This invention relates to an apparatus for sorting materials. More particularly, the invention relates to an apparatus that employs closed-system air separation to sort and recover materials from recyclable materials.
Recycling of waste materials is highly desirable from many viewpoints, not the least of which are financial and ecological. Properly sorted recyclable materials often can be sold for significant revenue. Many of the more valuable recyclable materials do not biodegrade within a short period. Therefore, recycling such materials significantly reduces the strain on local landfills and ultimately the environment.
Typically, waste streams are composed of a variety of types of waste materials. One such waste stream is generated from the recovery and recycling of automobiles or other large machinery and appliances. For example, at the end of its useful life, an automobile will be shredded. This shredded material can be processed to recover ferrous metals. The remaining materials, referred to as automobile shredder residue (ASR) typically would be disposed in a landfill. Recently, efforts have been made to recover additional materials from ASR, such as plastics and non-ferrous metals. Similar efforts have been made to recover materials from whitegood shredder residue (WSR), which are the waste materials left over after recovering ferrous metals from shredded machinery or large appliances. Other waste streams may include electronic components, building components, retrieved landfill material, or other industrial waste streams. These materials generally are of value only when they have been separated into like-type materials. However, in many instances, cost-effective methods are not available to effectively sort waste streams that contain diverse materials. This deficiency has been particularly true for non-ferrous materials, and particularly for non-metallic materials, such as high density plastics, and non-ferrous metals, including copper wiring. For example, one approach to recycling plastics has been to station a number of laborers along a sorting line, each of whom manually sorts through shredded waste and manually selects the desired recyclables from the sorting line. This approach is not sustainable in most economies because the labor cost component is too high. Also, while ferrous recycling has been automated for some time, mainly through the use of magnets, this technique is ineffective for sorting non-ferrous materials. Again, labor-intensive manual processing has been employed to recover wiring and other non-ferrous metal materials. Because of the cost of labor, many of these manual processes are conducted in other countries and transporting the materials to and from these countries adds to the cost.
Copper wiring and other valuable non-ferrous metals can be recovered and recycled. However, waste materials, including ASR and WSR, must be separated from a concentrated mass of recoverable materials. Typically, the waste materials will include wood, rubber, plastics, glass, fabric, and copper wiring and other non-ferrous metals. The fabric includes carpet materials from the shredded automobiles. Often, the fabric includes embedded ferrous materials accumulated during the shredding process. Methods are known for separating the non-ferrous metals from these other materials. These methods may include a “pre-concentration” process that roughly separates the materials for further processing. However, these methods typically involve density separation processes. These processes typically involve expensive chemicals or other separation media and are almost always a “wet” process. These wet processes are inefficient for a number of reasons. After separation, often the separation medium must be collected to be reused. Also, these wet processes typically are batch processes, and they cannot process a continuous flow of material.
Another known system uses an air aspirator, or separator, to separate a light fraction of materials, which typically contains the waste materials that are not worth recovering (that is, the wood, rubber, and fabric), from a heavy fraction of materials, which typically includes the metals to be recovered. These types of separators are known in other industries as well, such as the agricultural industry, which uses air separators to separate materials of differing densities. However, these known systems usually employ open systems, where air is moved through the system and then released to the atmosphere. One problem with these systems is that they need air permits to operate, which adds cost to the system.
Conventional systems also force air directly up from a bottom of the plenum, and the material being separated falls on top of a screen at the bottom of the plenum. Accordingly, such systems cannot process heavy materials because the heavy materials will damage the screen when those materials fall on top of the screen.
Accordingly, a need exists in the art for a system and method that processes materials to be separated while recycling air in a closed system. Additionally, a need exists for a system and method that can separate heavier materials without damaging the system.
The invention relates to a closed air system for separating materials. A fan directs air into a plenum in which the materials are separated. A heavier fraction of the materials falls through the air in the plenum to the bottom of the plenum. A stream of air carrying a lighter fraction of the materials exits the plenum and is directed to an expansion chamber. In the expansion chamber, the lighter fraction of the materials falls to the bottom as the velocity of the air slows. The air then flows from the expansion chamber to a centrifugal filter, which removes remaining material from the air. The air then returns to the fan where it is re-circulated through the system.
The separated materials can be removed from the system at the bottom of the plenum, the bottom of the expansion chamber, and the bottom of the centrifugal filter. Rotary Valves (“Air Locks”) at these locations prevent air from flowing therethrough while allowing the materials to pass.
Referring to the drawings, in which like numerals represent like elements, aspects of the exemplary embodiments will be described.
With reference to
An air flow producing device 102 produces air flow in the system 100 in the direction of the arrows illustrated in
The air flow producing device 102 pushes air into the air intake 104. The air then flows from the air intake 104 through a lower transition 106, through an air reducer 107, and into a plenum 108. The air reducer 107 comprises a butterfly valve 502 (
The plenum 108 includes two sections, a lower plenum 108a and an upper plenum 108b. The air enters the lower plenum 108a via a lower entrance 108c in the lower plenum 108a.
Material to be separated is introduced into the system 100 at location A via an intake feeder (not shown). The material to be separated is fed into a first rotary valve 110 (A), which allows the material to fall into the upper plenum 108b via an upper entrance 108d in the upper plenum 108b. The first rotary valve 110 (A) also prevents all or a substantial amount of air from exiting the system 100 via the upper entrance 108d in the upper plenum 108b. The rotary valve 110 (A) prevents a sufficient amount of, in some cases all, air from exiting the system 100 to maintain the desired static pressures and air flows therein.
The air flows through the air intake 104, into the plenum 108, and up the plenum 108, where it interacts with the material to be separated as the material to be separated falls through the plenum 108 via the force of gravity.
The movement of air through the material to be separated causes lighter material to be entrained in the air flow while heavier material falls through the plenum 108. The heavier material falls through a lower exit 108f in the lower plenum 108a and exits the system 100 at location B via a second rotary valve 110 (B) attached to the lower exit 108f in the lower plenum 108a. The second rotary valve 110 (B) also prevents air from exiting the system 100 via the lower exit 108f in the lower plenum 108a, similarly to the operation of the first rotary valve 110 (A).
Some light material could remain with the heavy material, as the light material is physically entwined with the heavy material and the force of the air is insufficient to entrain the light material. The system 100 can minimize the amount of light material that is not entrained in the air by optimizing the residence time of the material to be separated in the plenum 108. By optimizing the residence time, the chances are increased that the air flow will separate the heavy and light fractions of material and that the light fractions will be entrained in the air. This optimization allows for the separation of materials that have relatively close densities.
Residence time of the material to be separated in the plenum 108 can be optimized in a number of ways. This optimization allows for highly efficient separation of the materials—the residence time is such that the material to be separated that falls through the plenum 108 under gravity is mixed with the moving air to maximize the amount of light materials that are entrained in the air as it moves up through the plenum 108. This process, in turn, maximizes the amount of heavy material, including, for example, copper wire, that falls out of the plenum 108. In other words, this increased residence time allows for a more complete separation of the light and heavy fractions of materials.
The material to be separated can be sized, such as in a granulator or other size reducing equipment, prior to entering the plenum 108. In exemplary embodiments, this step can be omitted, and the system 100 can process the material to be separated directly from a shredder or other process equipment without sizing.
In one exemplary embodiment, the residence time in the plenum 108 is increased by matching the required air flow with the size of the material to be separated. An air diffuser plate 602 (
In the exemplary embodiment illustrated in
Alternatively or additionally, a depth of the plenum chamber can be optimized to achieve the maximum residence time for the waste material to be separated in the chamber. For example, the depth can be between 10 inches and 16 inches. The smaller depth can be used for smaller particle sizes. For example, the 10 inch depth can be matched to particles with a size range of 0-1 inch. In exemplary embodiments, a volume of the plenum 108, including a particular depth, width, height, and shape can be selected to obtain the desired static pressures and air flows in the plenum 108 and the system 100 and to process the desired type and size/density of materials.
In one exemplary embodiment, the following static pressures and air flow volumes for different particle size ranges are used:
The sizes of the air flow producing device 102, the passageways and transitions through which the air flows, the plenum 108, the air reducer 107, the expansion chamber 114, and other components can be selected to obtain the desired static pressures and air flows throughout the system 100 and to process the desired type and size/density of materials.
As illustrated in
The air with the entrained light fraction of materials moves up and out of the plenum 108, through an upper transition 112, and into an expansion chamber 114 via an entrance 114a in the expansion chamber 114. In the expansion chamber 114, the air and entrained light fraction of materials contact a redirecting plate 702 (
The air then flows from an upper exit 114c of the expansion chamber 114, through ducting 116, and into a centrifugal filtering device 118.
The air flow producing device 102 pushes the air through the expansion chamber 114 and also draws the air from the centrifugal filtering device 118, which in turn draws air from the expansion chamber 114. The expansion chamber 114 can comprise a make-up air vent to allow air into the expansion chamber 114 to maintain the desired air flow and static pressure throughout the system 100. In exemplary embodiments, the make-up air vent can comprise a butterfly-type vent, a pressure actuated vent, or other suitable vent.
Referring to
In exemplary embodiments, a volume of the expansion chamber 114, including a particular depth, width, height, and shape can be selected to obtain the desired static pressures and air flows in the expansion chamber 114 and the system 100 and to process the desired type and size/density of materials.
Referring back to
Additionally or alternatively, other devices can be used to filter the air and/or recover materials from the air that is flowing through the system 100. For example, an inline filter can be used in the ducting 116. Any suitable device that further cleans the air returning to the fan while maintaining the desired air flow and static pressures in the system 100 can be used.
Alternatively, in a non-closed loop system embodiment, the filter can filter the air as it exits the expansion chamber 114 into the atmosphere.
In the exemplary embodiment illustrated in
The air is then cycled back to the air intake 104. More specifically, the air flows from the centrifugal filtering device 118 through ducting 116 and returns to the air flow producing device 102. The air flow producing device 102 draws the air from the ducting 116 and pushes the air towards the plenum 108, thereby reusing the air throughout the system 100.
In this way, the process air loops through the system 100 and is not released to the atmosphere. The air path from the fan to the plenum 108 to the expansion chamber 114 to the centrifugal filter device 118 and back to the fan is closed. Valves (such as the rotary valves 110) and duct connections prevent the bleeding of air into the atmosphere.
The system 100 can comprise brackets 122 at various external locations to attach the system 100 to a support structure 124 that holds the components of the system 100 in place.
Materials separated via the system 100 can be usable materials or waste materials. In one exemplary embodiment, all of the materials can be waste materials that are separated and removed from the system 100 at locations A-D for proper disposal. In another exemplary embodiment, all of the materials can be recyclable materials that are separated and removed from the system 100 at locations A-D for recycling. In yet another exemplary embodiment, the materials can comprise both waste materials and recyclable materials that are separated and removed from the system 100 at locations A-D for proper disposal and recycling, respectively.
The rotary valves 110 described with reference to
An exemplary rotary valve 110 will now be described with reference to
The rotary valve 110 comprises in inlet 801 through which material enters the rotary valve 110 and an exit 803 through which material exits the rotary valve 110. An interior of the rotary valve 110 houses multiple vanes 804 supported on a shaft 806. The vanes 804 are sizes to contact the interior of the rotary valve 110 during operation such that air does not pass through the rotary valve 110. In operation, a motor 802 turns the shaft 806, thereby turning the vanes 804. As the vanes 804 turn, material disposed between the vanes 804 is transferred from the inlet 801 to the exit 803.
The vanes 804 can comprise a material that creates a suitable seal with the interior of the rotary valve 110 to prevent air flow through the rotary valve 110.
The description above uses the terms heavy fraction and light fraction to describe the two streams of material to be separated. One of ordinary skill in the art would understand that these terms are relative. In one exemplary embodiment, the light fraction can include fabric, rubber, and insulated wire, and the heavy fraction can include wet wood and heavier metals, such as non-ferrous metals including aluminum, zinc, and brass. In another exemplary embodiment, the light fraction can include fabric (“fluff”), and the heavy fraction can include insulated wire. Indeed, the apparatus of the present invention can be optimized to separate material within a narrow range of densities. As such, the processed material can range from raw shredder residue to a light fraction that was separated by a different separator technology, such as a Z-box air separator or sink/float separator.
One of ordinary skill in the art also would understand that the separator described above may be one step in a multi-step process that concentrates and recovers recyclable materials, such as copper wire from ASR and WSR.
Although specific embodiments of the present invention have been described in this application in detail, the description is merely for purposes of illustration. It should be appreciated, therefore, that many aspects of the invention were described above by way of example only and are not intended as required or essential elements of the invention unless explicitly stated otherwise. Certain steps and components in the exemplary processing methods and systems described herein may be omitted, performed and a different order, and/or combined with other steps or components. Various modifications of, and equivalent components corresponding to, the disclosed aspects of the exemplary embodiments, in addition to those described herein, can be made by those having ordinary skill in the art without departing from the scope and spirit of the present invention described herein and defined in the following claims, the scope of which is to be accorded the broadest interpretation so as to encompass such modifications and equivalent structures.
This application claims priority to U.S. Provisional Patent Application No. 61/214,794 filed Apr. 28, 2009 and entitled “Apparatus For Separating Recycled Materials Using Air.” The complete disclosure of the above-identified priority application is hereby fully incorporated herein by reference.
Number | Date | Country | |
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61214794 | Apr 2009 | US |