CN111722567B - Control method, system and device of monitoring equipment and computer readable storage medium - Google Patents

Control method, system and device of monitoring equipment and computer readable storage medium Download PDF

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CN111722567B
CN111722567B CN202010607522.3A CN202010607522A CN111722567B CN 111722567 B CN111722567 B CN 111722567B CN 202010607522 A CN202010607522 A CN 202010607522A CN 111722567 B CN111722567 B CN 111722567B
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preset
standard
parameters
judging whether
boiler
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CN111722567A (en
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郭键锋
张海红
汪兴业
余淼
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Shenzhen Ruijing Environmental Science And Technology Co ltd
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Shenzhen Ruijing Environmental Science And Technology Co ltd
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    • GPHYSICS
    • G05CONTROLLING; REGULATING
    • G05BCONTROL OR REGULATING SYSTEMS IN GENERAL; FUNCTIONAL ELEMENTS OF SUCH SYSTEMS; MONITORING OR TESTING ARRANGEMENTS FOR SUCH SYSTEMS OR ELEMENTS
    • G05B19/00Programme-control systems
    • G05B19/02Programme-control systems electric
    • G05B19/04Programme control other than numerical control, i.e. in sequence controllers or logic controllers
    • G05B19/042Programme control other than numerical control, i.e. in sequence controllers or logic controllers using digital processors
    • G05B19/0423Input/output

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Abstract

The invention discloses a control method, a system and a device of monitoring equipment and a computer readable storage medium, wherein the control method of the monitoring equipment comprises the following steps: acquiring environmental parameters of the incinerator during waste incineration; judging whether the environmental parameters meet preset reference standards or not; if so, controlling the monitoring equipment to keep a closed state, otherwise, controlling the monitoring equipment to be opened. Namely, the technical scheme of the invention can avoid the invalid operation of the monitoring equipment and reduce the monitoring cost.

Description

Control method, system and device of monitoring equipment and computer readable storage medium
Technical Field
The invention relates to the technical field of dioxin emission detection, in particular to a control method, a system and a device of monitoring equipment and a computer readable storage medium.
Background
Because dioxin causes pollution and toxicity to the environment and human beings, the emission amount of the dioxin generated by the incinerator is a pollution index which is mainly regulated by environmental protection departments. In order to avoid the excessive emission of dioxin, at present, the emission of dioxin generated by an incinerator is monitored according to the requirements of environmental protection departments, so that when the incinerator burns garbage, monitoring equipment needs to be started simultaneously with the incinerator to monitor the emission of dioxin. However, when the incinerator burns garbage sufficiently, the generated dioxin is negligible, and the dioxin discharge amount is not monitored, in this case, the monitoring device and the incinerator run synchronously, so that invalid operation of the monitoring device is undoubtedly caused, and meanwhile, after the dioxin is sampled on site, analysis is carried out in a laboratory, so that the monitoring cost is increased.
Disclosure of Invention
The invention mainly aims to provide a control method of monitoring equipment, aiming at avoiding the invalid operation of the monitoring equipment and reducing the monitoring cost.
In order to achieve the above object, the present invention provides a method for controlling a monitoring device, comprising the steps of:
acquiring environmental parameters of the incinerator during waste incineration;
judging whether the environmental parameters meet preset reference standards or not;
if so, controlling the monitoring equipment to keep a closed state, otherwise, controlling the monitoring equipment to be opened.
Optionally, the environmental parameters include boiler equipment working condition parameters, purification equipment working condition parameters and pollutant concentration;
the step of judging whether the environmental parameter meets the preset reference standard comprises the following steps:
judging whether the working condition parameters of the boiler equipment meet a first preset standard in the preset reference standards, judging whether the working condition parameters of the purifying equipment meet a second preset standard in the preset reference standards, and judging whether the concentration of the pollutants meet a third preset standard in the preset reference standards;
and if the results of the three judgments are all satisfied, determining that the environmental parameter satisfies a preset reference standard, otherwise determining that the environmental parameter does not satisfy the preset reference standard.
Optionally, the contaminants include hydrogen chloride, sulfur dioxide, carbon dioxide, and particulates;
the step of determining whether the concentration of the pollutant meets a third preset standard in the preset reference standard further comprises:
and calculating the concentration of the pollutant according to the concentration of the hydrogen chloride, the concentration of the sulfur dioxide, the concentration of the carbon dioxide and the concentration of the particulate matters.
Optionally, the boiler equipment working condition parameters include boiler body operation parameters and chiller operation parameters;
the step of judging whether the working condition parameters of the boiler equipment meet a first preset standard in the preset reference standards comprises the following steps of:
judging whether the boiler body operation parameters meet the boiler body operation standard in the first preset standard or not, and judging whether the chiller operation parameters meet the chiller operation standard in the first preset standard or not;
and if the two judgment results are both satisfied, determining that the working condition parameters of the boiler equipment satisfy a first preset standard in the preset reference standards, otherwise determining that the working condition parameters of the boiler equipment do not satisfy the first preset standard in the preset reference standards.
Optionally, the operating parameters of the boiler body comprise the incineration temperature in the boiler, the incineration time in the boiler, the air flow in the boiler, the smoke temperature at the outlet of the boiler and the retention time of smoke;
the step of judging whether the boiler body operation parameters meet the boiler body operation standard in the first preset standard comprises the following steps:
judging whether the burning temperature in the boiler is greater than a preset burning temperature, judging whether the burning time in the boiler is greater than a preset burning time, judging whether the air flow in the boiler is greater than a preset air flow, judging whether the smoke temperature at the outlet of the boiler is less than the preset smoke temperature, and judging whether the smoke retention time is greater than the preset retention time;
and if the judgment results of the five times are yes, determining that the boiler body operation parameters meet the boiler body operation standard in the first preset standard, otherwise, determining that the boiler body operation parameters do not meet the boiler body operation standard in the first preset standard.
Optionally, the purification equipment working condition parameters include a dust remover operating parameter and an adsorber operating parameter;
the step of judging whether the working condition parameters of the purifying equipment meet a second preset standard in the preset reference standards comprises the following steps of:
judging whether the dust remover operation parameters meet dust remover operation standards in second preset standards or not, and judging whether the adsorber operation parameters meet adsorber operation standards in the second preset standards or not;
and if the two judgment results are both satisfied, determining that the working condition parameter of the purifying equipment satisfies a second preset standard in the preset reference standards, otherwise determining that the working condition parameter of the purifying equipment does not satisfy the second preset standard in the preset reference standards.
Optionally, the precipitator operating parameters include a precipitator outlet temperature and a precipitator pressure drop;
the step of judging whether the dust remover operation parameters meet the dust remover operation standard in the second preset standard comprises the following steps:
judging whether the temperature of the outlet of the dust remover is less than 150 ℃ or not, and judging whether the pressure drop of the dust remover is more than 1KPa or not;
and if the two judgment results are yes, determining that the dust remover operation parameters meet the dust remover operation standard in the second preset standard, otherwise, determining that the dust remover operation parameters do not meet the dust remover operation standard in the second preset standard.
The invention also provides a control system of the monitoring device, which comprises:
the acquisition unit is used for acquiring environmental parameters during waste incineration in the incinerator;
the judging unit is used for judging whether the environmental parameters meet preset reference standards or not;
and the control unit is used for controlling the monitoring equipment to keep a closed state if the monitoring equipment is in the closed state, and controlling the monitoring equipment to be opened if the monitoring equipment is not in the closed state.
The invention also provides a control device of the monitoring equipment, which comprises the following components: a memory, a processor, and a control program of a monitoring device stored on the memory and executable on the processor, the control program of the monitoring device implementing the steps of the control method of the monitoring device when executed by the processor, the control method of the monitoring device comprising the steps of:
acquiring environmental parameters of the incinerator during waste incineration;
judging whether the environmental parameters meet preset reference standards or not;
if so, controlling the monitoring equipment to keep a closed state, otherwise, controlling the monitoring equipment to be opened.
The present invention also provides a computer-readable storage medium having stored thereon a control program of a monitoring device, the control program of the monitoring device implementing the steps of the control method of the monitoring device when executed by the processor, the control method of the monitoring device including the steps of:
acquiring environmental parameters of the incinerator during waste incineration;
judging whether the environmental parameters meet preset reference standards or not;
if so, controlling the monitoring equipment to keep a closed state, otherwise, controlling the monitoring equipment to be opened.
Because the generation amount of the dioxin during the waste incineration in the incinerator is related to the environmental parameters during the waste incineration in the incinerator, when the environmental parameters during the waste incineration in the incinerator meet the preset reference standard, the generation amount of the dioxin during the waste incineration in the incinerator does not cause the discharge amount of the dioxin to exceed the standard, and at the moment, monitoring equipment does not need to be started; and only when the environmental parameters in the incineration process of the garbage in the incinerator do not meet the preset reference standard, the generation amount of the dioxin in the incineration process of the garbage in the incinerator can cause the problem that the emission amount of the dioxin exceeds the standard, and at the moment, the monitoring equipment needs to be started to monitor the emission amount of the dioxin. Therefore, the technical scheme of the invention can more accurately know the starting time of the monitoring equipment by judging whether the environmental parameters meet the preset reference standard when the garbage is incinerated in the incinerator so as to start the monitoring equipment; and the monitoring equipment can be kept closed in other states, so that the invalid operation of the monitoring equipment is avoided, and the monitoring cost is reduced.
Drawings
In order to more clearly illustrate the embodiments of the present invention or the technical solutions in the prior art, the drawings used in the description of the embodiments or the prior art will be briefly described below, it is obvious that the drawings in the following description are only some embodiments of the present invention, and for those skilled in the art, other drawings can be obtained according to the structures shown in the drawings without creative efforts.
FIG. 1 is a schematic diagram of a hardware structure involved in the operation of a control device of the monitoring apparatus according to the present invention;
FIG. 2 is a schematic flow chart of a control method of the monitoring device according to the present invention;
FIG. 3 is a detailed flowchart of step S20 in FIG. 2;
FIG. 4 is a detailed flowchart of step S21 in FIG. 3;
FIG. 5 is a detailed flowchart of step S211 in FIG. 2;
FIG. 6 is a detailed flowchart of step S22 in FIG. 3;
FIG. 7 is a detailed flowchart of step S221 in FIG. 7;
FIG. 8 is a schematic structural diagram of an embodiment of a control system of a monitoring device according to the present invention;
Figure BDA0002555942330000041
Figure BDA0002555942330000051
the implementation, functional features and advantages of the objects of the present invention will be further explained with reference to the accompanying drawings.
Detailed Description
The technical solutions in the embodiments of the present invention will be clearly and completely described below with reference to the drawings in the embodiments of the present invention, and it is obvious that the described embodiments are only a part of the embodiments of the present invention, and not all of the embodiments. All other embodiments, which can be derived by a person skilled in the art from the embodiments given herein without making any creative effort, shall fall within the protection scope of the present invention.
It should be noted that all the directional indicators (such as up, down, left, right, front, and rear … …) in the embodiment of the present invention are only used to explain the relative position relationship between the components, the movement situation, etc. in a specific posture (as shown in the drawing), and if the specific posture is changed, the directional indicator is changed accordingly.
The main solution of the embodiment of the invention is as follows: acquiring environmental parameters of the incinerator during waste incineration; judging whether the environmental parameters meet preset reference standards or not; if so, controlling the monitoring equipment to keep a closed state, otherwise, controlling the monitoring equipment to be opened.
In the prior art, when the incinerator burns garbage, the monitoring equipment starts sampling at the same time so as to detect whether dioxin generated by the incineration of the garbage by the incinerator exceeds the standard or not. However, the monitoring device and the incinerator are operated synchronously, which undoubtedly causes the ineffective operation of the monitoring device and increases the monitoring cost.
The invention provides the solution, and aims to avoid the invalid operation of the monitoring equipment and reduce the monitoring cost.
The invention provides a control device of monitoring equipment, which is applied to control of the monitoring equipment.
In an embodiment of the present invention, referring to fig. 1, a control device of a monitoring apparatus includes: a processor 1001, such as CYU, a memory 1002 and a control program for a monitoring device stored on said memory 1002 and being executable on said processor 1001, said control program for a monitoring device realizing the steps of the method for controlling a monitoring device described below when executed by said processor 1001. The processor 1001 is connected to the memory 1002. The memory 1002 may be a high-speed RXM memory, or may be a non-volatile memory (non-volatile memory), such as a disk memory. The memory 1002 may alternatively be a storage device separate from the processor 1001. Those skilled in the art will appreciate that the configuration shown in fig. 1 does not constitute a limitation of the device and may include more or fewer components than those shown, or some components may be combined, or a different arrangement of components.
As shown in fig. 1, a memory 1002, which is a readable storage medium, includes a control program of the monitoring apparatus. In the device shown in fig. 1, the processor 1001 may be configured to call a control program of the monitoring device stored in the memory 1002 and perform operations of relevant steps of a control method of the monitoring device in the following embodiments.
As shown in fig. 2, the present invention further provides a method for controlling a monitoring device, including the following steps:
step S10, acquiring environmental parameters of the incinerator when the garbage is incinerated;
step S20, judging whether the environmental parameters meet the preset reference standard;
and step S30, if yes, controlling the monitoring equipment to keep a closed state, otherwise, controlling the monitoring equipment to be opened.
Because the generation amount of the dioxin during the waste incineration in the incinerator is related to the environmental parameters during the waste incineration in the incinerator, when the environmental parameters during the waste incineration in the incinerator meet the preset reference standard, the generation amount of the dioxin during the waste incineration in the incinerator does not cause the discharge amount of the dioxin to exceed the standard, and at the moment, monitoring equipment does not need to be started; and only when the environmental parameters in the incineration process of the garbage in the incinerator do not meet the preset reference standard, the generation amount of the dioxin in the incineration process of the garbage in the incinerator can cause the problem that the emission amount of the dioxin exceeds the standard, and at the moment, the monitoring equipment needs to be started to monitor the emission amount of the dioxin. Therefore, the technical scheme of the invention can more accurately know the starting time of the monitoring equipment by judging whether the environmental parameters meet the preset reference standard when the garbage is incinerated in the incinerator so as to start the monitoring equipment; and the monitoring equipment can be kept closed in other states, so that the invalid operation of the monitoring equipment is avoided, and the monitoring cost is reduced.
It should be noted that, because the content of dioxin generated by burning garbage in the incinerator is related to the environmental parameters of the incinerator, the environmental parameters of the incinerator can reflect the content of dioxin generated by burning garbage in the incinerator, that is, when the environmental parameters of the incinerator during burning garbage meet the preset reference standard, the amount of dioxin generated during burning garbage in the incinerator does not cause the discharge amount of dioxin to exceed the standard, and the monitoring device is controlled to be kept closed; environmental parameters when the waste in the incinerator is incinerated do not meet the preset reference standard, the problem that the discharge amount of the dioxin exceeds the standard is possibly caused by the generation amount of the dioxin during the waste incineration in the incinerator, and the monitoring device is controlled to be started. For example, when the preset reference standard of the incineration temperature in the incinerator is greater than 900 ℃ and the preset reference standard of the incineration time in the incinerator is greater than 4 hours, under the condition that the incineration temperature is greater than 900 ℃ and greater than 4 hours, the garbage in the incinerator is fully combusted, and the content of dioxin generated by the incinerator is very low and can be ignored. When the obtained furnace burning temperature is 1000 ℃ and the furnace burning time is 5 hours, the 1000 ℃ is more than 900 ℃, the 5 hours is less than 4 hours, the obtained furnace burning temperature meets the furnace temperature of a preset reference standard, and the obtained furnace burning time meets the time of the preset reference standard, so that the obtained result is defined as a, and a is a first result; when the obtained furnace burning temperature is 800 ℃ and the furnace burning time is 3 hours, the 800 ℃ is less than 900 ℃, the 3 hours is less than 4 hours, the obtained furnace burning temperature is less than the furnace temperature of the preset reference standard, and the obtained furnace burning time is less than the time of the preset reference standard, therefore, the obtained result a is the second result, of course, the first result can be assigned to 0, the second result can be assigned to 1, and then whether the monitoring equipment is opened or kept closed is controlled according to whether the assignment of a is 0 or 1.
Correspondingly, the environmental parameters further include furnace air flow, boiler outlet smoke temperature, smoke residence time, quencher operating parameters, dust remover outlet temperature, dust remover pressure drop, adsorber operating parameters and conventional pollutant concentration, the result of the furnace air flow is defined as b, the result of the boiler outlet smoke temperature is c, the result of the smoke residence time is d, the result of the quencher operating parameters is defined as e, the results of the dust remover outlet temperature and dust remover pressure drop are defined as g, the result of the adsorber operating parameters is defined as h, and the result of the conventional pollutant concentration is defined as f, so that an expression of the starting parameter (K) of the monitoring equipment can be obtained: k is a + b + c + d + e + g + h + f, the first result of reducing the amount of dioxin emission is assigned to 0, and the second result of causing an increase in the amount of dioxin emission is assigned to 1. That is, when the air flow in the boiler, the smoke temperature at the outlet of the boiler, the residence time of the smoke, the operation parameters of the quencher, the outlet temperature of the dust remover, the pressure drop of the dust remover, the operation parameters of the adsorber and the concentration of the conventional pollutants respectively meet the preset reference standards, a, b, c, d, e, g, h and f all obtain a first result with the value of 0; on the contrary, when the air flow in the boiler, the smoke temperature at the outlet of the boiler, the retention time of the smoke, the operation parameter of the quencher, the outlet temperature of the dust remover, the pressure drop of the dust remover, the operation parameter of the adsorber and the concentration of the conventional pollutants respectively do not meet the preset reference standard, a, b, c, d, e, g, h and f all obtain a second result with the value of 1; therefore, the starting parameters can be calculated according to the first result and the second result, whether the monitoring equipment needs to be controlled to start or not can be judged by judging whether K is greater than or equal to 1, and obviously, when K is greater than or equal to 1 and the value of K is larger, more dioxin is generated, and the monitoring equipment needs to be started to monitor the content of the dioxin; on the contrary, when K is less than 1, all the factors are to reduce the emission amount of dioxin, and the content of the dioxin can be ignored at the moment, so that standard exceeding emission can not be caused, and monitoring equipment is not required to be started to monitor the dioxin. Therefore, the starting of the monitoring equipment is controlled by judging whether the starting parameter of the monitoring equipment is more than or equal to 1.
As shown in fig. 3, based on the first embodiment, the present invention further provides a second embodiment of a control method for a monitoring device. In a second embodiment, the environmental parameters include boiler plant operating condition parameters, purification plant operating condition parameters, and contaminant concentrations; the step of judging whether the environmental parameter meets the preset reference standard comprises the following steps:
step S21, judging whether the working condition parameters of the boiler equipment meet a first preset standard in the preset reference standards; step S22, judging whether the working condition parameters of the purifying equipment meet a second preset standard in the preset reference standards; step S23, judging whether the concentration of the pollutant meets a third preset standard in the preset reference standard; and if the results of the three judgments are all satisfied, determining that the environmental parameter satisfies a preset reference standard, otherwise determining that the environmental parameter does not satisfy the preset reference standard.
It should be noted that, a start parameter K of the monitoring device is M + N + f, where K represents a start parameter of the monitoring device, M represents a result of a working condition parameter of the boiler device, N represents a result of a working condition parameter of the purifying device, and f represents a result of a concentration of a conventional pollutant, and when the working condition parameter of the boiler device meets a first preset standard in the preset reference standard, the value of M is 0, otherwise, the value of M is greater than or equal to 1; when the working condition parameters of the purifying equipment meet a second preset standard in the preset reference standards, the value of N is 0, otherwise, the value of N is more than or equal to 1; when the concentration of the conventional pollutants meets a third preset standard in the preset reference standard, the value of f is 0, otherwise, the value of f is more than or equal to 1; thus, when the three are satisfied, a first result with a value of 0 is obtained; otherwise, a second result with the value being more than or equal to 1 is obtained, and therefore effective control over the monitoring equipment can be achieved according to whether the obtained result is the first result or the second result.
Further, based on the second embodiment, the present invention provides a fourth embodiment of a method for controlling a monitoring device. In a fourth embodiment, the contaminants include hydrogen chloride, sulfur dioxide, carbon dioxide, and particulates; the step of determining whether the concentration of the pollutant meets a third preset standard in the preset reference standard further comprises:
and calculating the concentration of the pollutant according to the concentration of the hydrogen chloride, the concentration of the sulfur dioxide, the concentration of the carbon dioxide and the concentration of the particulate matters.
It should be noted that the presence of sulfur dioxide in flue gas generated by incineration of refuse can suppress the generation of dioxin, which accompanies SO2The concentration increases and the content of dioxin decreases. However, the presence of hydrogen chloride, carbon dioxide and particulates leads to the generation of dioxin, and the content of dioxin increases as the content thereof increases. Thus, embodiments of the present invention provide a method for calculating the concentration of a contaminant by establishing: x is 0.5 × Δ dust +0.4 × Δ HCl +0.3 × Δ CO2-0.2×ΔSO2) Wherein Δ dust represents the increase in particulate matter, Δ HCl represents the increase in hydrogen chloride, and Δ CO2Denotes the carbon dioxide increase,. DELTA.SO2The sulfur dioxide increase is expressed, and the above increases are calculated in the following manner, respectively.
Figure BDA0002555942330000091
Figure BDA0002555942330000092
Figure BDA0002555942330000093
Figure BDA0002555942330000094
When the content of dioxin in flue gas generated by waste incineration is very low, the value of x is less than 0, and the obtained result f is 0; when the content of dioxin in flue gas generated by waste incineration is high, the value of x is more than 0, and the obtained result f is 1. And then, the result f is substituted into a calculation formula of the starting parameter of the monitoring device, so that the monitoring device is controlled to be started or kept to be closed.
As shown in fig. 4, further, based on the second embodiment, the present invention provides a fifth embodiment of a control method of a monitoring apparatus. In a fifth embodiment, the boiler equipment working condition parameters comprise boiler body operation parameters and chiller operation parameters;
the step of judging whether the working condition parameters of the boiler equipment meet a first preset standard in the preset reference standards comprises the following steps of:
step S211, determining whether the boiler body operation parameters meet the boiler body operation standards in the first preset standard, step S213, and determining whether the chiller operation parameters meet the chiller operation standards in the first preset standard;
and if the two judgment results are both satisfied, determining that the working condition parameters of the boiler equipment satisfy a first preset standard in the preset reference standards, otherwise determining that the working condition parameters of the boiler equipment do not satisfy the first preset standard in the preset reference standards.
In addition, M is Y + e, Y represents the result of the boiler body operation parameters, and e represents the result of the chiller operation parameters. The operation parameters of the quencher comprise the operation power of the quencher and the flow parameters of the quencher, whether the quencher works normally or not is determined through the operation power of the quencher and the flow parameters of the quencher, when the quencher works normally, the operation power of the quencher is in the preset power range of the quencher, the flow parameters of the quencher are in the preset flow range of the quencher, the quencher reduces the smoke temperature rapidly, the regeneration of dioxin substances is reduced, the dioxin content in boiler equipment is very low, and the value of e is 0; when the quencher cannot work normally, the operation power of the quencher is not in the preset power range of the quencher, the flow parameter of the quencher is not in the preset flow range of the quencher, and the dioxin is quickly synthesized in the cooling section, so that the content of the dioxin in the boiler equipment is increased, and the value of e is 1; when the boiler body operation parameters meet a first range in the first preset standard, the value of Y is 0, otherwise, the value of Y is more than or equal to 1; thus, when both of the above are satisfied, a first result with a value of 0 is obtained; otherwise, a second result with the value being more than or equal to 1 is obtained, and thus, effective control over the monitoring equipment can be realized by determining the starting parameters according to the obtained result.
As shown in fig. 5, further, based on the fifth embodiment, the present invention proposes a sixth embodiment of a control method of a monitoring apparatus. In a sixth embodiment, the boiler body operation parameters comprise furnace incineration temperature, furnace incineration time, furnace air flow, boiler outlet smoke temperature and smoke retention time;
the step of judging whether the boiler body operation parameters meet the boiler body operation standard in the first preset standard comprises the following steps:
step S2111, judging whether the incineration temperature in the furnace is greater than a preset incineration temperature; step S2112, judging whether the incineration time in the furnace is longer than the preset incineration time; step S2113, judging whether the air flow in the furnace is greater than a preset air flow; step S2114, judging whether the temperature of the boiler outlet smoke is lower than a preset outlet smoke temperature; step S2115, judging whether the smoke retention time is longer than a preset retention time;
and if the judgment results of the five times are yes, determining that the boiler body operation parameters meet the boiler body operation standard in the first preset standard, otherwise, determining that the boiler body operation parameters do not meet the boiler body operation standard in the first preset standard. Y is a + b + c + d, a represents the results of the furnace firing temperature and the furnace firing time, b represents the results of the furnace air flow rate, c represents the results of the boiler outlet flue gas temperature, and d represents the results of the flue gas residence time. In the embodiment of the invention, the preset incineration temperature is 900 ℃, the preset incineration time is 4 hours, the preset air flow is determined according to the size of the actual boiler body and the specific combustion state, the invention is not limited by the preset incineration temperature, the preset outlet smoke temperature is 200 ℃, and the preset retention time is 2 s. When the incineration temperature in the boiler is more than 900 ℃ and the incineration time in the boiler is more than 4 hours, the garbage is fully incinerated in the boiler body, the content of dioxin generated in the boiler body is very low, the discharge amount of the dioxin can be ignored, and the value of a is 0; when the burning temperature in the furnace is not more than 900 ℃ or the burning time in the furnace is not more than 4 hours, the garbage is not fully burned in the boiler body, the content of dioxin generated in the boiler body is very high, and the value of a is 1; when the air flow in the boiler is larger than the preset air flow, the garbage is fully incinerated in the boiler body, an oxygen-enriched combustion state is formed, the generation of dioxin is effectively inhibited, the content of the dioxin generated in the boiler body is very low, and the value of b is 0; when the air flow in the boiler is not more than the preset air flow, the garbage and the air cannot be fully mixed and form an oxygen-enriched combustion state, the content of dioxin generated in the boiler body is very high, and the value of b is 1; when the temperature of the smoke at the outlet of the boiler is less than 200 ℃, on one hand, the generation of dioxin in the boiler body is reduced, on the other hand, the heat efficiency of the boiler body is improved, the content of the dioxin generated in the boiler body is very low, and the value of c is 0; when the temperature of the smoke at the outlet of the boiler is more than 200 ℃, the dioxin is generated by the reaction again in the temperature range of 200 ℃ and 400 ℃, the content of the dioxin generated in the boiler body is very high, and the value of c is 1; when the residence time of the flue gas is more than 2s, the residence time of the dioxin in the boiler body is very long, so that most of the dioxin generated in the boiler body is decomposed, the content of the dioxin generated in the boiler body is very low, and the value of d is 0; when the residence time of the flue gas is not more than 2s, the residence time of the dioxin in the boiler body is very short, and the dioxin generated in the boiler body cannot be effectively decomposed, so that the content of the dioxin generated in the boiler body is very high, and the value of d is 1; thus, when the burning temperature in the furnace is more than 900 ℃, the burning time in the furnace is more than 4 hours, the air flow in the furnace is more than the preset air flow, the smoke temperature at the outlet of the boiler is less than 200 ℃, and the retention time of the smoke is more than 2 seconds, the Y value is 0; when the burning temperature in the furnace is not more than 900 ℃, and/or the burning time in the furnace is not more than 4 hours, and/or the air flow in the furnace is not more than the preset air flow, and/or the smoke temperature at the outlet of the boiler is not less than 200 ℃, and/or the smoke retention time is not more than 2 seconds, Y is not less than 1, the starting parameter K is not less than 1, the monitoring equipment is controlled to be started, and the monitoring equipment monitors the discharge amount of dioxin.
Referring to fig. 6, the present invention further proposes a seventh embodiment of a control method of a monitoring apparatus based on the second embodiment. In the seventh embodiment, the first and second embodiments,
the working condition parameters of the purification equipment comprise dust remover operating parameters and adsorber operating parameters;
the step of judging whether the working condition parameters of the purifying equipment meet a second preset standard in the preset reference standards comprises the following steps of:
step S221, judging whether the dust remover operation parameters meet the dust remover operation standards in a second preset standard, and step S223, judging whether the adsorber operation parameters meet the adsorber operation standards in the second preset standard;
and if the two judgment results are both satisfied, determining that the working condition parameter of the purifying equipment satisfies a second preset standard in the preset reference standards, otherwise determining that the working condition parameter of the purifying equipment does not satisfy the second preset standard in the preset reference standards.
It should be noted that N ═ g + h, g denotes the result of the outlet temperature of the dust remover and the pressure drop of the dust remover, h denotes the result of the operation parameter of the adsorber, most of the dioxin generated in the boiler equipment is adsorbed on the surface of the dust, when the operation parameter of the dust remover meets the operation standard of the dust remover, the dust with dioxin adsorbed on the surface is adsorbed by the dust remover, so that the discharge amount of the dioxin in the incinerator is reduced, and the value of g is 0; when the operation parameters of the dust remover do not meet the operation standard of the dust remover, the discharge amount of dioxin in the incinerator is increased, and the value of g is 1; the method comprises the following steps that the adsorber is set as a jet pump capable of spraying activated carbon, the activated carbon has a large specific surface area and has strong adsorption capacity on dioxin, and the jet pump sprays the activated carbon so that the dioxin is fully adsorbed, so that the operation parameters of the adsorber are jet pump operation parameters which comprise jet pump jet flow and jet pump operation power, the operation state of the jet pump is monitored by detecting the jet pump jet flow and the jet pump operation power, when the jet pump is in the operation state, the jet pump jet flow reaches the jet pump preset flow range, the jet pump operation power is in the jet pump preset power range, the dioxin in boiler equipment is fully absorbed, the content of the dioxin in the incinerator is reduced, and the value of h is 0; when the jet pump is not in a working state, the jet flow of the jet pump does not reach the preset flow range of the jet pump, the running power of the jet pump does not reach the preset power range of the jet pump, the dioxin cannot be effectively adsorbed, the content of the dioxin in boiler equipment is very high, and the value of h is 1; thus, when the dust remover operation parameter and the adsorber operation parameter both meet the second preset standard, the value of N is 0, otherwise, the value of N is more than or equal to 1. And when the value of N is more than or equal to 1, K is more than or equal to 1, and at the moment, starting parameters to control the monitoring equipment to be started.
As shown in fig. 7, the present invention further provides an eighth embodiment of a control method for a monitoring device according to the seventh embodiment. In an eighth embodiment, the precipitator operating parameters include a precipitator outlet temperature and a precipitator pressure drop;
the step of judging whether the dust remover operation parameters meet the dust remover operation standard in the second preset standard comprises the following steps: and S2211, judging whether the outlet temperature of the dust remover is less than 150 ℃, S2213, judging whether the pressure drop of the dust remover is greater than 1KPa, if the two judgment results are yes, determining that the operation parameters of the dust remover meet the operation standards of the dust remover in a second preset standard, otherwise, determining that the operation parameters of the dust remover do not meet the operation standards of the dust remover in the second preset standard.
It should be noted that when the outlet temperature of the dust remover is less than 150 ℃ and the pressure drop of the dust remover is greater than 1KPa, the value of g is 0; when the outlet temperature of the dust remover is not less than 150 ℃, and the pressure drop of the dust remover is not more than 1KPa, the dust remover cannot realize the full separation of dioxin and dust, the dioxin is adsorbed on the dust, the value of g is 1, at the moment, K is not less than 1, and the monitoring equipment is started up under the control of starting parameters.
As shown in fig. 8, an embodiment of the present invention further provides a control system of a monitoring device, including: an obtaining unit 100, configured to obtain an environmental parameter when the refuse in the incinerator is incinerated; a judging unit 200, configured to judge whether the environmental parameter meets a preset reference standard; and the control unit 300 is used for controlling the monitoring equipment to keep a closed state if the monitoring equipment is in the closed state, and controlling the monitoring equipment to be opened if the monitoring equipment is not in the closed state.
Because the generation amount of the dioxin during the waste incineration in the incinerator is related to the environmental parameters during the waste incineration in the incinerator, when the environmental parameters during the waste incineration in the incinerator meet the preset reference standard, the generation amount of the dioxin during the waste incineration in the incinerator does not cause the discharge amount of the dioxin to exceed the standard, and at the moment, monitoring equipment does not need to be started; and only when the environmental parameters in the incineration process of the garbage in the incinerator do not meet the preset reference standard, the problem that the discharge amount of the dioxin exceeds the standard can be caused only by the generation amount of the dioxin in the incineration process of the garbage in the incinerator, and at the moment, the monitoring equipment needs to be started to monitor the discharge amount of the dioxin in real time. Therefore, the technical scheme of the invention can more accurately know the starting time of the monitoring equipment by judging whether the environmental parameters meet the preset reference standard when the garbage is incinerated in the incinerator so as to start the monitoring equipment; and the monitoring equipment can be kept closed in other states, so that the invalid operation of the monitoring equipment is avoided, and the monitoring cost is reduced.
In addition, an embodiment of the present invention further provides a computer-readable storage medium, where a control program of a monitoring device is stored on the computer-readable storage medium, and when the control program of the monitoring device is executed, the relevant steps of any embodiment of the above control method of the monitoring device are implemented.
It should be noted that, in this document, the terms "comprises," "comprising," or any other variation thereof, are intended to cover a non-exclusive inclusion, such that a process, method, article, or system that comprises a list of elements does not include only those elements but may include other elements not expressly listed or inherent to such process, method, article, or system. Without further limitation, an element defined by the phrase "comprising an … …" does not exclude the presence of other like elements in a process, method, article, or system that comprises the element.
The above-mentioned serial numbers of the embodiments of the present invention are merely for description and do not represent the merits of the embodiments.
Through the above description of the embodiments, those skilled in the art will clearly understand that the method of the above embodiments can be implemented by software plus a necessary general hardware platform, and certainly can also be implemented by hardware, but in many cases, the former is a better implementation manner. Based on such understanding, the technical solution of the present invention essentially or contributing to the prior art can be embodied in the form of a software product, which is stored in a storage medium (e.g. ROM/RXM, magnetic disk, optical disk) as described above and includes several instructions for enabling a terminal device (e.g. a mobile phone, a computer, a server, or a network device) to execute the method according to the embodiments of the present invention.
The above description is only a preferred embodiment of the present invention, and not intended to limit the scope of the present invention, and all modifications and equivalents of the present invention, which are made by the contents of the present specification and the accompanying drawings, or directly/indirectly applied to other related technical fields, are included in the scope of the present invention.

Claims (10)

1. A control method of a monitoring apparatus, characterized by comprising the steps of:
acquiring environmental parameters during waste incineration in an incinerator, wherein the environmental parameters comprise boiler equipment working condition parameters, purification equipment working condition parameters and pollutant concentration;
judging whether the environmental parameters meet preset reference standards or not;
if so, controlling the monitoring equipment to keep a closing state, wherein the discharge amount of the dioxin does not exceed the standard; otherwise, the discharge amount of the dioxin exceeds the standard, and the monitoring equipment is controlled to be started.
2. The control method of a monitoring device according to claim 1, wherein the step of "determining whether the environmental parameter satisfies a preset reference criterion" includes:
judging whether the working condition parameters of the boiler equipment meet a first preset standard in the preset reference standards, judging whether the working condition parameters of the purifying equipment meet a second preset standard in the preset reference standards, and judging whether the concentration of the pollutants meet a third preset standard in the preset reference standards;
and if the results of the three judgments are all satisfied, determining that the environmental parameter satisfies a preset reference standard, otherwise determining that the environmental parameter does not satisfy the preset reference standard.
3. The control method of the monitoring device according to claim 2, wherein the contaminants include hydrogen chloride, sulfur dioxide, carbon dioxide, and particulate matter;
the step of determining whether the concentration of the pollutant meets a third preset standard in the preset reference standard further comprises:
and calculating the concentration of the pollutant according to the concentration of the hydrogen chloride, the concentration of the sulfur dioxide, the concentration of the carbon dioxide and the concentration of the particulate matters.
4. The control method of the monitoring equipment according to claim 2, wherein the boiler equipment operating parameters comprise boiler body operating parameters and chiller operating parameters;
the step of judging whether the working condition parameters of the boiler equipment meet a first preset standard in the preset reference standards comprises the following steps of:
judging whether the boiler body operation parameters meet the boiler body operation standard in the first preset standard or not, and judging whether the chiller operation parameters meet the chiller operation standard in the first preset standard or not;
and if the two judgment results are both satisfied, determining that the working condition parameters of the boiler equipment satisfy a first preset standard in the preset reference standards, otherwise determining that the working condition parameters of the boiler equipment do not satisfy the first preset standard in the preset reference standards.
5. The control method of the monitoring device according to claim 4, wherein the boiler body operation parameters include furnace incineration temperature, furnace incineration time, furnace air flow, boiler outlet smoke temperature and smoke residence time;
the step of judging whether the boiler body operation parameters meet the boiler body operation standard in the first preset standard comprises the following steps:
judging whether the burning temperature in the boiler is greater than a preset burning temperature, judging whether the burning time in the boiler is greater than a preset burning time, judging whether the air flow in the boiler is greater than a preset air flow, judging whether the smoke temperature at the outlet of the boiler is less than the preset smoke temperature, and judging whether the smoke retention time is greater than the preset retention time;
and if the judgment results of the five times are yes, determining that the boiler body operation parameters meet the boiler body operation standard in the first preset standard, otherwise, determining that the boiler body operation parameters do not meet the boiler body operation standard in the first preset standard.
6. The control method of the monitoring device according to claim 2, wherein the purge device operating parameters include a dust collector operating parameter and an adsorber operating parameter;
the step of judging whether the working condition parameters of the purifying equipment meet a second preset standard in the preset reference standards comprises the following steps of:
judging whether the dust remover operation parameters meet dust remover operation standards in second preset standards or not, and judging whether the adsorber operation parameters meet adsorber operation standards in the second preset standards or not;
and if the two judgment results are both satisfied, determining that the working condition parameter of the purifying equipment satisfies a second preset standard in the preset reference standards, otherwise determining that the working condition parameter of the purifying equipment does not satisfy the second preset standard in the preset reference standards.
7. The control method of the monitoring device of claim 6, wherein the precipitator operating parameters include a precipitator outlet temperature and a precipitator pressure drop;
the step of judging whether the dust remover operation parameters meet the dust remover operation standard in the second preset standard comprises the following steps:
judging whether the temperature of the outlet of the dust remover is less than 150 ℃ or not, and judging whether the pressure drop of the dust remover is more than 1KPa or not;
and if the two judgment results are yes, determining that the dust remover operation parameters meet the dust remover operation standard in the second preset standard, otherwise, determining that the dust remover operation parameters do not meet the dust remover operation standard in the second preset standard.
8. A control system for a monitoring device, comprising:
the system comprises an acquisition unit, a control unit and a control unit, wherein the acquisition unit is used for acquiring environmental parameters during waste incineration in an incinerator, and the environmental parameters comprise boiler equipment working condition parameters, purification equipment working condition parameters and pollutant concentration;
the judging unit is used for judging whether the environmental parameters meet preset reference standards or not;
the control unit is used for controlling the monitoring equipment to keep a closing state if the discharge amount of the dioxin does not exceed the standard; otherwise, the discharge amount of the dioxin exceeds the standard, and the monitoring equipment is controlled to start sampling.
9. A control device of a monitoring apparatus, characterized by comprising: memory, a processor and a control program of a monitoring device stored on the memory and executable on the processor, the control program of the monitoring device implementing the steps of the method of controlling a monitoring device according to any one of claims 1 to 7 when executed by the processor.
10. A computer-readable storage medium, characterized in that the computer-readable storage medium has stored thereon a control program of a monitoring apparatus, which when executed implements the steps of a control method of a monitoring apparatus according to any one of claims 1 to 7.
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Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN205174393U (en) * 2015-11-24 2016-04-20 浙江春晖环保能源有限公司 Garbage incineration boiler
CN108050528A (en) * 2017-11-21 2018-05-18 北京石油化工学院 A kind of waste incinerator control method, device and system
CN110081440A (en) * 2019-05-05 2019-08-02 绿色动力环保集团股份有限公司 The on-line prediction method of dioxin and early warning and control system in consumer waste incineration

Family Cites Families (12)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
JP3802899B2 (en) * 2003-12-26 2006-07-26 九州電力株式会社 Fluidized bed boiler monitoring device, fluidized bed boiler monitoring method, fluidized bed boiler monitoring program, and fluidized bed boiler monitoring recording medium
CN102155935B (en) * 2011-03-08 2012-09-05 四川电力科学研究院 Detection method of icing reversing angle detection device for transmission line divided leads
US9856568B2 (en) * 2014-02-20 2018-01-02 Ecosphere Technologies, Inc. System to verify rod anode integrity
CN104404257B (en) * 2014-12-15 2017-06-16 湖南省加嘉锑业科技有限公司 One heavy metal species process control method and system
CN206965507U (en) * 2017-07-27 2018-02-06 曲靖云能投新能源发电有限公司 A kind of research on flue gas treatment system of waste incineration of stage purification
CN108662602B (en) * 2018-03-13 2019-12-27 中国神华能源股份有限公司 Method and system for controlling the temperature of the exhaust smoke of a boiler
US10677834B2 (en) * 2018-09-14 2020-06-09 Schweitzer Engineering Laboratories, Inc. Distance protection of electric power delivery systems using time domain and frequency domain
CN110701620A (en) * 2019-06-30 2020-01-17 上海康恒环境股份有限公司 Garbage incinerator water spray cooling system and automatic control method thereof
CN110376108A (en) * 2019-07-29 2019-10-25 滁州智慧城市环保科技有限责任公司 A kind of smoke stack emission solid-state dioxin rapid detection method
CN111023143A (en) * 2019-12-17 2020-04-17 大唐郓城发电有限公司 Combustion control method
CN111174575A (en) * 2020-02-27 2020-05-19 北京保利洁科技发展有限公司 Device for treating electronic waste and using method thereof
CN112183709B (en) * 2020-09-22 2023-11-10 生态环境部华南环境科学研究所 Method for predicting and early warning excessive dioxin in waste incineration gas

Patent Citations (3)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN205174393U (en) * 2015-11-24 2016-04-20 浙江春晖环保能源有限公司 Garbage incineration boiler
CN108050528A (en) * 2017-11-21 2018-05-18 北京石油化工学院 A kind of waste incinerator control method, device and system
CN110081440A (en) * 2019-05-05 2019-08-02 绿色动力环保集团股份有限公司 The on-line prediction method of dioxin and early warning and control system in consumer waste incineration

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