exhaust gases 207 from the drying and grinding system 203 are vented to the atmosphere.
  • a flow diagram 300 of a method and apparatus according to another embodiment of the present invention is shown incorporated into a cement- making process.
  • raw coal and/or coke 301 and dried biosolids containing Class A biosolids and/or other biomass fuels 302 are separately fed directly into a coal/coke drying and grinding system 303.
  • Waste heat 304 in the form of exhaust gases collected from the kiln and/or clinker cooler elements of the kiln system 305 are fed to the drying and grinding system 303, where they contact the mixture of coal and/or coke and dried biosolids to effect further drying thereof.
  • the finished fuel or fuel additive containing the mixed, ground, and dried coal and/or coke and dried biosolids 306 are fed into the kiln system 305 to be used as fuel in the cement-making process.
  • the exhaust gases 307 from the drying and grinding system 303 are vented to the atmosphere.
  • FIG. 4 a schematic 400 of a cement-making method and apparatus according to another embodiment of the present invention is shown.
  • Dried biosolids comprising Class A biosolids and/or other biomass fuels are pneumatically conveyed from a storage silo 401 to a cyclone separator to separate the dried biosolids from the conveying air.
  • the separated biosolids are mixed with raw coal from a coal storage system 403 to be fed to a coal mill 404.
  • the conveying air from the biosolids cyclone separator is fed to a baghouse 405 to remove biosolid fines; the conveying air is vented from the baghouse 405 to the atmosphere, and the solids recovered in the baghouse 404 are added to the unground mixed coal and dried biosolids fed to the coal mill 404.
  • the mixed coal and dried biosolids are ground and dried.
  • the drying of the coal and biosolid mixture is effected by contacting the mixture in the coal mill 404 with hot exhaust gases collected from the preheater section 406 of a kiln and clinker cooler system 407 and blown by a preheater fan 408 into the coal mill 404.
  • the dried and ground coal and biosolid mixture now suitable as a fuel or fuel additive for a cement-making process, is collected from the coal mill dust collector 411 and conveyed to storage bins 409, from which the fuel or fuel additive is fed as needed to the main burner 410 or the calciner 414 of the kiln and clinker cooler system 407.
  • the ground coal and biosolids are added to the the coal storage bins 409.
  • the exhaust gases are conveyed from the coal mill bag house 411 by a coal mill fan 412 to the main stack 413 for venting directly to the atmosphere.
  • the method and apparatus of the present invention may incorporate a biosolids unloading, storage, and metering system where the Class A biosolids and/or other biomass materials are unloaded, stored, and distributed to the drying and grinding system.
  • the storage unit is typically an insulated storage silo, loaded via a pneumatic or mechanical system from transport vehicles carrying the biosolids materials.
  • the silo may be provided with one or more of a pressure relief, odor control, C0 2 inerting, or dry air system.
  • the stored material may be metered by volumetric or gravimetric means to the drying and grinding system.
  • the method and apparatus of the present invention will include a system capable of grinding the coal/coke and biomass materials together and at the same time drying the materials being ground by contact with the kiln or clinker cooler exhaust gases.
  • a suitable apparatus for this operation is a vertical roller mill for crushing and grinding coal or coke. Heated gases, which may be as high as 400 °F (approx. 200 °C) from the clinker cooler and as high as 750 °F (approx. 400 °C) from the kiln, are conducted to coal grinder and directly contact the mixed and ground coal/coke and biosolid materials, which are then dried to form the finished fuel or fuel additive.
  • the finished fuel is conveyed pneumatically to storage bins for distribution as needed into the kiln combustion processes.
  • the dry bio-solids can be stored and used as necessary in the overall process, for example, directly in the main burner of the kiln, or in the calciner burner.
  • the method and apparatus of the present invention do not require further treatment of the dryer exhaust gases to remove the moisture and volatile organic compounds evolved from the biomass materials.
  • the method and apparatus of the present invention require no further operations, such as a condenser separator, to treat the dryer exhaust gases before it can be vented to the atmosphere.
  • the coal grinder/dryer will be operated to obtain less than approximately 2%, preferably 1%, and even more preferably 0.5% moisture content by weight in the dried fuel mixture comprising coal or coke and the dried biosolids materials when it leaves the grinding and drying system.
  • Monitoring the material and vapor discharge temperatures and varying the temperature of the incoming heat to the grinder/dryer makes it possible to control the moisture content of the fuel materials leaving the system.
  • the dried fuel mixture containing biosolids materials is pneumatically conveyed to a storage device or silo. Depending upon the temperature of the dried material, it may be necessary to either cool the dried fuel in a separate heat exchange device or by using cool conveying gas to transport the dried fuel to the storage silo.
  • Any storage device must be designed in accordance with all applicable local, state and federal codes and regulations to insure safe handling of such material. It is believed that procedures and methods that are used for the storage and handling of pulverized coal will enable a user to comply with such laws and regulations for storage and handling of dried biosolid materials.
  • the storage system will have the ability to withdraw and dose the dried fuel material as needed, alternate transport methods may be practical in some cement processes.
  • Some cement plants have existing pneumatic transport systems for conveying a primary fuel such as pulverized coal. With such a system it is possible to deposit a controlled flow rate of dried fuel materials directly into an existing pneumatic transport line. In this aspect, the dosing systems would discharge through a rotary air lock directly into the pneumatic transport system.
  • the dried fuel materials may be transported to the combustion (burning) zone of a kiln in several ways. If the fuel is conveyed to the main burning zone of kiln by an independent pneumatic conveying line, a separate burner pipe can be used to introduce the dried fuel into the rotary kiln.
  • the nozzle or discharge end can be placed at any location proximate the discharge end or nozzle end of the main burner.
  • the dried fuel can be conveyed to the burning (combustion) zone of the kiln via an independent pneumatic conveying line that terminates in a conduit inside of the burner.
  • the burner can be a multi-port or a concentric tube burner, such burners being well known in the art.
  • the particle size of fuels burned in the main combustion zone of the cement kiln is of critical importance. If too many large particles of fuel enter this portion of the kiln there is a possibility that some of them may fall into the reaction zone of the kiln and adversely affect the quality of the clinker produced. For this reason the degree of fineness of the dried biosolids must be monitored closely.
  • the particle size of the dried biosolids is to be reduced and harmonized with the coal or coke with which it is mixed to optimize the combustion characteristics of the resulting fuel mixtures.
  • the finished fuel mixture obtained according to the process of the invention will have a particle size distribution wherein no particles exceed 1 mm in size, less than 20% are retained at 90 pm and less than 2% are retained at 200 pm.
  • particle size is not as critical for dried bio-solids introduced into the calciner and the loop duct combustion zone of the cement plant. Larger particle size dried biosolids can be accommodated in these areas because of the longer retention time in the combustion zone and the fluidizing effect of high gas flows. Furthermore, any particles or fuel that become mixed with the raw meal (feed) will have ample time to oxidize before they are added to the more critical reaction zone of the kiln.
  • the combustion zone of a cement kiln is one of the hottest industrial processes. Gas temperatures in the main combustion zone can exceed 3500 °F (approx. 1930 °C). Additionally, these gases remain above 1800 °F (approx. 980 °C) for as long as 5 seconds as they move away from the combustion zone. The combination of preheated high oxygen content air, high combustion temperatures and long residence time above 1800 °F (approx. 980 °C) insures complete combustion of all organic compounds.
  • the calciner loop duct combustion zone consists of the main calciner combustion chamber and the loop duct or riser duct. Gas temperatures in the calciner combustion chamber can reach 1650 °F (approx. 900 °C). These gases can remain above 1600 °F (approx. 870 °C) for as long as five (5) seconds as they leave the calciner combustion chamber and pass through the loop duct to the pre-heater cyclone chambers.
  • the main components of the raw materials used to manufacture cement are calcium, silica, alumina and iron.
  • the inorganic ash components of dried bio-solids have high concentrations of calcium and silica that can supplement the conventional minerals. Therefore, the inorganic ash residue of dried bio-solids can be beneficially recovered by incorporation into the cement clinker.
  • the intimate mixing of the combustion gases and the cement raw materials as the gases leave the combustion zone ensure complete integration of inorganic ash residues into the conventional raw materials. In this manner the inorganic ash residues become an integral part of the process chemistry. There are minor constituents in the inorganic ash residue of dried biosolids that must be monitored to insure the quality of the performance of the cement product.
  • Trace components in the ash such as P 2 0 5 , CI, Na 2 0, and K 2 0 must be measured on a regular basis to control any potentially deleterious effect of these components on the cement manufacturing process or the performance of the finished product.
  • P 2 0 5 from dried bio-solids will increase the concentration of phosphorus in the finished clinker.
  • Research has indicated that when the level of phosphorus in a clinker approaches 1.5% the strength development of the resulting concrete will be deleteriously impacted.
  • high concentrations of CI, Na 2 0, K 2 0, and S0 3 from dried bio-solids can cause build up in kiln or preheat tower, which, in turn, can cause operational interruptions.

Landscapes

  • Chemical & Material Sciences (AREA)
  • Ceramic Engineering (AREA)
  • Organic Chemistry (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • General Life Sciences & Earth Sciences (AREA)
  • Geochemistry & Mineralogy (AREA)
  • Geology (AREA)
  • Materials Engineering (AREA)
  • Structural Engineering (AREA)
  • Thermal Sciences (AREA)
  • Physics & Mathematics (AREA)
  • Oil, Petroleum & Natural Gas (AREA)
  • Solid Fuels And Fuel-Associated Substances (AREA)

Abstract

L'invention concerne un procédé et un appareil pour préparer un combustible amélioré ou un additif pour combustible pour un procédé de fabrication de ciment par séchage de biosolides de Classe A ou d'autres matières de biomasse séchées utilisant de la chaleur résiduelle provenant de refroidisseur de clinker ou de gaz d'échappement de four.
PCT/US2014/024007 2013-03-14 2014-03-12 Utilisation de chaleur résiduelle de four pour réduire la teneur en humidité de biosolides de classe a et d'autres combustibles de biomasse WO2014150695A1 (fr)

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US201361782454P 2013-03-14 2013-03-14
US61/782,454 2013-03-14

Publications (1)

Publication Number Publication Date
WO2014150695A1 true WO2014150695A1 (fr) 2014-09-25

Family

ID=51580809

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/US2014/024007 WO2014150695A1 (fr) 2013-03-14 2014-03-12 Utilisation de chaleur résiduelle de four pour réduire la teneur en humidité de biosolides de classe a et d'autres combustibles de biomasse

Country Status (1)

Country Link
WO (1) WO2014150695A1 (fr)

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2020067852A1 (fr) * 2018-09-28 2020-04-02 한국토지주택공사 Système de recyclage intelligent pour des opérations automatiques de collecte de déchets et de transformation de ceux-ci en combustible
ES2812673A1 (es) * 2018-12-26 2021-03-17 Cogcem Proyectos S L Sistema de integración de calderas de biomasa en procesos de fabricación de Clinker de cemento

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20040001424A (ko) * 2002-06-28 2004-01-07 벽산엔지니어링주식회사 폐합성수지의 건류가스 연소열을 이용한 슬러지 건조장치및 방법
US20050274293A1 (en) * 2004-06-14 2005-12-15 Lehigh Cement Company Method and apparatus for drying wet bio-solids using excess heat recovered from cement manufacturing process equipment
US20050274068A1 (en) * 2004-06-14 2005-12-15 Morton Edward L Bio-solid materials as alternate fuels in cement kiln, riser duct and calciner
JP2006273970A (ja) * 2005-03-29 2006-10-12 Sumitomo Osaka Cement Co Ltd バイオマス含有石炭粉末燃料の製造方法及びその利用方法並びにバイオマス含有石炭粉末燃料の製造装置
JP5067408B2 (ja) * 2009-09-24 2012-11-07 住友大阪セメント株式会社 バイオマスの処理方法

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR20040001424A (ko) * 2002-06-28 2004-01-07 벽산엔지니어링주식회사 폐합성수지의 건류가스 연소열을 이용한 슬러지 건조장치및 방법
US20050274293A1 (en) * 2004-06-14 2005-12-15 Lehigh Cement Company Method and apparatus for drying wet bio-solids using excess heat recovered from cement manufacturing process equipment
US20050274068A1 (en) * 2004-06-14 2005-12-15 Morton Edward L Bio-solid materials as alternate fuels in cement kiln, riser duct and calciner
JP2006273970A (ja) * 2005-03-29 2006-10-12 Sumitomo Osaka Cement Co Ltd バイオマス含有石炭粉末燃料の製造方法及びその利用方法並びにバイオマス含有石炭粉末燃料の製造装置
JP5067408B2 (ja) * 2009-09-24 2012-11-07 住友大阪セメント株式会社 バイオマスの処理方法

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
MORTON, E. L.: "A SUSTAINABLE USE FOR DRIED BIOSOLIDS", WATER ENVIRONMENT FEDERATION. WEFTEC 2006 : SESSION 21 THROUGH SESSION 30, pages 2060 - 2067 *

Cited By (2)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
WO2020067852A1 (fr) * 2018-09-28 2020-04-02 한국토지주택공사 Système de recyclage intelligent pour des opérations automatiques de collecte de déchets et de transformation de ceux-ci en combustible
ES2812673A1 (es) * 2018-12-26 2021-03-17 Cogcem Proyectos S L Sistema de integración de calderas de biomasa en procesos de fabricación de Clinker de cemento

Similar Documents

Publication Publication Date Title
CA2570278C (fr) Procede et appareil de sechage de bio-solides mouilles a l'aide de l'exces de chaleur recupere d'un equipement de processus de fabrication de ciment
US7434332B2 (en) Method and apparatus for drying wet bio-solids using excess heat from a cement clinker cooler
CN101528614B (zh) 高含水率有机废弃物的处理方法和处理装置
US20050274068A1 (en) Bio-solid materials as alternate fuels in cement kiln, riser duct and calciner
US20050066860A1 (en) Use of organic waste/mineral by-product mixtures in cement manufacturing processes
PL123885B1 (en) Method of treating the waste water sludge
JPS5911545B2 (ja) ポルトランドセメント製造及び廃棄物の利用
WO2014024498A1 (fr) Installation de traitement des boues et procédé associé
US20130263501A1 (en) System and method for biomass fuel production and integrated biomass and biofuel production
TWI722316B (zh) 污泥之處理方法及水泥製造系統
JP4628773B2 (ja) 有機系汚泥の処理方法及び処理装置
US7461466B2 (en) Method and apparatus for drying wet bio-solids using excess heat from a cement clinker cooler
JP2006035189A (ja) セメント製造プロセスを利用した有機性汚泥の処理方法
WO2014150695A1 (fr) Utilisation de chaleur résiduelle de four pour réduire la teneur en humidité de biosolides de classe a et d'autres combustibles de biomasse
JP2006212594A (ja) 廃棄物乾燥排ガスの処理方法
JP6696053B2 (ja) 有機汚泥の処理装置及び処理方法
WO2021006155A1 (fr) Procédé de traitement de boue et système de fabrication de ciment
JP2005279501A (ja) 有機性廃棄物の処理方法及びその装置
JP3929371B2 (ja) 木材由来燃料及びその製造方法
US8636840B2 (en) Process for utilizing organic waste materials
US20130263499A1 (en) System and method for densification of renewable coal replacement fuel
RU2783180C1 (ru) Способ переработки твердых бытовых отходов во вторичное сырье
JPH10110176A (ja) 廃棄物からの固形化燃料の製造方法
JP2022151281A (ja) コーヒー粕のセメント燃料化利用
TW202106653A (zh) 可燃物的處理方法及處理裝置

Legal Events

Date Code Title Description
121 Ep: the epo has been informed by wipo that ep was designated in this application

Ref document number: 14770869

Country of ref document: EP

Kind code of ref document: A1

NENP Non-entry into the national phase

Ref country code: DE

122 Ep: pct application non-entry in european phase

Ref document number: 14770869

Country of ref document: EP

Kind code of ref document: A1