Patent Application
20100136665
The present invention relates to a system and method for recycling used disposable diapers, in which used disposable diapers are processed into a predetermined product (hereinafter such a product may be referred to as “processed waste”), whereby the disposable diapers can be effectively recycled while CO2 emission is reduced.
In recent years, disposable diapers for infants and adults have been increasingly used in, for example, hospitals, nursing homes, and individual homes. Used disposable diapers are generally disposed of through incineration. However, since used disposable diapers contain water from human waste, etc., combustion of the diapers requires high temperature, which poses problems in terms of an increase in disposal cost and an increase in amount of CO2 emission during incineration.
Under such circumstances, there have been proposed various processing methods for utilizing used disposable diapers as, for example, fuels. The proposed methods include a carbonization method making use of high-temperature steam, and a thermal processing method making use of vegetable oil.
Techniques employing the carbonization method making use of high-temperature steam include a waste processing method in which waste products are carbonized by exposing them to high-temperature steam under stirring in the absence of oxygen (see Patent Documents 1 and 2). Meanwhile, techniques employing the thermal processing method making use of vegetable oil include a method for producing a fuel, in which waste products (e.g., used disposable diapers) are thermally processed with waste vegetable oil or waste mineral oil without shredding of the waste products (see Patent Document 3).
However, each of these techniques employs a boiler or a similar apparatus during the course of production of processed waste serving as a fuel, and thus poses a problem in that the amount of CO2 emission is not reduced, which may lead to harming the environment. That is, each of these techniques is focused only on recycling of used disposable diapers, and does not take into account reduction in the amount of CO2, which is eventually emitted.
Patent Document 1: Japanese Patent Application Laid-Open (kokai) No. 2000-313884
Patent Document 2: Japanese Patent Application Laid-Open (kokai) No. 2001-123175
Patent Document 3: Japanese Patent Application Laid-Open (kokai) No. 2001-214173
In view of the foregoing, an object of the present invention is to provide a system and method for recycling used disposable diapers, which realizes effective recycle of used disposable diapers in the form of processed waste, and which can flexibly contribute to reduction in CO2 emission, as compared with the case where used disposable diapers are disposed of without being converted into processed waste.
In a first mode of the present invention for solving the aforementioned problems, there is provided a system for recycling used disposable diapers (hereinafter may be referred to as a “used disposable diaper recycling system”), characterized by comprising, at least, a processing apparatus for producing, from used disposable diapers serving as a raw material, processed waste having a predetermined water content and a volume reduced to a predetermined level; and a recovering facility for reutilizing the used disposable diapers by burning the processed waste as a fuel and also by recovering thermal energy.
According to the first mode, predetermined processed waste is produced from used disposable diapers serving as a raw material, and the used disposable diapers are recycled by recovering thermal energy through combustion of the processed waste as a fuel. That is, according to the first mode, used disposable diapers can be effectively recycled in the form of processed waste.
A second mode of the present invention is drawn to a specific embodiment of the used disposable diaper recycling system according to the first mode, wherein the processing apparatus and the recovering facility are provided in the same institution; the recovering facility is a combustion facility for burning the processed waste as a fuel as is; and the processed waste is employed as an auxiliary fuel for heat supply in the institution.
According to the second mode, the processing apparatus and the recovering facility are provided in the same institution; the recovering facility is a combustion facility for burning the processed waste as a fuel as is; and the processed waste is employed as an auxiliary fuel for heat supply in the institution. That is, according to the second mode, used disposable diapers can be effectively recycled in the form of processed waste in the same institution.
A third mode of the present invention is drawn to a specific embodiment of the used disposable diaper recycling system according to the first mode, wherein the recovering facility is provided outside of an institution in which the processing apparatus is provided, and, in the recovering facility, the processed waste is employed as a combustion material as is, or transformed into a combustion material suitable for use in the recovering facility.
According to the third mode, in the recovering facility provided outside of an institution in which the processing apparatus is provided, the processed waste is employed as a combustion material as is, or transformed into a combustion material suitable for use in the recovering facility. That is, according to the third mode, even when the recovering facility is provided outside of an institution in which the processing apparatus is provided, used disposable diapers can be effectively recycled in the form of processed waste.
A fourth mode of the present invention is drawn to a specific embodiment of the used disposable diaper recycling system according to any of the first to third modes, wherein the processing apparatus comprises, at least, shredding means for shredding used disposable diapers and stirring the shredded disposable diapers together with a fermentative bacterium; and heating means for heating the shredded disposable diapers so as to regulate the water content of the shredded disposable diapers to a predetermined level, and performing sterilization through heating for a predetermined period of time, and wherein the processing apparatus produces, from used disposable diapers fed to the apparatus, processed waste which has a volume reduced to a predetermined level, and which realizes reduction in amount of CO2 emission, as compared with the case where the used disposable diapers are burned as is.
According to the fourth mode, the processing apparatus produces, from used disposable diapers fed to the apparatus, processed waste which has a volume reduced to a predetermined level, and which realizes reduction in amount of CO2 emission, as compared with the case where the used disposable diapers are burned as is. That is, according to the fourth mode, used disposable diapers can be effectively recycled in the form of processed waste, and CO2 emission can be reduced, as compared with the case where used disposable diapers are disposed of without being converted into processed waste.
A fifth mode of the present invention is drawn to a specific embodiment of the used disposable diaper recycling system according to any of the first to fourth modes, wherein the combustion facility is a boiler for burning the processed waste without solidification of the processed waste.
According to the fifth mode, the processed waste can be burned without being solidified. That is, according to the fifth mode, used disposable diapers can be more effectively recycled in the form of processed waste.
A sixth mode of the present invention is drawn to a specific embodiment of the used disposable diaper recycling system according to any of the first to fifth modes, wherein the recycling system further comprises CO2 reduction management means for calculating and managing the amount of CO2 emission resulting from combustion of processed waste produced by the processing apparatus, the CO2 emission amount being reduced as compared with the case where used disposable diapers are burned as is, wherein the CO2 emission amount is converted to a CO2 emission right of a certain value through calculation, and is either offered to a requesting third-party organization for payment of a reasonable value or returned to a source that has introduced the processing apparatus.
According to the sixth mode, the amount of CO2 emission resulting from combustion of processed waste—which CO2 emission amount is reduced as compared with the case where used disposable diapers are burned as is—is calculated, and the CO2 emission amount is converted to a CO2 emission right through calculation on the basis a certain value, and is either offered to a requesting third-party organization for payment of a reasonable value or returned to a source that has introduced the processing apparatus. That is, according to the sixth mode, employment of processed waste can flexibly contribute to reduction in CO2 emission, as compared with the case where used disposable diapers are disposed of without being converted into processed waste.
A seventh mode of the present invention is drawn to a specific embodiment of the used disposable diaper recycling system according to the sixth mode, wherein the CO2 emission right is calculated by the CO2 reduction management means on the basis of, at least, the amount of processed waste fed to the recovering facility, and the amount of CO2 emitted from the waste-fed recovering facility.
According to the seventh mode, the CO2 emission right is calculated on the basis of, at least, the amount of processed waste fed to the recovering facility, and the amount of CO2 emitted from the waste-fed recovering facility. That is, according to the seventh mode, the amount of CO2 emission can be reliably managed, and more flexible contribution to reduction in CO2 emission can be achieved.
In an eighth mode of the present invention, there is provided a method for recycling used disposable diapers (hereinafter may be referred to as a “used disposable diaper recycling method”), characterized by comprising, at least, producing, from used disposable diapers serving as a raw material, processed waste having a predetermined water content and a volume reduced to a predetermined level; and reutilizing the used disposable diapers by burning the processed waste as a fuel and also by recovering thermal energy.
According to the eighth mode, processed waste having a predetermined water content and a volume reduced to a predetermined level is produced from used disposable diapers serving as a raw material, and thermal energy is recovered through combustion of the processed waste. That is, according to the eighth mode, used disposable diapers can be effectively recycled in the form of processed waste.
A ninth mode of the present invention is drawn to a specific embodiment of the used disposable diaper recycling method according to the eighth mode, wherein the processed waste has a water content of 5% and a volume ⅓ that of the used disposable diapers.
According to the ninth mode, processed waste having a water content of 5% and a volume ⅓ that of used disposable diapers is effectively recycled.
A tenth mode of the present invention is drawn to a specific embodiment of the used disposable diaper recycling method according to the eighth or ninth mode, wherein the amount of CO2 emission resulting from combustion of the processed waste, the CO2 emission amount being reduced as compared with the case where used disposable diapers are burned as is, is calculated; and a CO2 emission right which has been calculated through conversion of the CO2 emission amount on the basis of a certain value is offered to a requesting third-party organization for payment of a reasonable value, or the CO2 emission right is returned to a source that has introduced the processing apparatus.
According to the tenth mode, the amount of CO2 emission resulting from combustion of the processed waste—which CO2 emission amount is reduced as compared with the case where used disposable diapers are burned as is—is calculated, and the CO2 emission amount is converted to a CO2 emission right through calculation on the basis of a certain value, and is either offered to a requesting a third-party organization for payment of a reasonable value or returned to a source that has introduced the processing apparatus. That is, according to the tenth mode, flexible contribution to reduction in CO2 emission can be achieved, as compared with the case where used disposable diapers are disposed of without being converted into processed waste.
An eleventh mode of the present invention is drawn to a specific embodiment of the used disposable diaper recycling method according to any of the eighth to tenth modes, wherein the CO2 emission right, which is calculated through conversion on the basis of a certain value, is managed by an institution possessing a predetermined apparatus for producing the processed waste.
According to the eleventh mode, the CO2 emission right, which is calculated through conversion on the basis of a certain value, is managed by an institution possessing a predetermined apparatus for producing the processed waste. That is, according to the eleventh mode, more flexible contribution to reduction in CO2 emission can be achieved.
According to the present invention, there can be provided a system and method for recycling used disposable diapers, in which predetermined processed waste is produced so that used disposable diapers are reutilized in a predetermined facility. The system and method of the present invention realize effective recycling of used disposable diapers in the form of processed waste, and can flexibly contribute to reduction in CO2 emission, as compared with the case where used disposable diapers are disposed of without being converted into processed waste.
A most preferred embodiment of the present invention will next be described with reference to the drawings. The embodiment is given only for an illustration purpose, and the invention is not limited to the embodiment.
As shown in
The recycling system 1 employs the recovering facility 70 for using the processed waste 101 inside of the institution 2 for thermal recycling; or the recovering facility 90 for using the processed waste 101 outside of the institution 2 for thermal recycling. As shown in
The recovering facility 70 and the processing apparatus 20 are provided in the same institution 2, and the recovering facility 70 is a combustion facility for burning the processed waste 101 as a fuel as is. The processed waste 101 is employed as an auxiliary fuel for heat supply 102 in the institution 2. The combustion facility is a boiler (e.g., a hot water boiler) for burning the processed waste 101 without solidification thereof. The heat supply 102 corresponds to a medium supplied through employment of the processed waste 101 as an auxiliary fuel in an apparatus or facility including a hot water system (e.g., a hot-water heater, a heated pool, or a water heater). Thus, when, for example, the institution 2 is a hospital, used disposable diapers 100 can be recycled for thermal recycling in the hospital for, for example, bathing of patients or temperature regulation in wards.
The recovering facility 90 is provided outside of the institution 2 in which the processing apparatus 20 is provided. In the recovering facility 90, the processed waste 101 is employed as a fuel as is, or transformed into a fuel suitable for use in the recovering facility. As shown in
The transformation means 91 is an apparatus for transforming the processed waste 101 into, for example, the aforementioned solid fuel, and the transformation means 91 is, for example, a compressor. The transformation means 91 may be provided inside of the recovering facility 90, or may be provided at a site different from the site where the recovering facility 90 is provided. Thus, when, for example, the processed waste 101 is reduced in volume through compression by means of a compressor, or transformed into a solid fuel by means of a predetermined apparatus, the processed waste 101 can be employed as a combustion material in the recovering facility 90.
Upon request of a third-party organization, the processed waste 101 or a combustion material transformed therefrom may be transported to and employed in the institution. Examples of the recovering facility 90 include an electricity generating facility, a facility having a hot-water supplier or heater for providing steam or hot water, a paper-making plant, and a cement plant.
The processing apparatus 20 includes, at least, shredding means 22 for shredding used disposable diapers 100 and stirring the shredded disposable diapers together with fermentative bacteria; and heating means 23 for heating the shredded disposable diapers 100 so as to regulate the water content of the shredded disposable diapers to a predetermined level, and performing sterilization through heating for a predetermined period of time. The processing apparatus 20 produces, from used disposable diapers 100 fed to the apparatus, processed waste 101 which has a volume reduced to a predetermined level, and which realizes reduction in amount of CO2 emission, as compared with the case where used disposable diapers are burned as is. The processing apparatus 20 may be incorporated into a disposal apparatus 10 in combination with gas discharging means 40 for aspirating and discharging atmosphere gas generated in the interior of the processing apparatus 20, thereby attaining negative pressure in the processing apparatus 20, and deodorizing means 50 for deodorizing odorous gas which is aspirated by the gas discharging means 40.
The used disposable diaper recycling system 1 may further include, in the institution 2, CO2 reduction management means 80 for calculating and managing the amount of CO2 emission resulting from combustion of processed waste 101 produced by the processing apparatus 20, the CO2 emission amount being reduced as compared with the case where used disposable diapers 100 are burned as is. When the amount of CO2 emitted through usual disposal of used disposable diapers, and the amount of CO2 emitted through employment of the processed waste 101 are input to and managed by the CO2 reduction management means 80 per unit amount of used disposable diapers 100 fed to the apparatus 20, the amount of reduction in CO2 emission is calculated.
Specifically, the recycling system 1 further includes, for the purpose of assisting the CO2 reduction management means 80, processed waste feed amount management means 81 for managing the amount of the processed waste 101 fed to the recovering facility 70; feed amount/electricity usage amount management means 82 for managing the amount of used disposable diapers 100 fed to the processing apparatus 20, and the amount of electricity used during processing in the disposal apparatus 10 including the processing apparatus 20; and processed waste shipment management means 83 for managing data on shipment of the processed waste 101. When data managed by the management means 81, 82, and 83, and the amount of CO2 emitted from the recovering facility 70 or 90 are input to the CO2 reduction management means 80, the amount of CO2 emission, which is eventually reduced inside or outside of the institution 2, is calculated. Data managed by the processed waste shipment management means 83 are input when the amount of CO2 emitted outside of the institution 2 is calculated. Meanwhile, data managed by the feed amount/electricity usage amount management means 82 are not necessarily input when the amount of CO2 emitted inside of the institution 2 is calculated. Specifically, since the feed amount/electricity usage amount management means 82 manages data on the amount of electricity consumed for the production of the processed waste 101, when, for example, the amount of processing per day is predetermined, and the amount of used disposable diapers 100 fed or the amount of electricity usage is not varied, a fixed value may be input to the CO2 reduction management means 80. The processed waste shipment management means 83 employs detailed arrangements (e.g., shipment destination, shipment completion, and shipment period) contracted and concluded in advance according to, for example, a manifest.
The amount of CO2 emission calculated by the CO2 reduction management means 80 is converted, on the basis of a certain value, into a CO2 emission right having a trading value, and the CO2 emission right is managed as a value corresponding to right of CO2 emission. The CO2 reduction management means 80 is managed by an institution possessing the disposal apparatus 10 including the processing apparatus 20. No particular limitation is imposed on the CO2 reduction management means 80, so long as the means 80 has, for example, common computer functions. The CO2 reduction management means 80 is, for example, a server or a personal computer. The CO2 reduction management means 80 may be operated in a wired or wireless communication environment.
Thus, the amount of reduction in CO2 emission is converted into a CO2 emission right having a trading value, and, for example, the CO2 emission right is offered to a requesting third-party organization for payment of a reasonable value, or is returned to a source that has introduced the disposal apparatus 10. Specifically, the CO2 emission right converted by the CO2 reduction management means 80 is stored and managed by the institution possessing the disposal apparatus 10 (i.e., the supplier of the processing apparatus 20), and the CO2 emission right is offered to, for example, a requesting third-party organization for payment of a reasonable value.
The apparatus 20 will now be described specifically.
As shown in
As shown in
Specifically, the processing bath 21 has a box-like shape, and has a semi-cylindrical inner bottom corresponding to rotation of the below-described vanes 32. That is, the processing bath 21 has a vaulted space therein. As shown in
The processing bath 21 has, on a top surface thereof (in a vertical direction), a lid member 25 for covering the opening 24. The opening 24 can be opened or closed by automatically moving the lid member 25 by means of, for example, a non-illustrated drive motor. The disposal bag 100a is fed through the opening 24, and, if necessary, fermentative bacteria required for fermentation are appropriately fed through the opening 24. As used herein, the term “fermentation” refers to degradation of human waste, pulp, etc. by microorganisms. No particular limitation is imposed on the specific fermentative bacterium employed for degradation of human waste, etc., and any known fermentative bacteria may be employed. The fermentative bacterium employed for fermentation may be an aerobic microorganism or an anaerobic microorganism. However, an aerobic microorganism is preferably employed, from the viewpoints of easy management and low level of odor generated during fermentation.
The processing bath 21 has, at the center of a side thereof (in a longitudinal direction), a rectangular hand hole for performing inspection and maintenance of the interior of the bath. The hand hole can be opened or closed by means of a hand hole door 27. The hand hole door 27 is provided with a circular suction port 28 to which a transportation means 60 is connected.
The processing bath 21 includes therein the shredding means 22 for shredding used disposable diapers 100. The shredding means 22 includes a rotary shaft 30 provided so as to extend in a longitudinal direction of the processing bath 21; drive means 31 (e.g., a drive motor) for rotating the rotary shaft 30, the drive means 31 being provided on one end portion of the rotary shaft 30; and a plurality of vanes 32 provided in an axial direction of the rotary shaft 30 at predetermined intervals. When a plurality of vanes 32 are spirally provided around the rotary shaft 30 at predetermined intervals, in accordance with the direction of rotation of the rotary shaft, used disposable diapers 100 are brought together to a suction port 28 provided at the center of the processing bath, or diffused to left and right sides of the bath.
In the shredding means 22, as described above, while used disposable diapers 100 are shredded and cut under stirring, they are brought together to the suction port 28 through forward rotation of the rotary shaft, or diffused to both ends of the processing bath 21 through reverse rotation of the rotary shaft. Since fermentative bacteria are fed into the processing bath 21 through the opening 24 together with used disposable diapers 100, in the shredding means 22, the used disposable diapers 100 are stirred together with the fermentative bacteria while being shredded and cut, whereby fermentation is performed.
The processing bath 21 has, on the top thereof, the heating means 23 for heating the processing bath 21. As shown in
The hot gas reservoir 38, which has a predetermined length, is provided on the top of the processing bath 21 so as to extend from one end of the bath, at which the opening 24 is provided, to the vicinity of an exhaust port 44 which is provided at the other end of the bath. A plurality of spray pipes 39 are provided on the bottom (in a vertical direction) of the hot gas reservoir 38 at predetermined intervals in a longitudinal direction so that one end of each of the spray pipes 39 is fixed to and communicated with the hot gas reservoir 38. The exhaust port 44, to which the gas discharging means 40 for aspirating and discharging atmosphere gas in the processing bath 21 is connected, is provided on the top of the processing bath 21 at the end opposite the longitudinal one end at which the opening 24 is provided. The hot gas reservoir 38 does not extend to a region on which the exhaust port 44 is provided, so that the spray pipes 39 are provided a predetermined distance away from the exhaust port 44. Therefore, oxygen-containing gas sprayed from the spray pipes 39 is not discharged directly through the exhaust port 44, and reduction in heating efficiency of the processing bath 21 is prevented.
Through use of the heating means 23, heated oxygen-containing gas in the hot gas reservoir 38 can be uniformly sprayed from the spray pipes 39 into the processing bath 21, to thereby heat the entire processing bath 21 to a predetermined temperature. The heating means 23 according to the present embodiment is configured so that a shredded product obtained through the shredding means 22 is controlled by a first heating temperature for heating the processing bath 21 for promoting the activity of fermentative bacteria during fermentation and drying the shredded product, to thereby yield a fermented product, and by a second heating temperature for sterilizing the fermented product in the processing bath 21 through heating, and evaporating water remaining in the fermented product, to thereby yield predetermined processed product. Through use of the heating means 23, predetermined processed waste 101 can be produced.
Fermentation capacity of the processing apparatus 20 varies depending on, for example, the size of the processing bath 21. The processing apparatus 20 according to the present embodiment has a fermentation capacity of 300 kg/day (fermentation time: about 12 hours). When used disposable diapers 100 are fed to the processing apparatus 20 for shredding/cutting, fermentation, drying, and heating/sterilization, processed waste 101 having a volume about ⅓ that of the used disposable diapers 100 can be produced. Thus, since the processed waste 101 produced in the processing apparatus 20 is reduced in volume and is finely divided, the processed waste 101 can be readily transported and subjected to granulation or molding. In addition, since the processed waste 101 is dried to form only a substance suitable for combustion, the processed waste 101 has physical properties which are very suitable for resource recycling (e.g., thermal recycling).
As shown in
Specifically, the exhaust port 44 is provided on the top of the processing bath 21, and a box-shaped dust collection section 42 including a filter 41 therein is provided on a region facing the exhaust port 44. The gas discharging means 40 is connected to the dust collection section 42 via the exhaust pipe 43 connected to the section 42.
When atmosphere gas in the processing bath 21 is aspirated and discharged by the gas discharging means 40 so that negative pressure is attained in the bath 21, fine dust, etc. contained in the atmosphere gas are collected by the filter 41.
The deodorizing means 50 for deodorizing atmosphere gas aspirated from the processing bath 21 by the gas discharging means 40 is provided on the way of the exhaust pipe 43 provided between the processing bath 21 and the gas discharging means 40, whereby the atmosphere gas is deodorized through heat exchange treatment.
As shown in
The transportation apparatus main body 62 is, for example, a gas-blowing/discharging apparatus or a vacuum pump for aspirating processed waste 101 in the processing bath 21, thereby transporting the processed waste 101. The processed waste 101 aspirated by the transportation apparatus main body 62 is stored in a bucket member 63 provided below the transportation apparatus main body 62. Atmosphere gas in the processing bath 21, which is aspirated simultaneous with aspiration of the processed waste 101 by the transportation means 60, is deodorized by the deodorizing means 50 connected to the exhaust pipe 43 of the gas discharging means 40, and then discharged to the outside.
Since used disposable diapers 100 fed to the aforementioned processing apparatus 20 is converted into processed waste 101 having a volume about ⅓ that of the used disposable diapers 100, when the processed waste 101 is employed as a fuel inside or outside of the institution 2, the amount of CO2 emission can be reduced, as compared with the case where used disposable diapers 100 are burned as is.
Next will be specifically described the amount of CO2 emission under the assumption that used disposable diapers 100 contain water in an amount of 65%. In general, when used disposable diapers 100 are burned as is at 300 kg/day for one month, the amount of CO2 emission is 169 kg per month (30 days). In contrast, in the present embodiment, when used disposable diapers 100 (300 kg/day) are recycled in the form of processed waste 101 as a fuel for one month (30 days), the amount of CO2 emission is reduced by 2,209 kg per month. Therefore, as compared with the case where used disposable diapers 100 are disposed of without being converted into processed waste 101, the amount of CO2 emission can be reduced by 2,378 kg/month, and the amount of CO2 emission can be reduced by 28,536 kg (i.e., about 30 t) per year. In the present embodiment, the amount of electricity used (consumed) by the disposal apparatus 10 is 333 kWh per month.
Next will be described a procedure for recycling used disposable diapers 100.
Firstly, in the institution 2, used disposable diapers 100 are fed in a predetermined amount to the processing apparatus 20, and processed waste 101 is produced (S1). The amount of the used disposable diapers 100 fed to the processing apparatus 20 and the amount of electricity used for producing the processed waste 101 are calculated and managed by the feed amount/electricity usage amount management means 82 (S2). In the case where the institution 2 includes the recovering facility 70 for employing the processed waste 101 (S3; YES), when a predetermined amount of the processed waste 101 is fed, as a fuel, to the recovering facility 70 (i.e., a combustion facility), the amount of combustion of the processed waste 101 is managed (S4), and the resultant heat is supplied in the institution 2 (S5). That is, the amount of the processed waste 101 fed to the recovering facility 70 is managed by the processed waste feed amount management means 81, and the amount of combustion of the thus-fed processed waste 101 is managed as the amount of CO2 emission. In this case, the amount of CO2 emission is reduced, as compared with the case where used disposable diapers 100 are burned as is. The amount of reduction in CO2 emission is converted into a CO2 emission right, and the CO2 emission right is stored in and managed by the CO2 reduction management means 80 (S6). In the CO2 reduction management means 80, data on the processed waste 101 produced by the processing apparatus 20 and employed inside or outside of the institution 2 are managed by an institution possessing the disposal apparatus 10 including the processing apparatus 20. The institution manages, for example, the amount of CO2 emission in the case where used disposable diapers 100 are disposed of through incineration as usual; the amount of CO2 emission per unit volume of the processed waste 101; the amount of reduction in CO2 emission; and a value converted from the amount of reduction in CO2 emission for managing the reduction amount in the form of a CO2 emission right. This system can contribute to reduction in amount of CO2 emission by recycling used disposable diapers 100.
Meanwhile, in the case where the institution 2 does not include the recovering facility 70 for employing the processed waste 101 (S3; NO), the thus-produced processed waste 101 is provided to the recovering facility 90 outside of the institution 2. That is, the shipment amount of the processed waste 101 provided outside of the institution 2 is managed by the processed waste shipment management means 83 (S7). Whether or not the processed waste 101 can be employed as is in the recovering facility 90 (i.e., whether or not the processed waste 101 must be subjected to treatment (e.g., compression)) is determined (S8). Since the processed waste 101 is a cut product produced mainly from paper and having a water content of 5%, if necessary, the processed waste is further processed into a form suitable for use in the recovering facility 90.
When the processed waste 101 is not required to be subjected to any treatment (e.g., compression) (S8; NO), the processed waste 101 is employed as a fuel as is in the recovering facility 90 (S9). In this case, similar to the case of step 5 (S5), the amount of CO2 emission is reduced, as compared with the case where used disposable diapers 100 are burned as is. The amount of reduction in CO2 emission is converted into a CO2 emission right, and the CO2 emission right is stored in and managed by the CO2 reduction management means 80 (S6).
Meanwhile, when the processed waste 101 must be subjected to treatment (e.g., compression) (S8; YES), the processed waste 101 is transformed so as to be suitable for the recovering facility 90 and then employed therein (S10). For example, the processed waste 101 is reduced in volume by a compressor included in the recovering facility 90 or the transformation means 91, or transformed into a solid fuel (e.g., RPF or RDF) by means of a predetermined facility, whereby the processed waste 101 can be flexibly applied to a variety of uses. Thus, the processed waste 101 in the form of solid fuel can be employed instead of a fossil fuel (e.g., coal or coke). The thus-transformed processed waste 101 may be transported to and employed in another facility.
As described above, in the present embodiment, processed waste 101 produced from used disposable diapers 100 (i.e., a raw material) in the processing apparatus 20 is burned (employed) in the recovering facility 70 or 90, whereby, eventually, the amount of CO2 emission can be reduced, as compared with the case where used disposable diapers 100 are burned as is. When the amount of CO2 emission, which is reduced through production of the processed waste 101, is converted into another element (i.e., a CO2 emission right), for example, a third-party organization or an institution discharging CO2 can flexibly take measures to reduce CO2 emission upon request.
According to the present embodiment, for example, an institution possessing the disposal apparatus 10 including the aforementioned processing apparatus 20 can manage a CO2 emission right having a trading value on the basis of the amount of CO2 emission, which is reduced through production of the processed waste 101. For example, the managed CO2 emission right can be offered to a requesting third-party organization for, for example, payment of a reasonable value.
The used disposable diaper recycling system and method of the present invention are useful in, for example, a variety of industries handling CO2 as a commodity, and various service businesses for trading, management, and operation of a predetermined amount of CO2.
| Number | Date | Country | Kind |
|---|---|---|---|
| 2005-174024 | Jun 2005 | JP | national |
| Filing Document | Filing Date | Country | Kind | 371c Date |
|---|---|---|---|---|
| PCT/JP2006/011869 | 6/13/2006 | WO | 00 | 12/13/2007 |
