Control method, device and equipment of waste incineration system, medium and product
By constructing a mapping model and intelligently determining the grabbing position, the problem of low efficiency and poor environmental protection of garbage with complex types and unstable proportions in the waste incineration system is solved, and an efficient and environmentally friendly incineration process is achieved.
Patent Information
- Application Number
- CN202411433438.9
- Authority / Receiving Office
- CN · China
- Patent Type
- Applications(China)
- Current Assignee / Owner
- Filing Date
- 2024-10-14
- Publication Date
- 2025-01-24
AI Technical Summary
When existing waste incineration systems deal with garbage of complex types and unstable proportions, they have low incineration efficiency and poor environmental protection.
By constructing a mapping model based on historical operating data, the target flue gas outlet component concentration and target calorific value are determined, and the target grabbing position of the garbage grab crane is intelligently determined.
It improves the thermal load stability and environmental protection of the waste incineration system and ensures that the incineration efficiency and pollutant emissions meet the requirements.
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Figure CN119353681A_ABST
Abstract
Description
Technical Field
[0001] The present invention relates to the technical field of solid waste treatment, and in particular to a control method, device, control equipment, medium and product of a garbage incineration system. Background Art
[0002] Domestic waste is an important environmental problem in modern urban life. With the continuous advancement of urbanization and the improvement of people's living standards, the amount and types of domestic waste are increasing, and the impact on the environment and resources is becoming more and more serious. The high-level treatment and disposal of domestic waste has become one of the important issues that need to be solved in today's society.
[0003] In the treatment technology of domestic waste, incineration power generation is the mainstream treatment method, accounting for more than 50% of the world. Its basic process is to convert waste into ash and flue gas through high-temperature combustion, thereby reducing the volume of waste, and recover the heat in the flue gas through the boiler to realize the resource utilization of waste. However, urban waste comes from a wide range of sources, including but not limited to plastics, glass, soil, paper, metal, kitchen waste, etc. In places where the collection link is not sound, there are complex and varied types, and the proportion of various types is unstable, which leads to fluctuations in calorific value and pollutant emissions during waste incineration, seriously affecting the efficiency and environmental protection of incineration treatment.
[0004] Therefore, there is an urgent need to provide a control method, device, control equipment, medium and product for a waste incineration system to improve the calorific value and pollutant emissions of complex and varied types of waste with unstable proportions during the incineration process, thereby ensuring the incineration efficiency and environmental protection. Summary of the invention
[0005] In view of this, it is necessary to provide a control method, device, control equipment, medium and product for a waste incineration system to solve the technical problems existing in the prior art that the types of waste are complex and changeable, and the proportions of various types are unstable, resulting in low incineration efficiency and poor environmental protection during waste incineration.
[0006] On the one hand, in order to solve the above technical problems, the present invention provides a control method for a garbage incineration system, the garbage incineration system comprising a garbage grab crane and a recovery furnace, the garbage grab crane is used to grab garbage in a garbage pit to the recovery furnace for incineration, the method comprising: A mapping model is constructed based on the historical operation data of the waste incineration system; the mapping model is a model representing the mapping relationship between the component concentration and calorific value of the flue gas outlet of the recovery furnace and the garbage grabbing position in the garbage pit; Determining a target flue gas outlet component concentration and a target calorific value of the waste incineration system within a preset operating time; The target grabbing position of the garbage grab crane for the next grabbing is determined based on the target smoke outlet component concentration, the target calorific value and the mapping model.
[0007] In a possible implementation, the historical operation data includes the component concentration and calorific value of the flue gas outlet and visual information of each garbage area in the garbage pit, and the visual information includes visual feature information and spatial coordinate information; then the mapping model is constructed based on the historical operation data of the garbage incineration system, including: Constructing a first correspondence between the smoke outlet component concentration, the calorific value and the visual feature information; Constructing a second correspondence between the visual feature information and the spatial coordinate information; The mapping model is constructed based on the first corresponding relationship and the second corresponding relationship.
[0008] In a possible implementation, the historical operation data includes RGB image data and laser reflectivity data of each of the garbage areas. Before building a mapping model based on the historical operation data of the garbage incineration system, the method further includes: splicing the RGB image data and the laser reflectivity data to obtain garbage splicing data; Then the first corresponding relationship is the relationship between the smoke outlet component concentration, the calorific value and the garbage splicing data, and the visual feature information is the garbage splicing data.
[0009] In a possible implementation, the mapping model includes a first mapping model and a second mapping model, the first mapping model is a model representing the mapping relationship between the smoke outlet component concentration and the garbage grabbing position, and the second mapping model is a model representing the mapping relationship between the calorific value and the garbage grabbing position; then determining the target grabbing position of the garbage grabbing bucket for the next grabbing based on the target smoke outlet component concentration, the target calorific value and the mapping model includes: determining a plurality of initial grab locations in the trash pit; Inputting each of the initial grabbing positions into the first mapping model and the second mapping model respectively to obtain initial smoke outlet component concentration and initial calorific value; A target grabbing position among the plurality of initial grabbing positions is determined based on the initial smoke outlet component concentration, the initial calorific value, the target smoke outlet component concentration, and the target calorific value.
[0010] In a possible implementation, the determining a plurality of initial grabbing positions in the garbage pit includes: Dividing the garbage pit into a plurality of original grabbing positions according to a preset range; The multiple original grasping positions are clustered based on the visual feature information of each of the original grasping positions and the grasping range of the garbage grab crane to obtain the multiple initial grasping positions.
[0011] In a possible implementation, the determining a target grabbing position among the multiple initial grabbing positions based on the initial smoke outlet component concentration, the initial calorific value, the target smoke outlet component concentration, and the target calorific value includes: Determine the similarity between the initial smoke outlet component concentration, the initial calorific value and the target smoke outlet component concentration, the target calorific value; The initial grabbing position corresponding to the initial smoke outlet component concentration and the initial calorific value with the highest similarity is used as the target grabbing position.
[0012] In a possible implementation, the determining the similarity between the initial smoke outlet component concentration, the initial calorific value, and the target smoke outlet component concentration and the target calorific value includes: Constructing initial two-dimensional coordinate points based on the initial flue gas outlet component concentration and the initial calorific value; Constructing a target two-dimensional coordinate point based on the target flue gas outlet component concentration and the target calorific value; The Euclidean distance between the initial two-dimensional coordinate point and the target two-dimensional coordinate point is determined, and the Euclidean distance is used as the similarity.
[0013] In a possible implementation, the determining the similarity between the initial smoke outlet component concentration, the initial calorific value, and the target smoke outlet component concentration and the target calorific value includes: Obtain weight distribution of flue gas outlet component concentration and calorific value; Determining an initial weighted value based on the weight distribution, the initial flue gas outlet component concentration and the initial calorific value; Determining a target weighted value based on the weight distribution, the target flue gas outlet component concentration and the target calorific value; The difference between the initial weighted value and the target weighted value is used as the similarity.
[0014] In a possible implementation, the determining of the target flue gas outlet component concentration and target calorific value of the waste incineration system within a preset operating time includes: Obtaining the mean value of the main steam flow rate, the mean value of the temperature, and the mean value of the component concentration at the flue gas outlet of the waste incineration system within the preset operating time; Determining a target flow condition based on the main steam flow mean, the temperature mean and a preset flow condition category range; Determining a target concentration condition based on the mean value of the flue gas outlet component concentration and a preset concentration condition category range; The target calorific value corresponding to the target flow rate condition and the target flue gas outlet component concentration corresponding to the target concentration condition are obtained.
[0015] In a possible implementation, the time span of the historical operation data is greater than a preset time span.
[0016] In a possible implementation, the time span of the historical operation data is 3 months, and the preset operation time is 1 hour.
[0017] In a possible implementation, the recovery furnace includes a mechanical grate furnace and a waste heat boiler, the mechanical grate furnace is used to incinerate the garbage to obtain heat energy, the waste heat boiler is used to generate high-temperature steam based on the heat energy, the recovery furnace also includes a primary fan connected to the mechanical grate furnace and a secondary fan connected to the waste heat boiler; the method also includes: Acquiring a plurality of boundary conditions of fan frequencies of the primary fan and the secondary fan; Determining the fan frequencies of the primary fan and the secondary fan based on a particle swarm optimization algorithm and the plurality of boundary conditions; The frequency of the primary fan and the secondary fan is adjusted based on the fan frequency.
[0018] In a possible implementation, the boundary condition is: The furnace outlet temperature of the waste heat boiler is greater than or equal to 950° C. and less than or equal to 1100° C.; The carbon monoxide emission concentration in the flue gas outlet of the waste heat boiler is less than or equal to 50 mg / Nm 3 ; The fan frequency of the primary fan and the secondary fan is less than or equal to 50 Hz.
[0019] In a possible implementation, the frequency of adjusting the fan frequency is once every 5 minutes.
[0020] In a possible implementation, the waste incineration system further includes a flue gas purification component, which is used to purify the flue gas generated by the recovery furnace, and the flue gas purification component includes a slaked lime storage tank, which is used to put slaked lime into the pipeline through which the flue gas flows; then the method further includes: Obtaining the sulfur dioxide emission concentration and the hydrogen chloride emission concentration at the outlet of the flue gas purification component; When the sulfur dioxide emission concentration and the hydrogen chloride emission concentration do not meet the emission requirements, the flow rate of slaked lime released from the slaked lime storage tank is increased.
[0021] In a possible implementation, the method further includes: The mapping model is updated based on continuous operation data of the waste incineration system.
[0022] On the other hand, the present invention also provides a control device for a garbage incineration system, the garbage incineration system comprising a garbage grab crane and a recovery furnace, the garbage grab crane is used to grab garbage in a garbage pit to the recovery furnace for incineration, and the device comprises: A mapping model building unit, used to build a mapping model based on the historical operation data of the waste incineration system; the mapping model is a model representing the mapping relationship between the component concentration and calorific value of the flue gas outlet of the recovery furnace and the garbage grabbing position in the garbage pit; A target parameter determination unit, used to determine a target flue gas outlet component concentration and a target calorific value of the waste incineration system within a preset operating time; The target grabbing position determination unit is used to determine the target grabbing position of the garbage grabbing bucket for the next grabbing based on the target smoke outlet component concentration, the target calorific value and the mapping model.
[0023] On the other hand, the present invention further provides a control device, including a memory and a processor, wherein: The memory is used to store programs; The processor is coupled to the memory and is used to execute the program stored in the memory to implement the steps in the control method of the waste incineration system described in any one of the possible implementations above.
[0024] On the other hand, the present invention also provides a computer-readable storage medium, on which a program or instruction is stored. When the program or instruction is executed by a processor, the steps of the control method of the waste incineration system described in any possible implementation method mentioned above are implemented.
[0025] On the other hand, the present invention also provides a computer program product, including a computer program / instruction, which, when executed by a processor, implements the steps of the control method for a waste incineration system described in any one of the possible implementations described above.
[0026] The beneficial effects of the present invention are as follows: the control method of the garbage incineration system provided by the present invention constructs a mapping model based on the historical operation data of the garbage incineration system. The mapping model can be used to obtain the target grabbing position of the garbage grabbing bucket for grabbing the garbage next time according to the determined target flue gas outlet component concentration and target calorific value. The intelligent determination of the grabbing position can make the garbage grabbed and put into the recovery furnace meet the calorific value requirements during the incineration process, ensure the thermal load of the garbage incineration system is stable, and thus improve the incineration efficiency. In addition, the intelligent determination of the grabbing position can make the flue gas outlet component concentration of the garbage meet the requirements during the incineration process, avoid pollutant emissions exceeding the limit, and ensure the environmental protection of the garbage incineration system during the garbage incineration process. In other words, the present invention can eliminate the technical problems of low incineration efficiency and poor environmental protection caused by uneven garbage input or feeding through the intelligent determination of the grabbing position, so that the garbage put into the recovery furnace has a higher incineration efficiency and better environmental protection during the incineration process. BRIEF DESCRIPTION OF THE DRAWINGS
[0027] In order to more clearly illustrate the technical solutions in the embodiments of the present invention, the following briefly introduces the drawings required for use in the description of the embodiments. Obviously, the drawings described below are only some embodiments of the present invention. For those skilled in the art, other drawings can be obtained based on these drawings without creative work.
[0028] Figure 1 A schematic diagram of the structure of an embodiment of a waste incineration system provided by the present invention; Figure 2 A schematic flow chart of an embodiment of a control method for a waste incineration system provided by the present invention; Figure 3 For the present invention Figure 2 A schematic flow chart of an embodiment of S201; Figure 4 For the present invention Figure 2 A schematic flow chart of an embodiment of S203; Figure 5 For the present invention Figure 4 A schematic flow chart of an embodiment of S401; Figure 6 For the present invention Figure 4 A schematic flow chart of an embodiment of S403; Figure 7 For the present invention Figure 6 A schematic diagram of an embodiment of S601; Figure 8 For the present invention Figure 6 Another embodiment of S601 is a flowchart of another embodiment; Fig. 9 For the present invention Figure 2 A schematic flow chart of an embodiment of S202; Fig.10 A schematic diagram of a flow chart of an embodiment of frequency regulation of a primary fan and a secondary fan provided by the present invention; Fig.11 A schematic flow chart of an embodiment of regulating the flow of slaked lime provided by the present invention; Fig.12 A schematic structural diagram of an embodiment of a control device for a waste incineration system provided by the present invention; Fig.13 A schematic structural diagram of an embodiment of the control device provided by the present invention. DETAILED DESCRIPTION
[0029] The following will be combined with the drawings in the embodiments of the present invention to clearly and completely describe the technical solutions in the embodiments of the present invention. Obviously, the described embodiments are only part of the embodiments of the present invention, not all of the embodiments. Based on the embodiments of the present invention, all other embodiments obtained by those skilled in the art without creative work are within the scope of protection of the present invention.
[0030] It should be understood that the schematic drawings are not drawn to scale. The flowchart used in the present invention shows the operations implemented according to some embodiments of the present invention. It should be understood that the operations of the flowchart can be implemented out of order, and the steps without logical context can be reversed in order or implemented simultaneously. In addition, those skilled in the art, under the guidance of the content of the present invention, can add one or more other operations to the flowchart, and can also remove one or more operations from the flowchart. Some of the block diagrams shown in the accompanying drawings are functional entities, which do not necessarily correspond to physically or logically independent entities. These functional entities can be implemented in software form, or in one or more hardware modules or integrated circuits, or in different networks and / or processor systems and / or microcontroller systems.
[0031] Reference to an "embodiment" herein means that a particular feature, structure, or characteristic described in conjunction with the embodiment may be included in at least one embodiment of the present invention. The appearance of the phrase in various places in the specification does not necessarily refer to the same embodiment, nor is it an independent or alternative embodiment that is mutually exclusive with other embodiments. It is explicitly and implicitly understood by those skilled in the art that the embodiments described herein may be combined with other embodiments.
[0032] The present invention provides a control method, device, control equipment, medium and product of a garbage incineration system, which are respectively described below.
[0033] Before presenting the embodiments, the waste incineration system is introduced first.
[0034] like Figure 1 As shown, the garbage incineration system 10 includes a garbage grab crane 100 and a recovery furnace 200. The garbage grab crane 100 is used to grab the garbage in the garbage pit 20 and bring it to the recovery furnace 200 for incineration. The incineration of garbage in the recovery furnace 200 includes three stages: drying, burning, and burning. In addition, in the specific process of recycling garbage by the recovery furnace 200: a large amount of high-temperature flue gas generated after the garbage is burned is heat exchanged to heat the liquid medium to generate superheated steam, and the superheated steam enters the steam turbine generator set to generate electricity.
[0035] based on Figure 1 The waste incineration system 10 in the embodiment of the present invention is as follows: Figure 2 As shown, the control method of the waste incineration system includes: S201, constructing a mapping model based on historical operation data of the waste incineration system; the mapping model is a model representing the mapping relationship between the component concentration and calorific value of the flue gas outlet of the recovery furnace and the garbage grabbing position in the garbage pit; S202, determining the target flue gas outlet component concentration and target calorific value of the waste incineration system within a preset operating time; S203, determining the target grabbing position of the garbage grab crane for the next grabbing based on the target flue gas outlet component concentration, the target calorific value and the mapping model.
[0036] Among them, calorific value refers to the heat released by the combustion of unit fuel.
[0037] It should be noted that the target grabbing position refers to the grabbing position that matches the target flue gas outlet component concentration and target calorific value, so as to ensure that the next time the garbage is grabbed, the concentration and calorific value of the target flue gas outlet are not much different during incineration, thereby reducing the concentration fluctuation of pollutant emissions and ensuring the environmental protection of the garbage incineration system.
[0038] Among them, the preset running time can be set or adjusted according to actual conditions.
[0039] In a specific embodiment of the present invention, the preset running time is 1 hour.
[0040] It should be understood that the model structure of the mapping model can be any deep learning network structure that can accurately characterize the mapping relationship between the smoke outlet component concentration, calorific value and the garbage grabbing position in the garbage pit.
[0041] It should also be understood that the construction of the mapping model should include training, testing and verification processes, and the larger the sample size, the more accurate the constructed mapping model. Therefore, in a specific embodiment of the present invention, the time span of the historical operation data should be greater than the preset time length.
[0042] Among them, the preset duration can be set or adjusted according to the actual application scenario. Specifically, the preset duration is 3 months.
[0043] It should also be noted that the concentration of flue gas outlet components includes but is not limited to sulfur dioxide concentration and hydrogen chloride concentration.
[0044] Compared with the prior art, the control method of the garbage incineration system provided by the embodiment of the present invention constructs a mapping model based on the historical operation data of the garbage incineration system. Through the mapping model, the target grabbing position of the garbage grabbing bucket for grabbing the garbage next time can be obtained according to the determined target flue gas outlet component concentration and target calorific value. The intelligent determination of the grabbing position can make the garbage grabbed and put into the recovery furnace meet the calorific value requirements during the incineration process, ensure the thermal load of the garbage incineration system is stable, and thus improve the incineration efficiency. In addition, the intelligent determination of the grabbing position can make the flue gas outlet component concentration of the garbage meet the requirements during the incineration process, avoid pollutant emissions exceeding the limit, and ensure the environmental protection of the garbage incineration system during the garbage incineration process. In other words, the embodiment of the present invention can eliminate the technical problems of low incineration efficiency and poor environmental protection caused by uneven garbage input or feeding through the intelligent determination of the grabbing position, so that the garbage put into the recovery furnace has a higher incineration efficiency and better environmental protection during the incineration process.
[0045] Since the calorific value and the smoke outlet component concentration are related to factors such as the type of garbage, the position coordinate data alone cannot represent these factors. Therefore, in order to realize the mapping relationship between the smoke outlet component concentration, the calorific value and the grabbing position, in some embodiments of the present invention, the historical operation data includes the smoke outlet component concentration, the calorific value and the visual information of each garbage area in the garbage pit, and the visual information includes the visual feature information and the spatial coordinate information; Figure 3 As shown, step S201 includes: S301, constructing a first correspondence between the smoke outlet component concentration, calorific value and visual feature information; S302, constructing a second correspondence between visual feature information and spatial coordinate information; S303: Construct a mapping model based on the first corresponding relationship and the second corresponding relationship.
[0046] The embodiment of the present invention uses visual feature information as a bridge between the smoke outlet component concentration, calorific value and spatial coordinate information, and uses visual feature information to represent the features of different positions, thereby associating the features with the coordinate position and the smoke outlet component concentration and calorific value, thereby achieving the purpose of determining the spatial position through the smoke outlet component concentration and calorific value, that is, achieving the determination of the target capture position.
[0047] It can be seen from the above description that the accuracy of the visual feature information is crucial to the accurate determination of the target grasping position. Therefore, in some embodiments of the present invention, the historical operation data includes the RGB image data and the laser reflectivity data of each garbage area, and before step S201, it also includes: splicing the RGB image data and the laser reflectivity data to obtain garbage spliced data; The first corresponding relationship in step S301 is the relationship between the smoke outlet component concentration, calorific value and garbage splicing data, that is, the visual feature information is the garbage splicing data.
[0048] The embodiment of the present invention uses junk splicing data obtained by splicing RGB image data and laser reflection data as visual feature information, which can increase the amount of information in the visual feature information and further ensure the accuracy of the determined target capture position.
[0049] In a specific embodiment of the present invention, the RGB image data includes data of three channels, namely, red, green and blue, and the garbage stitching image includes RGB data of three channels and laser reflectivity data of one channel, namely, stitching data of four channels.
[0050] In a specific embodiment of the present invention, the RGB image data and the laser reflection data are obtained as follows: Figure 1 As shown, the image is acquired through an image monitor 30 and a laser radar 40 arranged in the garbage pit 20 , and the image monitor 30 and the laser radar 40 are respectively arranged on the opposite walls of the garbage pit 20 .
[0051] Furthermore, the outlet component concentration of the flue gas is obtained by monitoring the outlet flue gas component concentration monitor 50 disposed at the outlet of the recovery furnace 200 .
[0052] Because the waste incineration system is controlled based on the calorific value and the concentration of the components at the flue gas outlet when incinerating the waste, that is, the target grabbing position is determined based on the parameters of the two dimensions of calorific value and the concentration of the components at the flue gas outlet.
[0053] Therefore, in order to simplify the model structure of the mapping model and accurately determine the target grabbing position, in some embodiments of the present invention, the mapping model includes a first mapping model and a second mapping model, the first mapping model is a model representing the mapping relationship between the smoke outlet component concentration and the garbage grabbing position, and the second mapping model is a model representing the mapping relationship between the calorific value and the garbage grabbing position; then Figure 4 As shown, step S203 includes: S401, determining a plurality of initial grab positions in the garbage pit; S402, inputting each initial grabbing position into the first mapping model and the second mapping model respectively to obtain the initial smoke outlet component concentration and initial calorific value; S403 , determining a target grabbing position among a plurality of initial grabbing positions based on the initial smoke outlet component concentration, the initial calorific value, the target smoke outlet component concentration, and the target calorific value.
[0054] The embodiment of the present invention sets a mapping model including a first mapping model and a second mapping model. The first mapping model is only used to determine the smoke outlet component concentration, and the second mapping model is only used to determine the calorific value. This simplifies the model complexity of the first mapping model and the second mapping model, thereby improving the accuracy of the first mapping model and the second mapping model, that is, improving the accuracy of the obtained initial smoke outlet component concentration and initial calorific value, thereby accurately determining the target grasping position.
[0055] In some embodiments of the present invention, Figure 5 As shown, step S401 includes: S501, dividing the garbage pit into a plurality of original grabbing positions within a preset range; S502: Clustering multiple original grabbing positions based on visual feature information of each original grabbing position and the grabbing range of the garbage grab crane to obtain multiple initial grabbing positions.
[0056] The embodiment of the present invention determines the initial grabbing position based on visual feature information, thereby ensuring that the visual feature information of garbage at the same initial grabbing position is not much different, that is, the performance of garbage at the same initial grabbing position when burning is not much different, so as to ensure that the emission of flue gas pollutants during garbage combustion fluctuates less, thereby ensuring its environmental protection.
[0057] Furthermore, the embodiment of the present invention uses the grabbing range of the garbage grab crane as a constraint condition when determining the initial grabbing position, thereby ensuring that the garbage grab crane can grab the garbage at an initial grabbing position and avoid exceeding the grabbing range of the garbage grab crane.
[0058] Specifically, step S501 is: dividing the garbage pit into a plurality of original grabbing positions with an area within a preset range based on a preset number of rows and columns.
[0059] The clustering algorithm in step S502 is the K-Means clustering algorithm.
[0060] In some embodiments of the present invention, Figure 6 As shown, step S403 includes: S601, determining the similarity between the initial flue gas outlet component concentration, initial calorific value and the target flue gas outlet component concentration, target calorific value; S602: The initial grabbing position corresponding to the initial flue gas outlet component concentration and initial calorific value with the highest similarity is used as the target grabbing position.
[0061] The embodiment of the present invention takes the target smoke outlet component concentration and the target calorific value as the target, and takes the initial grabbing position that is most similar to the target smoke outlet component concentration and the target calorific value among multiple initial grabbing positions as the target grabbing position, so that the grabbed garbage meets the calorific value and smoke outlet component concentration requirements.
[0062] In a specific embodiment of the present invention, Figure 7 As shown, step S601 includes: S701, constructing initial two-dimensional coordinate points based on initial flue gas outlet component concentration and initial calorific value; S702, constructing a target two-dimensional coordinate point based on the target flue gas outlet component concentration and the target calorific value; S703: Determine the Euclidean distance between the initial two-dimensional coordinate point and the target two-dimensional coordinate point, and use the Euclidean distance as the similarity.
[0063] Specifically, the initial flue gas outlet component concentration is denoted as MS i , the initial calorific value is PI i , the target flue gas outlet component concentration is MS, the target calorific value is PI, then the initial two-dimensional coordinate point is (MS i , P.I. i ), the target two-dimensional coordinate point is (MS, PI), and the calculation formula of the Euclidean distance is:
[0064] In another specific embodiment of the present invention, Figure 8 As shown, step S601 includes: S801, obtaining weight distribution of flue gas outlet component concentration and calorific value; S802, determining an initial weighted value based on weight distribution, initial flue gas outlet component concentration and initial calorific value; S803, determining a target weighted value based on weight distribution, target flue gas outlet component concentration, and target calorific value; S804: Taking the difference between the initial weighted value and the target weighted value as the similarity.
[0065] Specifically, the similarity for:
[0066] In the formula, is the weight of the component concentration at the flue gas outlet.
[0067] The embodiment of the present invention provides two methods for calculating similarity, which improves the diversity and redundancy of similarity calculation methods. The two methods can be selected according to actual application scenarios.
[0068] Since the combustion of garbage is a dynamic process, its calorific value and the concentration of smoke outlet components are dynamically changing processes. In order to accurately determine the target smoke outlet component concentration and target calorific value, in some embodiments of the present invention, such as Fig. 9 As shown, step S202 includes: S901, obtaining the average value of the main steam flow rate, the average value of the temperature, and the average value of the component concentration at the flue gas outlet of the waste incineration system within the preset operating time; S902, determining a target flow condition based on a main steam flow average, a temperature average, and a preset flow condition category range; S903, determining a target concentration condition based on the mean value of the component concentration at the flue gas outlet and a preset concentration condition category range; S904. Obtain a target calorific value corresponding to a target flow rate condition and a target flue gas outlet component concentration corresponding to a target concentration condition.
[0069] The embodiment of the present invention uses the mean value of the main steam flow rate, the mean value of the temperature, and the mean value of the component concentration at the flue gas outlet within the preset operating time as the basis for determining the target calorific value and the target component concentration at the flue gas outlet, and uses the mean value to replace the value that fluctuates continuously over a period of time, which is simple and accurate. In addition, the embodiment of the present invention determines the target component concentration at the flue gas outlet and the target calorific value based on the calibrated concentration condition and flow condition, thereby improving the representativeness and accuracy of the target component concentration at the flue gas outlet and the target calorific value.
[0070] It should be noted that different concentration conditions and different flow conditions can be established based on historical operating data, and the flue gas outlet component concentrations corresponding to different concentration conditions and the calorific values corresponding to different flow conditions can be determined to ensure the adaptability and accuracy of the calorific value and flue gas outlet component concentration to the actual operating scenario.
[0071] In a specific embodiment of the present invention, Figure 1 As shown, the main steam flow average value and the temperature average value in step S901 can be obtained based on the main steam flow and temperature detector 60 set on the recovery furnace 200.
[0072] In some embodiments of the present invention, Figure 1 As shown, the recovery furnace 200 includes a mechanical grate furnace 210 and a waste heat boiler 220. The mechanical grate furnace 210 is used to incinerate garbage to obtain thermal energy, and the waste heat boiler 220 is used to generate high-temperature steam based on thermal energy. The recovery furnace 200 also includes a primary fan 230 connected to the mechanical grate furnace 210 and a secondary fan 240 connected to the waste heat boiler 220.
[0073] The primary fan 230 and the secondary fan 240 are used to supply primary air and secondary air to the mechanical grate furnace 210 and the waste heat boiler 220 respectively. The function of the primary air is to dry and assist combustion of the mechanical grate furnace 210, and the function of the secondary air is to enhance combustion in the combustion zone of the waste heat boiler 220.
[0074] From the above description, it can be seen that the primary air and the secondary air are crucial to the garbage combustion process. On the basis of accurately determining the target grabbing position, in order to further improve the garbage combustion efficiency, in some embodiments of the present invention, such as Fig.10 As shown, the control method of the waste incineration system also includes: S1001, obtaining multiple boundary conditions of fan frequencies of a primary fan and a secondary fan; S1002. Determine the fan frequencies of the primary fan and the secondary fan based on a particle swarm optimization algorithm and multiple boundary conditions; S1003. Adjust the frequency of the primary fan and the secondary fan based on the fan frequency.
[0075] The embodiment of the present invention can ensure the rationality of the fan frequency by adjusting the fan frequency of the primary fan and the secondary fan based on multiple boundary conditions, so as to improve the combustion efficiency of garbage.
[0076] In a specific embodiment of the present invention, the boundary conditions are: The furnace outlet temperature of the waste heat boiler is greater than or equal to 950°C and less than or equal to 1100°C; The carbon monoxide emission concentration in the flue gas outlet of the waste heat boiler is less than or equal to 50mg / Nm 3 ; The fan frequency of the primary fan and the secondary fan is less than or equal to 50 Hz.
[0077] Since the combustion of garbage is a fast and dynamic process, the adjustment of the fan frequency of the primary fan and the secondary fan should also be constantly changing, that is, it needs to be adjusted according to the progress of the combustion process.
[0078] In a specific embodiment of the present invention, the frequency of adjusting the fan frequency is once every 5 minutes.
[0079] In addition to generating heat energy, waste heat boilers also produce high-risk flue gas, which includes carbon monoxide, sulfur dioxide, hydrogen chloride and other substances. If they are directly discharged into the atmosphere, they will cause serious air pollution. Therefore, if Figure 1 As shown, the waste incineration system 10 further includes a flue gas purification component 300 , which is used to purify the flue gas generated by the recovery furnace 200 .
[0080] In a specific embodiment of the present invention, the flue gas purification component 300 adopts the treatment process of "rotary spray semi-dry deacidification + injection of activated carbon to remove heavy metals and dioxins + injection of slaked lime desulfurization". Specifically, the flue gas purification component 300 includes a rotary spray drying desulfurization device 310, a slaked lime storage tank 320, an activated carbon injection device 330 and a slaked lime injection device 340. A slaked lime flow regulating valve 70 is provided between the slaked lime storage tank 320 and the rotary spray drying desulfurization device 310, and the slaked lime flow regulating valve 70 is used to adjust the flow of slaked lime added to the rotary spray drying desulfurization device 310.
[0081] Furthermore, the flue gas purification component 300 also includes a dust collector 350, which removes dust from the flue gas passing through the rotary spray drying desulfurization device 310, the slaked lime storage tank 320, the activated carbon injection device 330 and the slaked lime injection device 340, and discharges the dust-removed flue gas into the atmosphere through the chimney 360.
[0082] In order to ensure that the flue gas discharged into the atmosphere meets the emission requirements and does not cause adverse effects on the environment, in some embodiments of the present invention, Fig.11 As shown, the control method of the waste incineration system also includes: S1101. Obtaining sulfur dioxide emission concentration and hydrogen chloride emission concentration at the outlet of the flue gas purification component; S1102. When the sulfur dioxide emission concentration and hydrogen chloride emission concentration do not meet the emission requirements, increase the flow rate of slaked lime released into the slaked lime storage tank.
[0083] Among them, the outlet of the flue gas purification component in step S1101 is the chimney outlet.
[0084] The embodiment of the present invention controls the concentration of flue gas components discharged into the atmosphere by adjusting the flow rate of slaked lime released from the slaked lime storage tank, thereby ensuring the environmental friendliness of the waste incineration system 10. At the same time, it avoids excessive input of slaked lime and reduces costs.
[0085] Since the waste incineration system 10 is a continuous and long-term operating system, in order to ensure the accuracy of its control, in some embodiments of the present invention, the control method of the waste incineration system further includes: The mapping model is updated based on the continuous operating data of the waste incineration system.
[0086] The embodiment of the present invention can ensure the real-time and accuracy of the mapping model by updating the mapping model based on the continuous operation data, thereby improving the accurate control of the waste incineration system in various time periods.
[0087] Specifically, the specific means for updating the mapping model may be: updating the mapping model based on the data of the three or four months of operation every three or four months of operation.
[0088] In another specific embodiment of the present invention, the mapping model may be updated by: rolling updating the mapping model based on continuous operation data, specifically, the mapping model used on August 20, 2024 is constructed based on the operation data from June 19, 2024 to August 19, 2024, and the mapping model used on August 21, 2024 is constructed based on the operation data from June 20, 2024 to August 20, 2024, to ensure the real-time and accuracy of the mapping model.
[0089] In summary, the control method of the waste incineration system proposed in the embodiment of the present invention achieves the following technical effects: 1. Accurate feeding, intelligent selection of the grabbing position according to the characteristics of the garbage, avoiding uneven incoming and feeding materials, and ensuring the stability of the thermal load of the incinerator; 2. Stable emission of flue gas pollutants and saving of environmentally friendly consumables: on the one hand, by determining the grabbing position, the type of waste entering the furnace is effectively controlled, the fluctuation of the flue gas pollutant concentration at the furnace outlet is reduced, and the stable operation of the flue gas treatment system is ensured; on the other hand, according to the flue gas pollutant outlet requirements and the reaction environment conditions, the consumables demand is accurately calculated to avoid excessive input of slaked lime and reduce costs.
[0090] In order to better implement the control method of the garbage incineration system in the embodiment of the present invention, based on the control method of the garbage incineration system, the embodiment of the present invention also provides a control device of the garbage incineration system. The garbage incineration system includes a garbage grab crane and a recovery furnace. The garbage grab crane is used to grab garbage in the garbage pit and bring it to the recovery furnace for incineration. Fig.12 As shown, the control device 1200 of the garbage incineration system includes: A mapping model building unit 1201 is used to build a mapping model based on historical operation data of the waste incineration system; the mapping model is a model representing the mapping relationship between the component concentration and calorific value of the flue gas outlet of the recovery furnace and the garbage grabbing position in the garbage pit; The target parameter determination unit 1202 is used to determine the target flue gas outlet component concentration and target calorific value of the waste incineration system within a preset operating time; The target grabbing position determination unit 1203 is used to determine the target grabbing position of the garbage grab crane for the next grabbing based on the target flue gas outlet component concentration, the target calorific value and the mapping model.
[0091] The control device 1200 of the waste incineration system provided in the above embodiment can implement the technical solution described in the above white light interference effective image extraction method embodiment. The specific implementation principles of the above modules or units can refer to the corresponding contents in the above control method embodiment of the waste incineration system, which will not be repeated here.
[0092] like Fig.13As shown, the present invention also provides a control device 1300. The control device 1300 includes a processor 1301, a memory 1302 and a display 1303. Fig.13 Only some components of the control device 1300 are shown, but it should be understood that it is not required to implement all of the components shown, and more or fewer components may be implemented instead.
[0093] In some embodiments, the processor 1301 may be a central processing unit (CPU), a microprocessor or other data processing chip, used to run program codes or process data stored in the memory 1302, such as the control method of the waste incineration system in the present invention.
[0094] In some embodiments of the present invention, processor 1301 may be a single server or a server group. The server group may be centralized or distributed. In some embodiments, processor 1301 may be local or remote. In some embodiments, processor 1301 may be implemented in a cloud platform. In one embodiment, the cloud platform may include a private cloud, a public cloud, a hybrid cloud, a community cloud, a distributed cloud, an internal cloud, a multi-cloud, etc., or any combination thereof.
[0095] In some embodiments, the memory 1302 may be an internal storage unit of the control device 1300, such as a hard disk or memory of the control device 1300. In other embodiments, the memory 1302 may also be an external storage device of the control device 1300, such as a plug-in hard disk, a smart media card (SMC), a secure digital (SD) card, a flash card, etc., equipped on the control device 1300.
[0096] Furthermore, the memory 1302 may include both an internal storage unit of the control device 1300 and an external storage device. The memory 1302 is used to store application software installed in the control device 1300 and various data.
[0097] In some embodiments, the display 1303 may be an LED display, a liquid crystal display, a touch-sensitive liquid crystal display, an OLED (Organic Light-Emitting Diode) touch device, etc. The display 1303 is used to display information of the control device 1300 and to display a visual user interface. The components 1301-1303 of the control device 1300 communicate with each other via a system bus.
[0098] In some embodiments of the present invention, when the processor 1301 executes the control program of the waste incineration system in the memory 1302, the following steps may be implemented: A mapping model is constructed based on the historical operation data of the waste incineration system; the mapping model is a model that represents the mapping relationship between the component concentration and calorific value of the flue gas outlet of the recovery furnace and the garbage grabbing position in the garbage pit; Determine the target flue gas outlet component concentration and target calorific value of the waste incineration system within the preset operating time; The target grabbing position of the garbage grab crane for the next grab is determined based on the target flue gas outlet component concentration, target calorific value and mapping model.
[0099] It should be understood that: when the processor 1301 executes the white light interference effective image extraction program in the memory 1302, in addition to the above functions, other functions can also be implemented. For details, please refer to the description of the corresponding method embodiment above.
[0100] Furthermore, the embodiment of the present invention does not specifically limit the type of the control device 1300 mentioned. The control device 1300 may be a portable control device such as a mobile phone, a tablet computer, a personal digital assistant (PDA), a wearable device, a laptop computer, etc. Exemplary embodiments of portable control devices include but are not limited to portable control devices equipped with IOS, Android, Microsoft or other operating systems. The above-mentioned portable control device may also be other portable control devices. It should also be understood that in some other embodiments of the present invention, the control device 1300 may not be a portable control device, but a desktop computer with a touch-sensitive surface (such as a touch panel).
[0101] Correspondingly, an embodiment of the present invention also provides a computer-readable storage medium, which is used to store computer-readable programs or instructions. When the program or instructions are executed by a processor, it can implement the steps or functions of the control method of the waste incineration system provided by the above-mentioned method embodiments.
[0102] Accordingly, an embodiment of the present invention further provides a computer program product, including a computer program / instruction, which implements the steps of the control method of the waste incineration system in any of the above embodiments when the computer program / instruction is executed by a processor.
[0103] Those skilled in the art will appreciate that all or part of the processes of the above-mentioned embodiments can be implemented by instructing related hardware (such as a processor, a controller, etc.) through a computer program, and the computer program can be stored in a computer-readable storage medium, wherein the computer-readable storage medium is a disk, an optical disk, a read-only storage memory, or a random access memory, etc.
[0104] The control method, device, control equipment, medium and product of a waste incineration system provided by the present invention are introduced in detail above. Specific examples are used in this article to illustrate the principle and implementation mode of the present invention. The description of the above embodiments is only used to help understand the method of the present invention and its core idea; at the same time, for technical personnel in this field, according to the idea of the present invention, there will be changes in the specific implementation mode and application scope. In summary, the content of this specification should not be understood as a limitation on the present invention.
Claims
1. A control method for a waste incineration system, characterized in that: The garbage incineration system comprises a garbage grab crane and a recovery furnace, wherein the garbage grab crane is used to grab garbage in a garbage pit and bring it to the recovery furnace for incineration. The method comprises: A mapping model is constructed based on the historical operation data of the waste incineration system; the mapping model is a model representing the mapping relationship between the component concentration and calorific value of the flue gas outlet of the recovery furnace and the garbage grabbing position in the garbage pit; Determining a target flue gas outlet component concentration and a target calorific value of the waste incineration system within a preset operating time; The target grabbing position of the garbage grab crane for the next grabbing is determined based on the target smoke outlet component concentration, the target calorific value and the mapping model.
2. The control method of the waste incineration system according to claim 1, characterized in that: The historical operation data includes the component concentration and calorific value of the flue gas outlet and the visual information of each garbage area in the garbage pit, wherein the visual information includes visual feature information and spatial coordinate information; The step of constructing a mapping model based on the historical operation data of the waste incineration system includes: Constructing a first correspondence between the smoke outlet component concentration, the calorific value and the visual feature information; Constructing a second correspondence between the visual feature information and the spatial coordinate information; The mapping model is constructed based on the first corresponding relationship and the second corresponding relationship.
3. The control method of the waste incineration system according to claim 2, characterized in that: The historical operation data includes RGB image data and laser reflectivity data of each of the garbage areas. Before building a mapping model based on the historical operation data of the garbage incineration system, the method further includes: splicing the RGB image data and the laser reflectivity data to obtain garbage splicing data; Then the first corresponding relationship is the relationship between the smoke outlet component concentration, the calorific value and the garbage splicing data, and the visual feature information is the garbage splicing data.
4. The control method of the waste incineration system according to claim 2, characterized in that: The mapping model includes a first mapping model and a second mapping model, wherein the first mapping model is a model representing the mapping relationship between the smoke outlet component concentration and the garbage grabbing position, and the second mapping model is a model representing the mapping relationship between the calorific value and the garbage grabbing position; then determining the target grabbing position for the next grabbing of the garbage grabbing bucket based on the target smoke outlet component concentration, the target calorific value and the mapping model includes: determining a plurality of initial grab locations in the trash pit; Inputting each of the initial grabbing positions into the first mapping model and the second mapping model respectively to obtain initial smoke outlet component concentration and initial calorific value; A target grabbing position among the plurality of initial grabbing positions is determined based on the initial smoke outlet component concentration, the initial calorific value, the target smoke outlet component concentration, and the target calorific value.
5. The control method of the waste incineration system according to claim 4, characterized in that: The determining of a plurality of initial grabbing positions in the garbage pit comprises: Dividing the garbage pit into a plurality of original grabbing positions according to a preset range; The multiple original grasping positions are clustered based on the visual feature information of each of the original grasping positions and the grasping range of the garbage grab crane to obtain the multiple initial grasping positions.
6. The control method of the waste incineration system according to claim 4, characterized in that: The determining of a target grabbing position among the multiple initial grabbing positions based on the initial smoke outlet component concentration, the initial calorific value, the target smoke outlet component concentration, and the target calorific value comprises: Determine the similarity between the initial smoke outlet component concentration, the initial calorific value and the target smoke outlet component concentration, the target calorific value; The initial grabbing position corresponding to the initial smoke outlet component concentration and the initial calorific value with the highest similarity is used as the target grabbing position.
7. The control method of the waste incineration system according to claim 6, characterized in that: The determining of the similarity between the initial smoke outlet component concentration, the initial calorific value, and the target smoke outlet component concentration and the target calorific value comprises: Constructing initial two-dimensional coordinate points based on the initial flue gas outlet component concentration and the initial calorific value; Constructing a target two-dimensional coordinate point based on the target flue gas outlet component concentration and the target calorific value; The Euclidean distance between the initial two-dimensional coordinate point and the target two-dimensional coordinate point is determined, and the Euclidean distance is used as the similarity.
8. The control method of the waste incineration system according to claim 6, characterized in that: The determining of the similarity between the initial smoke outlet component concentration, the initial calorific value, and the target smoke outlet component concentration and the target calorific value comprises: Obtain weight distribution of flue gas outlet component concentration and calorific value; Determining an initial weighted value based on the weight distribution, the initial flue gas outlet component concentration and the initial calorific value; Determining a target weighted value based on the weight distribution, the target flue gas outlet component concentration and the target calorific value; The difference between the initial weighted value and the target weighted value is used as the similarity.
9. The control method of the waste incineration system according to claim 1, characterized in that: The step of determining the target flue gas outlet component concentration and target calorific value of the waste incineration system within a preset operating time includes: Obtaining the mean value of the main steam flow rate, the mean value of the temperature, and the mean value of the component concentration at the flue gas outlet of the waste incineration system within the preset operating time; Determining a target flow condition based on the main steam flow mean, the temperature mean and a preset flow condition category range; Determining a target concentration condition based on the mean value of the flue gas outlet component concentration and a preset concentration condition category range; The target calorific value corresponding to the target flow rate condition and the target flue gas outlet component concentration corresponding to the target concentration condition are obtained.
10. The control method of a waste incineration system according to any one of claims 1 to 9, characterized in that: The time span of the historical operation data is greater than a preset time span.
11. The control method of the waste incineration system according to claim 10, characterized in that: The time span of the historical operation data is 3 months, and the preset operation time is 1 hour.
12. The control method of the waste incineration system according to claim 1, characterized in that: The recovery furnace comprises a mechanical grate furnace and a waste heat boiler, wherein the mechanical grate furnace is used to incinerate the garbage to obtain heat energy, and the waste heat boiler is used to generate high-temperature steam based on the heat energy, and the recovery furnace also comprises a primary fan connected to the mechanical grate furnace and a secondary fan connected to the waste heat boiler; the method further comprises: Acquiring a plurality of boundary conditions of fan frequencies of the primary fan and the secondary fan; Determining the fan frequencies of the primary fan and the secondary fan based on a particle swarm optimization algorithm and the plurality of boundary conditions; The frequency of the primary fan and the secondary fan is adjusted based on the fan frequency.
13. The control method of the waste incineration system according to claim 12, characterized in that: The boundary conditions are: The furnace outlet temperature of the waste heat boiler is greater than or equal to 950° C. and less than or equal to 1100° C.; The carbon monoxide emission concentration in the flue gas outlet of the waste heat boiler is less than or equal to 50 mg / Nm 3 ; The fan frequency of the primary fan and the secondary fan is less than or equal to 50 Hz.
14. The control method of the waste incineration system according to claim 13, characterized in that: The frequency of adjusting the fan frequency is once every 5 minutes.
15. The control method of a waste incineration system according to claim 1, characterized in that: The waste incineration system further includes a flue gas purification component, which is used to purify the flue gas generated by the recovery furnace, and the flue gas purification component includes a slaked lime storage tank, which is used to put slaked lime into the pipeline through which the flue gas flows; the method further includes: Obtaining the sulfur dioxide emission concentration and the hydrogen chloride emission concentration at the outlet of the flue gas purification component; When the sulfur dioxide emission concentration and the hydrogen chloride emission concentration do not meet the emission requirements, the flow rate of slaked lime released from the slaked lime storage tank is increased.
16. The control method of a waste incineration system according to claim 1, characterized in that: The method further comprises: The mapping model is updated based on continuous operation data of the waste incineration system.
17. A control device for a waste incineration system, characterized in that: The garbage incineration system includes a garbage grab crane and a recovery furnace. The garbage grab crane is used to grab garbage from a garbage pit and bring it to the recovery furnace for incineration. The device includes: A mapping model building unit, used to build a mapping model based on the historical operation data of the waste incineration system; the mapping model is a model representing the mapping relationship between the component concentration and calorific value of the flue gas outlet of the recovery furnace and the garbage grabbing position in the garbage pit; A target parameter determination unit, used to determine a target flue gas outlet component concentration and a target calorific value of the waste incineration system within a preset operating time; The target grabbing position determination unit is used to determine the target grabbing position of the garbage grabbing bucket for the next grabbing based on the target smoke outlet component concentration, the target calorific value and the mapping model.
18. A control device, characterized in that: comprising a memory and a processor, wherein: The memory is used to store programs; The processor is coupled to the memory and is used to execute the program stored in the memory to implement the steps in the control method of the waste incineration system described in any one of claims 1 to 16.
19. A computer-readable storage medium, characterized in that: The computer-readable storage medium stores a program or instruction, and when the program or instruction is executed by the processor, the steps of the control method of the waste incineration system described in any one of claims 1 to 16 are implemented.
20. A computer program product comprising a computer program / instructions, characterized in that When the computer program / instructions are executed by a processor, the steps of the method for controlling a waste incineration system according to any one of claims 1 to 16 are implemented.
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