US20100006014A1 - Targeted reagent injection for slag control from combustion of coals high in iron and/or calcium - Google Patents
Targeted reagent injection for slag control from combustion of coals high in iron and/or calcium Download PDFInfo
- Publication number
- US20100006014A1 US20100006014A1 US12/501,590 US50159009A US2010006014A1 US 20100006014 A1 US20100006014 A1 US 20100006014A1 US 50159009 A US50159009 A US 50159009A US 2010006014 A1 US2010006014 A1 US 2010006014A1
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- US
- United States
- Prior art keywords
- slag
- coal
- reagent
- pounds
- per ton
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Abandoned
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Classifications
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23C—METHODS OR APPARATUS FOR COMBUSTION USING FLUID FUEL OR SOLID FUEL SUSPENDED IN A CARRIER GAS OR AIR
- F23C99/00—Subject-matter not provided for in other groups of this subclass
-
- 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
- C10L10/00—Use of additives to fuels or fires for particular purposes
- C10L10/06—Use of additives to fuels or fires for particular purposes for facilitating soot removal
-
- 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
- C10L10/00—Use of additives to fuels or fires for particular purposes
- C10L10/04—Use of additives to fuels or fires for particular purposes for minimising corrosion or incrustation
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J3/00—Removing solid residues from passages or chambers beyond the fire, e.g. from flues by soot blowers
-
- F—MECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
- F23—COMBUSTION APPARATUS; COMBUSTION PROCESSES
- F23J—REMOVAL OR TREATMENT OF COMBUSTION PRODUCTS OR COMBUSTION RESIDUES; FLUES
- F23J7/00—Arrangement of devices for supplying chemicals to fire
-
- 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
- C10L2200/00—Components of fuel compositions
- C10L2200/02—Inorganic or organic compounds containing atoms other than C, H or O, e.g. organic compounds containing heteroatoms or metal organic complexes
- C10L2200/0204—Metals or alloys
- C10L2200/0213—Group II metals: Be, Mg, Ca, Sr, Ba, Ra, Zn, Cd, Hg
-
- 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
- C10L2200/00—Components of fuel compositions
- C10L2200/02—Inorganic or organic compounds containing atoms other than C, H or O, e.g. organic compounds containing heteroatoms or metal organic complexes
- C10L2200/0204—Metals or alloys
- C10L2200/0218—Group III metals: Sc, Y, Al, Ga, In, Tl
-
- 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
- C10L2200/00—Components of fuel compositions
- C10L2200/02—Inorganic or organic compounds containing atoms other than C, H or O, e.g. organic compounds containing heteroatoms or metal organic complexes
- C10L2200/0254—Oxygen containing compounds
-
- 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
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/14—Injection, e.g. in a reactor or a fuel stream during fuel production
- C10L2290/141—Injection, e.g. in a reactor or a fuel stream during fuel production of additive or catalyst
-
- 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
- C10L2290/00—Fuel preparation or upgrading, processes or apparatus therefore, comprising specific process steps or apparatus units
- C10L2290/18—Spraying or sprinkling
Definitions
- the invention relates to a process that increases the output of a combustor fired with coal having high iron and/or calcium content, by reducing the tendency of slag to form on heat exchange surfaces, changing the nature of the slag to make it easier to remove and actually removing slag.
- the tendency to form slag and the properties of the slag for such high iron content coals have been a major concern of combustion engineers and plant operators for decades.
- Slag accumulation is a problem that causes decreased heat transfer and often leads to long periods of downtime for cleaning.
- a yet further but more specific object is to provide a process to more effectively control slag by decreasing the amount of downtime associated with slag removal.
- the invention provides a process for reducing slag cohesiveness and/or adhesiveness in a combustor, thereby decreasing the rate of fouling, comprising: combusting a slag-forming coal, having high iron and/or calcium content, with an overall excess of oxygen; moving the resulting combustion gases though heat exchange equipment under conditions which cause cooling of slag formed by burning the coal; and prior to contact with said heat exchange equipment, introducing aqueous aluminum trihydroxide in amounts and with droplet sizes and concentrations effective to decrease the rate of fouling, and preferably, increase the friability of the resulting slag.
- the aluminum trihydroxide reagent is introduced in the form of an aqueous liquid and computational fluid dynamics is employed to determine flow rates and select reagent introduction rates, reagent introduction location(s), reagent concentration, reagent droplet size and/or reagent momentum.
- magnesium hydroxide is introduced as an aqueous slurry along with the slurry of aluminum trihydroxide.
- the invention provides a process for cleaning furnace surfaces having a slag buildup, by introducing aqueous aluminum trihydroxide in amounts and with droplet sizes and concentrations effective to contact for fine particulates resulting from drying the slurry to contact existing slag deposits.
- the invention provides a process a cleaning and maintenance of a combustor comprising a regimen of initial dosing of from about 3 to 6 pounds of ATH per ton of coal and about 1 to 2 pounds of Mg(OH) 2 per ton of coal for a time sufficient to reduce slag, followed by a reduced reducing the dosing of from about 10 to about 50% of the initial values for maintaining the combustor clean and operating efficiently.
- FIG. 1 is a schematic view of one embodiment of the invention.
- FIG. 2 is a photograph of a slag sample obtained after operation for 24 hours of aluminum trihydroxide into a combustor operated on a high iron content coal as set out in Example 2 below.
- FIG. 1 is a schematic view of one embodiment of the invention.
- FIG. 1 shows a large combustor 10 of the type used for producing steam for electrical power generation, process steam, heating or incineration.
- Coal is fed by burners 20 and 20 a and burned with air in a combustion zone 21 .
- coal that is high in iron (e.g., iron contents of greater than about 15%, e.g., from about 20 to 35%, based on the weight of the ash and expressed as Fe 2 O 3 ) and/or calcium content (e.g., calcium contents of greater than 5%, e.g., from about 10 to 25%, based on the weight of the ash and expressed as CaO).
- iron e.g., iron contents of greater than about 15%, e.g., from about 20 to 35%, based on the weight of the ash and expressed as Fe 2 O 3
- calcium content e.g., calcium contents of greater than 5%, e.g., from about 10 to 25%, based on
- Air for combustion supplied by fan 22 and ductwork 24 , is preferably preheated by a gas-to-gas heat exchangers (not shown) which transfer heat from ductwork (not shown) at the exit end of the combustor.
- Hot combustion gases rise and flow past heat exchangers 26 , which transfer heat from the combustion gases to water for the generation of steam.
- Other heat exchangers including an economizer (downstream and not shown) may also be provided according to the design of the particular boiler. Slag left untreated would tend to form on these heat exchanger surfaces, which are positioned within specific combustors based on design considerations important to individual locations.
- modeling techniques such as computational fluid dynamics, are employed to initially direct treatment chemicals (especially, those identified as effective for particular types of coal according to the invention) to the optimum locations for reducing and/or controlling slag buildup and maintaining efficient operation of the boiler.
- a series of suitable, preferably air assisted atomizing, nozzles in each of nozzle banks 30 and 30 a are provided for introducing aluminum trihydroxide alone or with magnesium hydroxide slurry from vessels 40 and 40 a respectively.
- Both the ATH and the magnesium hydroxide are preferably aqueous, as slurries and/or solutions as appropriate.
- Supply lines e.g., 41
- Valves e.g., 42
- temperature sensors e.g., 44
- Both valves 42 and temperature sensors 44 are connected to controller 46 via electrical leads (e.g., 48 ) shown in dotted lines.
- the controller 46 can be a general purpose digital computer programmed in accord with a predetermined control regimen with both feed forward and feedback features.
- Aluminum trihydroxide (Al(OH) 3 ), which has been found effective according to the invention for greatly lessening the deposition of slag or cleaning deposited slag from troublesome coal types, is also known under other names such as ATH, aluminum hydroxide and hydrated alumina. Regardless of the form of aluminum trihydroxide raw material, it is preferred that it is mixed with water for introduction from tank 40 through associated lines 41 , with or without chemical stabilizers, to concentrations suitable for storage and handling, e.g., at least about 25%, and preferably at least about 65%, solids by weight.
- the concentration and flow rates will be initially determined by modeling to assure that the proper amount of chemical is supplied to the correct location in the combustor in the correct physical form to achieve the desired results of reduced slagging and ease of clean up.
- it is diluted as determined, e.g., by computational fluid dynamics (CFD) to within the range of from about 0.1 to about 10%, more narrowly from about 1 to about 5%.
- CFD computational fluid dynamics
- the aqueous aluminum trihydroxide contacts the hot gases in the combustor, it is believed to be reduced to very small particles, e.g., nano-sized particles, e.g., under 200 nanometers and preferably below about 100 nanometers.
- Median particle sizes of from 50 to about 150 nanometers are useful ranges for the process of the invention. To approach this size, it is important that the ATH be introduced with water. The small particles are believed to disrupt the normal crystalline or glass that forms the slag. Regardless of the mechanism involved it is a distinct advantage of the invention that the slag that does form is highly friable and breaks easily with brushing and can be crushed by hand.
- the friability of slag that is formed is increased, making it easier to remove.
- the invention also slows or eliminates the buildup of slag.
- the invention can actually remove slag that has already formed.
- increase the friability of the slag it is meant that the slag after treatment requires less force per unit area to crush than slag formed under the same conditions without the treatment.
- remove slag it is meant that the weight of the slag adhering to boiler, particularly heat exchange, surfaces is reduced from initial values by the treatment of the invention.
- the process for most coals works best with a combination of ATH and magnesium hydroxide. While some coals, e.g., with low silicate compositions can be burned with reduced problems attributed to slag, the use of magnesium hydroxide, at least initially, is preferred.
- the magnesium hydroxide reagent can preferably be prepared from brines containing calcium and other salts, usually from underground brine pools or seawater. Dolomitic lime is mixed with these brines to form calcium chloride solution and magnesium hydroxide which is precipitated and filtered out of the solution. This form of magnesium hydroxide can be mixed with water, with or without stabilizers, to concentrations suitable for storage and handling, e.g., from 25 to 65% solids by weight.
- CFD computational fluid dynamics
- it is diluted as determined by computational fluid dynamics (CFD) to within the range of from 0.1 to 10%, more narrowly from 1 to 5%.
- CFD computational fluid dynamics
- nano-sized particles e.g., under 200 nanometers and preferably below about 100 nanometers.
- Median particle sizes of from 50 to about 150 nanometers are useful ranges for the process of the invention.
- Other forms of MgO can also be employed where necessary or desired, e.g., “light burn” or “caustic” can be employed where it is available in the desired particle size range.
- the invention will preferably take advantage of CFD to project initial flow rates and select initial reagent introduction rates, reagent introduction location(s), reagent concentration, reagent droplet size and reagent momentum.
- CFD is a well understood science, and it is utilized with full benefit in this case, where it is desired to supply a minimum amount of chemical for maximum effect.
- the initial feed rate for the best economics for combustors operating similar to the one exemplified below can be up to about 6 pounds of ATH(as dry active ATH) or 8 pounds (as a 65-70% slurry) per ton of coal.
- amounts of from about 1 to about 6 pounds of slurry will be effective (more narrowly, e.g., about 2 to about 3 pounds of slurry). It is preferred to also use up to about 2 pounds of Mg(OH) 2 slurry (at about 50-60% solids) per ton of coal.
- amounts of from about 0.5 to about 2 pounds of Mg(OH) 2 slurry per ton of coal e.g., from about 0.7 to about 1 pounds of Mg(OH) 2 slurry per ton of coal can be utilized.
- the slurries are diluted as necessary, typically to a solids concentration of from about 5% for smaller applications to about 35% or more.
- the weight of the slag adhering to a combustor, particularly heat exchange, surfaces is effectively reduced from initial values by the treatment of the invention, especially when the ATH and Mg(OH) 2 are used at high concentrations within the above ranges, e.g., from about 3 to 6 pounds of ATH per ton of coal and about 1 to 2 pounds of Mg(OH) 2 per ton of coal.
- This ability to remove slag provides the ability to provide a cleaning and maintenance regimen wherein the initial dosing is as just mentioned for removing slag, with the dosing then reduced to from about 10 to about 50% of the initial values for maintaining the combustor clean and operating efficiently.
- combustion catalysts and or effluent treatment chemicals can be added to the fuel, combustion zone or otherwise as described, for example in U.S. Pat. No. 7,162,960 to Smyrniotis, et al.
- Al(OH) 3 aluminum trihydroxide slurry or ATH for short
- aqueous slurry at a rate of 5 pounds slurry per ton of coal consumed from two banks of three air-cooled nozzles positioned on the wall opposite of two banks of pulverized coal burners—one bank at an elevation between the two burners and one bank at an elevation above the uppermost coal burners.
- the slurry is diluted to a concentration of 35 weight % ATH.
- the density of the ATH slurry before dilution is about 14 pounds/gallon, meaning that the feed rate is about 193 gallons per day (about 5 pounds per ton of coal) for ATH slurry.
- an effective feed rate for this particular combustor will be from about 1 to about 6 pounds of ATH slurry per ton of coal, e.g., about 2 to about 3 pounds per ton.
- Example 2 This example illustrates the effect of introducing Mg(OH) 2 (magnesium hydroxide) into a furnace burning 540 tons of coal per day in addition to the aluminum trihydroxide fed in Example 1.
- the coal was a blend of Illinois basin and Appalachian bituminous coals, as illustrated in Example 1.
- the magnesium hydroxide was fed as a slurry at 2 lbs of 50 to 60 weight % slurry per ton of coal consumed. Density of the magnesium hydroxide slurry was approximately 12 lbs/gallon. Therefore, the feed rate was about 90 gallons per day for the Mg(OH) 2 slurry. As before, we fed the aluminum trihydroxide slurry at about 5 pounds of slurry per ton of coal consumed. The density of the ATH was about 14 pounds/gallon, making the feed rate about 193 gallons per day for ATH.
- FIG. 2 is a photograph of a slag sample obtained after operation for 24 hours of ATH feed only. The slag was unexpectedly friable.
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- Chemical & Material Sciences (AREA)
- Engineering & Computer Science (AREA)
- Combustion & Propulsion (AREA)
- Oil, Petroleum & Natural Gas (AREA)
- Organic Chemistry (AREA)
- Mechanical Engineering (AREA)
- General Engineering & Computer Science (AREA)
- Incineration Of Waste (AREA)
- Solid Fuels And Fuel-Associated Substances (AREA)
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Priority Applications (1)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US12/501,590 US20100006014A1 (en) | 2008-07-11 | 2009-07-13 | Targeted reagent injection for slag control from combustion of coals high in iron and/or calcium |
Applications Claiming Priority (2)
Application Number | Priority Date | Filing Date | Title |
---|---|---|---|
US8000408P | 2008-07-11 | 2008-07-11 | |
US12/501,590 US20100006014A1 (en) | 2008-07-11 | 2009-07-13 | Targeted reagent injection for slag control from combustion of coals high in iron and/or calcium |
Related Parent Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
US61080004 Continuation-In-Part | 2008-07-11 |
Publications (1)
Publication Number | Publication Date |
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US20100006014A1 true US20100006014A1 (en) | 2010-01-14 |
Family
ID=41507460
Family Applications (1)
Application Number | Title | Priority Date | Filing Date |
---|---|---|---|
US12/501,590 Abandoned US20100006014A1 (en) | 2008-07-11 | 2009-07-13 | Targeted reagent injection for slag control from combustion of coals high in iron and/or calcium |
Country Status (18)
Country | Link |
---|---|
US (1) | US20100006014A1 (ja) |
EP (1) | EP2318489B1 (ja) |
JP (1) | JP5657533B2 (ja) |
KR (1) | KR101298932B1 (ja) |
CN (1) | CN102089413B (ja) |
AR (1) | AR072502A1 (ja) |
AU (1) | AU2009268391C1 (ja) |
CA (1) | CA2729959C (ja) |
CL (1) | CL2009001571A1 (ja) |
CO (1) | CO6300873A2 (ja) |
ES (1) | ES2554165T3 (ja) |
HK (1) | HK1157810A1 (ja) |
MX (1) | MX2011000275A (ja) |
MY (1) | MY156010A (ja) |
PL (1) | PL2318489T3 (ja) |
RU (1) | RU2493240C2 (ja) |
TW (1) | TWI482852B (ja) |
WO (1) | WO2010006325A1 (ja) |
Cited By (4)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US20120312206A1 (en) * | 2011-06-13 | 2012-12-13 | Dorner Robert W | Method for reducing slag in biomass combustion |
US9127228B2 (en) | 2011-01-14 | 2015-09-08 | Enviornmental Energy Serivces, Inc. | Process for operating a furnace with a bituminous coal and method for reducing slag formation therewith |
WO2017053499A1 (en) * | 2015-09-25 | 2017-03-30 | Fuel Tech, Inc. | Process and apparatus for reducing plume |
US9863632B2 (en) | 2008-01-15 | 2018-01-09 | Environmental Energy Services, Inc. | Process for operating a coal-fired furnace with reduced slag formation |
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US4428310A (en) * | 1982-07-26 | 1984-01-31 | Nalco Chemical Company | Phosphated alumina as slag modifier |
US6289827B1 (en) * | 1999-06-24 | 2001-09-18 | Martin Marietta Magnesia Specialties Inc. | Process for the control of ash accumulation and corrosivity associated with selective catalytic reduction technology |
US20040010969A1 (en) * | 2001-01-11 | 2004-01-22 | Anupam Sanyal | Inhibition of reflective ash build-up in coal-fired furnaces |
US20050150441A1 (en) * | 2004-01-08 | 2005-07-14 | Smyrniotis Christopher R. | Process for reducing plume opacity |
US20060121398A1 (en) * | 2004-12-07 | 2006-06-08 | Meffert Michael W | Additive atomizing systems and apparatus |
US7332002B2 (en) * | 2000-06-26 | 2008-02-19 | Ada Environmental Solutions, Llc | Low sulfur coal additive for improved furnace operation |
US7361319B2 (en) * | 2003-12-05 | 2008-04-22 | Intercat, Inc. | Mixed metal oxide sorbents |
US7361264B2 (en) * | 2004-06-02 | 2008-04-22 | Intercat, Inc. | Mixed metal oxide additives |
US20090071067A1 (en) * | 2007-09-17 | 2009-03-19 | Ian Macpherson | Environmentally-Friendly Additives And Additive Compositions For Solid Fuels |
US20090178599A1 (en) * | 2008-01-15 | 2009-07-16 | Environmental Energy Services, Inc. | Process for operating a coal-fired furnace with reduced slag formation |
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JP3153091B2 (ja) * | 1994-03-10 | 2001-04-03 | 株式会社荏原製作所 | 廃棄物の処理方法及びガス化及び熔融燃焼装置 |
CA1136078A (en) * | 1978-09-21 | 1982-11-23 | George P. Masologites | Process for removing sulfur from coal |
JPS59189144A (ja) * | 1983-04-12 | 1984-10-26 | Hokuriku Electric Power Co Inc:The | ゴム用充填剤 |
US4498402A (en) * | 1983-06-13 | 1985-02-12 | Kober Alfred E | Method of reducing high temperature slagging in furnaces and conditioner for use therein |
JPH0586374A (ja) * | 1991-09-26 | 1993-04-06 | Teikoku Sekiyu Kk | 炭水化物を可燃性のガスに分解する方法 |
RU2086293C1 (ru) * | 1993-05-28 | 1997-08-10 | Олег Порфирьевич Кочетков | Способ мокрой очистки газов и устройство для его осуществления (варианты) |
JP3745973B2 (ja) * | 2001-03-23 | 2006-02-15 | タイホー工業株式会社 | スラッギング防止用石炭添加剤及び石炭の燃焼方法 |
JP2003090530A (ja) * | 2001-07-10 | 2003-03-28 | Ishikawajima Harima Heavy Ind Co Ltd | クリンカ堆積防止装置 |
JP3746026B2 (ja) * | 2002-08-28 | 2006-02-15 | タイホー工業株式会社 | スラッギング防止用燃料添加剤及び燃料の燃焼方法 |
CN101522287B (zh) * | 2005-02-04 | 2012-11-21 | 燃料技术公司 | 用于so3控制的定位管道注入 |
CA2612415A1 (en) * | 2005-06-16 | 2006-12-28 | Warner Chilcott Company, Inc. | Estrogen compositions for vaginal administration |
-
2009
- 2009-07-10 TW TW098123559A patent/TWI482852B/zh not_active IP Right Cessation
- 2009-07-10 CL CL2009001571A patent/CL2009001571A1/es unknown
- 2009-07-13 AU AU2009268391A patent/AU2009268391C1/en not_active Ceased
- 2009-07-13 JP JP2011517673A patent/JP5657533B2/ja not_active Expired - Fee Related
- 2009-07-13 PL PL09795277T patent/PL2318489T3/pl unknown
- 2009-07-13 CN CN2009801268715A patent/CN102089413B/zh not_active Expired - Fee Related
- 2009-07-13 ES ES09795277.4T patent/ES2554165T3/es active Active
- 2009-07-13 KR KR1020117003171A patent/KR101298932B1/ko not_active IP Right Cessation
- 2009-07-13 AR ARP090102634A patent/AR072502A1/es not_active Application Discontinuation
- 2009-07-13 EP EP09795277.4A patent/EP2318489B1/en not_active Not-in-force
- 2009-07-13 MX MX2011000275A patent/MX2011000275A/es active IP Right Grant
- 2009-07-13 MY MYPI2011000010A patent/MY156010A/en unknown
- 2009-07-13 US US12/501,590 patent/US20100006014A1/en not_active Abandoned
- 2009-07-13 WO PCT/US2009/050354 patent/WO2010006325A1/en active Application Filing
- 2009-07-13 CA CA2729959A patent/CA2729959C/en not_active Expired - Fee Related
- 2009-07-13 RU RU2011103846/04A patent/RU2493240C2/ru not_active IP Right Cessation
-
2011
- 2011-02-04 CO CO11012993A patent/CO6300873A2/es active IP Right Grant
- 2011-11-07 HK HK11111996.8A patent/HK1157810A1/zh not_active IP Right Cessation
Patent Citations (12)
Publication number | Priority date | Publication date | Assignee | Title |
---|---|---|---|---|
US4428310A (en) * | 1982-07-26 | 1984-01-31 | Nalco Chemical Company | Phosphated alumina as slag modifier |
US6289827B1 (en) * | 1999-06-24 | 2001-09-18 | Martin Marietta Magnesia Specialties Inc. | Process for the control of ash accumulation and corrosivity associated with selective catalytic reduction technology |
US7332002B2 (en) * | 2000-06-26 | 2008-02-19 | Ada Environmental Solutions, Llc | Low sulfur coal additive for improved furnace operation |
US20040010969A1 (en) * | 2001-01-11 | 2004-01-22 | Anupam Sanyal | Inhibition of reflective ash build-up in coal-fired furnaces |
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US9863632B2 (en) | 2008-01-15 | 2018-01-09 | Environmental Energy Services, Inc. | Process for operating a coal-fired furnace with reduced slag formation |
US9127228B2 (en) | 2011-01-14 | 2015-09-08 | Enviornmental Energy Serivces, Inc. | Process for operating a furnace with a bituminous coal and method for reducing slag formation therewith |
US9541288B2 (en) | 2011-01-14 | 2017-01-10 | Environmental Energy Services, Inc. | Process for operating a furnace with bituminous coal and method for reducing slag formation therewith |
US20120312206A1 (en) * | 2011-06-13 | 2012-12-13 | Dorner Robert W | Method for reducing slag in biomass combustion |
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Also Published As
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CA2729959A1 (en) | 2010-01-14 |
EP2318489A4 (en) | 2013-05-15 |
CL2009001571A1 (es) | 2010-03-12 |
WO2010006325A1 (en) | 2010-01-14 |
RU2493240C2 (ru) | 2013-09-20 |
CA2729959C (en) | 2015-09-01 |
EP2318489A1 (en) | 2011-05-11 |
AR072502A1 (es) | 2010-09-01 |
MY156010A (en) | 2015-12-31 |
JP2011527000A (ja) | 2011-10-20 |
CN102089413B (zh) | 2013-12-18 |
CN102089413A (zh) | 2011-06-08 |
RU2011103846A (ru) | 2012-08-20 |
PL2318489T3 (pl) | 2016-03-31 |
AU2009268391C1 (en) | 2014-12-11 |
AU2009268391B2 (en) | 2014-05-08 |
AU2009268391A1 (en) | 2010-01-14 |
MX2011000275A (es) | 2011-03-02 |
KR101298932B1 (ko) | 2013-08-22 |
KR20110043656A (ko) | 2011-04-27 |
TW201009067A (en) | 2010-03-01 |
TWI482852B (zh) | 2015-05-01 |
ES2554165T3 (es) | 2015-12-16 |
HK1157810A1 (zh) | 2012-07-06 |
EP2318489B1 (en) | 2015-09-02 |
CO6300873A2 (es) | 2011-07-21 |
JP5657533B2 (ja) | 2015-01-21 |
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