Not applicable.
Municipal solid waste (“MSW”) contains that which its name implies, solid waste from a municipality. MSW may include, for example, glass, plastic, rubber, PVC, rock, ceramic material, cardboard, paper waste, food waste, fabric waste, and the like. Often it is wet as it is exposed to environmental conditions, such as rain, as well as moisture from organic products within it and half finished water bottles and the like. However, part of it may be dry. It contains many different materials.
Processing MSW presents challenges. The general condition of the waste offers unique problems that need to be solved. Depending on exposure to physical elements, such as rain or the drying effects of the sun, in addition to the wide variety of storage conditions for MSW, processing it in order to isolate certain materials is challenging. Processing MSW requires a procedure which overcomes these physical characteristics in order to allow for the separation and isolation which is desired. The need is great for enhancing existing processing methods.
The present invention provides a method of sorting waste material to separate compostable material. The method includes the steps of sizing a waste material to be a first size waste material; delivering the first size waste material to a sizing screen; separating out a second size waste material from the first size waste material by use of a sizing screen, wherein the second size waste material is removed and the remaining first size waste material is referred to as suitable size waste material; delivering to a first vibrating feeder the suitable size waste material; vibrating the suitable size waste material; sorting the suitable size waste material in a first sorter in order to separate the suitable size waste material into a first organic fraction and a first inorganic fraction; vibrating the first organic fraction in a second vibrating feeder; sorting the first organic fraction in a second sorter into a second organic fraction and a second inorganic fraction so that the second organic fraction contains less inorganic material than the first organic fraction; and collecting the second organic fraction. In certain embodiments, the method further includes vibrating the first inorganic fraction in a third vibrating feeder; sorting the first inorganic fraction in a third sorter into a third organic fraction and a third inorganic fraction in order to increase the yield of organic material available for collection; and collecting the third organic fraction. In other embodiments, the method further includes adding the third organic fraction to the second organic fraction. In still other embodiments of the method, sorting the first inorganic fraction in the third sorter further includes sorting the first inorganic fraction in an x-ray sorter. In other embodiments, sorting the first inorganic fraction in the third sorter further includes sorting the first inorganic fraction in an air aspiration type sorter. In yet other embodiments, sorting the first inorganic fraction in the third sorter further includes sorting the first inorganic fraction in a density type sorter. In certain embodiments, sizing the waste material to be the first size further includes sizing the waste material to be two inch minus waste material. In yet other embodiments, separating out the second size waste material further includes separating out waste material being 0.5 inch minus waste material.
In alternate embodiments, the invention is a method of sorting waste material to separate compostable material, including sizing a waste material to be a first size waste material; delivering the first size waste material to a sizing screen; separating out a second size waste material from the first size waste material by use of a sizing screen, wherein the second size waste material is removed and the remaining first size waste material is referred to as suitable size waste material; delivering to a first vibrating feeder the suitable size waste material; vibrating the suitable size waste material; sorting the suitable size waste material in a first sorter in order to separate the suitable size waste material into a first organic fraction and a first inorganic fraction; vibrating the first inorganic fraction in a second vibrating feeder; sorting the first inorganic fraction in a second sorter into a second organic fraction and a second inorganic fraction so that the second inorganic fraction contains less organic material than the first inorganic fraction; and collecting the second organic fraction. In certain embodiments, the method further includes adding the second organic fraction to the first organic fraction. In yet other embodiments, sorting the suitable size waste material in the first sorter further includes sorting the suitable size waste material in an x-ray sorter. In yet other embodiments, sorting the first organic fraction in the second sorter further includes sorting the first organic fraction in an x-ray sorter. In alternate embodiments, the method is performed generally in line so that the suitable size waste material being sorted does not encounter any sharp side to side changes in its path.
Other embodiments of the invention disclose a sorting system, including a sizing screen, wherein the sizing screen defines a plurality of interfacial openings of a second size so that second size or smaller waste material is filtered out from a waste material being sorted by the sizing screen; a first vibrating feeder positioned to receive the waste material from the sizing screen so that the waste material being sorted is received and vibrated; an accelerated conveyor positioned to receive the waste material from the first vibrating feeder; a first sorting device positioned to receive the waste material from the accelerated conveyor, wherein the first sorting device is calibrated to sort the waste material into a first organic fraction and a first inorganic fraction; a second vibrating feeder positioned to receive the first organic fraction from the first sorting device; and a second sorting device positioned to receive the first organic fraction from the second vibrating feeder, wherein the second sorting device is calibrated to sort the first organic fraction into a second organic fraction and a second inorganic fraction. In certain embodiments, the sorting system further includes a third vibrating feeder positioned to receive the first inorganic fraction from the first sorting device; and a third sorting device positioned to receive the first inorganic fraction form the third vibrating feeder, wherein the third sorting device is calibrated to sort the first inorganic fraction into a third organic fraction and a third inorganic fraction so that the yield of organic material increases. In yet other embodiments, each of the sizing screen, the first vibrating feeder, the accelerated conveyor, the first sorting device, the second vibrating feeder, the second sorting device, the third vibrating feeder, and the third sorting device are positioned generally in line so that the waste material being sorted does not travel on a sharply angled horizontal path. In alternate embodiments, the sorting system further includes a material sizing device positioned to deliver the waste material to be sorted to the sizing screen, wherein the sizing device sizes waste material to a first size. In certain embodiments, the first size is two inch minus. In other embodiments, each of the sizing screen, first vibrating feeder, accelerated conveyor, first sorting device, second vibrating feeder, and second sorting device are positioned generally in line so that the waste material being sorted does not travel on a sharply angled horizontal path. In still other embodiments, the plurality of interfacial openings are sized so that 0.5 inch minus waste material is filtered out from the waste material being sorted by the sizing screen. In other embodiments, the third sorting device is an x-ray sorter. In alternate embodiments, the third sorting device is an aspiration type sorter. In still other embodiments, the third sorting device is a vibratory destoner sorter. In certain embodiments, the sorting system further includes a collection container positioned to receive the second organic fraction from the second sorting device. In still other embodiments, the sorting system further includes a collection container positioned to receive the third organic fraction from the third sorting device. In yet other embodiments, the sizing screen is a debris roll screen.
The present invention disclosed herein is a method of processing waste material to render a compostable product. Municipal solid waste (“MSW”) is a material that is difficult to process due to the wide spectrum of physical conditions that make up its content. MSW contains that which its name implies, solid waste from a municipality. MSW may include, for example, glass, plastic, rubber, PVC, rock, ceramic material, cardboard, paper waste, food waste, fabric waste, and the like. Often it is wet as it is exposed to environmental conditions, such as rain, as well as moisture from organic products within it and half finished water bottles and the like. However, part of it may be dry. It contains many different materials. Depending on exposure to physical elements, such as rain or the drying effects of the sun, in addition to the wide variety of storage conditions for MSW, processing it in order to isolate materials which may be used for compost is challenging. There is a real propensity for MSW to clump and aggregate due to it final content and storage conditions. Accordingly, processing MSW requires a procedure which overcomes these physical characteristics in order to allow for the separation and isolation of organic material which may be used as a compost material in a residential setting, an alternate daily cover in an industrial setting, or for anaerobic digestion processes The need is great for such a compost material in the residential and agricultural arenas.
Multiple methods for processing MSW for the isolation of compostable material are disclosed herein. Each method allows for the isolation of compostable material having varying levels of purity and varying levels of yield. By way of example, isolation of compostable for use as an alternative daily cover will differ from the method of isolating a residential grade compostable material.
Isolation of a material that will be a preferred material for composting requires the ability to break apart, or fragment, aggregated clumps of MSW. The method then requires the ability to identify and separate organic material from inorganic material. Organic material is the compostable material. The non-compostable material is the inorganic material, such as glass, rock, metals, and other materials containing significant amounts of high Z (i.e. high atomic number) elements. Inorganic materials do not decompose or break down and actually continue to exist for many, many years. Accordingly, removal of inorganic material from a compostable material is important. For example if small pieces of broken glass (inorganic material) are included in compost material for agricultural fields, at a point in the future after the organic material has decomposed, the small pieces of glass will remain in soil which, clearly, is not desirable in an agricultural field.
The first part of the method of processing MSW is to properly size the solid waste 126 which will be sorted. Material sizing devices 142 are known in the industry and are readily commercially available. An example of such a material sizing device 142 is a trommel screen. By the way of example, the trommel screen is commercially available from Central Manufacturing in Groveland, Ill. Another example is a debris roll screen 112 which relies on shafts with sizing discs, that is commercially available from Bulk Handling Systems of Eugene, Oreg. In still other embodiments of the invention, a sizing screen device that utilizes vibration to agitate material over a sizing surface may be used. By way of example, the vibratory screen is commercially available from Ball Engineering in Huntington Beach, Calif. In the preferred methods disclosed herein the solid waste 126 is sized by a material sizing device 142 to be two inches or less in size. In certain embodiments, the material sizing device 142 may be a debris roll screen 112 which sizes the solid waste 126 to be two inches or less in size. For the avoidance of doubt, sizing screens 111 include trommel screens, debris roll screens, vibratory screens and the like, as is known to those of ordinary skill in the art. Other sizes of materials could be used. In alternate embodiments, the solid waste 126 is sized to be three inches or less in size. Properly sized solid waste 126 is then delivered to a conveyor system 150 to next be subjected to a fines screen. A fines screen is also called a sizing screen 111 within this application. Sizing screens 111 are well known in the industry and are readily commercially available. For the avoidance of doubt, sizing screens 111 include trommel screens, debris roll screens, vibratory screens and the like, as is known to those of ordinary skill in the art. In certain embodiments of the present invention, within the methods described herein, the sizing screen 111 is a debris roll screen 112. A suitable debris roll screen 112 is commercially available from Bulk Handling Systems of Eugene, Oreg. The debris roll screen 112 of the current method has a plurality of interfacial openings 115 so that smaller sized material is separated out, as best seen in
Clearly, an important aspect of the system and method disclosed herein is the proper sizing of waste material before starting the sorting process. Specifically, with regard to isolating compostable material, action is needed to identify an upper size limit as well as a lower size limit for the solid waste material 126 which is the subject of sorting. In certain embodiments of the invention, the upper size limit of the waste material 126 is a first size waste material 156, which is a size to be identified one of ordinary skill in the art with regard to specific details relevant to the sorting activity being performed. In alternate embodiments of the present invention, the first size waste material 156, or upper limit, may be about two inches, so that material having a size of two inches or less is the subject of sorting. In yet another embodiment of the present invention, the first size waste material 156, or upper limit, may be about three inches, so that material having a size of three inches or less is the subject of sorting. Equally important is the establishment of a lower size limit so that the machinery and methodology perform at an optimal level. In certain embodiments of the present invention, after first being sized to a first size waste material 156, the waste material 126 is then placed on a sizing screen 111 such as a debris roll screen 112 in order to separate out waste material of a second size 158, that is, if waste material is a second size or smaller, it is removed so that such small waste material is not subject to further sorting. In alternate embodiments of the present invention, the second size waste material 158, or lower size limit, may be 0.5 inches. Accordingly, waste material having a size of 0.5 inches or less is removed from the sorting process. In alternate and still other embodiments, the lower size limit may be 0.38 inch. In yet other embodiments, the lower size limit may be 0.375 inch, which is ⅜ inch. MSW which is properly sized does not contain significant amounts of material larger than the first size 156, or upper limit, and does not contain significant amounts of material smaller in size than the second size 158, or lower size limit. Such properly sized MSW is referred to herein as suitable size waster material 160. Suitable size waste material 160 is the subject of sorting by use of the invention disclosed herein.
Referring now to
The first sorting device 118 is a sorting device capable of distinguishing organic material from inorganic material. In certain embodiments of the present invention, the sorting device technology will be measuring and detecting the Z value of the waste material 160 passing through the device and identifying its compounded atomic number. An example of a suitable first sorting device 118 is the model DXRT sorter, which is commercially available from National Recovery Technologies, LLC of Nashville, Tenn. In certain embodiments of the invention, the sorting devices 118, 124, and 148 may have a 40 inch wide sorting area. Further details of this specific sorting device are disclosed below. In alternate embodiments of the present invention, an alternate sorting device may be used as long as it is capable of identifying and separating organic material from inorganic material.
Still referring to
Referring now to
The process of sorting MSW disclosed herein allows for a complete flexibility in the purification of organic material as well as other steps in order to increase the yield of organic material. In addition to further purifying the first organic fraction 130, as was described above, action may be taken to further separate the content of the first inorganic fraction 132. In certain embodiments of the present invention, rather than sorting the first organic fraction 130 in the second sorting device 124, it may be desirable to sort the first inorganic fraction 132 in the second sorting device 124. The action of the second sorting device 124 results in a second organic fraction 134 and a second inorganic fraction 136. It is noted that this separation step generates a second organic fraction 134 which was contained within the first inorganic fraction 132 and, but for the second separation, such additional organic material may have been discarded, or otherwise disposed of, as contents within the first inorganic fraction 132. Such an embodiment is described in detail in Example 2, below.
Referring now to
One of ordinary skill in the art is familiar with the manner of positioning, arranging, and/or attaching the various elements of the system disclosed herein. One of ordinary skill in the art also is familiar with the power requirements of such elements of the system so that one of ordinary skill in the art may operate the systems which are disclosed herein.
Referring now to
Referring now to
In certain embodiments of the present invention, the sorting steps may be performed at the rates as described in this paragraph. The material sizing device 142 produces roughly 17 tons per hour (tph) of two inch minus material. The debris roll screen 112 produces roughly 12 tph to about 13 tph of material over top of the screen to be fed to sorting system. The difference of roughly 3-6 tons is sub 0.5 inch minus material. The vibrating feeders and sorting devices 118, 124 and 148, when having a 40 inch wide conveyor, operate at a rate of 8-9 tph. The overall system can process up to 17 tph of MSW material.
Another aspect of the present invention is that the sorting method disclosed herein is to be performed generally in line so that the waste material being sorted does not encounter any sharp side-to-side changes in its path. Due to momentum of the MSW, and the rate at which the waste material being sorted moves through the system, any sharp or abrupt changes in direction complicate the sorting process. Vertical changes are tolerable. Accordingly, using gravity to drop MSW from a vibrating feeder onto a conveyor is acceptable. By way of a similar example, using gravity to transport an organic fraction from a sorting device into a collection bin is not problematic. However, abrupt horizontal changes in direction complicate sorting because of the lack of predicitabily of the position of each piece of waste in relation to the sorting process. By performing the method disclosed herein generally in line, abrupt side to side changes in the path of the waste material are avoided which enhances the results of the sorting activities. It is common for MSW to contain objects having circular or oval shapes which would be subject to rolling in response to an abrupt horizontal change of direction. As a further example, certain items in MSW may be wet or slippery such that those items when experiencing a sharp horizontal change of direction may slip or slide along its surface in response to physical forces. As disclosed herein, and shown in
The method and system disclosed herein reference a number of sorting devices. For the avoidance of doubt, depending upon the embodiment of the method or system, the first sorting device 118, second sorting device 124, third sorting device 148, and any additional sorting devices, as needed, may be of the same type. In still other embodiments of the invention, each of the sorting devices may use a different sorting technology. For example, in a first embodiment, all sorting devices may be of an x-ray sorter type. In an alternate embodiment, the first sorting device 118 and second sorting device 124 may be of an x-ray sorter type, while the third sorting device 148 is an air aspiration type sorter, such as an air-knife. In still another embodiment, the third sorting device 148 may be a density type sorter, such as a vibratory destoner. With regard to the x-ray sorter type, disclosed below are details of an x-ray type sorter which is readily commercially available from National Recovery Technologies, LLC of Nashville, Tenn. Regarding the other types of sorter devices, note that air aspiration type sorters are well known in the industry and readily commercially available. For example, an air aspiration type sorter is commercially available from Air Assisted Aspirator from CSL, of Eugene, Oreg. The same is true of the density type sorters. Density type sorters are well know in the industry and readily commercially available from a source, for example, such as Destoner by Oliver of Rocky Form, Colo.
The sorter described below uses analyses of x-ray absorptions in a material at differing energy levels in order to determine the relative atomic density (atomic number Z) of the material. The information below is from U.S. Pat. No. 7,564,943. Other U.S. patents related to that patent are U.S. Pat. Nos. 8,144,831; 7,848,484; and 7,099,433. All patents and references listed herein are hereby incorporated by reference herein, each in its entirety.
X-ray absorption in a material is a function of the atomic density of the material and also a function of the energy of the incident x-rays. A given piece of material will absorb x-rays to differing degrees depending upon the energy of the incident x-rays. Materials of differing atomic numbers will absorb x-rays differently. For instance copper (Z=29) will absorb x-rays much more readily than will aluminum (Z=13). Also the absorption profile of a given piece of copper over a range of x-ray energies will be different than the absorption profile of a given piece of aluminum over that same range of energies. X-ray transmission through a material is given by the equation
N
(t)
=N
0
e
−ηρ
Where N(t) is the number of photons remaining from an initial N0 photons after traveling through thickness t in a material of density ρ. The mass attenuation coefficient η is a property of the given material and has a dependence upon photon energy. The value ηρ is referred to as the mass absorption coefficient (μ) for a given material. Values of the coefficient μ have been established by researchers to high accuracy for most materials and these values are dependent upon the energy of incident x-ray photons. Values of μ/ρ(=η) for most materials can be found at the National Institute of Standards and Technology (NIST) internet website. The lists of values are extensive covering all stable elements for various values of photon energy (kev). The value of ρ for a given material is simply its density in gm/cm3 and can be found in many textbooks and also at the NIST website. The ratio N(t))/N0 is the transmittance of photons through a thickness t of material and is often given as a percentage, ie. the percentage of photons transmitted through the material.
The following table, by way of example, gives values of the mass absorption coefficient μ for aluminum and copper over a range of incident x-ray photon energies and the percentage of photons remaining after passing through 0.2 cm of material (% transmission).
Using the information in the table above we can illustrate how aluminum in this case can be differentiated from copper by comparing ratios of % Transmission (TE) at two different photon energy levels. For instance:
Ratios: T100/T50=1.11 for aluminum, T100/T50=47.3 for copper
The ratio for copper is much higher than that for aluminum. Further, we find that for differing thicknesses of materials it is possible to distinguish between materials of differing Z value by comparing such ratios while correlating to levels of transmission of photon energy through the materials as is discussed in more detail later. This innovative analytical technique allows effectively differentiating between the materials independent of knowing or determining thickness of the materials as is further discussed in reference to
The x-ray technology measures changes in amount of x-ray transmission through an object as a function of energy. This technology can evaluate the entire object and looks through the entire object taking into consideration exterior and interior variations. The technology evaluates how the quantities of transmitted x-rays at various energy levels change as a function of the incident x-ray energy. One embodiment may be a multi-energy cadmium zinc telluride (CZT) pixel detection system arranged into a linear detector array of very small size is suitable to collect x-ray transmission information at each detector site and transmit it to an on-board computer system to collect data from multiple sensors simultaneously. Another embodiment may be an arrangement of multiple individual multi-energy detection systems such as those provided by Amptek, Bedford, Mass. Such systems could provide a greater number of energy bins. Multiple sub-systems could cover a wide conveyor belt. The data from the multi-detector array will provide multi-energy readings from each detector to provide an energy dispersive x-ray transmission profile of an object for assessing composition of a broad range of matter. Such a multi-energy CZT linear detector array having 32 CZT detectors at 0.5 mm pitch is available with supporting electronics from Nova R&D, Riverside, Calif. Each detector in the Nova R&D detection system can read and report x-ray transmission levels at up to five energy bands simultaneously at high rates of data acquisition and this capability is expected to expand to more energy bands as the technology is further developed. Further, the detectors have a spatial resolution of 0.02 inches per pixel in the array allowing detailed high resolution multi-energy profiling of x-ray transmission through an object under inspection. In effect one can build a high resolution multi-energy image of an object under inspection as the object is conveyed through the inspection region as well as simultaneously measuring the relative average atomic number of bits of matter within the image.
Such a system is functionally analogous to a line-scan camera commonly found in industrial inspection processes. Whereas a line-scan camera detects multiple “colors” within the visible spectrum, the system detects “colors” within the x-ray spectrum. Thus, the system may be characterized as a multi-spectral, x-ray camera providing a much richer data set than the dual energy techniques described in more detail herein. This multi-energy data set allows expanded imaging and material identification capabilities as described in general terms below.
While the new system provides data that can be represented by an x-ray image, an intelligent interpretation of that image is essential to identification and sortation of material. The presence of any atomic element is manifest by spectral peaks (from fluorescence) or discontinuities (from transmission) that result from electron-state transitions unique to that element. Since these peaks or edges occur in spectrally narrow regions (on the order of eV), detection of an element only requires monitoring a small portion of the spectrum. Unfortunately, the absorption edges of “interesting” elements span a wide energy range, from less than 1 keV to more than 80 keV. Additionally, material morphology and composition, processing rates and environment, and sensor response renders peak or edge detection as the exclusive method of sorting a wide variety of materials impractical. Peaks or edges may be used to discriminate among a subset of elements, but it is thought that interrogating a material's spectrum over a shorter energy range (shorter than 1 keV→80 keV) will divulge information sufficient for recycling purposes although a range double that (up to 160 keV) could be useful. In particular, applying derivatives, tangential intersections and spectral correlation to the absorption curve of a material could provide adequate discrimination among categories of recyclables.
When compared to the simple discriminators of difference or ratio, the proposed operations are, in general, more susceptible to noise within the response curve of a material. Thus, to generate meaningful descriptors, mitigating all forms of “noise” is advantageous. Since in one embodiment the system measures individual photons, the inherent noise from this method of detection is described by a Poisson distribution and can be reduced by collecting more photons. The nature of the CZT detectors in the Nova R&D linear array system limits the photon counting rate to approximately 50 million counts per second (MCount/Sec): the ensuing electrons further limit this rate to approximately 1 MCount/Sec. New systems under development could extend the counting rate by an order of magnitude (up to 500 MCount/sec). Since sufficiently “smooth” curves may require thousands of counts per acquisition, noise reduction through increased photon counts can result in decreased processing rates.
A material's absorption curve could prove sufficient for identification and sortation. However, certainty during the identification process may be augmented by fluorescence information. When x-rays pass through a material, some x-rays with energies greater than the electron excitation energy of constituent elements are absorbed and re-emitted as fluoresced photons. This process of absorption and re-emission is characterized in the transmission spectrum as an “absorption edge” and a “fluorescence peak,” where the peak is always near, but at a slightly lower energy than the edge. In a traditional absorption curve, the fluorescent peak is negligible. However, as a detector is gradually removed from the primary path of x-ray transmission, the signal contribution from primary x-rays are reduced and the contribution from secondary x-rays, such as fluorescence and scatter, are increased. Understandably, fluorescence is considered a “surface” phenomenon, but perhaps this information could enhance identification under certain conditions.
In an embodiment a classification and sorting algorithm 40, represented in
All references, publications, and patents disclosed herein are expressly incorporated by reference.
In a first embodiment of the process disclosed herein, the solid waste 126 being sorted is placed in a material sizing device 142 so that waste 126 having a size of two inches or less is then delivered to a conveyor 150 for delivery to a debris roll screen 112. The debris roll screen 112 separates out any material having a size of a one half inch or less. Such one half inch or less material is removed by placement on a residue collection conveyor. The suitable size waste material 160 having a size from about two inches to about a one half inch is delivered to a first vibrating feeder 114. The first vibrating feeder 114 helps breaks apart the waste 160 for more efficient separation. The first vibrating feeder 114 then delivers the waste 160 to a first accelerated conveyor 116 which feeds the waste 160 into the first sorting device 118 for sorting. The first sorting device 118 may be a device as described herein which is commercially available from National Recovery Technologies, LLC. As a result of the action of the first sorting device 118, the waste 160 is separated into a first organic fraction 130 and a first inorganic fraction 132. The first organic fraction 130 may be used as described elsewhere herein, such as for compost.
In certain embodiments of the process disclosed herein, further purification of the first organic fraction 130 is desirable. Further purification is accomplished by performing the following steps on the first organic fraction 130 from Example 1. The first organic fraction 130 is delivered to a second vibrating feeder 120 to allow fragmenting, or breaking apart of the material. The first organic fraction 130 is placed on a second accelerated conveyor 122 for delivery to a second sorting device 124. The result of the action of the second sorting device 124 is to separate the first organic fraction 130 into a second organic fraction 134 and a second inorganic fraction 136. The resulting second organic fraction 134 is a product that is available for use in composting or as otherwise described herein.
In still other embodiments of the process disclosed herein, further purification of the first inorganic fraction 132 may be desirable in order to increase the yield of organic matter available for use as a compost, or the like. In such an embodiment, further increase of yield is accomplished by performing the following steps on the first inorganic fraction 132 from Example 1. The first inorganic fraction 132 is delivered to a second vibrating feeder 120 to allow fragmenting, or breaking apart of the material. The first inorganic fraction 132 is placed on a second accelerated conveyor 122 for delivery to a second sorting device 124. The result of the action of the second sorting device 124 is to separate the first inorganic fraction 132 into a second organic fraction 134 and a second inorganic fraction 136. The resulting second organic fraction 134 is further product that is available for use in composting or as otherwise described herein.
In yet another embodiment of the present invention, the following steps result in the separation of the waste 126 into organic and inorganic fractions, with the additional separation of both of the organic and inorganic materials so that further organic material may be obtained from the inorganic material, in order to increase organic material yield. Also, the initial organic material is purified through the steps as disclosed in Example 2.
The first inorganic fraction 132 resulting from Example 1 goes through further separation. The first inorganic fraction 132 is subjected to fragmenting, or breaking apart, on a third vibrating feeder 134. The first inorganic fraction 132 is placed on a third accelerated conveyor 146 for delivery to a third sorting device 148 for sorting of it into a third organic fraction 138 and a third inorganic fraction 140. The third organic fraction 138 may be combined with the second organic fraction 134. The final organic composition is then put in use as described elsewhere in this application.
Thus, it is seen that the system and method of the present invention readily achieves the ends and advantages mentioned as well as those inherent therein. While certain preferred embodiments of the invention have been illustrated and described for purposes of the present disclosure, numerous changes in the arrangement and construction of parts may be made by those skilled in the art which changes are encompassed within the scope and spirit of the present invention as defined by the following claims.
This application claims benefit of U.S. Provisional Patent Application Ser. No. 61/703,355, filed Sep. 20, 2012, entitled “Methods of Processing Waste Material to Render a Compostable Product” which is hereby incorporated by reference in its entirety.
Number | Date | Country | |
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61703355 | Sep 2012 | US |