WO2004055139A1 - Fuel from ash - Google Patents

Fuel from ash Download PDF

Info

Publication number
WO2004055139A1
WO2004055139A1 PCT/CA2003/001932 CA0301932W WO2004055139A1 WO 2004055139 A1 WO2004055139 A1 WO 2004055139A1 CA 0301932 W CA0301932 W CA 0301932W WO 2004055139 A1 WO2004055139 A1 WO 2004055139A1
Authority
WO
WIPO (PCT)
Prior art keywords
fuel
process according
coal ash
initial carbon
coal
Prior art date
Application number
PCT/CA2003/001932
Other languages
French (fr)
Other versions
WO2004055139B1 (en
Inventor
David Bridson Oates
Alan Van Sloten
Jeffrey Fair
Trent Renfro
Craig Plunk
Original Assignee
Lafarge Canada Inc.
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 Lafarge Canada Inc. filed Critical Lafarge Canada Inc.
Priority to AU2003291895A priority Critical patent/AU2003291895A1/en
Priority to CA002509352A priority patent/CA2509352A1/en
Priority to EP03767353A priority patent/EP1572843A2/en
Publication of WO2004055139A1 publication Critical patent/WO2004055139A1/en
Publication of WO2004055139B1 publication Critical patent/WO2004055139B1/en

Links

Classifications

    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS 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
    • C10L5/00Solid fuels
    • C10L5/02Solid fuels such as briquettes consisting mainly of carbonaceous materials of mineral or non-mineral origin
    • C10L5/34Other details of the shaped fuels, e.g. briquettes
    • C10L5/36Shape
    • C10L5/361Briquettes
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS 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
    • C10L5/00Solid fuels
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS 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
    • C10L5/00Solid fuels
    • C10L5/02Solid fuels such as briquettes consisting mainly of carbonaceous materials of mineral or non-mineral origin
    • C10L5/04Raw material of mineral origin to be used; Pretreatment thereof
    • CCHEMISTRY; METALLURGY
    • C10PETROLEUM, GAS OR COKE INDUSTRIES; TECHNICAL GASES CONTAINING CARBON MONOXIDE; FUELS; LUBRICANTS; PEAT
    • C10LFUELS 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
    • C10L5/00Solid fuels
    • C10L5/02Solid fuels such as briquettes consisting mainly of carbonaceous materials of mineral or non-mineral origin
    • C10L5/34Other details of the shaped fuels, e.g. briquettes
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/02Incineration of waste; Incinerator constructions; Details, accessories or control therefor with pretreatment
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2201/00Pretreatment
    • F23G2201/60Separating
    • F23G2201/602Separating different sizes
    • YGENERAL 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
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02EREDUCTION OF GREENHOUSE GAS [GHG] EMISSIONS, RELATED TO ENERGY GENERATION, TRANSMISSION OR DISTRIBUTION
    • Y02E20/00Combustion technologies with mitigation potential
    • Y02E20/12Heat utilisation in combustion or incineration of waste

Definitions

  • the invention relates to a fuel, a process to produce the fuel from coal ash and a method of burning the fuel.
  • the process to produce the fuel from coal ash is based on a pneumatic separation where the coal ash is separated into at least two size fractions.
  • the size fractions obtained by the process of this invention include; a major fine fraction containing lower carbon and a minor coarse fraction containing increased levels of carbon in sufficient quantity, to be used as a fuel.
  • Coal ash is a very fine granular solid residue obtained as a by-product of coal ' combustion. Due to its abundance and cementitious properties, coal ash is widely used in the production of concrete. Coal ash is made up of various categories and comprises fly ash. Fly ash is a specific type * of coal ash collected from the combustion gases of coal fired heaters and coal burning power plants. Fly ash is further segregated into several groups which are classified in large part, by the coal source the fly ash is derived from.
  • Cochran in US Patent 5,160,539 teaches a method and low carbon product obtained in an bubbling fluid bed produced by the introduction of air and whose operating conditions are between 1300 and 1800°F.
  • the product of this invention is a useful pozzolanic material.
  • US Patent 5,555,821 by Martinez discloses a stainless steel apparatus arid a process for removing unburned carbon from fly ash. The fly ash is heated from 800 to 1200 °C in a double auger where an oxygen containing gas is injected, .cooled and then finally recovered. The oxygen is said to accelerate the burning of the carbon in the fly ash and the process is said to achieve carbon levels of 0.7% in the fly ash.
  • One object of this invention is to provide a process for producing a fuel from coal ash having an initial amount of carbon. This process comprising the pneumatic separation of coal ash into at least two size fractions;
  • the two size fractions comprise and are separated into
  • a minor coarse fraction being the fuel; and containing at least 45% of the initial carbon amount
  • Another object of the invention is a fuel derived from coal ash having an initial amount of carbon.
  • the fuel is produced by a pneumatic separation of the coal ash wherein the coal ash is separated into at least two fractions;
  • the two size fractions comprise and a.re separated into
  • Yet another object of the invention is a method of burning a fuel derived from coal ash.
  • the coal ash having an initial carbon amount and the fuel being produced by, the pneumatic separation of coal ash into at least two size fractions;
  • the two size fractions comprise and are separated into
  • a minor coarse fraction being the fuel; and containing at least 45% of the initial carbon amount
  • Fig. 1 is a process flow diagram for producing the fuel derived from coal ash with a single classifier means illustrated.
  • Fig. 2 is a process flow diagram for producing fuel ⁇ derived from coal ash, where the fuel is classified and removed from the solid gas contactor.
  • Fig. 3 is a process flow diagram wherein there are multiple particle size classification steps and intermediate products .
  • Fig. 1 illustrates the process of the separation used to obtain the coal ash derived fuel.
  • the coal ash is introduced into the process via the coal ash inlet (10) near the bottom of the circulating solid gas contactor (100) .
  • the coal ash to be added to the solid gas contactor should contain at least 5% initial carbon amount (%LOI) , and preferably at least 10% initial carbon and most preferably 14% initial carbon. It must also be noted, that nearly half of the carbon initially present in the coal ash is found in the coarse fraction
  • This fraction contains at least 45% (w/w) of the initial carbon, and preferably more than 50% (w/w) of the initial carbon.
  • the type of solid gas contactor represented in Fig. 1 is, a fluidized bed, a circulating fluidized bed, a transport vessel or a classifying transport vessel.
  • These four equipment types would usually be referred to as a fluidized bed reactor, a circulating fluidized bed reactor, a transport reactor or a classifying transport reactor, but because there is only particle classification without a reaction taking place, the word "reactor" has been either omitted or replaced with "vessel".
  • the gas distributor in the solid-gas contactor may be a perforated plate, although no plate is needed if the solid gas contactor is a transport vessel or classifying transport vessel.
  • the gas used as the means of separation of the coal ash is typically ambient air (20) and no particular pretreatment other than that required for the efficient operation of the blower is required.
  • the coal ash may be damp with moisture
  • the gas (22) may be heated to temperatures where the surface moisture is removed while the carbon content is unaffected.
  • the maximum , gas temperature would be 200 °C but preferably temperatures around 150 °C are used. This heating can be accomplished through combustion of a fuel, or some other hot gas source, with the mixing of the hot gases (21) and ambient air used to attain the relatively low temperatures required. This mixing would occur near the intake of the blower (400) which would be designed to handle the higher temperatures.
  • the velocity of the gas in the contactor is such, that the coal ash is elutriated almost completely in the gas.
  • the blower is design to be of a sufficient size (pressure and flowrate) to perform this elutriation.
  • the gas stream with the suspended coal ash particles entrained (24) leaves the contactor and enters a size classifier, which is represented in the flowsheet as one cyclone (200) but can also be a bank of multiple cyclones arranged in parallel.
  • the size classifier is designed to separate the coarse fraction containing carbon from the fine fraction (28) .
  • the coarse fraction leaving the bottom of the cyclone is split into two streams.
  • the major portion of the stream (26) is returned to the bottom of the solid gas contactor, while the minor portion (30) is the coal ash fuel product.
  • the fuel is recovered in a silo from where it can be transferred towards it eventual utilization.
  • the coal ash fuel obtained is found to have a carbon content of between 40% and 60% and a thermal value between 4000 and 6000 Btu/lb. '
  • Stream (26) is returned to the solid gas contactor to increase the solids loading in the contactor, which improves the efficiency of separation in the cyclone.
  • the fine particle size fraction leaving the cyclone (28) is treated in a dust collector (300) where almost all of the fine fraction is collected (32) .
  • the gas leaving the dust collector is typically drawn away by a fan (not shown on the diagram) and depending on the collection efficiency of the dust collector, the gases are exhausted to the atmosphere.
  • Fig. 2 is very similar to Fig. 1 but represents an embodiment of- the invention where the solid gas contactor has a gas velocity that is reduced in the contactor itself by an increase in the cross sectional area of the contactor or other means.
  • the lower gas velocity will be such that the coarse particles will no longer be elutriated into the classifier and can be collected.
  • the vessel used is a circulating fluidized bed, or a classifying transport vessel and most preferably a toroidal (TorbedTM) vessel.
  • the elutriating gas (22) can once again be optionally heated by the addition of hot gases (21) at the intake of the blower (400) .
  • the elutriated portion of the dust once again enters the cyclone system (24) where two fractions are separated.
  • the fine fraction (28) going towards the dust collector.
  • the return coarse solid stream (26) from the classifier underflow once again serves to increase the solids loading in the contactor.
  • the coarse particle stream from the cyclone (26) can be split to obtain another size fraction represented in Fig. 2 as stream (31) .
  • the fuel derived from fly ash thus obtained can be transported towards a combustion system that is suitable for the combustion of fine combustible solids.
  • the fuel is meant to be used in a same way as coal and in installations that include; coal fired heaters, coal fired boilers, cement kilns and a coal burning power generating stations .
  • the means of transporting the fuel include pneumatic or mechanical means.
  • ⁇ larger size fuel feed such as briquettes, to ensure that the fuel be burned in a safe manner.
  • This agglomeration or densification step will increase the fuel value by at least 15% (becoming 4600 Btu/lb. to 6900 Btu/lb) and reduce the difficulties of handling a combustible powder.
  • the TorbedTM used in the testing gave the possibility of removing various size fractions of coal ash directly from the vessel.
  • the air temperature of 20 °C was measured at the inlet of the blower.
  • the thermal value of the combined fraction was measured at 5372 Btu/lb, and the percentage of carbon in the final fuel product obtained is 52.1% weight percentage.
  • the thermal value of the coal ash fuel obtained places it in the range typically considered that of lignite coal which is between 4000 and 8300 Btu/lb.

Abstract

Coal ash, which also consists of fly ash, is a very fine granular solid residue obtained as a by-product of coal combustion. The invention relates to the surprising result that a fuel can be obtained from coal ash. The process involves a pneumatic separation of the coal ash at relatively low temperatures. The coal ash is separated into at least two size fractions. The size fractions obtained by the process of this invention include at least one with lower carbon and another containing increased levels of carbon in the range of 50% by weight and a heating value in the range of 4000 to 6000 Btu/lb.

Description

FUEL FROM ASH
BACKGROUND OF THE INVENTION
FIELD OF THE INVENTION
The invention relates to a fuel, a process to produce the fuel from coal ash and a method of burning the fuel. The process to produce the fuel from coal ash is based on a pneumatic separation where the coal ash is separated into at least two size fractions. The size fractions obtained by the process of this invention include; a major fine fraction containing lower carbon and a minor coarse fraction containing increased levels of carbon in sufficient quantity, to be used as a fuel.
DESCRIPTION OF THE PRIOR ART
Coal ash is a very fine granular solid residue obtained as a by-product of coal ' combustion. Due to its abundance and cementitious properties, coal ash is widely used in the production of concrete. Coal ash is made up of various categories and comprises fly ash. Fly ash is a specific type* of coal ash collected from the combustion gases of coal fired heaters and coal burning power plants. Fly ash is further segregated into several groups which are classified in large part, by the coal source the fly ash is derived from.
High carbon levels in coal ash adversely affect the durability of concrete, particularly to freeze thaw cycles therefore concrete producers have commonly, tried to reduce carbon to low levels in coal ash and fly ash used for concrete. 3% LOI (Loss-on-Ignition) is considered to be the maximum carbon level permitted to produce a concrete of good durability.
Due to this low carbon requirement in concrete the prior art in the field of carbon/coal ash and particularly fly ash, has been primarily concerned with the reduction of carbon from coal ash and chiefly by thermal processes. Therefore, it is well known that the carbon in coal ash burns or at least volatilizes at higher temperatures and particularly in the presence of oxygen.
Cochran in US Patent 5,160,539 teaches a method and low carbon product obtained in an bubbling fluid bed produced by the introduction of air and whose operating conditions are between 1300 and 1800°F. The product of this invention is a useful pozzolanic material. Similarly, US Patent 5,555,821 by Martinez discloses a stainless steel apparatus arid a process for removing unburned carbon from fly ash. The fly ash is heated from 800 to 1200 °C in a double auger where an oxygen containing gas is injected, .cooled and then finally recovered. The oxygen is said to accelerate the burning of the carbon in the fly ash and the process is said to achieve carbon levels of 0.7% in the fly ash.
US Patent 5,996,808 by Levy et al, discloses an inclined fluidized bed reactor with sound wave agitation which enhances the fluidization of the fine fly ash for processing fly ash into various fractions. According to Levy et al, the lighter and coarser fractions are separated, with the coarse fraction containing more carbon. The object of the Levy invention is to reduce the carbon levels to between 3 and 5% in the fly ash. SUMMARY OF THE INVENTION
One object of this invention is to provide a process for producing a fuel from coal ash having an initial amount of carbon. This process comprising the pneumatic separation of coal ash into at least two size fractions;
the separation taking place in a solid-gas contactor in association with a classifier means wherein,
the two size fractions comprise and are separated into
a major fine fraction, and
a minor coarse fraction, being the fuel; and containing at least 45% of the initial carbon amount, and
a recovery of the fuel.
Another object of the invention is a fuel derived from coal ash having an initial amount of carbon. The fuel is produced by a pneumatic separation of the coal ash wherein the coal ash is separated into at least two fractions;
the separation taking place in a solid-gas contactor in association with a classifier means wherein,
the two size fractions comprise and a.re separated into
a major fine fraction, and
a minor coarse fraction, being the fuel; and '■ containing at least 45% of the initial carbon amount, and
a recovery of the fuel. Yet another object of the invention is a method of burning a fuel derived from coal ash. The coal ash having an initial carbon amount and the fuel being produced by, the pneumatic separation of coal ash into at least two size fractions;
the separation taking place in a solid-gas contactor in association, with a classifier means wherein,
the two size fractions comprise and are separated into
a major fine fraction, and
a minor coarse fraction, being the fuel; and containing at least 45% of the initial carbon amount, and
a recovery of the fuel; and
a conveyance of the fuel to a combustion system.
BRIEF DESCRIPTION OF THE DRAWINGS
Further features and advantages of the present invention will become apparent from the following detailed description, taken in combination with the appended drawings :
Fig. 1 is a process flow diagram for producing the fuel derived from coal ash with a single classifier means illustrated.
Fig. 2 is a process flow diagram for producing fuel derived from coal ash, where the fuel is classified and removed from the solid gas contactor.
Fig. 3 is a process flow diagram wherein there are multiple particle size classification steps and intermediate products .
DETAILED DESCRIPTION OF THE PREFERRED EMBODIMENT
Fig. 1, illustrates the process of the separation used to obtain the coal ash derived fuel. The coal ash is introduced into the process via the coal ash inlet (10) near the bottom of the circulating solid gas contactor (100) . The coal ash to be added to the solid gas contactor, according to this invention, should contain at least 5% initial carbon amount (%LOI) , and preferably at least 10% initial carbon and most preferably 14% initial carbon. It must also be noted, that nearly half of the carbon initially present in the coal ash is found in the coarse fraction
(>=63 μm) . This fraction contains at least 45% (w/w) of the initial carbon, and preferably more than 50% (w/w) of the initial carbon.
The type of solid gas contactor represented in Fig. 1 is, a fluidized bed, a circulating fluidized bed, a transport vessel or a classifying transport vessel. These four equipment types would usually be referred to as a fluidized bed reactor, a circulating fluidized bed reactor, a transport reactor or a classifying transport reactor, but because there is only particle classification without a reaction taking place, the word "reactor" has been either omitted or replaced with "vessel".
Gas (22), usually air, is introduced at the bottom of the contactor, via a blower (400) and is distributed evenly in the bottom of the vessel. The gas distributor in the solid-gas contactor may be a perforated plate, although no plate is needed if the solid gas contactor is a transport vessel or classifying transport vessel.
It should be noted that the gas used as the means of separation of the coal ash is typically ambient air (20) and no particular pretreatment other than that required for the efficient operation of the blower is required. However, in some cases, the coal ash may be damp with moisture, the gas (22) may be heated to temperatures where the surface moisture is removed while the carbon content is unaffected. The maximum , gas temperature would be 200 °C but preferably temperatures around 150 °C are used. This heating can be accomplished through combustion of a fuel, or some other hot gas source, with the mixing of the hot gases (21) and ambient air used to attain the relatively low temperatures required. This mixing would occur near the intake of the blower (400) which would be designed to handle the higher temperatures.
The velocity of the gas in the contactor is such, that the coal ash is elutriated almost completely in the gas. The blower is design to be of a sufficient size (pressure and flowrate) to perform this elutriation.
The gas stream with the suspended coal ash particles entrained (24) leaves the contactor and enters a size classifier, which is represented in the flowsheet as one cyclone (200) but can also be a bank of multiple cyclones arranged in parallel. The size classifier is designed to separate the coarse fraction containing carbon from the fine fraction (28) .
The coarse fraction leaving the bottom of the cyclone is split into two streams. The major portion of the stream (26) is returned to the bottom of the solid gas contactor, while the minor portion (30) is the coal ash fuel product. The fuel is recovered in a silo from where it can be transferred towards it eventual utilization. The coal ash fuel obtained is found to have a carbon content of between 40% and 60% and a thermal value between 4000 and 6000 Btu/lb. '
Stream (26) is returned to the solid gas contactor to increase the solids loading in the contactor, which improves the efficiency of separation in the cyclone.
The fine particle size fraction leaving the cyclone (28) is treated in a dust collector (300) where almost all of the fine fraction is collected (32) . The gas leaving the dust collector is typically drawn away by a fan (not shown on the diagram) and depending on the collection efficiency of the dust collector, the gases are exhausted to the atmosphere.
Fig. 2 is very similar to Fig. 1 but represents an embodiment of- the invention where the solid gas contactor has a gas velocity that is reduced in the contactor itself by an increase in the cross sectional area of the contactor or other means. The lower gas velocity will be such that the coarse particles will no longer be elutriated into the classifier and can be collected. The vessel used is a circulating fluidized bed, or a classifying transport vessel and most preferably a toroidal (Torbed™) vessel.
We note that the elutriating gas (22) can once again be optionally heated by the addition of hot gases (21) at the intake of the blower (400) . The elutriated portion of the dust once again enters the cyclone system (24) where two fractions are separated. The fine fraction (28) going towards the dust collector.
The return coarse solid stream (26) from the classifier underflow, once again serves to increase the solids loading in the contactor. The coarse particle stream from the cyclone (26) can be split to obtain another size fraction represented in Fig. 2 as stream (31) .
Furthermore, only one classifier has been represented in Fig. 1 and Fig. 2, but clearly several can be placed in series which would in turn produce multiple size fractions with varying granulometries and carbon% . A process flow diagram of such an arrangement in presented in Fig. 3. This arrangement would be of interest to reduce the size of the dust collector which tend to be more costly than cyclones, and where specific intermediate coarse coal ash size fractions are found to contain high carbon. The main limitation on the number of cyclones would be the size of the blower required, and total equipment capital cost.
In Fig. 3, we see that multiple size fractions (nn) can be recovered from (nnn) classifiers. Clearly such an arrangement can also accommodate a circulating fluidized bed, or a classifying transport vessel similar to that represented in Fig. 2, with its additional product fuel stream.
The fuel derived from fly ash thus obtained can be transported towards a combustion system that is suitable for the combustion of fine combustible solids. The fuel is meant to be used in a same way as coal and in installations that include; coal fired heaters, coal fired boilers, cement kilns and a coal burning power generating stations . The means of transporting the fuel include pneumatic or mechanical means.
Although we have considered the fuel as the coarse fraction its granulometry may be sufficiently fine that dust explosions become a hazard if transported dry and dust clouds are formed. Some combustion systems may require a
larger size fuel feed, such as briquettes, to ensure that the fuel be burned in a safe manner. This may mean that the coal ash fuel requires some further treatment before use. Therefore, if the incinerator, power plant or kiln using the fuel, does not have the means to feed this type of fine fuel into its combustion system, an agglomeration step to produce a fuel briquette may be required before the fuel is fed to combustion. This agglomeration or densification step, will increase the fuel value by at least 15% (becoming 4600 Btu/lb. to 6900 Btu/lb) and reduce the difficulties of handling a combustible powder.
Example 1
Pilot tests were conducted on the fly ash from the Trenton Power Plant, whose coal source is a bituminous coal. The granulometry of the fly ash, as well as, the %LOI of the Trenton fly ash are presented in Table 1. The trials were conducted using a , pilot scale toroidal vessel (Torbed™) which is a pilot size classifying vessel. Table 1 Fly Ash Size Distribution versus Initial %LOI in the sample (Fly Ash from the Trenton Power Plant)
Figure imgf000012_0001
The Torbed™ used in the testing, gave the possibility of removing various size fractions of coal ash directly from the vessel. The air temperature of 20 °C was measured at the inlet of the blower. The two coarse fractions, (>=125 μm and >=63 μm) were removed separately and then re-combined. These two fractions make up 16.0% of the total ash while accounting for 55% of the total carbon in the coal ash, this is a surprising feature of the invention. The thermal value of the combined fraction was measured at 5372 Btu/lb, and the percentage of carbon in the final fuel product obtained is 52.1% weight percentage. The thermal value of the coal ash fuel obtained, places it in the range typically considered that of lignite coal which is between 4000 and 8300 Btu/lb.
It should be noted that although a fine fraction (<45 μm) is also obtained by this process which is lower in carbon than that prior to treatment, the carbon level is not reduced sufficiently to be considered a good source of pozzolanic material for use in concrete. Further treatment of this fine fraction is required if it is to be used in concrete.
Example 2
Similar pilot tests were conducted on fly ash from a Florida power plant which is also derived from a bituminous type of coal. The two fly ash coarse fractions were once again removed and combined, and resulted in a fuel with a weight fraction of 45.4% carbon and a heating value of 5051 Btu/lb. Here it was observed that in a 15% (w/w) of the coal ash, 50.9% (w/w) of the total carbon of the original ash is found. The Florida fly ash properties are presented in Table 2.
Table 2 Fly Ash Size Distribution versus Initial %LOI in the sample (Fly Ash from the Florida Power Plant)
Figure imgf000013_0001
Further tests were conducted with various other coal ashes. The test using a coal ash from a lignite coal source resulted in a fuel product of 1824 Btu/lb for the same particle fraction.
While a test with a coal ash from a sub-bituminous coal source resulted in a fuel value of 4251 Btu/lb for the same size fraction of >=63 μm.
The pilot tests resulted in the selection of the preferred type coal ash source as bituminou's coal with the preferred particle size cut at >=45 μm and preferably >=63 μm.

Claims

1. A process for producing a fuel from a coal ash having an initial carbon amount, comprising;
a pneumatic separation of the coal ash into at least two size fractions;
the separation taking place in a solid-gas contactor in association with a classifier means, wherein
the two size fractions comprise when separated,
a major fine fraction, and
a minor coarse fraction, being the fuel, and containing at least 45% of the initial carbon fuel amount, and
a recovery of the fuel.
2. The process according to claim 1, wherein the initial carbon amount is at least 5% by weight.
3. The process according to claim 1, wherein the initial carbon amount is at least 10% by weight.
4. The process according to claim 1, wherein the initial carbon amount is at least 14% by weight.
5. The process according to any one of claims' 1 to 4, wherein the fine fraction has a particle size distribution of less than 45 μm and the coarse fraction has a particle size distribution of greater than or equal to 45 μm.
6. The process according to any one of claims 1 to 4, wherein the coarse fraction has a particle size distribution greater than or equal to 63 μm.
7. The process according to any one of claims 1 to 6, wherein the fuel has a heating value between 4000 and 6000 Btu/lb.
8. The process according to any one of claims 1 to 7, wherein the solid-gas contactor is selected from the group consisting of a fluidized bed, a circulating fluidized bed, a transport vessel and a classifying transport vessel.
9. The process according to claim 8, wherein the classifying transport vessel is a Torbed™ toroidal vessel .
10. The process according to any one of claims 1 to 9, wherein the separation is conducted at ambient temperature or up to a temperature of 200 °C.
11. The process according to any one of claims 1 to 10, wherein the classifying means is a cyclone or a bank of cyclones .
12. The process according to claim 11, wherein the classifying means may be placed in series to obtain a number of different size fractions.
13. A fuel which is derived from a coal ash having an initial carbon amount and produced by,
a pneumatic separation of the coal ash wherein the coal ash is separated into at least two fractions; the separation taking place in a solid-gas contactor in association with a classifier means,
wherein the two size fractions comprising,
a major fine fraction, and
a minor coarse fraction, being the fuel, and containing at least 45% of the initial carbon fuel amount, and
a recovery of the fuel.
14. The process according to claim 13, wherein the initial carbon amount is at least 5% by weight.
15. The process according to claim 13, wherein the initial carbon amount is at least 10% by weight.
16. The process according to claim 13, wherein the initial carbon amount is at least 14% by weight.
17. A fuel according to any one of claims 13 to 16, wherein the fine fraction has a particle size distribution of less than 45 μm and the coarse fraction has a particle size distribution of greater than or equal to 45 μm.
18. The fuel according to any one of claims 13 to 16, wherein the coarse fraction has a particle size distribution of greater than or equal to 63 μm.
19. The fuel according to any one of claims 13 to 18, wherein the fuel has a heating value between 4000 and 6000 Btu/lb.
20. The fuel according to any one of claims 13 to 19, wherein the circulating solid-gas contactor is selected from the group consisting of a fluidized bed, a circulating fluidized bed, a transport vessel and a classifying transport vessel.
21. The fuel according to claim 20, wherein the classifying transport vessel is a Torbed™ toroidal vessel.
22. The fuel according to any one of claims 13 to 21, wherein the separation is conducted at ambient temperature or up to a temperature of 200 °C.
23. The fuel according to any one of claims 13 to 20, wherein the classifying means is a cyclone or a bank of cyclones.
24. The fuel according to claim 23, wherein the classifying means may be placed in series to obtain a number of different size fractions.
25. A method of burning a fuel derived from a coal ash having an initial carbon amount and produced by,
a pneumatic separation of the coal ash wherein the coal ash is separated into at least two fractions,
the separation taking place in a solid-gas contactor in association with a classifier means,
wherein the two size fractions comprising,
a major fine fraction, and
a minor coarse fraction, being the fuel, and containing at least 45% of the initial carbon fuel amount, and
a recovery of the fuel; and a conveyance of the fuel to a combustion system.
26. The method according to ■ claim 25, wherein before the conveyance of the fuel to the combustion system there is an optional agglomeration step.
27. The method according to claim 26, wherein the agglomeration step is a densification of the fuel into briquettes .
28. The method according to any one of claims 25 to 27, wherein the combustion system is selected from the group consisting of a coal fired heater, a coal fired boiler, a cement kiln and a coal burning power generating station.
PCT/CA2003/001932 2002-12-16 2003-12-15 Fuel from ash WO2004055139A1 (en)

Priority Applications (3)

Application Number Priority Date Filing Date Title
AU2003291895A AU2003291895A1 (en) 2002-12-16 2003-12-15 Fuel from ash
CA002509352A CA2509352A1 (en) 2002-12-16 2003-12-15 Fuel from ash
EP03767353A EP1572843A2 (en) 2002-12-16 2003-12-15 Fuel from ash

Applications Claiming Priority (2)

Application Number Priority Date Filing Date Title
US10/320,069 2002-12-16
US10/320,069 US20040111958A1 (en) 2002-12-16 2002-12-16 Fuel from ash

Publications (2)

Publication Number Publication Date
WO2004055139A1 true WO2004055139A1 (en) 2004-07-01
WO2004055139B1 WO2004055139B1 (en) 2004-09-02

Family

ID=32506788

Family Applications (1)

Application Number Title Priority Date Filing Date
PCT/CA2003/001932 WO2004055139A1 (en) 2002-12-16 2003-12-15 Fuel from ash

Country Status (5)

Country Link
US (1) US20040111958A1 (en)
EP (1) EP1572843A2 (en)
AU (1) AU2003291895A1 (en)
CA (1) CA2509352A1 (en)
WO (1) WO2004055139A1 (en)

Families Citing this family (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
KR101171799B1 (en) * 2010-06-29 2012-08-13 고려대학교 산학협력단 Method for recycling of silica etching waste and method for preparing mesoporous materials
DE102013112210A1 (en) * 2013-11-06 2015-05-07 Thyssenkrupp Ag Process for the purification of bypass gases of the cement or mineral industry as well as the cement or mineral industry
WO2016071575A1 (en) * 2014-11-07 2016-05-12 Fatec Oy Method and apparatus for handling of granular material and use of the method and apparatus for classifying fly ash
CN108339331B (en) * 2018-01-25 2021-11-16 新沂慧科智能科技有限公司 Landfill gas classification detects recycle device

Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4309190A (en) * 1979-10-11 1982-01-05 Metallgesellschaft Ag Process of producing coal briquettes for gasification or devolatilization
AU532788B2 (en) * 1980-12-11 1983-10-13 Texaco Development Corp. Recovery of unconverted solid fuel from ash
US4657561A (en) * 1981-12-22 1987-04-14 Kawasaki Jukogyo Kabushiki Kaisha Method of recovering fuel from coal ash
US5996808A (en) * 1996-03-05 1999-12-07 Levy; Edward Kenneth Fly ash processing using inclined fluidized bed and sound wave agitation
US6457425B1 (en) * 1999-11-02 2002-10-01 Consolidated Engineering Company, Inc. Method and apparatus for combustion of residual carbon in fly ash

Family Cites Families (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US3769053A (en) * 1967-12-04 1973-10-30 Enercon Int Ltd Process for the treatment of fly ash
US5024169A (en) * 1990-02-13 1991-06-18 Borowy William J Process to refine flyash captured from pulverized coal fired boilers and auxiliary equipment
US5160539A (en) * 1991-04-05 1992-11-03 Progress Materials Inc. Method and product of fly ash benefication by carbon burnout in a dry bubbling fluid bed
US5555821A (en) * 1994-12-02 1996-09-17 Martinez; Morris P. Apparatus and process for removing unburned carbon in fly ash

Patent Citations (5)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
US4309190A (en) * 1979-10-11 1982-01-05 Metallgesellschaft Ag Process of producing coal briquettes for gasification or devolatilization
AU532788B2 (en) * 1980-12-11 1983-10-13 Texaco Development Corp. Recovery of unconverted solid fuel from ash
US4657561A (en) * 1981-12-22 1987-04-14 Kawasaki Jukogyo Kabushiki Kaisha Method of recovering fuel from coal ash
US5996808A (en) * 1996-03-05 1999-12-07 Levy; Edward Kenneth Fly ash processing using inclined fluidized bed and sound wave agitation
US6457425B1 (en) * 1999-11-02 2002-10-01 Consolidated Engineering Company, Inc. Method and apparatus for combustion of residual carbon in fly ash

Also Published As

Publication number Publication date
CA2509352A1 (en) 2004-07-01
AU2003291895A1 (en) 2004-07-09
US20040111958A1 (en) 2004-06-17
EP1572843A2 (en) 2005-09-14
WO2004055139B1 (en) 2004-09-02

Similar Documents

Publication Publication Date Title
CA2107571C (en) Fly ash benefication by carbon burnout in a dry bubbling fluid bed
US6808390B1 (en) Process for carbonizing wood residues and producing activated carbon
CN101294765B (en) Low rank coal high temperature flue gas drying method and device
US4887722A (en) Method for beneficiating by carbonaceous refuse
US4259911A (en) Fluidized bed boiler feed system
US4263124A (en) Process for minimizing solids contamination of liquids from coal pyrolysis
CA1097139A (en) Dry coal feed systems for combustion reactors
US4414905A (en) Method and equipment for treatment of fuel for fluidized bed combustion
JP2019107620A (en) Method for manufacturing modified fly ash, and apparatus for manufacturing modified fly ash
US20040111958A1 (en) Fuel from ash
US4047489A (en) Integrated process for preparing and firing bagasse and the like for steam power generation
JP2018171568A (en) Treatment method and treatment apparatus of combustible waste
US4598653A (en) Combustion system for burning fuel having various particle sizes
US6907994B2 (en) Process for converting wet fly ash into dry useful industrial products
US4563264A (en) Method of dry distillation of volatile substances from mineral matter containing same
US20050188608A1 (en) Process for drying coal
US20090045103A1 (en) Thermal coal upgrading process
RU2651827C1 (en) Method of dry beneficiation of high-ash coal
JPS58200921A (en) Combsution of oil coke in fluidized bed type boiler
TWI342334B (en)
AU774667B2 (en) Process for carbonizing wood residues and producing activated carbon
US2833055A (en) Apparatus and method of fluidized drying of carbonaceous fuels
AU2004212548B2 (en) Process for carbonizing wood residues and producing activated carbon
TW434202B (en) Plant for manufacturing cement clinker
AU2003243816B2 (en) Coal drying and charring process

Legal Events

Date Code Title Description
AK Designated states

Kind code of ref document: A1

Designated state(s): AE AG AL AM AT AU AZ BA BB BG BR BW BY BZ CA CH CN CO CR CU CZ DE DK DM DZ EC EE EG ES FI GB GD GE GH GM HR HU ID IL IN IS JP KE KG KP KR KZ LC LK LR LS LT LU LV MA MD MG MK MN MW MX MZ NI NO NZ OM PG PH PL PT RO RU SC SD SE SG SK SL SY TJ TM TN TR TT TZ UA UG US UZ VC VN YU ZA ZM ZW

AL Designated countries for regional patents

Kind code of ref document: A1

Designated state(s): BW GH GM KE LS MW MZ SD SL SZ TZ UG ZM ZW AM AZ BY KG KZ MD RU TJ TM AT BE BG CH CY CZ DE DK EE ES FI FR GB GR HU IE IT LU MC NL PT RO SE SI SK TR BF BJ CF CG CI CM GA GN GQ GW ML MR NE SN TD TG

121 Ep: the epo has been informed by wipo that ep was designated in this application
B Later publication of amended claims

Effective date: 20040719

DFPE Request for preliminary examination filed prior to expiration of 19th month from priority date (pct application filed before 20040101)
WWE Wipo information: entry into national phase

Ref document number: 2509352

Country of ref document: CA

WWE Wipo information: entry into national phase

Ref document number: 2003767353

Country of ref document: EP

WWP Wipo information: published in national office

Ref document number: 2003767353

Country of ref document: EP

NENP Non-entry into the national phase

Ref country code: JP

WWW Wipo information: withdrawn in national office

Country of ref document: JP