The present invention relates generally to removing moisture from coal and more specifically to drying coal, coal fines and coal refuse.
In the continued push for cleaner technology, a concurrent growth trend is the better utilization of existing resources. A common and abundant energy resource is coal. But, there are various concerns and issues associated with coal that challenge the cost-effectiveness and product maximization in the current industry.
Processed coal typically has high moisture content as a result of techniques used to mine coal. Based on the structure of coal, this moisture content is surface level moisture. The inclusion of too much moisture in coal is problematic from both a cost perspective and a use perspective. Coal is processed into varying sizings, including coal, coal fines and coal refuse. Larger sized coal is readily dried using economically feasible methods including vibrating screen for coal pieces greater than 2″ and vibratory stoker centrifuges for pieces between ¼″ and 3″. For smaller coal particles, more intensive methods must be utilized such as vibratory centrifuges which are capable of reducing the moisture content of coal particles having a size between 28 mesh and ½″ to an economically attractive 8% moisture. Current technology is incapable of reducing coal having a size below 28 mesh to a moisture content of 8% or below.
In a typical environment, the coal is sorted by size using known sorting techniques. Then, the coal is segmented, with a lower quality material being separated from the higher quality material by, for example specific gravity in a wet process, the sorted sizes are re-combined and sold based on a corresponding moisture content rating. For coal, greater surface area means higher moisture content because the total moisture in coal is made up largely of surfactant moisture. Therefore, larger coal pieces, by volume, have a lower moisture percentage compared with the same corresponding volume of smaller coal pieces.
Coal fines having typical diameters from approximately 100 to 800 microns, and often smaller diameters, e.g., on the order of 50 microns or less. Traditional methods of drying the coal particles, including centrifugation and heating technologies, can readily dry these coal “fines” to approximately 30% moisture. Methods of drying coal fines beyond this point typically employ blowers and heaters which require capital intensive investment, require substantial energy use, and create environmental problems and hazards both from energy use and from aerosolization of the coal fines. The existing techniques of using coal beyond a moisture content of around 12% typically employs blowers and heaters, which require capital intensive investment, require substantial energy use, and creates environmental problems and hazards. These hazards are from both energy use and aerosolization of the coal.
Current thermal drying techniques cause the loss and therefore the disposal of a portion of the smallest coal pieces, also referred to as coal fines, because based on current thermal drying techniques, there lacks a known means to retain these dried smallest coal pieces. Also, the known thermal drying technique requires that, generally, all of the sellable coal, regardless of its size, must be included in the thermal drying process to prevent the creation of a dangerous and hazardous atmosphere in the thermal dryer caused when only fine coal is placed into the thermal dryer. This requires an excess cost to dry this coal. The costs associated with the highest percent of moisture on the finer sized coal are greater than the return achieved by selling this size coal themselves. As a result, coal fines have been pumped into coal impoundments which represent an environmental hazard and waste of energy resources.
From a cost perspective, customers pay for coal by weight. Inclusion of high moisture content increases the weight of the coal, thus having to be sold at a lower price. Similarly, coal's use for energy purposes is based on the burning of the coal. The inclusion of excess moisture content reduces the effectiveness of the coal because of energy wasted to evaporate off the moisture. When coal is sold, it typically includes a moisture level rating, where a portion of the price is based on this rating. The lower the moisture content, the greater the expected costs for purchasing coal. Accordingly, there has long been a desire to dewater coal fines in order to increase their value in manner that would allow for economic use of coal fines rather than treating it as a byproduct that is simply discarded into impoundments.
The problem of dewatering coal fines has long eluded the coal industry. The abundance of coal impoundments throughout coal producing locales worldwide whereby coal fine slurries are pumped into settlement ponds is a testament to this longstanding problem. For example, the United States Mine Safety and Health Administration oversees over 600 coal impoundments. These coal fine impoundments can lead to safety and environmental concerns from run-off and other associated problems.
Recently attempts at dewatering coal fines have been explored which involve addition of various reagents that further reduce moisture content in filter cakes. For example, Eraydin, “Evaluation of Novel Fine Coal Dewatering Aids,” Masters Thesis, Virginia Polytechnical Institute and State University, Jun. 18, 2004. These treatments included the addition of acid/base (to control pulp pH), sodium carbonate (Na2CO3), ethylenediamine tetraacetic acid (EDTA), sodium silicate (Na2SiO3) to precipitate Ca2+ ions, oxalic acid, succinic acid, ammonium oxalate, Na-hexametaphoshate, calcium oxide and hydrogen peroxide (H2O2) to coal slurries prior to filtration and/or centrifugation. The results showed that the use of sequestrating reagents for water treatment in conjunction with dewatering aids reduced the cake moistures by a greater percentage than by using the reagents alone, the extent of which depend on the particle size, cake thickness, drying time, reagent dosage, conditioning time, reagent type, water chemistry, etc. Although these techniques successfully reduced the water content of coal fines, these technologies still produced coal fines having greater than 20% moisture.
Technologies have been explored outside of the field of coal drying that involve adsorption of water using desiccants and zeolites. These technologies have only been employed where the use of high temperatures degrade the materials which are sought to be dried, such as foodstuffs and materials that are known to chemically react and/or degrade with heat thereby making conventional thermal drying techniques infeasible. For example, U.S. Pat. No. 3,623,233, entitled “Method of Drying a Damp Pulverant,” filed Dec. 3, 1969 to Severinghaus describes heat drying of calcite (CaCO3). Severinghaus teaches that heat drying of calcite results in calcination and production of calcine (CaO), which is detrimental to the use of calcite in fillers and extenders. Similarly, U.S. Pat. No. 6,986,213, entitled “Method for Drying Finely Divided Substances,” filed Jul. 3, 2003 to Kruithof describes drying foodstuffs such as wheat flour which are degraded using thermal drying techniques. The use of such techniques for drying materials such as coal fines that can be dried without degradation using conventional techniques has not been explored.
A longstanding need exists for an economical method and system for drying coal fines to reduce the moisture content and to prevent the substantial loss of coal in the drying process. Any reduction in moisture thereby increases the cost-effectiveness of coal processing.
The present invention provides a method and system for drying coal, coal fines and fine coal refuse using granular drying media. As described herein, coal refers to coal in all available sizings, including coal above coal fines, e.g. 28 mesh and larger, such as but not limited to 1 millimeter, coal fines, e.g. 28 mesh and smaller, as well as the coal fine refuse. The method and system dries the coal by combining them with the granular drying media. While in combination, the mixture is agitated to maximize surface contact with granular drying media. The surface moisture on the coal is then adsorbed by the granular drying media. After a period of agitation, the method and system thereby separates the granular drying media and the coal based on differences in size. The granular media is capable of withstanding agitation in a particulate coal bed for several cycles, readily separated from coal including coal fines, has a large capacity to remove water from the coal particulate surface, and can be regenerated without requiring excessive energy. Preferred granular media according to the present invention are zeolites and desiccants, including preferably activated alumina.
The method and system may use additional techniques for adjusting the volume of coal and/or granular drying medium, as well as or in addition to adjust the agitation time-period to maximize the percentage of moisture removal. The method and system may also dry the granular drying medium to remove the extracted moisture and thus re-use the activated granular drying medium for future moisture removal operations. The method and system may also add the coal having the moisture removed therefrom back into a coal pile having coal pieces of varying sizes for sale.
Thereby, the method and system provides the recapture and utilization of coal by allowing for the removal of moisture using granular drying medium. The utilization of granular drying medium significantly reduces processing inefficiencies found in other processing techniques, as well as being environmentally friendly by eliminating the waste of coal in the existing drying technology.
The invention is illustrated in the figures of the accompanying drawings which are meant to be exemplary and not limiting, in which like references are intended to refer to like or corresponding parts, and in which:
In the following description, reference is made to the accompanying drawings that form a part hereof, and in which is shown by way of illustration specific embodiments in which the invention may be practiced. It is to be understood that other embodiments may be utilized and design changes may be made without departing from the scope of the present invention.
Bulk coal may be separated into various size components using conventional techniques. Larger size coal pieces and particles may be separated and dewatered using conventional techniques. Coal fines may be separated from the bulk water (water in excess of that which is associated with coal fines when they settle, or are filtered or centrifuged out aqueous suspension) used in the mining/recovery process by any one or more of a variety of known techniques. Such techniques include, but are not limited to one or more of, filtration (e.g., gravity based filtration, or filtration assisted by centrifugal force, pressure or vacuum), settling, centrifugation and the like, which can be used singly or in combination. Further amounts of water may optionally be removed from the coal fines by a second round of such treatments.
After one or more separation steps to remove bulk water, the wet coal fines are then mixed with granular drying medium. The granular drying medium preferably includes particles of a water-collecting material or combination of different types of water-collecting materials, e.g., particles of absorbent or adsorbent, to further reduce the amount of water associated with the fines. In one embodiment, the individual granules of drying medium are large enough to be separated from the coal fines by size (e.g., sifting with an appropriate size screen or mesh). In various embodiments, to facilitate their drying, the wet coal fines are mixed with one or more types of granular drying (i.e., water collecting) materials. The granular drying materials include, but are not limited to, molecular sieves, particles of hydratable polymers (e.g., polyacrylate or carboxymethyl cellulose/polyester particles), or desiccants (e.g., silicates).
The rate at which various water-collecting materials adsorb, absorb, or react with water present in coal fines may be affected by temperature. Each type of water-collecting material may have different optimum temperatures for the rate at which they will accumulate water from the coal fines. In some instances, as with molecular sieves, heating/warming the molecular sieves with the coal fines, or heating/warming molecular sieves immediately prior to mixing them with coal fines, may increase the rate at which water becomes associated with the molecular sieves. In other embodiments, materials such as alumina particles may accumulate water at suitable rate from coal fines at room temperature (e.g., about 20-25° C.). Water-collecting materials containing water formerly associated with the coal fines can subsequently be removed from the coal fines by a variety of means.
The system 100 operates to remove moisture from coal by contacting the granular drying medium with the coal (e.g., coal fines). The granular drying medium, as discussed below, is selected based on its ability to adsorb and/or absorb water from the coal, and is particularly adapted to remove surface moisture from the coal. By facilitating surface area contact between the granular drying medium and the coal, the moisture is then transferred out of the coal. Based on sizing differences between the granular drying medium and the coal, the coal may be readily separated from the granular drying medium. Thereby, once the separation occurs, the moisture content of the coal is reduced. The described techniques eliminates the need for energy-intensive drying operations and does not generate any airborne particulates common with the heat-based the drying techniques.
The coal distribution unit 104 introduces coal into the process. The coal to be dried is generated based on the sorting and separation of extracted coal into various sizes. The coal may be generated from known sorting techniques of sorting the coal into smaller and smaller pieces using any number of a variety of techniques, such as multiple screens wherein coal elements of smaller sizes fall through screens for separation. In general, the advantages of the present invention become more apparent as the particle size of the coal to be dried is lowered. Accordingly, the invention is particularly advantageous for coal having a particle size distribution whereby the mean particle size is 1.5 mm or less. Another suitable measure of coal distribution benefiting from the present invention is 28 mesh screen or lower, i.e., coal whereby particles not fitting through a 28 mesh sieve have been excluded. Alternatively, coal where a substantial fraction of the particles are 28 mesh or lower, or 1.5 mm or less, may be beneficially dried according to the present invention.
The combination unit 106 may be any number possible devices for combining the granular drying medium and coal. The combination unit 106 includes functionality for the contacting engagement of the coal with the granular drying medium, plus some degree of agitation. As noted above, the granular drying medium operate by removing surface moisture from the coal. The present inventors have found that increasing the agitation between the coal and drying medium accelerates the drying process by improving the surface contact between the coal and drying medium.
Because moisture in coal exists predominately as surface moisture, removal of surface moisture effectively lowers the moisture content of coal. The granular drying medium is selected based on its ability to attract surface moisture away from the coal surface, thereby overcoming any water that has bonded to surface sites on the coal particle through, for example, hydrogen bonding or other attractive forces.
The separated granular drying medium can be somewhat dusty and can carry a minute amount of coal with them after they have absorbed the water. Once separated, the granular drying medium can be passed to a dryer where they can be dried and sufficient moisture is removed to permit their reuse, if desired. Thus, the granular drying medium can be employed in a closed-loop system, where they are mixed with the coal, and after removing water/moisture (drying) they are separated from the coal and passed through a dryer and reused.
For example, in one embodiment the combination unit 106 may be a circular tube having a circular channel through which the combined mixture of coal and granular drying medium pass. This circular tube may be rotated at a particular speed and the tube extended for a particular distance so the coal and granular drying medium are engaged for a certain period of time. Typically, the longer the contact time between the granular drying medium and the coal, the more moisture that is removed. One way to increase contact time is to connect two or more combination units in a serial manner. As described in further embodiments below, additional feedback can be implemented to adjust the operating conditions of the combination unit 106 and thus adjust the moisture level of the coal. The ratio between granular drying medium and coal may range between 4 parts granular drying medium beads to 1 part wet coal to 1 part granular drying medium beads to 1 part wet coal, depending on the desired moisture content of the final product.
Another embodiment of the combination unit 106 may be an agitation device or other platform that includes vibration or rotation to increase surface area contact between the coal and the granular drying medium. Additional examples of the combination unit 106, may be utilized so long as they provide for the above-described functionality of facilitating contact between the coal and the granular drying medium.
Additional embodiments of mixers may include internal rotor mixers, continuous mixers, blenders, double arm mixers, planetary mixers, ribbon mixers and paddle mixers. Based on the various characteristics of the desiccants and the coal fines, different mixer embodiments provide varying degrees of moisture removal. The various types of mixers allow for customization of the agitation of granular drying medium and coal fines for moisture reduction, as well as processing for the re-usability of the granular drying medium in the continuous flow process.
The separator 108 may be any suitable separation device recognized by one skilled in the art. The separator 108 operates using known separator techniques, including for example in one embodiment vibration and vertical displacement. The separator 108 operates by, in one embodiment, providing holes or openings of an appropriate size that the granular drying medium will not pass through, but the coal readily pass therethrough. For example, one embodiment may include a high frequency, low amplitude circular screen for filtering the coal from the granular drying medium.
One embodiment of the operation of the system 100 is described relative to the flowchart of
The granular drying medium distribution unit 102 releases a predetermined volume of granular drying medium beads at a predetermined rate. This volume of beads is in proportion to the volume of coal. As noted above, the ratio of granular drying medium to coal generally ranges from 4:1 to 1:1. Both units 102 and 104 dispense the corresponding elements into the combination unit 106. One embodiment may rely on gravity to facilitate distribution, as well as additional conveyor or transport means may be used to direct the elements from the distribution units 102 and 104 to the combination unit 106. For example, one embodiment may include conveyor belts to move the coal and/or granular drying medium into the combination unit 106.
Once the combination unit 106 is charged with granular drying medium and coal, the next step of the method of
After the agitation of coal and granular drying medium in the combination unit 106, the mixture is passed to the separator 108. In one embodiment, a conveyor belt or any other movement means may be used to pass the mixture to the separator 108. In the method of
The moisture removal system 142 is a system that operates to remove the moisture from the granular drying medium 112. In one embodiment, the system 142 may be a microwave system that uses microwaves to dry the sieves. The imposition of microwaves heats up the sieves and causes the evaporation of the water molecules therefrom. The microwave signal strength and duration are determined based on calculations for removing the moisture and can be based on the volume of granular drying medium. For example, the large the volume of granular drying medium, the longer the duration of the drying and/or the higher the power of the microwave may be required. One particularly preferred example of a moisture drying system is shown in
Other embodiments may be utilized for the moisture removal system, wherein other usable systems include operations for removing moisture from the granular drying medium. For example, one embodiment may be a heating unit that uses heat to cause the moisture evaporation. Regardless of the specific implementation, the moisture removal system 142 thereby returns the granular drying medium to a state similar or identical to their state prior to insertion in the combination unit 106 by causing the moisture to be removed and/or eradicated from therefrom, thus generating the dried granular drying medium.
Additional systems for moisture removal from the granular drying media include a heating unit that uses heat to cause the moisture evaporation. Other types of dryers can include direct rotary drying systems, indirect rotary drying systems, catalytic infrared drying systems, bulk drying systems, pressure swing absorption systems, temperature swing absorption systems, aero-flight open chain conveyor drying systems, and, microwave drying systems. Exemplary drying systems that can be used in accordance with the present invention are shown in
The analyzer 146 is a moisture analyzing device that is operative to determine the moisture level of coal as it passes through the analyzer. The analyzer 146 may be any suitable type of moisture analysis device recognized by one skilled in the art, such as but not limited to a product by Sabia Inc. that uses a prompt gamma neutron activation (PGNA) elemental analysis combined with their proprietary algorithms to measure real time moisture content of a moving stream of coal on a belt using an integrated analyzer feature contained in their SABIA X1-S Sample Stream Analyzer. SABIA Inc. can also provide their coal blending software CoalFusion to further automate the moisture content measurement process.
For the sake of brevity, operations of one embodiment of the system 140 are described relative to the flowchart of
In the process of
The next steps of the method of
As illustrated in the system 140 of
Further illustrated in this embodiment, the system 140 is a continuous flow system such that in normal operations, the method of
In drying coal, it is not necessary to completely remove all moisture, but rather drying seeks to achieve a target range of moisture content. This moisture content then translates into an overall moisture content per weight, e.g. tonnage, of coal. The sale of coal being based on the moisture content, this embodiment allows for refinement of the coal drying process for coal based on accurate measuring of the moisture content. It is further noted that different types of coal having different drying characteristics, where the different types of coal typically vary based on the region or location where the coal is extracted from the earth, therefore the specific characteristics of the coal itself needs to be taken into account when determining the desired moisture content range for the drying operation using granular drying medium.
In one embodiment, following the step of forming an admixture of the coal fines with the granular drying material, at least 25% of the water (by weight) in the composition is associated with the water-collecting material. In other embodiments, the amount of water by weight that is associated with the water-collecting material is at least 30%, at least 35%, at least 40%, at least 45%, at least 50%, at least 55%, at least 60%, at least 65%, at least 70%, at least 75%, at least 80%, at least 85%, or at least 90%.
Step 160 is a decision step to determine if the moisture content is above or below a predetermined moisture level. By way of example and not meant to be a limiting value, the combination unit 106 may seek a moisture level at 9.5 percent within a standard deviation range. For example, the final level of moisture in the coal may be between 7.6 and 11.4 percent, preferably between 8.5 and 10.5 percent, and most preferably about 9.5 percent. If the moisture level is above or below that value, step 162 is to adjust the agitation reverting the process back to step 154. Step 162 represents one possible embodiment for adjusting the moisture level, wherein the system 140 is a continuous flow system such that the feedback loop 148 would adjust the combination unit 106 for current coal drying operations, not the drying of the coal already past the separator 108.
In one embodiment, the combination unit 106 may be a rotational unit including an actuator that controls the rotational speed. Based on the feedback loop 148, this may increase or decrease the speed. For example, if the moisture level is below the desired percentage, this implies that too much moisture is being removed and therefore the amount of contacting engagement between the coal and granular drying medium is too long such that the rotational speed is increased. Conversely, if the moisture level is too high, this may indicate the desire to slow down the combination unit 106 to increase the amount of surface engagement time.
Concurrent with the moisture level measurement by the analyzer 146, the method of
In the method of
With respect to the feedback loop 148, it is recognized that other modifications may be utilized and the feedback is not expressly limited to the combination unit 106. For example, in one embodiment the granular drying medium dispensing unit may include a flow regulator that regulates the volume of granular drying medium released into the combination unit 106. The adjustment of the volume of granular drying medium may be adjusted to change the moisture level of the coal, such as if there are more granular drying medium, it may provide for reducing more moisture and vice versa. In another embodiment, the feedback loop may provide for adjustment of the dispensing rate of coal from the coal distribution device 104.
Thereby, the various embodiments provide methods and systems for drying coal. The drying utilizes granular drying medium. Prior uses of granular drying medium were related primarily to gas and liquid applications because of the nature of passing molecules between and across the openings in these sieves and therefore was inapplicable to solids, such as to coal. Additionally, prior techniques for drying coal focused significantly on legacy technologies due to the infrastructure costs for building these drying systems, along with known environmental hazards which are currently permitted, as well as costs associated with trying new technologies. Therefore in addition to the inapplicability of granular drying medium to solids, the coal processing arts includes an inherent resistance to new technologies for cost and logistical concerns. As described above, the method and system overcome the shortcomings of drying coal with the application of granular drying medium in a new technological fashion.
I. Continuous Drying of Coal with Granular Drying Media
When an array of mixers is used as shown in
After mixing, the dried coal and moist granular drying media are separated using separator 504. The separator 504 can include one or more screens. As shown in
The moist granular drying media is routed from the separator 504 to the continuous drying unit (bead regeneration unit 702) in stream 510 as shown in
The granular drying media enters the drying unit in stream 510 as shown in
The continuous process according to the present invention drastically reduces the relative cost of drying fine coal relative to thermal drying as shown in
The present continuous process also outperforms traditional technologies for removing moisture such as a screenbowl or Centribaric™ systems. Specifically, the present process allows for reduction of moisture to below 10% regardless of the amount of fine coal material (smaller than 325 mesh) in the product feed. For example, a screenbowl is only capable of achieving moisture content below 10% when the level of fine coal is below 10% whereas the present invention will reduce the moisture of a coal feed consisting entirely of fine coal (smaller than 325 mesh) to below 10%.
The present invention provides a predictable and controllable method for reducing the moisture content of fine coal as shown in
Several types of granular drying media have been found efficacious for drying coal fines. As noted above, the preferred granular drying media can absorb significant quantities of water (e.g., up to 28% of its own weight), is capable of withstanding agitation in a particulate coal bed for several cycles, is readily separated from coal including coal fines, has a large capacity to remove water from the coal particulate surface, and can be regenerated without requiring excessive energy. Preferred granular media according to the present invention are zeolites and desiccants, including preferably activated alumina. The process when used with a preferred granular drying media will provide one or more desirable benefits such as a reduction in one or more of time, energy, cost, and/or adverse environmental impact, as compared to conventional processes for drying wet coal fines. Moreover, embodiments of this disclosure can substantially reduce the aerosolization of coal fines by blowers, which can pose health, fire and explosion hazards.
Although embodiments described herein do not require the drying and reuse of granular drying media, it is desirable that the granular drying media is reused one or more times. Embodiments described herein thus employ the drying and reuse water-collecting materials such as absorbents and adsorbents. In other embodiments all or a portion of the water-collecting material can be discarded, e.g., where an absorbent is degraded and cannot be effectively separated from the coal fines. In one embodiment, particles of water-collecting materials are separated by sieving or sifting to remove degraded particles which may be larger than particles of coal fine, but are smaller than desirable for processing wet coal fines. In other embodiments, some or all of the absorbent materials employed for use in removing moisture from coal fines may be biodegradable. The water-collecting material also may bond with the water to cause the water to be associated with the material instead of the coal fines.
The granular drying media of the present invention desirably results in low attrition rates when utilized in a continuous process of coal moisture reduction.
Molecular sieves are materials containing pores of a precise and uniform size (pore sizes are typically from about 3 to about 10 Angstroms) that are used as an adsorbent for gases and liquids. Without wishing to be bound by any theory, generally molecules small enough to pass through the pores are adsorbed while larger molecules cannot enter the pores. Molecular sieves are different from a common filter in that they operate on a molecular level. For instance, a water molecule may not be small enough to pass through while the smaller molecules in the gas pass through. Because of this, they often function as a desiccant. Some molecular sieves can adsorb water up to 22% of their dry weight. Molecular sieves often include aluminosilicate minerals, clays, porous glasses, microporous charcoals, zeolites, active carbons (activated charcoal or activated carbon), or synthetic compounds that have open structures through or into which small molecules, such as nitrogen and water can diffuse. In some embodiments, the molecular sieves are an aluminosilicate mineral (e.g., andalusite, kyanite, sillimanite, or mullite). In other embodiments, the molecular sieves comprise about 10%, 20%, 30%, 40%, 50%, 60%, 65%, 70%, 75%, 80%, 85%, 90%, 95%, 98%, 99% or greater (on a weigh basis) of an aluminosilicate mineral. In some embodiments, including those embodiments where the molecular sieves comprise an aluminosilicate mineral, the particles of molecular sieves may contain other minerals, such oxides of zirconium or titanium to enhance properties such as strength and wear (e.g., zirconia toughened aluminosilicates or alumina-titanate-mullite composites). In some embodiments the molecular sieves are 3 angstrom molecular sieves (e.g., MS3A4825 molecular sieves with 2.5-4.5 mm bead size and 14 lb crush strength from Delta Enterprises, Roselle, Ill.) or 4 angstrom molecular sieves (e.g., MS4A4810 molecular sieves with 2.5-4.5 mm bead size and 18 lb crush strength from Delta Enterprises, Roselle, Ill.).
A variety of molecular sieves can be employed alone or in combination to remove water or moisture from coal fines. In one embodiment, molecular sieves may be selected from aluminosilicate minerals, clays, porous glasses, microporous charcoals, zeolites, active carbons, or synthetic compounds that have open structures through or into which small molecules, such as nitrogen and water can diffuse. In other embodiments, molecular sieves may be selected from aluminosilicate minerals, clays, porous glasses, or zeolites.
Molecular sieves with pores large enough to draw in water molecules, but small enough to prevent any of the coal fines from entering the sieve particles, can be advantageously employed. Hardened molecular sieves or molecular sieves, or those with an especially hard shell, are useful in the methods described herein as such sieves will not be readily worn down and can be reused after removal of moisture.
In some embodiments molecular sieve particles are greater than 1, 1.25, 1.5, 1.75, 2.0, 2.25 or 2.5 mm in diameter and less than about 5 mm or 10 mm. In other embodiments the molecular sieve particles are greater than about 12, 14, 16, 18, 20, 22, 24 or 26 mm in diameter and less than about 28, 30 or 32 mm in diameter. When mixed with the wet coal fines having excess moisture (wet coal fines), the molecular sieves quickly draw the moisture from the coal fines. As the sieves are larger than the coal fines (e.g., over a millimeter in diameter), the mixture of sieves and coal fines can be lightly bounced on a fine mesh grid, where the dry coal fines can be separated from the molecular sieves. The separated molecular sieves can be a bit dusty and can carry a minute amount of coal fines with them after they have absorbed the water. Once separated, the molecular sieves can be passed to a heater where they can be dried and sufficient moisture is removed to permit their reuse if desired. Thus, the molecular sieves can be employed in a close-loop system, where they are mixed with the coal fines, and after removing water/moisture (drying) they are separated from the coal fines and passed through a heater and reused. Minimal agitation is required during dry the sieves.
Hydratable polymeric materials or compositions comprising one or more hydratable polymers may be employed to reduce the moisture content of coal fines (e.g., polyacrylate or carboxymethyl cellulose/polyester particles/beads).
In one embodiment the hydratable polymeric materials is polyacrylate (e.g., a sodium salt of polyacrylic acid). Polyacrylate polymers are the superabsorbents employed in a variety of commercial products such as in baby's diapers, because of their ability to absorb up to 400% of their weight in water. Polyacrylates can be purchased as a come a translucent gel or in a snowy white particulate form. Suitable amounts of polyacrylic acid polymers (polyacrylates) sufficient to adsorb the desired amounts of water from coal fines can be mixed with the fines, to quickly dry coal. The polyacrylate, which swells into particles or “balls,” may be separated from the coal fines on suitable size filters or sieves. The particles or “balls” can either be discarded or recycled by drying using any suitable method (direct heating, heating by exposure to microwave energy, and the like).
The properties of hydrateable polymers, including polyacrylate polymers, may be varied depending on the specifics of the process being employed to dry the coal fines. A skilled artisan will recognize that the properties (gel strength, ability to absorb water, biodegradability etc.) are controlled to a large degree by the type and extent of the cross-linking that is employed in the preparation of hydratable polymers. A skilled artisan will also recognize that it may be desirable to match the degree of cross-linking with the mechanical vigor of the process being used dry the coal fines and the number of times, if any, that the particles are intended to be reused in drying batches of coal fines. Typically, the use of more cross-linked polymers, which are typically mechanically more stable/rigid, will permit their use in more mechanically vigorous processes and the potential reuse of the particles.
In another embodiment the hydratable polymer composition employed is a combination of carboxymethylcellulose (CMC) and polyester (e.g., CMC gum available from Texas Terra Ceramic Supply, Mount Vernon, Tex.). Such compositions, or other super adsorbent hydratable polymeric substances, can be used to remove water from coal fines in a manner similar to that described above for molecular sieves or polyacrylate polymer compositions.
In other embodiments, desiccants are used as water-collecting materials to dry coal fines. A variety of desiccation agents (desiccants) may be employed to reduce the moisture content of coal fines including, but not limited to, silica, alumina, and calcium sulfate (Drierite, W. A. Hammond Drierite Col Ltd Xenia, Ohio) and similar materials. Desiccants, like the compositions described above can be used to remove water from coal fines in a manner similar to that described above for molecular sieves or polyacrylate polymer compositions.
In some embodiments, the desiccant material is comprised of activated alumina, a material that is effective in absorbing water. Without wishing to be bound by any theory, activated alumina's efficiency as a desiccant is based on the large and highly hydrophilic surface area of activated alumina (on the order of 200 m2/g) and water's attraction (binding) to the activated alumina surface. Other materials having high-surface areas that are hydrophilic are contemplated, e.g., materials that have hydrophilic surfaces and surface areas greater than 50 m2/g, 100 m2/g or 150 m2/g. In some embodiments the desiccant comprises about 10%, 20%, 30%, 40%, 50%, 60%, 65%, 70%, 75%, 80%, 85%, 90%, 95%, 98%, 99% or greater (on a weigh basis) of alumina.
Activated alumina is a very hard, durable ceramic capable of withstanding significant abrasion and wear, however, the wear resistance and mechanical properties of activated alumina may be enhanced by introducing other materials into particles of water-collecting materials that comprise alumina. In some embodiments, desiccants comprising alumina may contain about 0.5%, 1%, 2%, 3%, 4%, 5%, 6%, 7%, 8%, 9%, 10%, 15%, 20%, 25%, 30%, 40%, 50%, 60%, 70%, 80%, or 90% or more of other minerals, such oxides of zirconium or titanium to enhance properties such as strength and wear (e.g., zirconia alumina or zirconia toughened alumina ZTA).
Activated alumina has been found to provide advantages relative to the use of molecular sieves. The surface of activated alumina is hydroxylated which strongly attracts water to its surface and associates water through hydrogen bonding. This provides certain advantages relative to molecular sieves discussed in prior co-pending U.S. patent application Ser. No. 12/924,570 describes processing coal fines using varying desiccants, including molecular sieves.
Activated alumina is manufactured from aluminium hydroxide by dehydroxylating it in a way that produces a highly porous material; this material can have a surface area significantly over 200 square meters/g. It is made of aluminium oxide (alumina; Al2O3). It has a very high surface-area-to-weight ratio. The porous nature of activated alumina exhibits tunnel-like structures running throughout the particle which allow absorption of significant moisture to the porous surface.
Activated alumina with pores large enough to draw in water molecules, but small enough to prevent any of the coal from entering the particles, can be advantageously employed. Hardened activated alumina also provide the benefit of not breaking down as easily and are readily re-usable once the absorbed water is removed, as described below. In another embodiment, the activated alumina may include magnetic properties for separation from the coal using magnetic forces, if applicable.
A variety of activated alumina can be employed alone or in combination to remove water or moisture from coal as described in further detail below. Hardened granular drying medium also provide the benefit of not breaking down as easily and are readily re-usable once the absorbed water is removed, as described below.
In some embodiments activated alumina particles, in the form of beads, are greater than 1, 1.25, 1.5, 1.75, 2.0, 2.25 or 2.5 mm in diameter and less than about 5 mm or 10 mm. When mixed with the wet coal having excess moisture, the activated alumina quickly draw the moisture from the coal. As the particles are larger than the coal (e.g., over a millimeter in diameter), the mixture of activated alumina and coal can be readily separated based on size.
A particularly desirable activated alumina particle for use as a granular drying media in accordance with the present invention is a spherically-shaped activated alumina spheres. The activated alumina particles preferably have a uniform size and sphericity that makes subsequent separation of these particles from the coal particularly efficient. The diameter of the alumina particles preferably range from approximately 0.1 mm to 10 mm in diameter, preferably approximately 2.0 mm to approximately 4.7 mm, more preferably between about 3.0 and about 3.4 mm, and most preferably about 3.2 mm. The activated alumina also preferably has a high crush strength which allows for lower attrition and longer use. For example, the crush strength is greater than 25 lbf, more preferably about 30 lbf, and most preferably 35 lbf or more. The activated alumina preferably has a large surface area, which is preferably greater than 340 m2/g and most preferably about 350 m2/g. In general, the pore volume is about 0.5 cc/g, the bulk density is 48 lbs/ft3 (769 kg/m3), the crust strength is 30 lbs (14 kg) and abrasion loss is preferably less than 0.1 wt %.
As described above, a variety of water-collecting materials may be employed in systems for removing water from wet (or moist) coal fines. Such water-collecting materials include those that absorb water, those that adsorbs water, and those that bonds or react with water. Typically the water-collecting materials will be in the form of particles that can be of any shape suitable for forming an admixture with the wet (or moist) coal fines and that are capable of being recovered. Such particles may be irregular in shape, or have a regular shape. Where particles are not irregular in shape they may be of virtually any shape. In one embodiment, particles that are generally or substantially spherical, or generally or substantially oblate, or prolate may be employed. Suitable particle shapes also include cylindrical or conical particles, in addition to regular polygons such as icosahedral particles, cubic particles and the like. During use and reuse the particles may become abraded altering their shape.
Particles for use in the methods and systems for removing water (e.g., reducing the moisture content) of from coal fines described herein can be of a variety of sizes. In one embodiment, where the water-collecting materials are in the form of particles, the particles have an average size that is at least: 2, 3, 4, 6, 7, 8, 9, 10, 12, 14, 16, 18, 20, 25, or 30 times greater than the average size of the coal fines, which are typically in the range of 100 to 800 microns. In one embodiment the difference in size is based upon the difference in the average size of the largest dimension of the particles and coal fines.
Particles of water-collecting materials, including those that are spherical or substantially spherical, may have an average diameter (or largest dimension) that is at least: 1, at least 1.25, at least 1.5, at least 1.75, at least 2.0, at least 2.25, at least 2.5 mm, or at least 4 mm where the average diameter (or largest dimension) is less than about 5 mm, 7.5 mm, 10 mm or 15 mm. In another embodiment, the systems may employ particles that have an average diameter (or largest dimension) that is greater than about 4, 5, 6, 8, 10, 12, 14, 16, 18, 20, 22, 24 or 26 mm and less than about 28, 30 or 32 mm.
In embodiments where particles have an irregular shape, or are not spherical or substantially spherical, they may have a largest dimension that is at least: 1, at least 1.25, at least 1.5, at least 1.75, at least 2.0, at least 2.25, at least 2.5 mm, or at least 4 mm, and less than about 5 mm, 7.5 mm, 10 mm or 15 mm. In another embodiment, the methods and systems described herein may employ irregular or non-spherical particles that have a largest dimension that is greater than about one of 4, 5, 6, 8, 10, 12, 14, 16, 18, 20, 22, 24 or 26 mm and less than about one of 28, 30 or 32 mm.
In one embodiment the water-collecting materials are desiccants, such as activated alumina desiccants, which are manufactured in multiple forms. In some embodiments the desiccants particles used for water-collecting materials, which may be spherical or substantially spherical, are greater than about 1, 1.25, 1.5, 1.75, 2.0, 2.25 or 2.5 mm in diameter and less than about 5 mm or 10 mm in diameter. In other embodiments the desiccant particles have an average diameter or greatest dimension that is greater than about 4, 5, 6, 8, 10, 12, 14, 16, 18, 20, 22, 24 or 26 mm in and less than about 28, 30 or 32 mm. In one set of embodiments the desiccant particles are spheres (or substantially spherical) with diameters (e.g., average diameters) in those size ranges. In other embodiments, the desiccant particles are spheres (or substantially spherical) in sizes up to or about 6 mm in diameter. In other embodiments the desiccants are spherical or substantially spherical particles comprised of alumina having a size in a range selected from: about 2 mm to about 4 mm, about 4 mm to about 8 mm, about 8 mm to about 16 mm, about 16 mm to about 32 mm, about 5 mm to about 10 mm, about 8 mm to about 20 mm, and about 16 mm to about 26 mm. In still other embodiments, the water collecting materials are spherical or substantially spherical alumina particles having an average diameter of about: 4, 6, 8, 10, 12, 14, 16, 18, 20, 22, 24, 26, 28, 30, or 32 mm.
F. Separation by Size and/or Magnetic Means
Water-collecting materials may be separated from coal fines by any suitable technique including filtering, sieving or sifting, or the use of a stream of gas to carry coal fines away from larger and/or heavier particles water-collecting materials.
The separation of all types of water-collecting materials (e.g., molecular sieves, desiccants, or hydratable polymers) may also be accomplished using magnetic separation equipment where the water-collecting materials comprise material capable of, or susceptible to, being attracted by a magnet. Materials that render water-collecting materials capable of being attracted by a magnet include magnetic material and ferromagnetic material (e.g., iron, steel, or neodymium-iron-boron). Water-collecting materials need only comprise sufficient magnetic materials to permit their separation from coal fines. The amount of magnetic material employed permit the separation of water-collecting particles from coal fines will vary depending on, among other things, the strength of the magnet, the size of the particles, and the depth of the bed of coal fines from which the particles are to be collected. The amount of magnetic material may be greater than about 10%, 20%, 30%, 40%, 50%, 60%, 65%, 70%, 75%, 80%, 85%, or 90% of the total weight of the water-collecting material on a dry weight basis. In some embodiments the magnetic materials will be iron or an iron containing material such as steel.
Regardless of the magnetic material employed to render water-collecting materials susceptible to magnetic collection, the magnetic materials may be arranged in the water-collecting material as a solid core or as dispersed particles or layers within the water-collecting materials. Where dispersed particles employed are employed, they may be spread uniformly throughout the water-collecting material. In one embodiment the magnetic material is comprises iron containing particles that are admixed with water-collecting materials such as alumina or mullite prior to forming into pellets that will fired into a ceramic type of material. In still other embodiments the water-collecting materials may contain layers of materials that render the particles susceptible to attraction by a magnet (e.g. iron or steel). Examples of magnetic alumina particles that may be used as water-collecting materials may be found in U.S. Pat. No. 4,438,161 issued to Pollock titled Iron-containing refractory balls for retorting oil shale.
Coal fines (15 g) with a moisture content of 30% by weight were mixed with molecular sieves having a pore sizes of 3 angstroms (15 g, product MS3A4825 2.5-4.5 mm bead size from Delta Adsorbents, which is a division of Delta Enterprises, Inc., Roselle, Ill.) for about 60 minutes thereby drying the coal fines to <5% moisture by weight. After separating the coal fines from the sieves by sifting, the molecular sieves were weighed and dried in a 100° C. oven. The coal fines were weighed periodically to determine the length of time necessary to drive off the water absorbed from the coal. The data is plotted in
Coal fines (15 g) with a moisture content of 30% by weight are mixed with a polyacrylate polymer (0.5 g Online Science Mall, Birmingham, Ala.) for about 1 minute thereby drying the coal fines to <5% moisture by weight. After separating the coal fines from the polymer gently sifting the mix, the molecular polyacrylate polymer particles are recovered for reuse after drying.
Coal fines (100 g) with a moisture content of 21% by weight are mixed with activated alumina beads (6 mm diameter, AGM Container Controls, Inc, Tucson, Ariz.) for about 10 minutes, thereby drying the coal fines to about 7% moisture by weight. After separating the coal fines from the polymer gently sifting the mix, the activated alumina beads are recovered for reuse after drying.
The foregoing description of the specific embodiments so fully reveals the general nature of the invention that others can, by applying knowledge within the skill of the relevant art(s) (including the contents of the documents cited and incorporated by reference herein), readily modify and/or adapt for various applications such specific embodiments, without undue experimentation, without departing from the general concept of the present invention. Such adaptations and modifications are therefore intended to be within the meaning and range of equivalents of the disclosed embodiments, based on the teaching and guidance presented herein.
The present application is a continuation-in-part of patent application Ser. No. 13/168,186 entitled “COAL DRYING METHOD AND SYSTEM” filed Jun. 24, 2011 which continuation-in-part of patent application Ser. No. 12/924,570 entitled “COAL FINE DRYING METHOD AND SYSTEM” filed Sep. 30, 2010 which claims benefit from U.S. Provisional Patent Application Ser. No. 61/247,688 filed Oct. 1, 2009. The contents of these applications are incorporated by reference in their entirety.
Number | Date | Country | |
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61247688 | Oct 2009 | US |
Number | Date | Country | |
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Parent | 13168186 | Jun 2011 | US |
Child | 13841003 | US | |
Parent | 12924570 | Sep 2010 | US |
Child | 13168186 | US |