Organic waste composite dehydration system
The organic waste composite dehydration system that combines physical dehydration devices and biological dehydration devices solves the problem of deep dehydration of organic waste in the existing technology, achieves efficient and low-cost deep dehydration, and promotes environmental protection and resource utilization.
Patent Information
- Application Number
- CN202422458403.2
- Authority / Receiving Office
- CN · China
- Patent Type
- Utility models(China)
- Current Assignee / Owner
- Filing Date
- 2024-10-11
- Publication Date
- 2025-09-30
- Estimated Expiration
- 2034-10-11
AI Technical Summary
Existing technologies make it difficult to reduce the moisture content of organic waste from about 80% to below 40% efficiently and at low cost, and there is a lack of equipment that integrates mechanical physical dehydration with biological fermentation dehydration, making resource utilization difficult.
An organic waste composite dehydration system is adopted, which combines physical dehydration devices and biological dehydration devices, including ultra-high pressure stacked box or belt dehydration devices and breathable fermentation bags/cylinders. Deep dehydration is achieved by combining mechanical and physical dehydration with biological fermentation.
Without relying on other organic auxiliary materials, organic waste can be deeply dehydrated to a moisture content of less than 40% efficiently and at low cost, meeting the requirements of resource utilization, reducing processing costs, and promoting the improvement of environmental protection and resource utilization levels.
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Figure CN223400045U_ABST
Abstract
Description
Technical Field
[0001] The utility model belongs to the technical field of organic waste composite dehydration, in particular to an organic waste composite dehydration system. Background Art
[0002] According to data released by relevant departments, my country generates nearly 6 billion tons of various organic wastes in production and life every year, and most of them have a moisture content of more than 70% to 80%. The solid matter in organic wastes that has resource utilization value is basically the solid matter. Therefore, it is necessary to utilize these organic wastes with high moisture content as resources and make them "turn waste into treasure and turn waste into use". The key is to reduce the moisture content of organic wastes efficiently and at low cost.
[0003] In production practice, commonly used organic waste dewatering technologies and equipment include belt filter presses, plate and frame filter presses, screw presses, centrifuges, and vacuum filters, which operate based on mechanical and physical principles, and tank and tower fermenters, which operate based on biological fermentation dehydration. The former generally limit their dehydration efficiency to reducing the moisture content of organic waste from approximately 80% to approximately 60%, which falls short of resource utilization requirements, but further reduction is difficult and significantly increases costs. While the latter can reduce the moisture content of organic waste from approximately 60% to below 40%, they require the addition of a significant proportion of auxiliary materials. In particular, organic wastes such as municipal sludge, which have relatively low nutrient content, require the addition of large amounts of high-energy organic auxiliary materials to adjust the carbon-nitrogen ratio for proper fermentation, significantly increasing treatment costs. Furthermore, there is currently no integrated deep dehydration equipment on the market that combines mechanical and physical dehydration with biological fermentation dehydration. Consequently, most organic waste, particularly municipal sludge, which has a high moisture content and relatively low organic matter and other nutrient content, cannot be effectively treated and utilized in an environmentally friendly manner.
[0004] Based on the actual production needs for environmental protection treatment and resource utilization of organic waste, an innovative integrated equipment integrating mechanical physical dehydration and biological fermentation dehydration has been developed. Without relying on other organic auxiliary materials or greatly reducing dependence on other organic auxiliary materials, it can directly and deeply dehydrate organic waste with a moisture content of about 80% or even higher to a moisture content of less than 40% at high efficiency and low cost, meeting the index requirements of resource utilization. It will be of great benefit to promoting the level of environmental protection management and resource utilization of organic waste in society and promoting the smoother realization of my country's "dual carbon" goals. Utility Model Content
[0005] The purpose of the utility model is to provide an organic waste composite dehydration system, which is used to solve the problem of directly dehydrating organic waste to a depth of less than 40% for better resource utilization.
[0006] The purpose of the present invention and the technical problem it solves are achieved by adopting the following technical solutions. According to the present invention, a composite dehydration system for organic waste is proposed, which includes:
[0007] Physical dehydration equipment, material crushing equipment and biological dehydration equipment;
[0008] The material crushing device is connected and installed at the rear end of the physical dehydration device and the front end of the biological dehydration device;
[0009] The physical dehydration device includes: an ultra-high pressure stacked box dehydration device or an ultra-high pressure stacked belt dehydration device;
[0010] The ultra-high pressure stacked box-type dehydration device includes: a box-type cloth feeder, a cloth / discharger, a filter cloth, a filter press chamber, a filter chamber lifting hydraulic press, a box-type filter press hydraulic press, and a box-type filter press hydraulic station;
[0011] The box-type material distribution feeder is installed at the front end of the material distribution / discharger; the material distribution / discharger is installed on the upper side of the filter press chamber, and the filter cloth is wound on the material distribution / discharger; the material distribution / discharger is installed on the upper side of the filter press chamber; the filter chamber lifting hydraulic press is installed below the filter press chamber; the box-type filter press hydraulic press is installed above the filter press chamber; the box-type filter press hydraulic station is connected to the filter chamber lifting hydraulic press and the box-type filter press hydraulic press through oil pipes;
[0012] The ultra-high pressure stacked belt dehydration device includes: a belt cloth feeding machine, a filter belt, a filter belt tractor, a belt filter press hydraulic press, and a belt filter press hydraulic station;
[0013] The belt cloth feeding loader is installed at the front end of the filter belt tractor; the filter belt is wound on the filter belt tractor and passes through the belt filter press hydraulic press; the belt filter press hydraulic press is connected to the belt filter press hydraulic station through a hydraulic oil pipe.
[0014] The purpose of the present invention and the solution to its technical problems can be further achieved by adopting the following technical measures.
[0015] In one embodiment of the present invention, the biological dehydration device includes one or more of a breathable fermentation bag, a breathable fermentation cylinder, or a breathable fermentation tray.
[0016] In one embodiment of the present invention, the material crushing device includes one or more of a chain crusher, a hammer / blade crusher or a toothed shredder.
[0017] In one embodiment of the present invention, it further comprises:
[0018] Buffer feeding device;
[0019] The buffer feeding device includes: a buffer belt conveyor and a screw conveyor feeder;
[0020] The buffer belt conveyor is connected and installed at the rear end of the physical dehydration device, and the screw conveyor feeder is connected and installed at the rear end of the buffer belt conveyor and the front end of the material crushing device.
[0021] In one embodiment of the present invention, it further comprises:
[0022] Auxiliary ventilation device;
[0023] The auxiliary ventilation device includes: a ventilation tray and / or a ventilation pad;
[0024] The breathable tray is placed below the breathable fermentation bag, the breathable fermentation cylinder or the breathable fermentation tray, and the breathable mat is placed below or / and between the breathable fermentation bags.
[0025] In one embodiment of the present invention, it further comprises:
[0026] Buffer unloading device;
[0027] The buffer unloading device includes: a collecting bin, a discharger and a pressure relief dust removal bag;
[0028] The material collection bin is connected and installed at the rear end of the material crushing device; the discharger is connected and installed at the lower end of the material collection bin; and the pressure relief dust removal bag is connected and installed on the material collection bin.
[0029] In one embodiment of the present invention, it also includes a material weighing device; the material weighing device is connected to the rear end of the material crushing device and the front end of the biological dehydration device, or is connected to the rear end of the buffer unloading device and the front end of the biological dehydration device.
[0030] Compared with the existing technology, the present invention has obvious advantages and beneficial effects. By means of the above technical solution, the organic waste composite dehydration system provided by the present invention has at least the following advantages and beneficial effects:
[0031] It can meet the needs of environmental protection treatment and resource utilization of organic waste in actual production, realize the integrated fusion of mechanical physical dehydration and biological fermentation dehydration, and can directly dehydrate organic waste with a moisture content of about 80% or even higher to a moisture content of less than 40% efficiently and at low cost without relying on other organic auxiliary materials or greatly reducing dependence on other organic auxiliary materials, thereby meeting the index requirements of resource utilization and reducing the treatment cost of social organic waste. It is of great benefit to promoting the improvement of the level of environmental protection management and resource utilization of organic waste in society and promoting the smoother realization of my country's "dual carbon" goals.
[0032] The above description is only an overview of the technical solution of the present invention. In order to more clearly understand the technical means of the present invention, it can be implemented in accordance with the contents of the specification. In addition, in order to make the above and other purposes, features and advantages of the present invention more obvious and easy to understand, the following preferred embodiments are specifically cited and described in detail with reference to the accompanying drawings. BRIEF DESCRIPTION OF THE DRAWINGS
[0033] In order to more clearly illustrate the technical solutions in the present invention, the following briefly introduces the drawings required for use in the embodiments. Obviously, the drawings described below are only some embodiments of the present invention. For ordinary technicians in this field, other drawings can be obtained based on these drawings without creative work.
[0034] Figure 1 This is a schematic diagram of the main structure of the first embodiment of the organic waste composite dehydration system provided by the present utility model;
[0035] Figure 2 This is a schematic diagram of the main structure of the second embodiment of the organic waste composite dehydration system provided by the present utility model;
[0036] Figure 3 This is a schematic diagram of the main structure of the third embodiment of the organic waste composite dehydration system provided by the present utility model;
[0037] Figure 4 This is a schematic diagram of the main structure of a fourth embodiment of the organic waste composite dehydration system provided by the present utility model;
[0038] Figure 5 This is a schematic diagram of the main structure of a fifth embodiment of the organic waste composite dehydration system provided by the present utility model;
[0039] Reference numerals:
[0040] 1-Physical dehydration device;
[0041] 11-Ultra-high-pressure stacked box-type dehydration device; 111-Box-type cloth feeder; 112-Bag / discharger; 113-Filter cloth; 114-Filter press chamber; 115-Filter chamber lifting hydraulic press; 116-Box-type filter press hydraulic press; 117-Box-type filter press hydraulic station;
[0042] 12-Ultra-high-pressure stacked belt dewatering device; 121-Belt cloth feeder; 122-Filter belt; 123-Filter belt tractor; 124-Belt filter press hydraulic press; 125-Belt filter press hydraulic station;
[0043] 2-Material crushing device; 21-Chain crusher; 22-Hammer / blade crusher; 23-Tooth shredder;
[0044] 3-biological dehydration device; 31-breathable fermentation bag; 32-breathable fermentation cylinder; 33-breathable fermentation tray;
[0045] 4- cache feeding device; 41- cache belt conveyor; 42- screw conveyor feeder;
[0046] 5- auxiliary ventilation device; 51- ventilation tray; 52- ventilation pad;
[0047] 6-buffer unloading device; 61-collection bin; 62-discharger; 63-pressure relief dust bag;
[0048] 7-Material weighing device. DETAILED DESCRIPTION
[0049] In order to further illustrate the technical means and effects adopted by the present invention to achieve the predetermined purpose of the utility model, the specific implementation method, structure, characteristics and effects of the multi-source organic waste collaborative treatment system proposed by the present invention are described in detail below in combination with the accompanying drawings and preferred embodiments.
[0050] Example 1:
[0051] See also Figure 1 As shown, the organic waste composite dehydration system of the first embodiment of the present invention mainly includes: a physical dehydration device 1, a material crushing device 2 and a biological dehydration device 3; wherein, the material crushing device 2 is connected and installed at the rear end of the physical dehydration device 1 and the front end of the biological dehydration device 3. It can be understood that the physical dehydration device 1 is an ultra-high pressure stacked box-type dehydration device 11, and the ultra-high pressure stacked box-type dehydration device 11 includes: a box-type cloth feeder 111, a cloth / discharger 112, a filter cloth 113, a filter press chamber 114, a filter chamber lifting hydraulic machine 115, a box-type filter press hydraulic machine 116 and a box-type filter press hydraulic station 117; the box-type cloth feeder 111 is installed at the front end of the cloth / discharger 112, The filter cloth 113 is wound on the distribution / discharger 112, the distribution / discharger 112 is installed on the upper side of the filter press chamber 114, the filter chamber lifting hydraulic machine 115 is installed below the filter press chamber 114, the box-type filter press hydraulic machine 116 is installed above the filter press chamber 114, and the box-type filter press hydraulic station 117 is connected to the filter chamber lifting hydraulic machine 115 and the box-type filter press hydraulic machine 116 through an oil pipe.
[0052] It should be noted that, since the dehydrated material is organic waste such as cassava starch residue and pig manure with high fiber content, low bulk density and low hardness, the material crushing device 2 is a chain crusher 21 and the biological dehydration device 3 is a breathable fermentation bag 31.
[0053] Example 2:
[0054] See also Figure 2 As shown, the organic waste composite dehydration system of the second embodiment of the present invention is similar to that of the first embodiment, with the only difference being:
[0055] The physical dehydration device 1 is an ultra-high pressure laminated belt dehydration device 12 , which includes: a belt cloth feeder 121 , a filter belt 122 , a filter belt tractor 123 , a belt filter press hydraulic press 124 and a belt filter press hydraulic station 125 .
[0056] The belt feeder 121 is installed at the front end of the filter belt tractor 123, the filter belt 122 is wound on the filter belt tractor 123 and passes through the belt filter press hydraulic press 124, and the belt filter press hydraulic press 124 is connected to the belt filter press hydraulic station 125 through a hydraulic oil pipe.
[0057] The biological dehydration device 3 is a breathable fermentation cylinder 32.
[0058] It is understood that in order to facilitate the asynchronous and flexible operation of the physical dehydration device 1 while the material crushing device 2 performs intermittent operation while performing uninterrupted dehydration, a buffer feeding device 4 is additionally configured. The buffer feeding device 4 includes a buffer belt conveyor 41 and a screw conveyor feeder 42; the buffer belt conveyor 41 is connected to the rear end of the physical dehydration device 1, and the screw conveyor feeder 42 is connected to the rear end of the buffer belt conveyor 41 and the front end of the material crushing device 2.
[0059] It should be noted that if continuous dehydration and intermittent crushing operations are required, the material flakes dehydrated by the physical dehydration device 1 are first stored in the cache belt conveyor 41 of the cache feeding device 4. When crushing is required, the cache belt conveyor 41 and the screw conveyor feeder 42 are started again, and the cache belt conveyor 41 feeds the screw conveyor feeder 42, and the screw conveyor feeder 42 feeds the material crushing device 2.
[0060] Example 3:
[0061] See also Figure 3 As shown, the organic waste composite dehydration system of the third embodiment of the present invention is similar to the first embodiment, with the only difference being:
[0062] Since the dehydrated material is organic waste with high bulk density and hardness, such as municipal sludge and sugar filter mud, the material crushing device 2 is a hammer / blade crusher 22.
[0063] It is understood that in order to ensure better ventilation, oxygen supply, and heat dissipation when the organic waste, which has been crushed into powder by the hammer / blade crusher 22, is loaded into the breathable fermentation bags 31 for stacking, fermentation, and dehydration, thereby improving the efficiency of biological fermentation and dehydration, an auxiliary ventilation device 5 is added. The auxiliary ventilation device 5 includes a ventilation tray 51 and a ventilation mat 52. When the organic waste, which has been dehydrated by the physical dehydration device 1 and crushed by the material crushing device 2, is loaded into the breathable fermentation bags 31 for stacking and fermentation, the ventilation tray 51 is placed below the breathable fermentation bags 31, and the ventilation mat 52 is placed between the breathable fermentation bags 31.
[0064] Example 4:
[0065] See also Figure 4 As shown, the organic waste composite dehydration system of the fourth embodiment of the present invention is similar to the first embodiment, with the only difference being:
[0066] The biological dehydration device 3 is a breathable fermentation tray 33 .
[0067] It is understood that in order to facilitate the asynchronous and flexible operation of the material crushing device 2 while the crushed organic waste is intermittently loaded into the biological dehydration device 3, a buffer unloading device 6 is additionally configured. The buffer unloading device 6 includes a collection bin 61, a discharger 62, and a pressure relief dust removal bag 63; the collection bin 61 is connected to the rear end of the material crushing device 2, the discharger 62 is connected to the lower end of the collection bin 61, and the pressure relief dust removal bag 63 is connected to the collection bin 61.
[0068] It should be noted that if it is necessary to perform continuous crushing operations on organic waste and intermittent loading into the breathable fermentation tray 33, the material crushed by the material crushing device 2 is first stored in the collecting bin 61, and when it is needed to be loaded into the breathable fermentation tray 33, the discharger 62 is started, and the discharger 62 loads the crushed material into the breathable fermentation tray 33.
[0069] Embodiment 5:
[0070] See also Figure 5 As shown, the organic waste composite dehydration system of the fifth embodiment of the present invention is similar to that of the fourth embodiment, with the only difference being:
[0071] The material crushing device 2 is a toothed shredder 23 .
[0072] It is understood that in order to achieve quantitative loading of the organic waste crushed by the material crushing device 2 into the biological dehydration device 3 for biological fermentation and dehydration, a material weighing device 7 is additionally configured. The material weighing device 7 is connected and installed at the rear end of the buffer unloading device 6 and the front end of the biological dehydration device 3.
[0073] The dehydration method of the organic waste composite dehydration system of the utility model comprises the following steps:
[0074] S1 Physical dehydration of materials: The physical dehydration device 1 is started, and the dehydrated material is laid and clamped on the filter belt 122 by the belt cloth feeder 121, and is directly pulled and transported to the belt filter press hydraulic press 124 by the filter belt tractor 123 for ultra-high pressure filtration dehydration, or the dehydrated material is laid and clamped on the filter cloth 113 by the box cloth feeder 111 and the cloth / discharger 112, and the material layers clamped by the filter cloth 113 are folded into multiple layers by the cloth / discharger 112 and laid into the filter press chamber 114, and the multiple layers of dehydrated material in the filter press chamber 114 are subjected to ultra-high pressure filtration dehydration by the box filter press hydraulic press 116, and the belt filter press hydraulic press 124 or the box filter press hydraulic press 116 dehydrates the dehydrated material into sheets with a moisture content of 55% to 40%;
[0075] S2 Flake Crushing: Flakes with a moisture content of 55% to 40% are unloaded from the filter belt 122 or the filter cloth 113 by the filter belt tractor 123 or the cloth / discharger 112, and crushed into powder and / or small particles or flakes by the material crushing device 2;
[0076] S3 Biological Dehydration: Powdered and / or small granular or flake organic materials with a moisture content of 55% to 40% are loaded into the biological dehydration device 3 for 2 to 20 days of biological aerobic fermentation. Microorganisms decompose the materials to generate heat and raise the temperature to above 65°C, evaporating the moisture and dehydrating the materials to a moisture content of less than 40%.
[0077] In the first specific embodiment of the dehydration method of the organic waste composite dehydration system of the present invention, the physical dehydration device 1 used is the ultra-high pressure stacked box dehydration device 11, and the biological dehydration device 3 is the breathable fermentation bag 31 that compositely dehydrates municipal sludge with an initial moisture content of 80% to a moisture content of 30%. The specific steps of the dehydration method are as follows:
[0078] S1 Physical dehydration of materials: The ultra-high pressure stacked box-type dehydration device 11 is started, and the municipal sludge with a moisture content of 80% is conveyed to the distributing / discharging machine 112 via the box-type distributing feeder 111. The distributing / discharging machine 112 lays and sandwiches the municipal sludge with a moisture content of 80% on the filter cloth 113, and folds the municipal sludge with a moisture content of 80% sandwiched by the filter cloth 113 into multiple layers via the distributing / discharging machine 112 and distributes the layers into the filter press chamber 114. The multiple layers of municipal sludge in the filter press chamber 114 are subjected to ultra-high pressure filtration dehydration by the box-type filter press hydraulic press 116 into municipal sludge sheets with a moisture content of 45%;
[0079] S2 sheet crushing: Municipal sludge sheets with a moisture content of 45% are unloaded from the filter cloth 113 by the distributing / discharging machine 112 and crushed into municipal sludge powder with a particle size of less than 5 mm by the hammer / blade crusher 22;
[0080] S3 biological dehydration: The municipal sludge powder with a moisture content of 45% is loaded into the breathable fermentation bag 31 at a specification of 40 kg / bag and stacked in piles of 5 bags for 15 days of biological aerobic fermentation. The microorganisms decompose the materials to generate heat. After 12 hours of fermentation, the municipal sludge powder in the breathable fermentation bag 31 is fermented and the temperature rises to above 65°C. After 20 hours of fermentation, the temperature rises to above 75°C. After the 10th day, the fermentation temperature drops to below 60°C. By the 15th day, the fermentation temperature drops to below 40°C. The fermentation is basically nearing completion. The material in the breathable fermentation bag 31 is weighed, and the material weight is reduced from 40 kg / bag to an average of 29 kg / bag. The breathable fermentation bag 31 is opened and samples are taken for moisture detection. It is found that the municipal sludge powder has been biologically fermented and dehydrated to a moisture content of 30%, meeting the technical process requirements of the physical + biological composite deep dehydration of municipal sludge.
[0081] In the second specific embodiment of the dehydration method of the organic waste composite dehydration system of the present utility model, the physical dehydration device 1 used is the ultra-high pressure stacked belt dehydration device 12, and the biological dehydration device 3 is the air permeable fermentation cylinder 32 for composite dehydration of pig manure residue with an initial moisture content of 70% to a moisture content of 35%. The dehydration method is similar to that of the previous embodiment, except that:
[0082] In S1, the ultra-high pressure laminated belt dehydration device 12 is started, and the pig manure residue is laid and clamped on the filter belt 122 by the belt cloth feeder 121 and directly pulled and transported to the belt filter press hydraulic press 124 by the filter belt tractor 123 for ultra-high pressure filtration dehydration into sheets with a moisture content of 40%;
[0083] The pig manure slag sheet with 40% moisture in S2 is unloaded from the filter belt 122 by the filter belt tractor 123, and 1% potassium sulfate is added thereto, and the sheet is crushed into powdered pig manure slag by the chain crusher 21;
[0084] S3 biological dehydration: The powdered pig manure slag mixed with 1% potassium sulfate and 39.5% moisture is loaded into the breathable fermentation cylinder 32 at a weight standard of 50kg / cylinder for 2 days of biological aerobic fermentation. The microorganisms decompose the material to generate heat. After 8 hours of fermentation, the powdered pig manure slag in the breathable fermentation cylinder 32 is fermented to above 70°C. After 48 hours of fermentation, the fermentation temperature drops to below 50°C, and the fermentation is basically close to the end. The material in the breathable fermentation cylinder 32 is weighed, and the material weight is reduced from 50kg / cylinder to an average of 44kg / cylinder. The material in the breathable fermentation cylinder 32 is poured out and sampled for moisture detection. The pig manure slag has been biologically fermented and dehydrated to a moisture content of 35%, meeting the requirements of the physical + biological composite deep dehydration technology and subsequent fertilizer resource utilization of pig manure slag.
[0085] In the third specific embodiment of the dehydration method of the organic waste composite dehydration system of the present utility model, the dehydration method is similar to the first embodiment, with the only difference being:
[0086] In S1 , the box-type material distribution feeder 111 and the material distribution / discharger 112 add 5% of garden waste powder and 2% of potassium chloride to the municipal sludge before distribution.
[0087] In the fourth specific embodiment of the dehydration method of the organic waste composite dehydration system of the present invention, the dehydration method is similar to the first embodiment, with the only difference being:
[0088] The municipal sludge in S3 is crushed into small particles with a particle size of less than 10 mm and a moisture content of 45%, and is loaded into the breathable fermentation bag 31. Before fermentation, 10% powdered straw powder is added and stirred.
[0089] The organic waste composite dehydration system and dehydration method provided by the utility model have at least the following beneficial effects:
[0090] It can meet the needs of environmental protection treatment and resource utilization of organic waste in actual production, realize the integrated fusion of mechanical physical dehydration and biological fermentation dehydration, and can directly dehydrate organic waste with a moisture content of about 80% or even higher to a moisture content of less than 40% efficiently and at low cost without relying on other organic auxiliary materials or greatly reducing dependence on other organic auxiliary materials, thereby meeting the index requirements of resource utilization and reducing the treatment cost of social organic waste. It is of great benefit to promoting the improvement of the level of environmental protection management and resource utilization of organic waste in society and promoting the smoother realization of my country's "dual carbon" goals.
[0091] The above description is merely a preferred embodiment of the present invention and does not constitute any form of limitation to the present invention. Although the present invention has been disclosed as a preferred embodiment, it is not intended to limit the present invention. Any technician familiar with the profession can make some changes or modifications to equivalent embodiments of the technical content disclosed above without departing from the scope of the technical solution of the present invention. However, any simple modifications, equivalent changes and modifications made to the above embodiments based on the technical essence of the present invention without departing from the content of the technical solution of the present invention are still within the scope of the technical solution of the present invention.
[0092] In addition, although each operation is described in a specific order, this should not be understood as requiring these operations to be performed in the specific order shown or in a sequential order. Under certain circumstances, multitasking and parallel processing may be advantageous. Similarly, although some specific implementation details have been included in the above discussion, these should not be interpreted as limiting the scope of the present invention. Some features described in the context of a separate embodiment can also be implemented in a single embodiment in combination. On the contrary, the various features described in the context of a single embodiment can also be implemented in multiple embodiments individually or in any suitable sub-combination.
[0093] Finally, it should be noted that the above are merely preferred embodiments of the present invention and are not intended to limit the present invention. Those skilled in the art will readily appreciate that the present invention is susceptible to various modifications and variations. Any modifications, equivalent substitutions, or improvements made within the spirit and principles of the present invention are intended to be encompassed by the claims of the pending application.
Claims
1. An organic waste composite dehydration system, characterized in that: include: Physical dehydration equipment, material crushing equipment and biological dehydration equipment; The material crushing device is connected and installed at the rear end of the physical dehydration device and the front end of the biological dehydration device; The physical dehydration device includes: an ultra-high pressure stacked box dehydration device or an ultra-high pressure stacked belt dehydration device; The ultra-high pressure stacked box-type dehydration device includes: a box-type cloth feeder, a cloth / discharger, a filter cloth, a filter press chamber, a filter chamber lifting hydraulic press, a box-type filter press hydraulic press and a box-type filter press hydraulic station; The box-type material distribution feeder is installed at the front end of the material distribution / discharger, the material distribution / discharger is installed on the upper side of the filter press chamber, the filter cloth is wound on the material distribution / discharger, the filter chamber lifting hydraulic press is installed below the filter press chamber, the box-type filter press hydraulic press is installed above the filter press chamber, and the box-type filter press hydraulic station is connected to the filter chamber lifting hydraulic press and the box-type filter press hydraulic press through an oil pipe; The ultra-high pressure stacked belt dehydration device includes: a belt cloth feeder, a filter belt, a filter belt tractor, a belt filter press hydraulic press, and a belt filter press hydraulic station; The belt cloth feeder is installed at the front end of the filter belt tractor, the filter belt is wound on the filter belt tractor and passes through the belt filter press hydraulic press, and the belt filter press hydraulic press is connected to the belt filter press hydraulic station through a hydraulic oil pipe.
2. The organic waste composite dehydration system according to claim 1, characterized in that: The biological dehydration device includes one or more of a breathable fermentation bag, a breathable fermentation cylinder or a breathable fermentation tray.
3. The organic waste composite dehydration system according to claim 1, characterized in that: The material crushing device includes one or more of a chain crusher, a hammer / blade crusher or a toothed shredder.
4. The organic waste composite dehydration system according to claim 1, characterized in that: Also includes: Buffer feeding device; The buffer feeding device includes: a buffer belt conveyor and a screw conveyor feeder; The buffer belt conveyor is connected and installed at the rear end of the physical dehydration device, and the screw conveyor feeder is connected and installed at the rear end of the buffer belt conveyor and the front end of the material crushing device.
5. The organic waste composite dehydration system according to claim 2, characterized in that: Also includes: Auxiliary ventilation device; The auxiliary ventilation device includes: a ventilation tray and / or a ventilation pad; The breathable tray is placed below the breathable fermentation bag, the breathable fermentation cylinder or the breathable fermentation tray, and the breathable mat is placed below or / and between the breathable fermentation bags.
6. The organic waste composite dehydration system according to claim 1, characterized in that: Also includes: Buffer unloading device; The buffer unloading device includes: a collecting bin, a discharger and a pressure relief dust removal bag; The material collection bin is connected and installed at the rear end of the material crushing device; the discharger is connected and installed at the lower end of the material collection bin; and the pressure relief dust removal bag is connected and installed on the material collection bin.
7. The organic waste composite dehydration system according to claim 6, characterized in that: It also includes a material weighing device; the material weighing device is connected to the rear end of the material crushing device and the front end of the biological dehydration device, or is connected to the rear end of the buffer unloading device and the front end of the biological dehydration device.
Citation Information
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