CN114101296A - Organic matter degradation device and organic matter degradation method - Google Patents
Organic matter degradation device and organic matter degradation method Download PDFInfo
- Publication number
- CN114101296A CN114101296A CN202010885961.0A CN202010885961A CN114101296A CN 114101296 A CN114101296 A CN 114101296A CN 202010885961 A CN202010885961 A CN 202010885961A CN 114101296 A CN114101296 A CN 114101296A
- Authority
- CN
- China
- Prior art keywords
- far infrared
- organic matter
- degradation
- infrared ray
- energy
- Prior art date
- Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
- Granted
Links
Images
Landscapes
- Physical Or Chemical Processes And Apparatus (AREA)
Abstract
The invention relates to an organic matter degradation device, wherein the side wall of a reaction chamber at least comprises an energy resonance/reflection/energy storage unit, and the energy resonance/reflection/energy storage unit is made of an infrared material. The invention reflects the heat energy in each cycle of degradation reaction through the infrared material, and transfers the heat energy combined with the heat energy released by the infrared material to the undegraded organic matters in the accommodating space of the reaction chamber again, so that the organic matters are continuously subjected to degradation reaction again. The organic matter degradation device has the effects of active heat radiation to present uniform heat effect, low energy consumption and quick degradation time, and accumulated heat energy can achieve continuous degradation reaction after multiple times without being supplied with subsequent heat energy by the initial heating device all the time. The invention also provides a method for degrading the organic matters.
Description
Technical Field
The present invention relates to a degradation apparatus and a degradation method, and more particularly, to a degradation apparatus and a degradation method for treating organic substances.
Background
The existing degradation device such as the volume reduction device disclosed in taiwan patent publication No. TWI698292, mainly deposits organic matters in the reaction chamber, so that the organic matters can be slowly and simultaneously dried, carbonized and ashed, and because the reaction chamber does not have a chimney for diffusing waste gas to the atmosphere, in order to realize the drying, carbonization and ashing of the organic matters, an exhaust pipe for taking out the waste gas from the upper space of the reaction chamber and the subsequent treatment of the waste gas are provided; on the other hand, the low oxygen gas supply method is used to continue the steps of drying, carbonizing, ashing, etc. of the lower end portion of the organic matter for a long period of time. The gas supply mode is as disclosed in Chinese patent publication No. CN104456574B, which comprises a gas supply mechanism for supplying gas into the reaction chamber; wherein the air supply mechanism comprises an air supply mechanism for supplying air to the main pipe and a plurality of branch pipes which are branched from the main pipe in the length direction and blow air into the reaction chamber.
Regarding the drying, carbonization and ashing of the lower end part of the organic matter, taiwan patent publication No. TW200602134 discloses that a powdered ceramic magnetic layer, a charcoal fire layer, a sawdust layer and an organic waste layer are sequentially laid on the upper side of a bottom plate of a reaction chamber, and the powdered ceramic magnetic layer is preheated by the charcoal fire layer, so that the powdered ceramic magnetic layer stores heat and achieves a heat radiation effect. However, the ceramic layer can only store heat, and the ceramic magnetic layer can only generate heat radiation after storing heat. In addition, as in the case of the patent, the powdered ceramic layer must be scraped off when the residue is discharged, and the layer thickness of the remaining powdered ceramic layer is controlled; in other words, when the reaction chamber is used next time, the layer thickness of the powdered ceramic magnetic layer left in the previous time must be considered, and then the powdered ceramic magnetic layer is re-laid. Obviously, this causes operational troubles and inconveniences, such as time-consuming work site to measure the layer thickness of the powdered ceramic magnetic layer at different positions with a ruler, then repeatedly scraping the powdered ceramic magnetic layer back and forth with a scraper, then calculating the amount of powdered ceramic to be added, and repeatedly scraping back and forth with a scraper after the addition, so that the heat radiation exhibits uniform thermal effect on the organic waste layer.
The technology of the TW200602134 patent also discloses that the heat source is only from the powdered ceramic magnetic layer and the charcoal fire layer at the bottom of the reaction chamber. However, in practice, the thickness of the organic waste layer is much greater than that of the ceramic magnetic layer and the charcoal fire layer, and the heat energy for degrading the organic waste can only be gradually transferred from the powdered ceramic magnetic layer and the charcoal fire layer at the bottom of the reaction chamber to the organic waste layer at the upper layer, so that the heat transfer effect of the organic waste is known to be very poor, and thus the time for the technology of TW200602134 patent to convert the whole organic waste layer into the carbonized layer becomes very long. In addition, in the process, the heat energy transferred from the powder ceramic magnetic layer and the charcoal fire layer to the upper layer is also dissipated to the outside of the reaction chamber from the wall surface of the reaction chamber, which makes the heat energy generated by the powder ceramic magnetic layer and the charcoal fire layer not be effectively utilized and wasted.
Disclosure of Invention
The invention mainly aims to provide an organic matter degradation device and an organic matter degradation method, which have the main advantages of uniform thermal effect, low energy consumption and quick degradation time due to active thermal radiation.
The technical means adopted by the invention are as follows.
In order to achieve the above-mentioned object, an organic matter degradation device is provided, which at least comprises: the reaction chamber comprises a hearth, a side wall and a top cover, two ends of the side wall are respectively connected with the hearth and the top cover, and the hearth, the side wall and the top cover form an accommodating space together; wherein, the side wall at least comprises an energy resonance/reflection/energy storage unit which is made of an infrared material.
The organic matter degradation device as described above, wherein the infrared material is a far infrared material.
The organic matter degradation device as described above, wherein the far infrared material comprises a far infrared reflection material and a far infrared radiation material.
The organic matter degradation device as described above, wherein the inner surface layer of the sidewall is formed by the energy resonance/reflection/energy storage unit.
The organic matter degradation device as described above, wherein the energy resonance/reflection/energy storage unit is stacked from inside to outside with a far infrared radiation layer formed by the far infrared radiation material and a far infrared reflection layer formed by the far infrared reflection material.
The organic matter degradation device as described above, wherein the far infrared material further comprises a thermal insulation material, and the energy resonance/reflection/energy storage unit is stacked with the far infrared radiation layer, the far infrared reflection layer and the thermal insulation layer formed by the thermal insulation material from inside to outside.
The organic matter degradation device as described above, wherein the far infrared ray reflective material and/or the far infrared ray radiation material is a non-metallic material.
The organic matter degrading device as described above, wherein the far infrared reflecting material is selected from the group consisting of ZrC (zirconium carbide), TiC (titanium carbide), TaC (tantalum carbide), MoC (molybdenum carbide), WC (tungsten carbide), and B4C (boron carbide), SiC (silicon carbide), TiSi2(titanium silicide), WSi2(tungsten silicide), MoSi2Titanium disilicide, ZrB2(zirconium diboride), TiB2(titanium diboride), CrB2Chromium boride, ZrN, TiN, AlN, and Si3N4At least one of the group consisting of (silicon nitride).
The organic matter degradation device as described above, wherein the far infrared ray-emitting material is selected from the group consisting of MgO (magnesium oxide), CaO (calcium oxide), BaO (barium oxide), ZrO2(zirconium dioxide), TiO2(titanium dioxide) and Cr2O3(chromium oxide), MnO2(manganese dioxide), Fe2O3(iron oxide) and Al2O3At least one of the group consisting of (aluminum oxide), Ta (tantalum), Mo (molybdenum), W (tungsten), Fe (iron), Ni (nickel), Pt (platinum), Cu (copper) and Au (gold).
The organic matter degradation device as described above, wherein the far infrared ray reflective material is silicon carbide and the far infrared ray radiation material is magnesium oxide.
The organic matter degradation device as described above, wherein the far infrared material further comprises a thermal insulation material, and the thermal insulation material is a light porous inorganic material.
The organic matter degradation device as described above, wherein the far infrared ray radiation material has a particle size of 14 μm or less, preferably a particle size distribution of 0.4 to 14 μm (micrometer), a number average particle size of 3.83 μm, and 99% of the number of powder particles having a particle size of less than 11.85 μm, and an average far infrared ray radiation coefficient of 0.98 or more.
In order to achieve the above-mentioned implementation objective, a method for degrading organic substances is further provided, which sequentially comprises the following steps: a step of providing an organic matter degradation device: providing an organic matter degradation device and an initial heating device, wherein the initial heating device is arranged on the side wall or the hearth; a step of stacking organic matters: placing an organic matter pile in the accommodating space; a heat supply step: starting the initial heating device and continuing for a preset time period; a step of turning off the heat source: after the initial heating device is started for the preset time period, the initial heating device is closed; a continuous degradation step: after the initial heating device is closed, the far infrared ray reflecting material of the energy resonance/reflection/energy storage unit on the side wall reflects the heat energy generated by the degradation reaction of the organic matter in the accommodating space back to the accommodating space so as to provide the heat energy required by the degradation reaction of the organic matter again; the heat energy reflected back to the containing space and the far infrared heat energy radiated by the far infrared radiation material provide heat energy for the organic matter in the containing space for continuous degradation reaction; a degradation completion step: observing the state of the accommodating space until the degradation reaction of the organic matter is judged to be finished or a preset degradation degree is reached.
Drawings
FIG. 1: the invention discloses a three-dimensional schematic diagram of the whole framework of an organic matter degradation device.
FIG. 2: the invention relates to a reaction chamber section schematic diagram of an organic matter degradation device.
FIG. 3: the invention discloses a side wall structure schematic diagram (I) of an organic matter degradation device.
FIG. 4: the side wall structure of the organic matter degradation device is shown in the second step.
FIG. 5: the side wall structure of the organic matter degradation device is shown schematically (III).
FIG. 6: the invention relates to a flow chart of steps of an organic matter degradation method.
FIG. 7: the organic matter degradation device is provided with an integral framework three-dimensional schematic diagram of an air supply unit and an anion generating unit.
FIG. 8: the organic matter degradation device is provided with a schematic structural diagram of a negative ion generating unit.
FIG. 9: the negative ion generating unit of the organic matter degradation device is provided with a structural schematic diagram of a coil module.
Description of the figure numbers:
1: organic matter degradation device
10 reaction chamber
11: hearth
12 side wall
121: observation port
122 energy resonance/reflection/energy storage unit
1221 far infrared ray radiation layer
1222 far infrared reflecting layer
1223 insulating layer
123 supporting layer
13, top cover
131: inlet
14: discharge port
20 air supply unit
21 air box
22: trachea
23 branch pipe
231 first sub-tube
232 the second sub-pipe
2321 air outlet
30 negative ion generating unit
31 circuit module
32: lead module
33 coil module
331 loop portion
40 starting heating device
S is a containing space
S1 step of providing organic matter degradation device
S2 step of stacking organic matter
S3 step of providing heat source
S4 step of turning off heat source
S5 continuous degradation step
And S6, a degradation finishing step.
Detailed Description
First, referring to fig. 1 and fig. 2, an organic matter degradation apparatus 1 of the present invention at least comprises a reaction chamber 10 and an initial heating apparatus 40. The reaction chamber 10 includes a hearth 11, a sidewall 12 and a top cover 13, wherein two ends of the sidewall 12 are respectively connected to the hearth 11 and the top cover 13, the hearth 11, the sidewall 12 and the top cover 13 together form an accommodating space S, and organic substances (not shown) are accumulated in the accommodating space S. The side wall 12 may be a hollow cylinder (or referred to as hollow cylinder), such as a hollow cylinder, a hollow elliptic cylinder, a hollow rectangular or square body, or a hollow annular cylinder with any cross-section. Certainly, the sidewall 12 may be provided with a viewing port 121, the viewing port 121 is sealed by a transparent material (e.g., glass or quartz) to ensure that outside air does not enter the accommodating space S from the viewing port 121 to damage the reaction environment of the organic matter degradation reaction, and the viewing port 121 may be used for an operator to view the condition of the accommodating space S. The top cover 13 may be provided with a feeding port 131, the feeding port 131 is connected to the accommodating space S and the outside, and during operation, the door of the feeding port 131 may be opened first to feed organic substances into the accommodating space S from the upper side of the feeding port 131 through the feeding port 131, and then the door of the feeding port 131 is closed to ensure that the outside air does not enter the accommodating space S from the feeding port 131 to damage the reaction environment. The organic matter degradation device 1 may further include a discharge port 14, the discharge port 14 communicates the accommodating space S with the outside or an exhaust gas treatment device (not shown), the discharge port 14 may be disposed on the side wall 12 or the top cover 13, and the discharge port 14 discharges the exhaust gas generated by the reaction chamber 10 to the outside or the exhaust gas treatment device during operation.
Referring to fig. 3 and 4, the sidewall 12 at least includes an energy resonance/reflection/energy storage unit 122, and the sidewall 12 is entirely formed by the energy resonance/reflection/energy storage unit 122 (fig. 3); alternatively, the sidewall 12 is composed of a supporting layer 123 and the inner surface layer of the sidewall 12 adhered to the supporting layer 123, and the inner surface layer of the sidewall 12 is composed of the energy resonance/reflection/energy storage unit 122 (fig. 4). For example, the energy resonance/reflection/storage unit 122 is made of an infrared material capable of releasing infrared rays with a wavelength of 0.78 to 1000 μm, the sidewall 12 is made of the infrared material, or the inner surface layer of the sidewall 12 is made of the infrared material. Inside the side wall 12The surface layer is a surface layer of the side wall 12 constituting the receiving space S, in other words, an inner surface layer of the side wall 12 may contact with organic matter during a degradation reaction. Preferably, the infrared material is a far infrared material capable of releasing far infrared rays having a wavelength of 8 to 12 micrometers. The far infrared ray material comprises a far infrared ray reflecting material, a far infrared ray emitting material and a heat preserving material. The far infrared reflecting material is a non-oxide inorganic material, and is selected from ZrC (zirconium carbide), TiC (titanium carbide), TaC (tantalum carbide), MoC (molybdenum carbide), WC (tungsten carbide), and B4C (boron carbide), SiC (silicon carbide), TiSi2(titanium silicide), WSi2(tungsten silicide), MoSi2Titanium disilicide, ZrB2(zirconium diboride), TiB2(titanium diboride), CrB2Chromium boride, ZrN, TiN, AlN, and Si3N4At least one of the group consisting of (silicon nitride); the far infrared ray-emitting material is a metal oxide, and is selected from MgO (magnesium oxide), CaO (calcium oxide), BaO (barium oxide), and ZrO2(zirconium dioxide), TiO2(titanium dioxide) and Cr2O3(chromium oxide), MnO2(manganese dioxide), Fe2O3(iron oxide) and Al2O3(aluminum oxide) or the far infrared ray-emitting material is a metal material, the far infrared ray-emitting material is at least one selected from the group consisting of Ta (tantalum), Mo (molybdenum), W (tungsten), Fe (iron), Ni (nickel), Pt (platinum), Cu (copper) and Au (gold), and the far infrared ray-emitting material can release far infrared rays having a wavelength of 8 to 12 μm; the insulating material may be a lightweight porous inorganic material, such as zeolite. Preferably, the far infrared ray reflecting material is SiC, the far infrared ray emitting material is MgO, and the heat insulating material is zeolite. The far infrared ray reflecting material reflects the heat energy generated by the degradation reaction of the organic matters in the accommodating space S back to the accommodating space S so as to provide the heat energy required by the degradation reaction of the organic matters again; the heat energy reflected back to the accommodating space S,and far infrared ray heat energy radiated by the far infrared ray radiation material, which provides heat energy for the organic matter in the containing space S to continuously carry out degradation reaction so as to form the so-called 'energy resonance' to achieve the effects of uniform heat effect and quick degradation time; the heat insulating material is used to prevent heat energy from dissipating from the accommodating space S to the external environment, so that the whole organic matter degradation device 1 can turn off the initial heating device 40 during the organic matter degradation reaction process due to the so-called "energy resonance" and the heat insulating effect of the heat insulating material, thereby achieving the effect of low energy consumption.
The far infrared ray radiation material has a particle size of 14 μm or less, preferably a particle size distribution of 0.4 to 14 μm, a number average particle size of 3.83 μm, 99% of the powder particle size of less than 11.85 μm, and an average far infrared ray radiation coefficient of 0.98 or more. When the energy resonance/reflection/storage unit 122 is manufactured, the far infrared ray reflection material, the far infrared ray radiation material and the heat insulation material may be selectively mixed with an adhesive (such as an inorganic adhesive, inorganic ceramic powder) and then sintered. Alternatively, as shown in fig. 5, the energy resonance/reflection/storage unit 122 is stacked from inside to outside with a far infrared ray radiation layer 1221 formed by the far infrared ray radiation material, a far infrared ray reflection layer 1222 formed by the far infrared ray reflection material, and a thermal insulation layer 1223 formed by the thermal insulation material, wherein the thermal insulation layer 1223 is stacked inside the supporting layer 123.
Referring again to fig. 2, the initial heating device 40 can be disposed on the sidewall 12 or the hearth 11, and preferably the initial heating device 40 is disposed on the sidewall 12. The initial heating device 40 may be an electric heater, a hot air supplier, a charcoal fire, or other heat source to provide the required heat energy during the initial stage of the organic degradation reaction.
Referring to fig. 6, the organic matter degradation apparatus 1 degrades organic matter by an organic matter degradation method. The organic matter degradation method comprises the following steps in sequence.
A step S1 of providing an organic matter degradation device: the organic matter degradation device 1 described above is provided.
A step S2 of stacking organic matters: the organic matter is piled up in the accommodating space S, for example, the organic matter is thrown into the accommodating space S from above the inlet 131 through the inlet 131, and then the door of the inlet 131 is closed to ensure that the external air does not enter the accommodating space S from the inlet 131 to damage the reaction environment.
A heat supply step S3: when the initial heating device 40 is turned on, for example, the initial heating device 40 uses an electric heater, the initial heating device 40 can provide an initial degradation heat energy, for example, the initial degradation heat energy provides an activation energy for breaking carbon-hydrogen bonds (bond energy is about 100Kcal/mol) of organic substances, and for example, the initial degradation heat energy provides an activation energy for flameless combustion (also referred to as smoldering or low-oxygen combustion) reaction. Since smoldering is an exothermic reaction, the energy (heat energy) released by the exothermic reaction is more than the initial degradation heat energy used to provide the activation energy for the smoldering reaction, and thus the additional heat energy is transferred toward the energy resonance/reflection/accumulation unit 122 of the side wall 12, for example, in fig. 5. The initial heating means 40 may be turned on for a predetermined period of time.
A heat source off step S4: after the predetermined period of time has elapsed after the initial heating device 40 is turned on, the initial heating device 40 is turned off.
A continuous degradation step S5: the excess heat energy is transmitted toward the energy resonance/reflection/energy storage unit 122 of the sidewall 12 in fig. 5, wherein the excess heat energy is reflected by the far infrared ray reflection layer 1222, and then transmitted again toward the undegraded organic matter in the accommodating space S in combination with the heat energy released by the far infrared ray radiation layer 1221, so that the organic matter continues to undergo degradation reaction again. Thus, the heat energy generated by each degradation reaction is reflected by the far infrared reflection layer 1222, and combined with the heat energy released by the far infrared radiation layer 1221, the heat energy is transferred to the undegraded organic matter in the accommodating space S again, so that the organic matter continues to undergo the degradation reaction again. The insulating layer 1223 can reduce or prevent heat energy from dissipating from the accommodating space S to the outside, and the far infrared ray reflective layer 1222 is disposed outside the far infrared ray reflective layer 1221, so as to ensure that the heat energy released by the far infrared ray reflective layer 1221 is reflected by the far infrared ray reflective layer 1222 and can be re-transmitted to the undegraded organic matter in the accommodating space S. The accumulated heat energy after the multiple passes can thus achieve a continuous degradation reaction, i.e., a chain reaction, without the need for subsequent heat energy to be supplied from the initial heating device 40 all the time. In other words, as mentioned above, after the initial heating device 40 is turned off, the far infrared ray reflecting material reflects the heat energy generated by the degradation reaction of the organic substances in the accommodating space S back to the accommodating space S by the energy resonance/reflection/energy storage unit 122 of the side wall 12 to provide the heat energy for the degradation reaction of the organic substances again; the heat energy reflected back to the accommodating space S and the far infrared heat energy radiated by the far infrared radiation material provide heat energy for the organic matter in the accommodating space S together to carry out degradation reaction continuously so as to form the energy resonance to achieve the effects of uniform heat effect and quick degradation time; the heat insulating material is used to prevent heat energy from dissipating from the accommodating space S to the external environment, so that the whole organic matter degradation device 1 can turn off the initial heating device 40 in the organic matter degradation reaction process due to the so-called "energy resonance" and the heat insulating effect of the heat insulating material, thereby achieving the effect of low energy consumption.
A degradation completion step S6: the condition of the accommodating space S is observed through the observation port 121 until it is determined that the degradation reaction of the organic substance has been completed or a predetermined degradation degree is reached.
In addition, referring to fig. 7, 8 and 9, the organic matter degradation apparatus 1 further includes a gas supply unit 20 and a negative ion generation unit 30, the gas supply unit 20 is formed by combining a wind box 21, a plurality of gas pipes 22 and a plurality of branch pipes 23, wherein the wind box 21 is disposed outside the reaction chamber 10 and is substantially cylindrical, the wind box 21 is axially disposed along the height direction of the reaction chamber 10, and the wind box 21 supplies gas to the gas pipes 22 and the branch pipes 23 by a blower (not shown); in addition, the gas supply unit 20 includes a plurality of gas pipes 22 surrounding the reaction chamber 10 and arranged in parallel from top to bottom, wherein the gas pipes 22 are respectively connected to the wind boxes 21 to receive the gas from the wind boxes 21; furthermore, the air tube 22 is connected to the reaction chamber 10 by 12 branch tubes 23, that is, two ends of the branch tubes 23 are respectively connected to the air tube 22 and the accommodating space S of the reaction chamber 10, so that the air from the bellows 21 enters the accommodating space S through the air tube 22 and the branch tubes 23. The branch pipe 23 is composed of a first sub-pipe 231 disposed vertically and a second sub-pipe 232 disposed horizontally, in other words, the first sub-pipe 231 and the second sub-pipe 232 are disposed vertically, two ends of the first sub-pipe 231 are respectively connected to the air pipe 22 and the second sub-pipe 232, two ends of the second sub-pipe 232 are respectively connected to the first sub-pipe 231 and the accommodating space S of the reaction chamber 10, and the second sub-pipe 232 is connected to an air outlet 2321 of the accommodating space S of the reaction chamber 10 in an oblique manner. The negative ion generating unit 30 is disposed at one end of the branch pipe 23, for example: the negative ion generating unit 30 is disposed on the first sub-tube 231 vertically disposed, or the negative ion generating unit 30 is disposed on the second sub-tube 232 horizontally disposed; preferably, the negative ion generating unit 30 is disposed on the second sub-tube 232, which is disposed horizontally, so that the negative ions directly enter the reaction chamber 10, and the resistance of the negative ions generated by the negative ion generating unit 30 is effectively avoided. The negative ion generating unit 30 includes a circuit module 31 and a conducting wire module 32 connected to the circuit module 31, the circuit module 31 for generating a plurality of electrons is composed of a circuit board (not shown), a trigger circuit (not shown), a transformer (not shown) and a rectifying circuit (not shown), wherein the trigger circuit, the transformer and the rectifying circuit are respectively disposed on the circuit board and electrically connected to the circuit board, wherein the circuit board is electrically connected to a power source (not shown) for providing the power received from the power source to the electric energy required by the operation of the trigger circuit, the transformer and the rectifying circuit; one end of the lead module 32 away from the circuit module 31 extends into the second sub-tube 232 of the branch tube 23 and generates negative ions in the form of point discharge. The negative ion generating unit 30 includes a coil module 33 disposed around the outside of the lead module 32, and a portion of the coil module 33 forms a loop portion 331 and is disposed around the outside of the lead module 32, for example: the loop portion 331 is disposed around the front portion of the lead module 32, and the coil module 33 is electrically connected to the circuit module 31 or the power supply.
As can be seen from the above description, the organic matter degradation apparatus and the organic matter degradation method of the present invention have the following advantages compared with the prior art: the far infrared ray reflecting material reflects the heat energy generated by the degradation reaction of the organic matters in the accommodating space back to the accommodating space so as to provide the heat energy required by the degradation reaction of the organic matters again; the heat energy reflected back to the containing space and the far infrared heat energy radiated by the far infrared radiation material provide heat energy for the organic matter in the containing space to carry out degradation reaction continuously so as to form energy resonance and achieve the effects of uniform heat effect and quick degradation time; the heat-insulating material is used for preventing heat energy from being dissipated to the external environment from the accommodating space, so that the whole organic matter degradation device can be used for closing the initial heating device in the organic matter degradation reaction process due to the so-called energy resonance and the heat insulation effect of the heat-insulating material, and the effect of low energy consumption is achieved.
Claims (13)
1. An organic matter degradation device, characterized by comprising at least: the reaction chamber (10) comprises a hearth (11), a side wall (12) and a top cover (13), two ends of the side wall (12) are respectively connected with the hearth (11) and the top cover (13), and the hearth (11), the side wall (12) and the top cover (13) jointly form an accommodating space (S); wherein the sidewall (12) comprises at least one energy resonance/reflection/energy storage unit (122), and the energy resonance/reflection/energy storage unit (122) is made of an infrared material.
2. The organic matter degradation device according to claim 1, wherein the infrared material is a far infrared material.
3. The apparatus of claim 2, wherein the far infrared ray material comprises a far infrared ray reflecting material and a far infrared ray emitting material.
4. An organic matter degradation device according to claim 3, characterized in that the inner surface of the side wall (12) is formed by the energy resonance/reflection/storage unit (122).
5. The apparatus for degrading organic substances according to claim 3, wherein the energy resonance/reflection/storage unit (122) is stacked from inside to outside with a far infrared ray emitting layer (1221) made of the far infrared ray emitting material and a far infrared ray reflecting layer (1222) made of the far infrared ray reflecting material.
6. The apparatus for degrading organic substances according to claim 5, wherein the far infrared material comprises a thermal insulation material, and the energy resonance/reflection/energy storage unit (122) is formed by stacking the far infrared radiation layer (1221), the far infrared reflection layer (1222), and a thermal insulation layer (1223) made of the thermal insulation material from the inside to the outside.
7. The organic matter degrading device according to claim 3, wherein the far infrared ray reflecting material is a non-oxide inorganic material, and the far infrared ray emitting material is a metal oxide or a non-metal material.
8. The organic matter degrading device according to claim 3, wherein the far infrared reflecting material is selected from the group consisting of ZrC, TiC, TaC, MoC, WC, and B4C、SiC、TiSi2、WSi2、MoSi2、ZrB2、TiB2、CrB2ZrN, TiN, AlN and Si3N4At least one of the group consisting of.
9. The organic matter degrading device according to claim 3, wherein the far infrared ray radiating material is selected from MgO, CaO, BaO, ZrO, and the like2、TiO2、Cr2O3、MnO2、Fe2O3、Al2O3At least one of the group consisting of Ta, Mo, W, Fe, Ni, Pt, Cu and Au.
10. The organic substance degradation device according to claim 3, wherein the far infrared ray reflective material is silicon carbide and the far infrared ray emitting material is magnesium oxide.
11. The organic matter degradation device according to claim 10, wherein the far infrared material comprises a heat insulating material, and the heat insulating material is zeolite.
12. The organic matter degrading device according to claim 3, wherein the far infrared ray-emitting material has a particle size of 14 μm or less, a number average particle size of 3.83 μm, 99% by number of powder particles having a particle size of less than 11.85 μm, and an average far infrared ray radiation coefficient of 0.98 or more.
13. A method for degrading organic substances, which is characterized by sequentially comprising the following steps:
a step of providing an organic matter degradation device (S1): providing an organic matter degradation device (1) according to claim 3 and an initial heating device (40), wherein the initial heating device (40) is disposed on the sidewall (12) or the hearth (11);
a step of stacking organic materials (S2): placing an organic matter pile in the accommodating space (S);
a heat source providing step (S3): turning on the initial heating device (40) for a predetermined period of time;
a heat source off step (S4): turning off the initial heating device (40) after the predetermined period of time has elapsed after turning on the initial heating device (40);
a continuous degradation step (S5): after the initial heating device (40) is turned off, the far infrared ray reflecting material of the energy resonance/reflection/energy storage unit (122) of the side wall (12) reflects the heat energy generated by the degradation reaction of the organic matter in the accommodating space (S) back to the accommodating space (S) to provide the heat energy required by the degradation reaction of the organic matter again; the heat energy reflected back to the accommodating space (S) and the far infrared heat energy radiated by the far infrared radiation material provide heat energy for the organic matter in the accommodating space (S) together to carry out degradation reaction continuously;
a degradation completion step (S6): observing the condition of the accommodating space (S) until the degradation reaction of the organic matter is judged to be finished or a predetermined degradation degree is reached.
Priority Applications (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010885961.0A CN114101296B (en) | 2020-08-28 | 2020-08-28 | Organic matter degradation device and organic matter degradation method |
Applications Claiming Priority (1)
| Application Number | Priority Date | Filing Date | Title |
|---|---|---|---|
| CN202010885961.0A CN114101296B (en) | 2020-08-28 | 2020-08-28 | Organic matter degradation device and organic matter degradation method |
Publications (2)
| Publication Number | Publication Date |
|---|---|
| CN114101296A true CN114101296A (en) | 2022-03-01 |
| CN114101296B CN114101296B (en) | 2023-03-14 |
Family
ID=80375135
Family Applications (1)
| Application Number | Title | Priority Date | Filing Date |
|---|---|---|---|
| CN202010885961.0A Active CN114101296B (en) | 2020-08-28 | 2020-08-28 | Organic matter degradation device and organic matter degradation method |
Country Status (1)
| Country | Link |
|---|---|
| CN (1) | CN114101296B (en) |
Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3746504A (en) * | 1970-10-19 | 1973-07-17 | American Gas Ass | Radiant gas burner device for heating |
| CN201203144Y (en) * | 2007-12-21 | 2009-03-04 | 刘伟奇 | Biomass high-efficiency gasification reaction barrel |
| CN102603382A (en) * | 2012-03-16 | 2012-07-25 | 清华大学 | Organic waste aerobic composting test device |
| US20190195561A1 (en) * | 2017-12-27 | 2019-06-27 | National Chung-Shan Institute Of Science & Technology | Thermal insulation structure for heating device |
| CN210135586U (en) * | 2019-06-01 | 2020-03-10 | 云南联展科技有限公司 | Organic matter new material degradation device |
| CN211316199U (en) * | 2019-12-03 | 2020-08-21 | 盛势环球新材料股份有限公司 | Organic matter degradation device |
-
2020
- 2020-08-28 CN CN202010885961.0A patent/CN114101296B/en active Active
Patent Citations (6)
| Publication number | Priority date | Publication date | Assignee | Title |
|---|---|---|---|---|
| US3746504A (en) * | 1970-10-19 | 1973-07-17 | American Gas Ass | Radiant gas burner device for heating |
| CN201203144Y (en) * | 2007-12-21 | 2009-03-04 | 刘伟奇 | Biomass high-efficiency gasification reaction barrel |
| CN102603382A (en) * | 2012-03-16 | 2012-07-25 | 清华大学 | Organic waste aerobic composting test device |
| US20190195561A1 (en) * | 2017-12-27 | 2019-06-27 | National Chung-Shan Institute Of Science & Technology | Thermal insulation structure for heating device |
| CN210135586U (en) * | 2019-06-01 | 2020-03-10 | 云南联展科技有限公司 | Organic matter new material degradation device |
| CN211316199U (en) * | 2019-12-03 | 2020-08-21 | 盛势环球新材料股份有限公司 | Organic matter degradation device |
Also Published As
| Publication number | Publication date |
|---|---|
| CN114101296B (en) | 2023-03-14 |
Similar Documents
| Publication | Publication Date | Title |
|---|---|---|
| TWI360137B (en) | ||
| CN109851377B (en) | Laser-induced high-temperature solid-phase reaction for generating A2B2O7Method for forming thermal barrier coating material | |
| TWI243419B (en) | A barrier layer for a processing element and a method of forming the same | |
| US6632549B1 (en) | Corrosion-resistant member, wafer-supporting member, and method of manufacturing the same | |
| CN1550570A (en) | Fixing member for evaporation apparatus | |
| US20050016986A1 (en) | Ceramic heater | |
| CN104871305B (en) | Heat radiation barrier layer for substrate processing chamber component | |
| US20020185487A1 (en) | Ceramic heater with heater element and method for use thereof | |
| US20120122276A1 (en) | Thermal evaporation apparatus, use and method of depositing a material | |
| WO1989008605A1 (en) | Process for producing thin-film oxide superconductor | |
| CN114101296B (en) | Organic matter degradation device and organic matter degradation method | |
| US6432325B1 (en) | Electrode | |
| TWI748622B (en) | Organic matter degradation method | |
| US6383416B1 (en) | Electron-emitting material and preparing process | |
| JPH10204622A (en) | Thin film forming device | |
| US6379789B1 (en) | Thermally-sprayed composite selective emitter | |
| CN102531611B (en) | Method for preparing aluminum nitride | |
| TW201015615A (en) | Electrodeless bulb | |
| US11154386B2 (en) | Dental furnace | |
| JP2006236656A (en) | Manufacturing method for x-ray target member provided with cooling means and high-output x-ray generator for detecting heavy-metal provided with x-ray target member manufactured thereby | |
| US20100012478A1 (en) | Thermal treatment for inorganic materials | |
| JP2003246679A (en) | Apparatus for firing ceramic body to be fired and method of manufacturing ceramics | |
| JP3233300B2 (en) | Microwave sintering method | |
| CN210892720U (en) | Energy-conserving fritting furnace of high efficiency | |
| JP3398167B2 (en) | Picture tube |
Legal Events
| Date | Code | Title | Description |
|---|---|---|---|
| PB01 | Publication | ||
| PB01 | Publication | ||
| SE01 | Entry into force of request for substantive examination | ||
| SE01 | Entry into force of request for substantive examination | ||
| GR01 | Patent grant | ||
| GR01 | Patent grant |