CN114646066B - Underground and semi-underground domestic garbage comprehensive treatment system - Google Patents

Underground and semi-underground domestic garbage comprehensive treatment system Download PDF

Info

Publication number
CN114646066B
CN114646066B CN202210289135.9A CN202210289135A CN114646066B CN 114646066 B CN114646066 B CN 114646066B CN 202210289135 A CN202210289135 A CN 202210289135A CN 114646066 B CN114646066 B CN 114646066B
Authority
CN
China
Prior art keywords
garbage
project
current
cooperative
analysis
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.)
Active
Application number
CN202210289135.9A
Other languages
Chinese (zh)
Other versions
CN114646066A (en
Inventor
武朝平
李玉峰
李岩
张轩
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
First Construction Engineering Co Ltd of China Construction Second Engineering Bureau Co Ltd
Original Assignee
First Construction Engineering Co Ltd of China Construction Second Engineering Bureau Co Ltd
Priority date (The priority date 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 date listed.)
Filing date
Publication date
Application filed by First Construction Engineering Co Ltd of China Construction Second Engineering Bureau Co Ltd filed Critical First Construction Engineering Co Ltd of China Construction Second Engineering Bureau Co Ltd
Priority to CN202210289135.9A priority Critical patent/CN114646066B/en
Publication of CN114646066A publication Critical patent/CN114646066A/en
Application granted granted Critical
Publication of CN114646066B publication Critical patent/CN114646066B/en
Active legal-status Critical Current
Anticipated expiration legal-status Critical

Links

Classifications

    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44Details; Accessories
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/44Details; Accessories
    • F23G5/442Waste feed arrangements
    • F23G5/444Waste feed arrangements for solid waste
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G5/00Incineration of waste; Incinerator constructions; Details, accessories or control therefor
    • F23G5/50Control or safety arrangements

Landscapes

  • Engineering & Computer Science (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Processing Of Solid Wastes (AREA)
  • Incineration Of Waste (AREA)

Abstract

The invention discloses an underground and semi-underground household garbage comprehensive treatment system, which relates to the technical field of garbage treatment, solves the technical problem that the garbage cannot be cooperatively treated in the prior art, so that the resource recovery efficiency is reduced, classifies the garbage to be treated in a cooperative manner, improves the garbage treatment efficiency to be treated, improves the garbage recovery working efficiency, reduces the resource consumption and enhances the beneficial influence of garbage treatment; after the garbage to be treated is subjected to type division and cooperative treatment, the incineration equipment in the treatment process is subjected to type selection through the incineration equipment type selection unit, and the proper incineration equipment is selected, so that the working efficiency and pollution degree of garbage incineration can be reduced, and meanwhile, the expenditure cost of the incineration can be reduced, so that the operation efficiency of the incineration is enhanced; after the type selection of the incineration equipment is completed, the current project period and the actual operation are analyzed, so that the comprehensive treatment of the garbage is accurately managed and controlled.

Description

Underground and semi-underground domestic garbage comprehensive treatment system
Technical Field
The invention relates to the technical field of garbage treatment, in particular to an underground and semi-underground household garbage comprehensive treatment system.
Background
With the improvement of the industrialization degree of China and the continuous rising of the living standard of people, the amount of the household garbage is also increased. The urban domestic garbage cleaning and transporting amount of China is 2.42 hundred million tons in 2019, and the speed of the urban domestic garbage cleaning and transporting amount is rapidly increased by 3% -5% per year. The research results of the underground/semi-underground garbage comprehensive treatment facilities at home and abroad are very deficient, so that the construction of the underground/semi-underground garbage comprehensive treatment facilities is required to solve the key problems of environmental protection, ecological and environmental protection advanced concept innovation, organic cooperation of various garbage treatment processes, economic benefit of investment construction, ventilation system construction of the underground garbage comprehensive treatment plants, comprehensive construction of complex underground/semi-underground garbage comprehensive treatment facilities and the like.
However, in the prior art, garbage classification cannot be performed in the process of underground garbage treatment, cooperative treatment cannot be performed on garbage, so that the resource recovery efficiency is reduced, and meanwhile, the type of incineration equipment cannot be selected in real time, so that the incineration efficiency is reduced and the incineration cost cannot be controlled; in addition, the current garbage disposal project cannot be subjected to periodic analysis and economic analysis, and the feasibility of the project cannot be subjected to real-time analysis, so that the project cannot be completed in time, and the risk of project investment failure is increased.
In view of the above technical drawbacks, a solution is now proposed.
Disclosure of Invention
The invention aims to solve the problems, and provides an underground and semi-underground domestic garbage comprehensive treatment system which is used for carrying out cooperative treatment and classification on garbage to be treated, so that the garbage treatment efficiency to be treated is improved, the garbage recovery working efficiency is improved, the resource consumption is reduced, and the beneficial influence of garbage treatment is enhanced; after the garbage to be treated is subjected to type division and cooperative treatment, the incineration equipment in the treatment process is subjected to type selection through the incineration equipment type selection unit, and the proper incineration equipment is selected, so that the working efficiency of garbage incineration and the pollution degree can be reduced, and meanwhile, the expenditure cost of incineration can be reduced, so that the operation efficiency of incineration is enhanced; after the type selection of the incineration equipment is completed, the current project period and the actual operation are analyzed, and the current project period is judged to be qualified, so that the comprehensive treatment of the garbage is accurately controlled, and the problem that the garbage to be treated cannot be treated in the project period and the working efficiency of garbage treatment is reduced is avoided.
The aim of the invention can be achieved by the following technical scheme:
an underground and semi-underground domestic garbage comprehensive treatment system, comprising:
The comprehensive treatment terminal is used for treating the garbage, generating a garbage cooperative treatment signal and sending the garbage cooperative treatment signal to the garbage cooperative treatment unit;
The garbage cooperative processing unit is used for analyzing the garbage to be processed currently and judging whether the garbage to be processed currently can be cooperatively processed or not; dividing garbage to be treated into synergistic garbage and non-synergistic garbage through synergistic treatment;
the type selection unit of the incineration equipment is used for selecting the type of the incineration equipment in the garbage treatment process, and matching the corresponding non-cooperative garbage with a proper hearth through hearth performance analysis and garbage strength analysis to be treated;
the project period analysis unit is used for analyzing the period of the current garbage disposal project and judging whether the current project period accords with the project operation;
And the project economy analysis unit is used for carrying out economy analysis on the current project and judging whether the current project has a loss risk or not.
As a preferred embodiment of the invention, the garbage cooperative processing unit operates as follows:
dividing the current garbage to be treated according to types, setting the number i of the divided garbage types as a natural number larger than 1, collecting the number of times of the acquisition of the renewable resources of each type of garbage and the success rate of the acquisition of the corresponding renewable resources, and marking the number of times of the acquisition of the renewable resources of each type of garbage and the success rate of the acquisition of the corresponding renewable resources as CSI and GLi; collecting the number of the renewable resources after the renewable resources are successfully obtained by the garbage of each type, and marking the number of the renewable resources after the renewable resources are successfully obtained by the garbage of each type as ZYi; obtaining collaborative processing analysis coefficients Xi of various types of garbage through analysis;
Comparing the collaborative processing analysis coefficient Xi of each type of garbage with a collaborative processing analysis coefficient threshold value: if the collaborative processing analysis coefficient Xi of the corresponding type of garbage exceeds the collaborative processing analysis coefficient threshold, judging that the garbage of the corresponding type can be subjected to collaborative processing, marking the garbage of the corresponding type as the collaborative garbage, and simultaneously carrying out collaborative processing on the corresponding collaborative garbage; if the cooperative processing analysis coefficient Xi of the garbage of the corresponding type does not exceed the cooperative processing analysis coefficient threshold, judging that the garbage of the corresponding type cannot be subjected to cooperative processing, marking the garbage of the corresponding type as non-cooperative garbage, and simultaneously incinerating the corresponding non-cooperative garbage; generating an incineration equipment type selection signal and sending the incineration equipment type selection signal to an incineration equipment type selection unit.
As a preferred embodiment of the present invention, the operation of the incineration plant model selection unit is as follows:
The type of the incineration equipment is a hearth type, the existing type of hearth is analyzed, the amount, the running cost and the in-furnace residence time of single-time treatable garbage corresponding to the hearth are obtained, and the amount, the running cost and the in-furnace residence time of single-time treatable garbage corresponding to the hearth are respectively marked as ZL, ZJ and SC; the method comprises the steps of obtaining a performance analysis coefficient C of a hearth through analysis, and comparing the performance analysis coefficient C of the hearth with a performance analysis coefficient threshold range:
If the performance analysis coefficient C of the hearth exceeds the threshold range of the performance analysis coefficient, marking the corresponding hearth as a primary performance hearth; if the performance analysis coefficient C of the hearth is in the threshold range of the performance analysis coefficient, marking the corresponding hearth as a secondary performance hearth; if the performance analysis coefficient C of the hearth does not exceed the threshold range of the performance analysis coefficient, marking the corresponding hearth as a three-level performance hearth;
Analyzing non-cooperative garbage in the current garbage to be treated in real time to obtain the garbage quality, preset treatment time length and combustion medium demand corresponding to the non-cooperative garbage to be treated, and marking the garbage quality, preset treatment time length and combustion medium demand corresponding to the non-cooperative garbage to be treated as LJ, YS and JZ respectively; the method comprises the steps of obtaining a processing analysis coefficient V of non-cooperative garbage through analysis, and comparing the processing analysis coefficient V of the non-cooperative garbage with a threshold range of the processing analysis coefficient:
If the processing analysis coefficient V of the non-cooperative garbage exceeds the threshold range of the processing analysis coefficient, marking the corresponding non-cooperative garbage as first-level strength processing garbage; if the processing analysis coefficient V of the non-cooperative garbage is in the threshold range of the processing analysis coefficient, marking the corresponding non-cooperative garbage as the secondary strength processing garbage; if the processing analysis coefficient V of the non-cooperative garbage does not exceed the threshold range of the processing analysis coefficient, marking the corresponding non-cooperative garbage as three-level intensity processing garbage;
and matching the non-cooperative garbage to be treated with the hearth according to the corresponding grade, and sending the matched hearth name to the comprehensive treatment terminal, wherein the comprehensive treatment terminal controls the hearth to operate.
As a preferred embodiment of the present invention, the project period analysis unit operates as follows:
Collecting the number of garbage types for carrying out cooperative treatment on the current garbage to be treated and the average single time consumption for carrying out garbage transportation in the underground building where the current garbage to be treated is located, and comparing the number of garbage types for carrying out cooperative treatment on the current garbage to be treated and the average single time consumption for carrying out garbage transportation in the underground building where the current garbage to be treated with the garbage type number threshold and the single time consumption threshold respectively:
If the number of the garbage types for carrying out cooperative treatment on the current garbage to be treated exceeds a garbage type number threshold, or the average single time consumption for carrying garbage in the underground building where the current garbage to be treated is located exceeds a single time consumption threshold, judging that the current project is in a complex project;
If no buffer period exists between the preset period of the current project and the setting period of the actual project, judging that the analysis of the project in the current period is unqualified, generating a period adjustment signal and setting the buffer period of the current setting period according to the progress of the real-time project; if a buffer period exists between the preset period of the current project and the set period of the actual project, judging that the project analysis of the current period is qualified;
If the number of the garbage types for the cooperative treatment of the current garbage to be treated does not exceed the threshold of the number of the garbage types, and the average single time consumption for carrying the garbage in the underground building where the current garbage to be treated is positioned does not exceed the threshold of the single time consumption, judging that the current project is a simple project;
If the buffer period between the preset period of the current project and the set period of the actual project exceeds the buffer period threshold, judging that the project analysis in the current period is unqualified, and shortening the originally set buffer period according to the progress of the current project; if the buffer period between the preset period of the current project and the set period of the actual project does not exceed the buffer period threshold, judging that the project analysis of the current project is qualified.
As a preferred embodiment of the present invention, the project economy analysis unit operates as follows:
Collecting the average daily garbage disposal amount of the current project and the average daily input cost amount of garbage disposal of the current project, and comparing the average daily garbage disposal amount of the current project and the average daily input cost amount of garbage disposal of the current project with a disposal amount threshold and a cost amount threshold respectively:
If the average daily garbage disposal amount of the current project exceeds the disposal amount threshold value and the input cost amount of garbage disposal of the current project in each day does not exceed the cost amount threshold value, judging that the economic analysis of the current project is qualified; if the average daily garbage disposal amount of the current project exceeds a disposal amount threshold value and the input cost amount of garbage disposal of the current project exceeds a cost amount threshold value, judging that the economic analysis of the current project is abnormal, controlling the input cost of the corresponding project, and if the input cost cannot be controlled within the cost amount threshold value, judging that the economic analysis of the current project is unqualified;
if the average daily garbage disposal amount of the current project does not exceed the disposal amount threshold value, and the input cost amount of garbage disposal of the current project in each day exceeds the cost amount threshold value, judging that the economic analysis of the current project is unqualified; if the average daily garbage disposal amount of the current project does not exceed the disposal amount threshold value and the input cost amount of garbage disposal of the current project in each day does not exceed the cost amount threshold value, judging that the economic analysis of the current project is abnormal, controlling the average daily garbage disposal amount of the corresponding project, and if the garbage disposal amount cannot be increased to the disposal amount threshold value range, judging that the economic analysis of the current project is unqualified.
Compared with the prior art, the invention has the beneficial effects that:
According to the invention, the garbage to be treated is subjected to cooperative treatment classification, so that the garbage treatment efficiency is improved, the garbage recycling working efficiency is improved, the resource consumption is reduced, and the beneficial influence of garbage treatment is enhanced; after the garbage to be treated is subjected to type division and cooperative treatment, the incineration equipment in the treatment process is subjected to type selection through the incineration equipment type selection unit, and the proper incineration equipment is selected, so that the working efficiency of garbage incineration and the pollution degree can be reduced, and meanwhile, the expenditure cost of incineration can be reduced, so that the operation efficiency of incineration is enhanced; after the type selection of the incineration equipment is finished, analyzing the current project period and the actual operation, and judging that the current project period is qualified, so that the comprehensive treatment of the garbage is accurately controlled, and the problem that the garbage to be treated cannot be treated in the project period and the working efficiency of the garbage treatment is reduced is avoided; after the project period analysis is completed, judging whether the current project has a loss risk or not, improving the investment analysis accuracy of the current project, simultaneously analyzing the management efficiency of the comprehensive treatment of the current garbage, and being beneficial to optimizing the comprehensive treatment process.
Drawings
The present invention is further described below with reference to the accompanying drawings for the convenience of understanding by those skilled in the art.
Fig. 1 is a functional block diagram of the present invention.
Detailed Description
The technical solutions of the present invention will be clearly and completely described in connection with the embodiments, and it is obvious that the described embodiments are only some embodiments of the present invention, not all embodiments. All other embodiments, which can be made by those skilled in the art based on the embodiments of the invention without making any inventive effort, are intended to be within the scope of the invention.
The construction of underground/semi-underground garbage comprehensive treatment facilities is a brand new attempt facing garbage classification treatment in China, and the overall design and economic analysis research are of great significance to the development and implementation of the field. In the aspect of policy, the policy requirement of national green construction is actively responded, and the subject research is based on the principle of saving and reducing; in the aspect of industry development, the method is used as a first underground/semi-underground garbage comprehensive treatment facility in China, and provides experience and results for subsequent development;
in the prior art, a garbage truck enters a project-8 traffic layer along a special conveying tunnel for garbage, enters a discharging hall, then is discharged to a garbage bin, is hung from the garbage to a discharging hopper after being fermented, slides to a feeder along a hopper chute to enter an incinerator for burning, and generated steam is conveyed to a turbine through a pipeline to push a steam turbine to generate power for full-field power utilization, and the residual power is connected to a grid for power generation. The burned residues enter a slag bin and are conveyed to a slag treatment factory by a slag conveying belt, and the burned flue gas is purified and then discharged from a chimney;
the system is used for comprehensively treating garbage, and referring to FIG. 1, an underground and semi-underground household garbage comprehensive treatment system;
The garbage is treated through the comprehensive treatment terminal, meanwhile, a garbage cooperative treatment signal is generated and sent to the garbage cooperative treatment unit, after the garbage cooperative treatment unit receives the garbage cooperative treatment signal, the garbage to be treated is analyzed, whether the garbage to be treated can be treated currently or not is judged, wherein the cooperative treatment is represented as the garbage cooperative treatment, the traditional linear economic mode of 'resources-products-wastes' is transformed into a 'resources-products-renewable resources' closed-loop economic mode, and the waste is changed into valuable and recycled; however, the cooperative treatment is not suitable for all types of garbage, and the cooperative treatment judgment of garbage can improve the treatment efficiency of garbage and improve the accuracy and the recovery efficiency of resource recovery;
The garbage collaborative processing unit divides the garbage to be processed currently according to types, sets the marks i and i as natural numbers larger than 1, acquires the times of the acquisition of the renewable resources of the garbage of each type and the success rate of the acquisition of the corresponding renewable resources, and marks the times of the acquisition of the renewable resources of the garbage of each type and the success rate of the acquisition of the corresponding renewable resources as CSI and GLi; the renewable resources are expressed as material resources which can be cyclically and naturally generated, grown and reproduced through natural or artificial activities within a certain period of time (within one year or within decades) after being developed and utilized once by human beings, and can also continuously increase reserves, and comprise surface water, soil, plants, animals, aquatic organisms, microorganisms, forests, grasslands, air, sunlight (solar energy), climate resources, ocean resources and the like; the renewable resources are specifically limited to biogas, heat energy, electric energy, water and renewable building materials;
collecting the number of the renewable resources after the renewable resources are successfully obtained by the garbage of each type, and marking the number of the renewable resources after the renewable resources are successfully obtained by the garbage of each type as ZYi; by the formula Obtaining collaborative treatment analysis coefficients Xi of various types of garbage, wherein a1, a2 and a3 are preset proportionality coefficients, a1 is more than a2 and a3, and when the type of garbage is unsuccessful in completing the acquisition of the renewable resources, a3 takes a value of 0;
comparing the collaborative processing analysis coefficient Xi of each type of garbage with a collaborative processing analysis coefficient threshold value:
If the collaborative processing analysis coefficient Xi of the corresponding type of garbage exceeds the collaborative processing analysis coefficient threshold, judging that the garbage of the corresponding type can be subjected to collaborative processing, marking the garbage of the corresponding type as the collaborative garbage, and simultaneously carrying out collaborative processing on the corresponding collaborative garbage; if the cooperative processing analysis coefficient Xi of the garbage of the corresponding type does not exceed the cooperative processing analysis coefficient threshold, judging that the garbage of the corresponding type cannot be subjected to cooperative processing, marking the garbage of the corresponding type as non-cooperative garbage, and simultaneously incinerating the corresponding non-cooperative garbage; generating an incineration equipment type selection signal and sending the incineration equipment type selection signal to an incineration equipment type selection unit;
The comprehensive treatment terminal performs cooperative treatment on the cooperative garbage, treats the cooperative garbage to generate energy and resources, and when the cooperative garbage is organic garbage, the organic garbage comprises kitchen garbage, kitchen garbage and excrement; adopts a treatment process of mechanical pretreatment and combined high-temperature anaerobic digestion. The generated biogas slurry enters a sewage treatment station for treatment, the biogas residues enter a garbage incinerator for incineration, and the biogas enters a biogas power generation device. (the organic garbage is independently treated with the traditional organic garbage, and the complementation is realized in the aspects of fuel supply, steam supply, sewage treatment, biogas, residue utilization and the like, so that the full coverage of material conversion and energy conversion is truly realized); when the sludge treatment can be carried out in cooperation with garbage, a treatment process of 'steam drying and cooperative incineration' is adopted. The sludge treatment utilizes the steam of the garbage incineration plant as a heat source to carry out heat drying on the sludge, and the dried sludge is conveyed to a garbage incinerator; when the synergic garbage is medical garbage, the medical garbage adopts a steam high-temperature steam disinfection and sterilization process of a garbage power plant, the generated residues enter an incinerator to be incinerated, and the generated sewage is treated at a sewage treatment station of the factory; when sewage treatment can be performed in cooperation with garbage, the treatment object and the drainage standard: mainly comprises percolate generated by a household garbage incineration plant, filtrate obtained by dehydrating kitchen biogas residues, condensate obtained by drying and evaporating sludge, and the like. After being treated to reach the nano tube standard, the sewage enters a municipal sewage pipe network; the sewage treatment adopts a treatment process of pretreatment, anaerobic nitrification and membrane bioreactor MBR system, so that the water quality is ensured to reach the standard for emission; the biogas in the sewage treatment process enters a boiler to be incinerated, and the sludge is dried in a factory;
After the garbage to be treated is subjected to type division and cooperative treatment, the incineration equipment in the treatment process is subjected to type selection through the incineration equipment type selection unit, and the proper incineration equipment is selected, so that the working efficiency of garbage incineration and the pollution degree can be reduced, and meanwhile, the expenditure cost of incineration can be reduced, so that the operation efficiency of incineration is enhanced;
The type of the incineration equipment is a hearth type, the existing type of hearth is analyzed, the amount, the running cost and the in-furnace residence time of single-time treatable garbage corresponding to the hearth are obtained, and the amount, the running cost and the in-furnace residence time of single-time treatable garbage corresponding to the hearth are respectively marked as ZL, ZJ and SC; by the formula Obtaining a performance analysis coefficient C of a hearth, wherein b1, b2 and b3 are preset proportional coefficients, and b1 is more than b2 and more than b3 is more than 0;
Comparing the performance analysis coefficient C of the hearth with a threshold range of the performance analysis coefficient:
If the performance analysis coefficient C of the hearth exceeds the threshold range of the performance analysis coefficient, marking the corresponding hearth as a primary performance hearth; if the performance analysis coefficient C of the hearth is in the threshold range of the performance analysis coefficient, marking the corresponding hearth as a secondary performance hearth; if the performance analysis coefficient C of the hearth does not exceed the threshold range of the performance analysis coefficient, marking the corresponding hearth as a three-level performance hearth; and the smaller the hearth grade is, the better the performance is;
Analyzing non-cooperative garbage in the current garbage to be treated in real time to obtain the garbage quality, preset treatment time length and combustion medium demand corresponding to the non-cooperative garbage to be treated, and marking the garbage quality, preset treatment time length and combustion medium demand corresponding to the non-cooperative garbage to be treated as LJ, YS and JZ respectively; by the formula Obtaining a treatment analysis coefficient V of non-cooperative garbage, wherein c4, c5 and c6 are preset proportionality coefficients, and c4 is more than c5 and more than c6 is more than 0;
Comparing the processing analysis coefficient V of the non-cooperative garbage with a threshold range of processing analysis coefficients:
If the processing analysis coefficient V of the non-cooperative garbage exceeds the threshold range of the processing analysis coefficient, marking the corresponding non-cooperative garbage as first-level strength processing garbage; if the processing analysis coefficient V of the non-cooperative garbage is in the threshold range of the processing analysis coefficient, marking the corresponding non-cooperative garbage as the secondary strength processing garbage; if the processing analysis coefficient V of the non-cooperative garbage does not exceed the threshold range of the processing analysis coefficient, marking the corresponding non-cooperative garbage as three-level intensity processing garbage;
Matching the non-cooperative garbage to be treated with the hearth according to the corresponding grade, and sending the matched hearth name to a comprehensive treatment terminal, wherein the comprehensive treatment terminal controls the hearth to operate;
After the type selection of the incineration equipment is finished, analyzing the period of the current garbage disposal project through a project period analysis unit, analyzing the period of the current project and the actual operation, and judging that the period of the current project is qualified, so that the comprehensive garbage disposal is accurately managed and controlled, and the problem that the garbage disposal to be disposed cannot be completed in the project period, so that the working efficiency of the garbage disposal is reduced is avoided;
Collecting the number of garbage types for carrying out cooperative treatment on the current garbage to be treated and the average single time consumption for carrying out garbage transportation in the underground building where the current garbage to be treated is located, and comparing the number of garbage types for carrying out cooperative treatment on the current garbage to be treated and the average single time consumption for carrying out garbage transportation in the underground building where the current garbage to be treated with the garbage type number threshold and the single time consumption threshold respectively:
if the number of garbage types for carrying out cooperative treatment on the current garbage to be treated exceeds a garbage type number threshold, or the average single time consumption for carrying out garbage in an underground building where the current garbage to be treated is located exceeds a single time consumption threshold, judging that the current project is in a complex project, if no buffering period exists between a preset period of the current project and a set period of an actual project, judging that the current project is unqualified for analysis, generating a period integer signal, and setting the buffering period of the current set period according to the progress of the real-time project; if a buffer period exists between the preset period of the current project and the set period of the actual project, judging that the project analysis of the current period is qualified; the buffer period is represented as the duration with less pre-set period of the previous project and less set period of the actual project;
If the number of garbage types for collaborative treatment of the current garbage to be treated does not exceed the garbage type number threshold, and the average single time consumption for garbage transportation in the underground building where the current garbage to be treated is located does not exceed the single time consumption threshold, judging that the current project is in a simple project, if the buffer period between the preset period of the current project and the set period of the actual project exceeds the buffer period threshold, judging that the project analysis in the current period is unqualified, and shortening the originally set buffer period according to the progress of the current project; if the buffer period between the preset period of the current project and the set period of the actual project does not exceed the buffer period threshold, judging that the project analysis of the current project is qualified;
after the project period analysis is completed, the project economic analysis unit is used for carrying out economic analysis on the current project, judging whether the current project has loss risk or not, improving the investment analysis accuracy of the current project, simultaneously being capable of analyzing the management efficiency of the current garbage comprehensive treatment and being beneficial to optimizing the comprehensive treatment process;
Collecting the average daily garbage disposal amount of the current project and the average daily input cost amount of garbage disposal of the current project, and comparing the average daily garbage disposal amount of the current project and the average daily input cost amount of garbage disposal of the current project with a disposal amount threshold and a cost amount threshold respectively:
If the average daily garbage disposal amount of the current project exceeds the disposal amount threshold value and the input cost amount of garbage disposal of the current project in each day does not exceed the cost amount threshold value, judging that the economic analysis of the current project is qualified;
If the average daily garbage disposal amount of the current project exceeds a disposal amount threshold value and the input cost amount of garbage disposal of the current project exceeds a cost amount threshold value, judging that the economic analysis of the current project is abnormal, controlling the input cost of the corresponding project, and if the input cost cannot be controlled within the cost amount threshold value, judging that the economic analysis of the current project is unqualified;
if the average daily garbage disposal amount of the current project does not exceed the disposal amount threshold value, and the input cost amount of garbage disposal of the current project in each day exceeds the cost amount threshold value, judging that the economic analysis of the current project is unqualified; if the average daily garbage disposal amount of the current project does not exceed the disposal amount threshold value and the input cost amount of garbage disposal of the current project in each day does not exceed the cost amount threshold value, judging that the economic analysis of the current project is abnormal, controlling the average daily garbage disposal amount of the corresponding project, and if the garbage disposal amount cannot be increased to the disposal amount threshold value range, judging that the economic analysis of the current project is unqualified.
The formulas are all formulas obtained by collecting a large amount of data for software simulation and selecting a formula close to a true value, and coefficients in the formulas are set by a person skilled in the art according to actual conditions;
When the garbage collaborative processing system is used, garbage is processed through the comprehensive processing terminal, and meanwhile, garbage collaborative processing signals are generated and sent to the garbage collaborative processing unit; analyzing the garbage to be treated currently through a garbage cooperative treatment unit, and judging whether the garbage to be treated currently can be cooperatively treated or not; dividing garbage to be treated into synergistic garbage and non-synergistic garbage through synergistic treatment; the type of the incineration equipment in the garbage treatment process is selected by the type selection unit of the incineration equipment, and the corresponding non-cooperative garbage is matched with a proper hearth by the hearth performance analysis and the garbage strength analysis to be treated; analyzing the period of the current garbage disposal project through a project period analysis unit, and judging whether the current project period accords with project operation; and carrying out economic analysis on the current project through a project economic analysis unit, and judging whether the current project has a loss risk or not.
The preferred embodiments of the invention disclosed above are intended only to assist in the explanation of the invention. The preferred embodiments are not intended to be exhaustive or to limit the invention to the precise form disclosed. Obviously, many modifications and variations are possible in light of the above teaching. The embodiments were chosen and described in order to best explain the principles of the invention and the practical application, to thereby enable others skilled in the art to best understand and utilize the invention. The invention is limited only by the claims and the full scope and equivalents thereof.

Claims (3)

1. An underground and semi-underground domestic waste integrated treatment system, comprising:
The comprehensive treatment terminal is used for treating the garbage, generating a garbage cooperative treatment signal and sending the garbage cooperative treatment signal to the garbage cooperative treatment unit;
The garbage cooperative processing unit is used for analyzing the garbage to be processed currently and judging whether the garbage to be processed currently can be cooperatively processed or not; dividing garbage to be treated into synergistic garbage and non-synergistic garbage through synergistic treatment; the operation process of the garbage cooperative processing unit is as follows:
Dividing the current garbage to be treated according to types, setting the number i of the divided garbage types as a natural number larger than 1, collecting the number of times of the acquisition of the renewable resources of each type of garbage and the success rate of the acquisition of the corresponding renewable resources, and marking the number of times of the acquisition of the renewable resources of each type of garbage and the success rate of the acquisition of the corresponding renewable resources as CSI and GLi; collecting the number of the renewable resources after the renewable resources are successfully obtained by the garbage of each type, and marking the number of the renewable resources after the renewable resources are successfully obtained by the garbage of each type as ZYi; by the formula Obtaining collaborative treatment analysis coefficients Xi of various types of garbage, wherein a1, a2 and a3 are preset proportionality coefficients, a1 is more than a2 and a3, and when the type of garbage is unsuccessful in completing the acquisition of the renewable resources, a3 takes a value of 0;
Comparing the collaborative processing analysis coefficient Xi of each type of garbage with a collaborative processing analysis coefficient threshold value: if the collaborative processing analysis coefficient Xi of the corresponding type of garbage exceeds the collaborative processing analysis coefficient threshold, judging that the garbage of the corresponding type can be subjected to collaborative processing, marking the garbage of the corresponding type as the collaborative garbage, and simultaneously carrying out collaborative processing on the corresponding collaborative garbage; if the cooperative processing analysis coefficient Xi of the garbage of the corresponding type does not exceed the cooperative processing analysis coefficient threshold, judging that the garbage of the corresponding type cannot be subjected to cooperative processing, marking the garbage of the corresponding type as non-cooperative garbage, and simultaneously incinerating the corresponding non-cooperative garbage; generating an incineration equipment type selection signal and sending the incineration equipment type selection signal to an incineration equipment type selection unit;
The type selection unit of the incineration equipment is used for selecting the type of the incineration equipment in the garbage treatment process, and matching the corresponding non-cooperative garbage with a proper hearth through hearth performance analysis and garbage strength analysis to be treated; the operation process of the incineration equipment model selection unit is as follows:
The type of the incineration equipment is a hearth type, the existing type of hearth is analyzed, the amount, the running cost and the in-furnace residence time of single-time treatable garbage corresponding to the hearth are obtained, and the amount, the running cost and the in-furnace residence time of single-time treatable garbage corresponding to the hearth are respectively marked as ZL, ZJ and SC; by the formula Obtaining a performance analysis coefficient C of the hearth, wherein b1, b2 and b3 are preset proportional coefficients, b1 is larger than b2 and b3 is larger than 0, and comparing the performance analysis coefficient C of the hearth with a performance analysis coefficient threshold range:
If the performance analysis coefficient C of the hearth exceeds the threshold range of the performance analysis coefficient, marking the corresponding hearth as a primary performance hearth; if the performance analysis coefficient C of the hearth is in the threshold range of the performance analysis coefficient, marking the corresponding hearth as a secondary performance hearth; if the performance analysis coefficient C of the hearth does not exceed the threshold range of the performance analysis coefficient, marking the corresponding hearth as a three-level performance hearth;
Analyzing non-cooperative garbage in the current garbage to be treated in real time to obtain the garbage quality, preset treatment time length and combustion medium demand corresponding to the non-cooperative garbage to be treated, and marking the garbage quality, preset treatment time length and combustion medium demand corresponding to the non-cooperative garbage to be treated as LJ, YS and JZ respectively; the method comprises the steps of obtaining a processing analysis coefficient V of non-cooperative garbage through analysis, and comparing the processing analysis coefficient V of the non-cooperative garbage with a threshold range of the processing analysis coefficient:
If the processing analysis coefficient V of the non-cooperative garbage exceeds the threshold range of the processing analysis coefficient, marking the corresponding non-cooperative garbage as first-level strength processing garbage; if the processing analysis coefficient V of the non-cooperative garbage is in the threshold range of the processing analysis coefficient, marking the corresponding non-cooperative garbage as the secondary strength processing garbage; if the processing analysis coefficient V of the non-cooperative garbage does not exceed the threshold range of the processing analysis coefficient, marking the corresponding non-cooperative garbage as three-level intensity processing garbage;
Matching the non-cooperative garbage to be treated with the hearth according to the corresponding grade, and sending the matched hearth name to a comprehensive treatment terminal, wherein the comprehensive treatment terminal controls the hearth to operate;
the project period analysis unit is used for analyzing the period of the current garbage disposal project and judging whether the current project period accords with the project operation;
And the project economy analysis unit is used for carrying out economy analysis on the current project and judging whether the current project has a loss risk or not.
2. The system for comprehensively treating underground and semi-underground domestic garbage according to claim 1, wherein the project period analysis unit operates as follows:
Collecting the number of garbage types for carrying out cooperative treatment on the current garbage to be treated and the average single time consumption for carrying out garbage transportation in the underground building where the current garbage to be treated is located, and comparing the number of garbage types for carrying out cooperative treatment on the current garbage to be treated and the average single time consumption for carrying out garbage transportation in the underground building where the current garbage to be treated with the garbage type number threshold and the single time consumption threshold respectively:
If the number of the garbage types for carrying out cooperative treatment on the current garbage to be treated exceeds a garbage type number threshold, or the average single time consumption for carrying garbage in the underground building where the current garbage to be treated is located exceeds a single time consumption threshold, judging that the current project is in a complex project;
If no buffer period exists between the preset period of the current project and the setting period of the actual project, judging that the analysis of the project in the current period is unqualified, generating a period adjustment signal and setting the buffer period of the current setting period according to the progress of the real-time project; if a buffer period exists between the preset period of the current project and the set period of the actual project, judging that the project analysis of the current period is qualified;
If the number of the garbage types for the cooperative treatment of the current garbage to be treated does not exceed the threshold of the number of the garbage types, and the average single time consumption for carrying the garbage in the underground building where the current garbage to be treated is positioned does not exceed the threshold of the single time consumption, judging that the current project is a simple project;
If the buffer period between the preset period of the current project and the set period of the actual project exceeds the buffer period threshold, judging that the project analysis in the current period is unqualified, and shortening the originally set buffer period according to the progress of the current project; if the buffer period between the preset period of the current project and the set period of the actual project does not exceed the buffer period threshold, judging that the project analysis of the current project is qualified.
3. The system for comprehensively treating underground and semi-underground domestic garbage according to claim 1, wherein the project economy analysis unit operates as follows:
Collecting the average daily garbage disposal amount of the current project and the average daily input cost amount of garbage disposal of the current project, and comparing the average daily garbage disposal amount of the current project and the average daily input cost amount of garbage disposal of the current project with a disposal amount threshold and a cost amount threshold respectively:
If the average daily garbage disposal amount of the current project exceeds the disposal amount threshold value and the input cost amount of garbage disposal of the current project in each day does not exceed the cost amount threshold value, judging that the economic analysis of the current project is qualified; if the average daily garbage disposal amount of the current project exceeds a disposal amount threshold value and the input cost amount of garbage disposal of the current project exceeds a cost amount threshold value, judging that the economic analysis of the current project is abnormal, controlling the input cost of the corresponding project, and if the input cost cannot be controlled within the cost amount threshold value, judging that the economic analysis of the current project is unqualified;
if the average daily garbage disposal amount of the current project does not exceed the disposal amount threshold value, and the input cost amount of garbage disposal of the current project in each day exceeds the cost amount threshold value, judging that the economic analysis of the current project is unqualified; if the average daily garbage disposal amount of the current project does not exceed the disposal amount threshold value and the input cost amount of garbage disposal of the current project in each day does not exceed the cost amount threshold value, judging that the economic analysis of the current project is abnormal, controlling the average daily garbage disposal amount of the corresponding project, and if the garbage disposal amount cannot be increased to the disposal amount threshold value range, judging that the economic analysis of the current project is unqualified.
CN202210289135.9A 2022-03-23 2022-03-23 Underground and semi-underground domestic garbage comprehensive treatment system Active CN114646066B (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202210289135.9A CN114646066B (en) 2022-03-23 2022-03-23 Underground and semi-underground domestic garbage comprehensive treatment system

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202210289135.9A CN114646066B (en) 2022-03-23 2022-03-23 Underground and semi-underground domestic garbage comprehensive treatment system

Publications (2)

Publication Number Publication Date
CN114646066A CN114646066A (en) 2022-06-21
CN114646066B true CN114646066B (en) 2024-06-11

Family

ID=81996363

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202210289135.9A Active CN114646066B (en) 2022-03-23 2022-03-23 Underground and semi-underground domestic garbage comprehensive treatment system

Country Status (1)

Country Link
CN (1) CN114646066B (en)

Families Citing this family (1)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN115167313B (en) * 2022-08-03 2023-03-24 安徽联合创业可再生能源科技有限公司 Organic waste cooperative recycling treatment system based on 5G intelligent factory

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05285A (en) * 1991-06-24 1993-01-08 Fujita Corp Non-combustion type underground waste refuse regeneration treatment equipment having heated pool
JP2007217104A (en) * 2006-02-15 2007-08-30 Ohbayashi Corp Waste processing facility
CN101850349A (en) * 2010-04-29 2010-10-06 云南天兰环保科技开发有限公司 Processing method of changing food waste into resources
CN103242134A (en) * 2013-04-25 2013-08-14 深圳市炬能生物质气化科技有限公司 Pyrolysis gasification and purification method of household garbage
CN107133968A (en) * 2017-06-07 2017-09-05 武汉洁美雅科技有限公司 A kind of garbage disposal control system based on Internet of Things
JP2019032123A (en) * 2017-08-09 2019-02-28 川崎重工業株式会社 Heat quantity estimation method, heat quantity estimation device, and waste storage facility
CN109680156A (en) * 2019-01-31 2019-04-26 龙岩山青冶金科技有限公司 A kind of waste incineration and generating electricity cinder resourceization utilizes system and method
CN110046723A (en) * 2019-04-19 2019-07-23 周旭东 A kind of municipal solid wastes incineration power generation system
CN111027639A (en) * 2019-12-24 2020-04-17 北华大学 Cloud-based garbage sorting system and method, information processing terminal and storage medium
CN113262602A (en) * 2021-06-03 2021-08-17 北京基亚特环保科技有限公司 Waste incineration flue gas treatment device

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JPH05285A (en) * 1991-06-24 1993-01-08 Fujita Corp Non-combustion type underground waste refuse regeneration treatment equipment having heated pool
JP2007217104A (en) * 2006-02-15 2007-08-30 Ohbayashi Corp Waste processing facility
CN101850349A (en) * 2010-04-29 2010-10-06 云南天兰环保科技开发有限公司 Processing method of changing food waste into resources
CN103242134A (en) * 2013-04-25 2013-08-14 深圳市炬能生物质气化科技有限公司 Pyrolysis gasification and purification method of household garbage
CN107133968A (en) * 2017-06-07 2017-09-05 武汉洁美雅科技有限公司 A kind of garbage disposal control system based on Internet of Things
JP2019032123A (en) * 2017-08-09 2019-02-28 川崎重工業株式会社 Heat quantity estimation method, heat quantity estimation device, and waste storage facility
CN109680156A (en) * 2019-01-31 2019-04-26 龙岩山青冶金科技有限公司 A kind of waste incineration and generating electricity cinder resourceization utilizes system and method
CN110046723A (en) * 2019-04-19 2019-07-23 周旭东 A kind of municipal solid wastes incineration power generation system
CN111027639A (en) * 2019-12-24 2020-04-17 北华大学 Cloud-based garbage sorting system and method, information processing terminal and storage medium
CN113262602A (en) * 2021-06-03 2021-08-17 北京基亚特环保科技有限公司 Waste incineration flue gas treatment device

Non-Patent Citations (2)

* Cited by examiner, † Cited by third party
Title
垃圾焚烧与干化污泥协同处理的技术方案分析;祁司亮;洪光;王鸿飞;;临沂大学学报;20191210(06);全文 *
生活垃圾焚烧与餐厨垃圾处理协同处置的分析研究;蹇瑞欢;吴剑;宋薇;;环境卫生工程;20180425(02);全文 *

Also Published As

Publication number Publication date
CN114646066A (en) 2022-06-21

Similar Documents

Publication Publication Date Title
CN102500604B (en) Household solid garbage recycling and renewable biological carbon circulating technology
CN110105095A (en) A kind of innoxious and recycling processing method of kitchen garbage
CN101792246B (en) Method for generating biogas through intensified hydrolysis and anaerobic digestion of municipal domestic organic refuse
CN110976472B (en) Kitchen waste and household waste co-processing method
CN103381420A (en) Device and method for sewage collaborative reutilization comprehensive treatment
CN1843642A (en) Resource-reutilizing circulating process of biological garbage
CN105886330A (en) Municipal domestic solid waste integrated treatment process system
CN102321673B (en) Method for producing biogas by solid organic waste
CN106140780B (en) A kind of domestic garbage treating system
CN100560235C (en) Biological and the burning disposal integrated technique of dewatered city domestic garbage
CN205065727U (en) City solid waste burns power generation system in coordination
CN102049407A (en) Municipal bulk solid waste treatment industrial symbiotic system
CN115069739A (en) Bidirectional reinforced multi-source cooperative full-amount recycling treatment system and technology for kitchen waste
CN105983566A (en) Domestic sewage and rubbish, dining-room kitchen waste and riverway sludge integrated treatment process
CN114646066B (en) Underground and semi-underground domestic garbage comprehensive treatment system
CN100571912C (en) Biological and the gasification process integrated technique of dewatered city domestic garbage
CN1994596B (en) Household garbage-ecocycling resource reutilization integrated device
CN106927635B (en) Energy output type sewage treatment process
CN111750357A (en) Vein industrial park system with waste incineration power plant as core
CN107597797A (en) The high instant joint disposal of wet basis Chinese medicine slag energy utilizes system and method
CN207581802U (en) A kind of device of the mixed material fermentation and biogas production with hydro-thermal process
CN211734134U (en) Livestock and poultry manure and domestic garbage comprehensive treatment system
CN108178476A (en) A kind of fecal pollution and the dirty urine of cultivation and kitchen garbage and municipal sludge cooperative processing method
CN109807157A (en) A kind of domestic garbage resource processing integral process and system
CN203140420U (en) Organic garbage disposal system

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