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CN119059608A - A self-adaptive sterilization intensity control method, device and electronic equipment - Google Patents

A self-adaptive sterilization intensity control method, device and electronic equipment Download PDF

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Publication number
CN119059608A
CN119059608A CN202411284420.7A CN202411284420A CN119059608A CN 119059608 A CN119059608 A CN 119059608A CN 202411284420 A CN202411284420 A CN 202411284420A CN 119059608 A CN119059608 A CN 119059608A
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sterilization
concentration
water
target
sterilization intensity
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王靖杰
曹阳
林伟君
王思盼
刘培钦
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Institute Of Agricultural Economy And Information Guangdong Academy Of Agricultural Sciences
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Institute Of Agricultural Economy And Information Guangdong Academy Of Agricultural Sciences
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    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F1/00Treatment of water, waste water, or sewage
    • C02F1/30Treatment of water, waste water, or sewage by irradiation
    • C02F1/32Treatment of water, waste water, or sewage by irradiation with ultraviolet light
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2201/00Apparatus for treatment of water, waste water or sewage
    • C02F2201/32Details relating to UV-irradiation devices
    • C02F2201/326Lamp control systems
    • CCHEMISTRY; METALLURGY
    • C02TREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02FTREATMENT OF WATER, WASTE WATER, SEWAGE, OR SLUDGE
    • C02F2209/00Controlling or monitoring parameters in water treatment
    • C02F2209/005Processes using a programmable logic controller [PLC]
    • C02F2209/006Processes using a programmable logic controller [PLC] comprising a software program or a logic diagram
    • YGENERAL TAGGING OF NEW TECHNOLOGICAL DEVELOPMENTS; GENERAL TAGGING OF CROSS-SECTIONAL TECHNOLOGIES SPANNING OVER SEVERAL SECTIONS OF THE IPC; TECHNICAL SUBJECTS COVERED BY FORMER USPC CROSS-REFERENCE ART COLLECTIONS [XRACs] AND DIGESTS
    • Y02TECHNOLOGIES OR APPLICATIONS FOR MITIGATION OR ADAPTATION AGAINST CLIMATE CHANGE
    • Y02ATECHNOLOGIES FOR ADAPTATION TO CLIMATE CHANGE
    • Y02A40/00Adaptation technologies in agriculture, forestry, livestock or agroalimentary production
    • Y02A40/80Adaptation technologies in agriculture, forestry, livestock or agroalimentary production in fisheries management
    • Y02A40/81Aquaculture, e.g. of fish

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  • Health & Medical Sciences (AREA)
  • Toxicology (AREA)
  • Life Sciences & Earth Sciences (AREA)
  • Hydrology & Water Resources (AREA)
  • Engineering & Computer Science (AREA)
  • Environmental & Geological Engineering (AREA)
  • Water Supply & Treatment (AREA)
  • Chemical & Material Sciences (AREA)
  • Organic Chemistry (AREA)
  • Physical Water Treatments (AREA)

Abstract

The invention relates to the technical field of aquaculture and informatization, and provides a self-adaptive sterilization intensity regulation and control method, a device and electronic equipment, wherein the method comprises the steps of obtaining water quality index parameters of an aquaculture water environment in a preset time period and an actual concentration value of target pathogenic microorganisms at the current moment; determining the maximum bearing concentration value of the pathogenic microorganisms based on an immune balance equation of the target pathogenic microorganisms on the target aquatic products under the water quality condition within a preset time period, determining the concentration killing amount according to a preset safe concentration threshold value, the maximum bearing concentration value and the actual concentration value of the target pathogenic microorganisms, and dynamically regulating and controlling the sterilization process parameters based on the concentration killing amount in a grading manner to sterilize the aquaculture water environment. The self-adaptive sterilization intensity regulating and controlling method and the regulating process provided by the invention consider the dynamic balance of the infection process between the target pathogen and the cultivated species along with the change of water quality, improve the self-adaptability, pertinence and procedural performance of sterilization regulation and control, save energy consumption, and are green, efficient, scientific and reasonable.

Description

Self-adaptive sterilization intensity regulation and control method and device and electronic equipment
Technical Field
The invention relates to the technical field of aquaculture and informatization, in particular to a self-adaptive sterilization intensity regulation and control method and device and electronic equipment.
Background
The aquatic water environment directly carries the life and growth of the aquatic products, whether the aquatic products are good or not directly influences the health degree and the production efficiency of the aquatic products, and in order to keep the health state of the aquatic products, a sterilization technology is often needed to control the concentration of active pathogenic microorganisms in the water environment. The existing method is to recycle the aquaculture water after complete sterilization so as to reduce the risk of disease occurrence. However, the method has the defects that firstly, the method is not suitable for open water cultivation scenes with background active pathogenic microorganism concentration such as large water surfaces, ocean pastures and the like. Secondly, the existing method ignores the establishment and the effect of the autoimmune barrier of the cultured aquatic products. Finally, the existing method ignores dynamic balance among beneficial microorganism colonies in water environment, especially nitrifying bacteria, and the full-power sterilization operation can cause unbalance of beneficial bacterial groups of the water body, and the recovery time after unbalance is longer, so that the health of internal environments such as intestinal tracts of cultured aquatic products is influenced.
In the running of cultivation facilities such as factory cultivation, fish and vegetable symbiotic systems and the like, equipment such as a circulating water pump, a sterilizing and filtering device and the like are main sources of energy consumption in the cultivation process. If the system runs at full load or constant power throughout the day, the energy consumption is quite high, so that the economic benefit of farmers is greatly reduced. At present, physical sterilization and bacteria reduction technologies such as ultraviolet rays, filtration, electrostatic adsorption, heating sterilization, ionizing radiation and the like are often combined and applied to microbial sterilization and disease prevention and control of a aquaculture water environment, and energy conservation, consumption reduction and environmental protection are mainly focused on the realization of energy conservation, consumption reduction and the like in a mode of improving the efficiency of functional devices. For example, CN114600821B discloses an energy-saving method using multiple treatment modes in time-sharing mode, which uses the huge difference of water before and after feeding, day and night and before and after water treatment to perform time-sharing treatment in different modes, and also operates under full load in sterilization link. In addition, according to the ultraviolet dose-inactivation rate curve, the irradiation dose required for total inactivation is maximum, the energy consumption is maximum, and the sterilization device and the water circulation power in the sterilization link generally keep running continuously after fixed starting, and the adjustment of the sterilization intensity change is not considered. The analysis shows that the method still has unique advantages and innovative development space in the aspects of sterilization intensity, control time sequence and the like.
In view of the above problems, the existing method for killing pathogenic microorganisms in the aquaculture water environment cannot adapt to the development target of green cleaning, and a more scientific and reasonable sterilization intensity regulation method with strong pertinence is needed.
Disclosure of Invention
The invention provides a self-adaptive sterilization intensity regulating method, a self-adaptive sterilization intensity regulating device and electronic equipment, which are used for solving the problem that pathogenic microorganisms in a culture water body lack a scientific and reasonable sterilization intensity regulating method with strong pertinence in the prior art.
In a first aspect, the present invention provides a method for adjusting and controlling self-adaptive sterilization intensity, comprising:
Step 110, acquiring a plurality of water quality index parameters of the aquaculture water environment in a preset time period and an actual concentration value of target pathogenic microorganisms at the current moment;
Step 120, determining a maximum bearing concentration value of the target pathogenic microorganism based on an immune balance equation of the target pathogenic microorganism to the target aquatic product in the environment of the plurality of water quality index parameters within the preset time period;
130, determining the concentration killing amount of the target pathogenic microorganism based on a preset safe concentration threshold value, the maximum bearing concentration value and the actual concentration value of the target pathogenic microorganism;
Step 140, dynamically regulating and controlling sterilization process parameters in a grading manner based on the concentration killing amount to sterilize the aquaculture water environment;
Step 150, repeating the steps 110-140 to complete the self-adaptive sterilization process.
According to the self-adaptive sterilization intensity regulation method provided by the invention, the immune balance equation of the target pathogenic microorganism on the target aquatic product in the environment of the plurality of water quality index parameters within the preset time period is determined by the following modes:
determining the infection activity of target pathogenic microorganisms in the preset time period based on the plurality of water quality index parameters;
determining the anti-infection capability of the target aquatic product in the preset time period based on the plurality of water quality index parameters;
and determining an immune balance equation of the target pathogenic microorganism on the target aquatic product in the environment of the plurality of water quality index parameters within the preset time period based on the infection activity and the anti-infection capability.
According to the self-adaptive sterilization intensity regulation method provided by the invention, the concentration killing amount of the target pathogenic microorganism is determined based on the preset safe concentration threshold value, the maximum bearing concentration value and the actual concentration value of the target pathogenic microorganism, and the method comprises the following steps:
determining the moment when the result of the immune balance equation is zero as the moment when the target pathogenic microorganism has immune balance on the target aquatic product;
Determining a maximum sustained concentration value of the target pathogenic microorganism based on an immune balance equation at the time of immune balance;
Performing difference calculation on the maximum bearing concentration value and a preset safe concentration threshold value to obtain an actual concentration control target value of the target pathogenic microorganism;
and carrying out difference calculation on the actual concentration value and the actual concentration control target value to obtain the actual concentration killing amount of the target pathogenic microorganism.
According to the self-adaptive sterilization intensity regulation method provided by the invention, in the step S140, sterilization process parameters are regulated and controlled dynamically in a grading manner based on the concentration sterilization amount, and the cultivation water environment is sterilized, and the method comprises the following steps:
if the concentration killing amount is greater than zero, determining a sterilization intensity level based on the concentration killing amount and the preset safety concentration threshold;
Determining sterilization power and inflow water flow at different sterilization intensity levels based on a function between the inactivation rate and the ultraviolet dose;
And dynamically sterilizing the aquaculture water environment based on the sterilization power and the water inlet speed under the different sterilization intensity levels.
According to the method for adjusting and controlling self-adaptive sterilization intensity provided by the invention, in step S1401, the determining sterilization intensity level based on the concentration killing amount and the preset safety concentration threshold value includes:
If the concentration killing amount is larger than the preset safety concentration threshold value of the first preset times, determining that the sterilization intensity level is a primary sterilization intensity level;
If the concentration killing amount is smaller than the preset safety concentration threshold value of the first preset time and larger than the preset safety concentration threshold value of the second preset time, determining that the sterilization intensity level is a secondary sterilization intensity level;
and if the concentration killing amount is smaller than the preset safety concentration threshold value of the second preset times, determining that the sterilization intensity level is a three-level sterilization intensity level.
According to the self-adaptive sterilization intensity regulation method provided by the invention, in step S1402, sterilization power and water inflow under different sterilization intensity levels are determined based on the function of the inactivation rate and the ultraviolet dose, and the self-adaptive sterilization intensity regulation method comprises the following steps:
If the sterilization intensity level is the primary sterilization intensity level, sequentially determining a first sterilization power and a first water inflow according to the function of the inactivation rate y and the ultraviolet dose x, and respectively using a power value corresponding to correspondingly increased sterilization irradiation and a water inflow speed value of a water pump which is correspondingly increased as the first sterilization power and the first water inflow;
if the sterilization intensity level is the secondary sterilization intensity level, sequentially determining a second sterilization power and a second water inflow rate according to the function of the inactivation rate y and the ultraviolet dose x, wherein a power value corresponding to a normal sterilization irradiation value and a normal water inflow rate value of a water pump are respectively used as the second sterilization power and the second water inflow rate;
if the sterilization intensity level is the primary sterilization intensity level, sequentially determining a third sterilization power and a third water inflow according to the function of the inactivation rate y and the ultraviolet dose x, wherein the power value corresponding to the correspondingly reduced sterilization irradiation and the accelerated water inflow speed value of the water pump are respectively used as the third sterilization power and the third water inflow;
the inactivation rate and uv dose functions are pre-constructed based on uv dose-inactivation rate curves.
According to the self-adaptive sterilization intensity regulation method provided by the invention, in step S1403, when the aquaculture water environment is dynamically sterilized based on sterilization power and water inlet speed under different sterilization intensity levels, the following steps are executed aiming at the sterilization power and the water inlet speed:
If the sterilization intensity level is the primary sterilization intensity level, sterilizing the aquaculture water environment according to a first sterilization power and a first water inflow rate, wherein the first sterilization power is the sterilization power under the primary sterilization intensity level, and the first water inflow rate is the water inflow rate under the primary sterilization intensity level;
If the sterilization intensity level is the secondary sterilization intensity level, sterilizing the aquaculture water environment according to a second sterilization power and a second water inflow rate, wherein the second sterilization power is sterilization power under the secondary sterilization intensity level, and the second water inflow rate is water inflow rate under the secondary sterilization intensity level;
and if the sterilization intensity level is the three-level sterilization intensity level, sterilizing the aquaculture water environment according to a third sterilization power and a third water inflow rate, wherein the third sterilization power is the sterilization power under the three-level sterilization intensity level, and the third water inflow rate is the water inflow rate under the three-level sterilization intensity level.
The invention also provides a self-adaptive sterilization intensity regulating device which comprises a power supply module, a water body environment monitoring module, a model module, a maximum bearable concentration calculating module, a concentration killing amount calculating module, a control module, a sterilization intensity grading regulating module, an ultraviolet sterilization power regulating module, a water pump variable frequency motor and other flow control modules. Wherein,
The water body environment monitoring module is used for monitoring and acquiring a plurality of water quality index parameters of the aquaculture water environment in a preset time period and the actual concentration value of the target pathogenic microorganism at the current moment;
The model module is used for storing an immune balance equation, an inactivation rate and an ultraviolet dose function of target pathogenic microorganisms on target aquatic products under water quality parameters, various index values of constants determined by the structures of the target aquatic products in the immune balance equation and infection resistance in the immune balance equation, an optimal intermittent time value and a preset safe concentration threshold value, and also comprises storage of the processing water quantity, the processing time, the pathogen species prevention and the structural parameters of an ultraviolet sterilization device, and corresponding updating is completed.
The maximum bearable concentration calculation module is used for calculating and determining a maximum bearable concentration value of the target pathogenic microorganism based on an immune balance equation of the target pathogenic microorganism to the target aquatic product in the environment corresponding to the plurality of water quality index parameters in the preset time period;
the concentration killing amount calculating module is used for calculating according to the water quality parameter space and the concentration value of the target pathogenic microorganisms obtained by the water body environment monitoring module and the maximum bearing concentration value calculated by the maximum bearable concentration calculating module, so as to obtain the concentration killing amount of the target pathogenic microorganisms.
And the control module is used for executing the method and completing the self-adaptive sterilization process.
And the sterilization intensity grading regulation and control module is used for dynamically regulating and controlling sterilization process parameters in a grading manner based on the concentration sterilization amount, and guiding the ultraviolet sterilization power regulation module, the water pump variable frequency motor and other flow control modules to sterilize the aquaculture water environment.
In a third aspect, the present invention provides an apparatus comprising an electronic device comprising a memory, a processor and a computer program stored on the memory and executable on the processor, the processor implementing the steps of the adaptive sterilization intensity regulation method as described in any of the above when the program is executed.
In a fourth aspect, the present invention also provides a medium comprising a non-transitory computer readable storage medium having stored thereon a computer program which, when executed by a processor, implements the steps of the adaptive sterilization intensity regulation method as described in any of the above.
According to the self-adaptive sterilization intensity regulation and control method, the self-adaptive sterilization intensity regulation and control device and the electronic equipment, dynamic balance of the infection process between the target pathogenic microorganisms and the target aquatic products along with the change of water quality is considered, an immune balance equation of the target pathogenic microorganisms on the target aquatic products under the water quality of a certain water body environment is introduced, the maximum bearing concentration value of the target pathogenic microorganisms is determined, the concentration killing amount of the pathogens is determined according to the preset safe concentration threshold value, the maximum bearing concentration value and the actual concentration value of the target pathogenic microorganisms, sterilization process parameters are regulated and controlled dynamically based on the concentration killing amount in a grading manner, the aquaculture water environment is sterilized, and the self-adaptability, pertinence and the process of sterilization regulation and control are improved, and the method is energy-saving, green, efficient, scientific and reasonable. In addition, when the tolerance of the current aquatic product to the target pathogenic microorganisms is higher in the water quality of a certain water body environment, the sterilization intensity can be adaptively and properly reduced, and sterilization and disinfection are only needed when the tolerance of the target aquatic product to the target pathogenic microorganisms is reduced due to the water body environment and the infection process is deteriorated, so that the influence of the autoimmune system of the target aquatic product and the water body environment on the pathogen infection activity is utilized to the greatest extent, and the sterilization intensity and energy consumption of the water body are effectively reduced.
Drawings
In order to more clearly illustrate the invention or the technical solutions of the prior art, the following description will briefly explain the drawings used in the embodiments or the description of the prior art, and it is obvious that the drawings in the following description are some embodiments of the invention, and other drawings can be obtained according to the drawings without inventive effort for a person skilled in the art.
Fig. 1 is a schematic flow chart of the adaptive sterilization intensity control method provided by the invention.
Fig. 2 is a second flow chart of the adaptive sterilization intensity control method according to the present invention.
Fig. 3 is a schematic structural diagram of the adaptive sterilization intensity control device provided by the invention.
Fig. 4 is a schematic structural diagram of an electronic device provided by the present invention.
Detailed Description
For the purpose of making the objects, technical solutions and advantages of the present invention more apparent, the technical solutions of the present invention will be clearly and completely described below with reference to the accompanying drawings, and it is apparent that the described embodiments are some embodiments of the present invention, not all embodiments. All other embodiments, which can be made by those skilled in the art based on the embodiments of the invention without making any inventive effort, are intended to be within the scope of the invention.
The terms "first," "second," and the like in this specification are used for distinguishing between similar objects and not necessarily for describing a particular sequential or chronological order. It is to be understood that the data so used may be interchanged where appropriate such that embodiments of the invention may be practiced otherwise than as specifically illustrated or described herein.
The following describes a method, a device and an electronic device for adjusting and controlling self-adaptive sterilization intensity with reference to fig. 1 to 4.
The self-adaptive sterilization intensity regulating and controlling method provided by the embodiment of the invention is realized based on the self-adaptive sterilization intensity regulating and controlling device, the self-adaptive sterilization intensity regulating and controlling system and the medium. The self-adaptive sterilization intensity regulating method provided by the embodiment of the invention introduces the concept of maximum pathogenic microorganism tolerance concentration which changes along with water environment parameters, and realizes the control of the expansion of the sterilization process in the time dimension, namely the conversion from constant power (intensity) sterilization or periodic switch sterilization to intermittent variable power (intensity) sterilization when the self-adaptation of the aquaculture water environment is shorter, because the existing sterilization process control mainly runs with full power. The method provides possibility for saving power consumption by dynamically adjusting and reducing the concentration killing amount of pathogenic microorganisms in unit time, optimizes the sterilization intensity and control time sequence in the sterilization process, and realizes the stable control of repeated cycle intermittent sterilization.
The method has the advantages that the method is used for implementing variable-intensity sterilization by utilizing the maximum tolerance concentration value of pathogenic microorganisms which changes along with water quality parameters, and combines an automatic control technology, so that the sterilization accuracy is improved, and the damage to the flora environment of the aquaculture water body is reduced, aiming at the problems that sterilization is frequent, the sterilization time length and the automation degree of intensity control are low, the balance of beneficial bacterial colonies of the aquaculture water environment is damaged due to the fact that the sterilization dosage exceeds the standard, and the like in the water use process of aquaculture.
The embodiment of the invention describes an adaptive sterilization intensity control method by taking an adaptive sterilization intensity control device as an execution main body as an example.
Referring to fig. 1 and fig. 2, fig. 1 is a schematic flow chart of the adaptive sterilization intensity control method according to the present invention, and fig. 2 is a second schematic flow chart of the adaptive sterilization intensity control method according to the present invention.
As shown in fig. 1, the method comprises the following steps:
Step S110, acquiring a plurality of water quality index parameters of the aquaculture water environment in a preset time period and an actual concentration value of target pathogenic microorganisms at the current moment;
Step S120, determining a maximum bearing concentration value of the target pathogenic microorganism based on an immune balance equation of the target pathogenic microorganism to the target aquatic product in the environment of the plurality of water quality index parameters within the preset time period;
Step S130, determining the concentration killing amount of the target pathogenic microorganism based on a preset safe concentration threshold value, the maximum bearing concentration value and the actual concentration value of the target pathogenic microorganism;
Step S140, based on the concentration killing amount, dynamically regulating and controlling sterilization process parameters in a grading manner, and sterilizing the aquaculture water environment;
and step S150, repeating the steps S110-S140 to finish the self-adaptive sterilization process.
The method generates maximum bearable pathogen concentration for sterilization strength grading adjustment through the infection dynamic balance between pathogenic microorganism and target aquatic product which change along with water quality, and the technical principle is that the infection force which changes along with water quality condition is controlled at the inner side of a dynamic balance equation, so that the health of the aquatic product can be maintained.
As shown in fig. 2, the flow for one embodiment is described as follows:
specifically, the self-adaptive sterilization intensity regulating device determines a aquaculture water environment needing sterilization intensity regulation, acquires target aquatic product information and target pathogenic microorganism information in the aquaculture water environment, determines various constant index values in an infectivity balance equation, and generates subsequent maximum tolerance concentration and concentration killing amount based on the equation.
Based on step 110, the adaptive sterilization intensity control device obtains the water quality index parameters of the aquaculture water environment within a preset time period, wherein the preset time period is set by experience according to actual conditions, such as 1h, 10min and 5min.
It should be noted that, the water quality space formed by a plurality of water quality indexes and the values of the plurality of water quality indexes in the aquaculture water environment is called a water quality parameter space, and the plurality of water quality indexes include, but are not limited to, water temperature, PH value, dissolved oxygen, nitrate, illumination condition and turbidity. In an embodiment, the water quality parameter space may be expressed in aggregate as W φ =w (x, y, z.), x, y, z.,. Epsilon.r+, and in order to ensure the survival rate and quality of the cultured aquatic products, the parameter values corresponding to the water quality indexes should be within the suitable survival range of the target aquatic products. Wherein x, y and z are selected main water quality indexes, W ijk… is adopted to represent a water quality parameter space with water quality index parameters of x i, yj, zk, i, j, k is less than or equal to n, and n is a positive integer.
Therefore, the water quality parameter vector of the aquaculture water environment in the preset time period is composed of a plurality of water quality index parameters in the preset time period, the water quality index parameters can be obtained by measuring the water quality index, and the water quality parameter space is mainly used for simply representing the water quality index parameters.
Meanwhile, the self-adaptive sterilization intensity regulating device also needs to acquire the actual concentration value of the target pathogenic microorganism at the current moment.
Based on step 120, the adaptive sterilization intensity control device determines an immune balance equation of the target pathogenic microorganism to the target aquatic product in the water quality parameter space in the preset time period based on the water quality parameter space of the aquaculture water environment in the preset time period, namely based on a plurality of water quality index parameters of the aquaculture water environment in the preset time period.
Further, the self-adaptive sterilization intensity regulating device determines the moment when the target pathogenic microorganism has immune balance on the target aquatic product in the current water quality parameter space and the concentration value corresponding to the existence of the immune balance, namely the maximum bearing concentration value, based on a plurality of water quality index parameters in the current water quality parameter space.
Based on step 130, the adaptive sterilization intensity control device determines a concentration killing amount between an actual concentration value of the target pathogenic microorganism and an actual concentration control target value based on a maximum sustained concentration value, a specific preset safe concentration threshold value thereof, and an actual concentration value thereof when the target pathogenic microorganism has an immune balance on the target aquatic product.
Based on step 140, further, the adaptive sterilization intensity control device determines a sterilization intensity level required for the sterilization process based on the concentration killing amount.
The self-adaptive sterilization intensity regulating device is used for dynamically regulating and controlling sterilization process parameters in a grading manner after determining the sterilization intensity level, and intermittently sterilizing the aquaculture water environment.
The invention has the advantages that the target baseline of target pathogen concentration control can be adaptively adjusted according to the water quality parameter change, the sterilization intensity level can be adaptively adjusted according to the water quality parameter change, and the control method, the control time, the control intensity and other control quantity changes can be adaptively adjusted according to the concentration killing quantity, so that the sterilization process is more intelligent and the energy consumption is more saved.
Based on step 150, further, after the intermittent sterilization process is performed for the fixed sterilization period T, the adaptive sterilization intensity control device determines whether the task of the concentration sterilization amount in this period has been completed currently.
If the task of the concentration killing amount is not completed at the current moment, the intermittent sterilization treatment is continued to be carried out for fixing the sterilization period T, and then whether the task of the concentration killing amount in the period is completed is judged.
If the control period is not finished, the self-adaptive sterilization intensity regulating device returns to the first step, and the steps 110-140 are repeated, namely, the water quality parameter space of the aquaculture water environment in a preset period and the actual concentration value of the target pathogenic microorganisms at the current moment are obtained, and the sterilization intensity regulating process is continuously executed, so that the healthy dynamic management in the aquaculture process is realized.
According to the self-adaptive sterilization intensity regulation method provided by the invention, dynamic balance of the infection process of target pathogenic microorganisms and target aquatic products along with the change of water quality is considered, an immune balance equation of the target pathogenic microorganisms on the target aquatic products under the water quality of a certain water body environment is introduced, the maximum bearing concentration value of the target pathogenic microorganisms is determined, the concentration killing amount of the target pathogenic microorganisms is determined according to a preset safe concentration threshold value, the maximum bearing concentration value and an actual concentration value, sterilization process parameters are dynamically regulated and controlled in a grading manner based on the concentration killing amount, the aquaculture water environment is sterilized, the self-adaptability, pertinence and the process of sterilization regulation are improved, the energy consumption is saved, and the self-adaptive sterilization intensity regulation method is green, efficient, scientific and reasonable. In addition, when the tolerance of the target aquatic product to the target pathogenic microorganisms is higher in the water quality of a certain water body environment, the sterilization intensity can be adaptively and properly reduced, and sterilization and disinfection are only needed when the tolerance of the target aquatic product to the target pathogenic microorganisms is reduced due to the water body environment and the infection process is deteriorated, so that the influence of the autoimmune system of the target aquatic product and the water body environment on the pathogen infection activity is utilized to the greatest extent, and the sterilization intensity and the energy consumption of the water body are further effectively reduced.
In some embodiments, based on the content developed in step 120, the immune balance equation and various parameters of the target aquatic product by the target pathogenic microorganism in the environment of the plurality of water quality index parameters within the preset time period are pre-constructed, specifically determined by the following manner:
S1201, based on the plurality of water quality index parameters, determining the infection activity of target pathogenic microorganisms in the preset time period;
s1202, determining the anti-infection capability of the target aquatic product in the preset time period based on the plurality of water quality index parameters;
And S1203, determining an immune balance equation of the target pathogenic microorganism on the target aquatic product in the environment of the plurality of water quality index parameters within the preset time period based on the infection activity and the anti-infection capability.
Specifically, in S1201, the adaptive sterilization intensity control device determines the infection activity of the target pathogenic microorganism in the preset time period based on the plurality of water quality index parameters in the preset time period.
In one embodiment, U a (W, t) represents the infectivity activity of the target pathogenic microorganism a at the water quality parameter space W within the preset time period t, wherein the infectivity activity represents the value of the infectivity of the target pathogenic microorganism of a fixed intake to the target aquatic product.
U a(Wijk…, t) then represents the infecting activity of the target pathogenic microorganism a in a preset time period t at a water quality parameter space of W ijk…. The specific values of the infection activity at U a(Wijk...., t) can be determined experimentally or can be approximated based on the formula:
Wherein W 000… represents the optimal space value of the infection process of the target pathogenic microorganism a, P a is a first transformation matrix, and since the change trend of the infection process of the target pathogenic microorganism a is different between the infection process of the target pathogenic microorganism a and the infection process of the target pathogenic microorganism a, P a can be expressed in segments according to different change trends, namely P a is a segment function, and since P a is a segment function, U a(Wijk… and t) are segment functions.
Meanwhile, according to S1202, the adaptive sterilization intensity control device determines the anti-infective ability of the target aquatic product in the preset time period based on a plurality of water quality index parameters in the preset time period.
In one embodiment, V b (W, t) represents the anti-infective ability of the target aquatic product b (particularly related to the variety and specification of the aquatic product) at the water quality parameter space of W ijk…… within the preset time period t, wherein the anti-infective ability represents the maximum concentration value of pathogenic microorganisms of the target aquatic product, which does not attack in the water environment of different concentrations of pathogenic microorganisms.
V b(Wijk…, t) indicates the anti-infective ability of the target aquatic product b in the preset time period t at the water quality parameter space of W ijk…. The specific values of the anti-infective ability at V b(Wijk…, t) can be determined experimentally or can be approximated based on the formula:
Wherein W 000… represents the optimal space value of the anti-infection process of the target aquatic product b, P b is a second transformation matrix, and since the change trend of the anti-infection process of the target aquatic product b is different between the anti-infection process of the target aquatic product b and the anti-infection process of the target aquatic product b, P b can be represented by segments according to different change trends, namely P b is a segment function, and since P b is a segment function, V b(Wijk… and t) are segment functions.
Further, according to S1203, the adaptive sterilization intensity control device determines an immune balance equation of the target pathogenic microorganism on the target aquatic product in the environment of a plurality of water quality index parameters within a preset time period based on the infection activity and the anti-infection capability.
In one embodiment, the equation of the immune balance of the target pathogenic microorganism to the target aquatic product over the predetermined period of time is as follows:
Wherein, The method comprises the steps of expressing the infectivity of target pathogenic microorganisms a to target aquatic products b within a preset time period t, wherein the water quality parameter value is W ijk…, expressing the concentration value of the target pathogenic microorganisms a within the preset time period t, expressing the water intake or the water contact quantity of the target aquatic products b to the aquaculture water environment within unit time, expressing the total number of equivalent immune factors, and expressing constants determined by the structures of the target aquatic products b of both f and k through a large amount of experimental data.
It should be noted that the number of the substrates,The concentration value of the target pathogenic microorganism a in the preset time period t is represented, the concentration is determined by a pathogen detection reagent and the like or is obtained by a biosensor in real time, and a manual input or real-time monitoring value is input into the self-adaptive sterilization intensity regulating device and used as a feedback monitoring index of the self-adaptive sterilization intensity regulating device.
According to the embodiment of the invention, the infection activity of the target pathogenic microorganism and the anti-infection capability of the target aquatic product are comprehensively analyzed, so that the disease risk in the cultivation process can be effectively estimated and managed, and the health and safety of the cultivated aquatic product are ensured.
In some embodiments, the concentration killing amount of the target pathogenic microorganism is determined based on the preset safe concentration threshold value, the maximum sustained concentration value, and the actual concentration value of the target pathogenic microorganism in steps S120 and S130, and the specific contents of the process include:
S121, determining the moment when the result of the immune balance equation is zero as the moment when the target pathogenic microorganism has immune balance on the target aquatic product;
s122, determining the maximum bearing concentration value of the target pathogenic microorganism based on an immune balance equation in immune balance;
s131, calculating a difference value between the maximum bearing concentration value and a preset safe concentration threshold value to obtain an actual concentration control target value of the target pathogenic microorganism;
And S132, calculating the difference value between the actual concentration value and the actual concentration control target value to obtain the actual concentration killing amount of the target pathogenic microorganism.
Specifically, the self-adaptive sterilization intensity regulating device determines the moment when the result of the immune balance equation is zero as the moment when the target pathogenic microorganism has immune balance on the target aquatic product.
The self-adaptive sterilization intensity regulating device determines the maximum bearing concentration value of target pathogenic microorganisms based on an immune balance equation during immune balance.
In an embodiment, based on steps S121 and S122, a specific water quality parameter space W 0 and a time t 0 exist, so that the target pathogenic microorganism a has an immune balance to the target aquatic product b, satisfying the following conditionsI.e.And the number of the components is that,
,
Namely, the target aquatic product is in the water quality parameter spaceThe maximum bearing concentration value of target pathogenic microorganism, the corresponding water quality condition in each time periodOne corresponding toSubtracting a preset safety concentration threshold from the valueUnder the control of the actual sterilization intensity, the concentration of the target pathogenic microorganisms in the target water body is controlled to be @, and the concentration of the target pathogenic microorganisms in the target water body is controlled to be @) Below.
The balance formula can be considered as an immune balance dynamic model based on water quality indexes, and the sterilization intensity is regulated and controlled based on the concentration value generated by the immune balance dynamic model so as to effectively reduce the sterilization amount. The concentration of the target pathogenic microorganism can be obtained in real time by a pathogenic microorganism concentration sensor, and if the concentration of the corresponding target pathogenic microorganism cannot be obtained in real time by the sensor, the concentration can be manually measured and input or remotely input. The remote input values may be generated by a numerical variation simulation model based on the approximate input concentration to achieve energy-saving control. Specifically, the background concentration in some scenes is a constant value.
Further, based on step S131, the adaptive sterilization intensity control device calculates a difference between the maximum bearing concentration value and a preset safe concentration threshold value to obtain an actual concentration control target value of the target pathogenic microorganism, which may be expressed asThe preset safe concentration threshold is set according to practical conditions, and is generally not less than 20% of the maximum bearing concentration value, and can be a fixed value.
Subsequently, based on step S132, the adaptive sterilization intensity control device calculates the difference between the actual concentration value of the target pathogenic microorganism and the actual concentration control target value to obtain the concentration killing amount for actually killing the target pathogenic microorganism, which may be expressed as
It should be noted that, in an embodiment, if two or more pathogenic microorganisms are to be killed, the concentration killing amounts of the multiple pathogenic microorganisms are added up to multiply by the correction coefficient to achieve a synergistic effect, specifically: . Wherein, Is the sum of the concentration killing amount of m pathogenic microorganisms; representing a correction factor, generally greater than 1, which can be set to 1.2, which is adjusted according to the synergistic effect of actual multiple diseases, determined by empirical values; indicating the equivalent concentration kill of the population of the plurality of pathogenic microorganisms.
According to the embodiment of the invention, based on an immune balance equation under the condition of immune balance between the target pathogenic microorganisms and the target aquatic products, the concentration killing amount of the target pathogenic microorganisms is determined, and then the sterilization intensity of the aquaculture water environment is regulated and controlled based on the concentration killing amount, so that the dynamic sterilization intensity regulation and control based on the self-adaptability of the aquaculture water environment are realized, the sterilization intensity regulation which is dynamically balanced and varies with the water quality through pathogen infection can effectively save energy consumption, and the reasonable and targeted sterilization of the aquaculture water environment is realized.
In some embodiments, based on the content developed in step S140, based on the concentration killing amount, the sterilization intensity of the aquaculture water environment is regulated, and the specific content of the process includes:
s141, if the concentration killing amount is larger than zero, determining a sterilization intensity level based on the concentration killing amount and the preset safety concentration threshold;
s142, determining sterilization power and water inflow under different sterilization intensity levels based on a function between the inactivation rate y and the ultraviolet dose x;
S143, dynamically sterilizing the aquaculture water environment based on the sterilization power and the water inlet speed under the different sterilization intensity levels.
It should be noted that the function of the uv dose x and the inactivation rate y in this step is pre-constructed based on the uv dose-inactivation rate curve. Taking ultraviolet water disinfection equipment as an example, the specific steps are as follows:
first, a characteristic curve of the verification dose is constructed. The parameters which can be adjusted by the ultraviolet disinfection equipment are specified in the standard ultraviolet dose test method of ultraviolet water disinfection equipment (GB/T32091-2015) and comprise the water flow Q and the output power P of an ultraviolet lamp tube. The verification dosage of the ultraviolet water disinfection equipment is related to factors such as ultraviolet transmittance, ultraviolet light intensity, flow, lamp tube number and the like of a water body, and a a, b, c, d, e constant is calculated by a linear regression method according to experimental data of the dosage test of the disinfection equipment and the formula RED= a×A254 b×Pc×Qd×Be, so that a characteristic curve of the ultraviolet water disinfection equipment can be obtained. Wherein RED represents the verification dosage of the ultraviolet water disinfection device, A 254 represents the absorbance of water UV 254, P represents the output power of the ultraviolet water disinfection device, Q represents the corresponding flow of the device, B represents the number of ultraviolet module units (only for canal type disinfection device, the item of pipe type disinfection device is 1), and a, B, c, d, e is a constant. It will be appreciated that RED represents an equation constrained by P and Q. The water quality influence a 254 is mainly the influence of the turbidity of the water body, specifically, the absorbance of UV 254 =1-ultraviolet transmittance UVT, and the ultraviolet transmittance UVT is influenced by the water quality parameters. Thus, this effect is also taken into account in the acquired water quality parameters. The effect of the validation dose on equipment fouling and aging is referred to as the effective validation dose, and there is no specific distinction between the two in this example, and is described in detail in the standard. In addition, in the present embodiment, the verification dose RED is equivalent to the actual ultraviolet dose x.
Further, a function between the ultraviolet dose x and the inactivation rate y is constructed based on the ultraviolet dose-inactivation rate curve. Because the inactivation rate is affected by the ultraviolet dose, in order to dynamically adjust the ultraviolet dose according to the inactivation rate and explain the regulation relation of two parameter values of the sterilization power P and the inflow water flow Q in the water quality regulation and control process, according to the ultraviolet dose-inactivation rate curve described in the standard, a function of the ultraviolet dose x and the inactivation rate y is constructed and is marked as y=f (x) (x epsilon A, A is more than or equal to 0), the value range of the function is 0-100%, and the inverse function of the function can be correspondingly obtained and can be expressed as x=f -1 (y) =RED. The relation equation of two regulating variables of the inactivation rate y, the sterilization power P and the inflow water flow Q is that y=f (P, Q) =f (10 a×A254 b×Pc×Qd)), and the relation equation is taken as the basis for regulating and controlling two parameter values of the sterilization power P and the inflow water flow Q in the water quality regulating and controlling process, wherein the inactivation rate, namely the sterilization rate used in the embodiment, represents the ratio of the concentration sterilization amount to the initial concentration, is different from the sterilization logarithmic value, wherein the sterilization rate= [1-10 (sterilization logarithmic value) ]multipliedby 100 percent.
Before proceeding to step 140, the actual concentration killing amount value is determined. If the actual concentration killing amount of the target pathogenic microorganism is larger than zero, the self-adaptive sterilization intensity regulating device determines the sterilization intensity level based on the magnitude relation between the concentration killing amount and a preset safety concentration threshold value. This step is developed in the event that the actual concentration kill of the target pathogenic microorganism is greater than zero.
For the determination of the sterilization intensity level based on the concentration killing amount and the preset safety concentration threshold in the step S141, the specific content of the process includes:
If the concentration killing amount is larger than the preset safety concentration threshold value of the first preset times, determining that the sterilization intensity level is a primary sterilization intensity level;
If the concentration killing amount is smaller than the preset safety concentration threshold value of the first preset time and larger than the preset safety concentration threshold value of the second preset time, determining that the sterilization intensity level is a secondary sterilization intensity level;
and if the concentration killing amount is smaller than the preset safety concentration threshold value of the second preset times, determining that the sterilization intensity level is a three-level sterilization intensity level.
In particular, if the concentration of the target pathogenic microorganism is at a killing level(Or equivalent concentration kill amount)) The self-adaptive sterilization intensity regulating device determines that the sterilization intensity level is the first sterilization intensity level when the self-adaptive sterilization intensity regulating device is larger than a preset safety concentration threshold value of a first preset multiple, wherein the first preset multiple can be set to be 1 time according to actual conditions, and the concentration killing amount is larger than the preset safety concentration threshold value c 0.
Further, if the concentration of the target pathogenic microorganism is a killing amount(Or equivalent concentration kill amount)) The self-adaptive sterilization intensity regulating device determines that the sterilization intensity level is a secondary sterilization intensity level, wherein the second preset time is set according to actual conditions, can be set to 0.5 time, and the 0.5 time preset safety concentration threshold c 0 < concentration sterilization amount < preset safety concentration threshold c 0 is higher, and in the case, the water quality change is not great, and the infection force balance change caused by the water quality change can be kept in a controllable range by adopting normal sterilization intensity.
Further, if the concentration of the target pathogenic microorganism is a killing amount(Or equivalent concentration kill amount)) The self-adaptive sterilization intensity regulating device determines that the sterilization intensity level is three-level sterilization intensity level when the concentration killing amount is smaller than a preset safety concentration threshold value of a second preset multiple, namely a preset safety concentration threshold value c 0 of the second preset multiple, wherein if the second preset multiple is set to be 0.5 time, the preset safety concentration threshold value c 0 of the concentration killing amount is smaller than 0.5 time, and under the condition, the water quality change is considered to be smaller, the sterilization intensity can be reduced, and the infection force balance change caused by the water quality change is kept in a controllable range.
The sterilization power and inflow rate at different sterilization intensity levels are determined for the function based on the inactivation rate y and the ultraviolet dose x described in step S142 above.
In this embodiment, the adaptive sterilization intensity control device is correspondingly classified into three levels based on the functions of the ultraviolet dose x and the inactivation rate y, and the first sterilization power and the first water inlet flow of the first level sterilization intensity level, the second sterilization power and the second water inlet flow of the second level sterilization intensity level, and the third sterilization power and the third water inlet flow of the third level sterilization intensity level are correspondingly and sequentially determined. Optionally, the second sterilizing power may be considered to be half of the standard power in the prior art, and the water inlet flow rate regulating value is half of the water inlet speed normally set by the water pump.
It should be noted that, the function of the inactivation rate y and the ultraviolet dose x, that is, based on the inactivation rate y, the sterilization power P, and the equation of the inflow water flow Q, the inactivation rate y is constrained by the sterilization power P and the inflow water flow Q, that is, x=f -1(y) =RED=10a×A254 b×Pc×Qd. Therefore, the different inactivation rates y correspond to the combinations of the sterilization power P and the inflow water flow Q, and can be classified into more levels according to the functions of the inactivation rates y and the ultraviolet dose x, but in this example, the inactivation rates y and the ultraviolet dose x are only classified into three groups.
Specifically, if the sterilization intensity level is the primary sterilization intensity level, sequentially determining a first sterilization power and a first water inflow rate according to a function of the inactivation rate y and the ultraviolet dose x, and respectively using a corresponding power value corresponding to increased sterilization irradiation and a corresponding water inflow rate value of a reduced water pump as the first sterilization power and the first water inflow rate;
if the sterilization intensity level is the secondary sterilization intensity level, sequentially determining a second sterilization power and a second water inflow rate according to the function of the inactivation rate y and the ultraviolet dose x, wherein a power value corresponding to a normal sterilization irradiation value and a normal water inflow rate value of a water pump are respectively used as the second sterilization power and the second water inflow rate;
if the sterilization intensity level is the primary sterilization intensity level, sequentially determining a third sterilization power and a third water inflow according to the function of the inactivation rate y and the ultraviolet dose x, wherein the power value corresponding to the correspondingly reduced sterilization irradiation and the accelerated water inflow speed value of the water pump are respectively used as the third sterilization power and the third water inflow;
it should be noted that in this step, the value of the inflow rate may be determined first, and then the corresponding sterilizing power P may be determined.
Aiming at the dynamic sterilization of the aquaculture water environment based on the sterilization power and the water inflow speed under the different sterilization intensity levels in the step 143, the following steps are executed for the regulation and control of the sterilization power and the water inflow flow:
If the sterilization intensity level is the primary sterilization intensity level, sterilizing the aquaculture water environment according to a first sterilization power and a first water inflow rate, wherein the first sterilization power is the sterilization power under the primary sterilization intensity level, and the first water inflow rate is the water inflow rate under the primary sterilization intensity level;
If the sterilization intensity level is the secondary sterilization intensity level, sterilizing the aquaculture water environment according to a second sterilization power and a second water inflow rate, wherein the second sterilization power is sterilization power under the secondary sterilization intensity level, and the second water inflow rate is water inflow rate under the secondary sterilization intensity level;
and if the sterilization intensity level is the three-level sterilization intensity level, sterilizing the aquaculture water environment according to a third sterilization power and a third water inflow rate, wherein the third sterilization power is the sterilization power under the three-level sterilization intensity level, and the third water inflow rate is the water inflow rate under the three-level sterilization intensity level.
Further, the self-adaptive sterilization intensity regulating device regulates and controls adjustable parameters of the sterilizing equipment in a grading manner according to three levels of sterilization power and inflow water flow determined by different sterilization intensity levels, wherein the adjustable parameters comprise sterilization power P and inflow water flow Q, and dynamically sterilizes the aquaculture water environment. Wherein, the sterilization power P and the water inflow rate Q are reflected on the quantity of ultraviolet lamp tubes and the adjustment of the water inflow speed of the water pump.
Specifically, if the sterilization intensity level is a primary sterilization intensity level, the self-adaptive sterilization intensity regulating device performs sterilization on the aquaculture water environment according to the first sterilization power and the first water inflow, namely by adopting regulating measures of increasing sterilization irradiation amount and reducing water inflow speed of the water pump. In one embodiment, the increase of the original sterilization irradiation amount can use the arrangement of a plurality of ultraviolet lamp tubes to enhance the upper limit of the intensity regulation of the sterilization irradiation amount.
In another case, if the sterilization intensity level is a secondary sterilization intensity level, the self-adaptive sterilization intensity regulating device performs sterilization on the aquaculture water environment according to the second sterilization power and the second water inflow rate, namely using the normal sterilization irradiation amount and the normal water inflow rate.
In another case, if the sterilization intensity level is a three-level sterilization intensity level, the self-adaptive sterilization intensity regulating device performs sterilization on the aquaculture water environment according to the third sterilization power and the second water inflow rate, namely, by adopting the radiation amount of halving sterilization and improving the water inflow speed of the water pump. In one embodiment, halving the original germicidal irradiation level may employ halving the use of ultraviolet lamps or power adjustment to reduce the germicidal irradiation level intensity.
Based on step S150, in the flow described in fig. 2, steps S110 to S140 are repeated to complete the adaptive sterilization process. Specifically, if the concentration killing amount of the target pathogenic microorganism is less than or equal to zero, the self-adaptive sterilization intensity regulating device judges whether the prevention and control period is finished.
Further, if the prevention and control period is over, the self-adaptive sterilization intensity regulating device ends the sterilization intensity regulating process, and if the prevention and control period is not over, the self-adaptive sterilization intensity regulating device returns to the first step, and the steps 110-140 are repeated, so that the water quality parameter space of the aquaculture water environment in the preset period and the actual concentration value of the target pathogenic microorganisms at the current moment are obtained, the sterilization intensity regulating process is continuously executed, and the healthy dynamic management in the aquaculture process is realized.
In summary, the embodiment of the invention combines the flow of an embodiment shown in fig. 2, and describes that different sterilization intensity selections are executed according to concentration sterilization amount, so that the sterilization intensity is regulated and controlled in a grading manner, the sterilization irradiation amount is further controlled dynamically, the sterilization process is refined in an energy-saving manner, and the accurate quantitative energy consumption control is realized, thereby realizing the reasonable and targeted sterilization of the aquaculture water environment.
The adaptive sterilization intensity control device provided by the invention is described below, and the adaptive sterilization intensity control device described below and the adaptive sterilization intensity control method described above can be referred to correspondingly.
Referring to fig. 3, fig. 3 is a schematic structural diagram of the adaptive sterilization intensity control device provided by the invention. As shown in fig. 3, the self-adaptive sterilization intensity regulating device specifically includes a power supply module 330, a water environment monitoring module 311, a model module 312, a maximum bearable concentration calculating module 313, a concentration killing amount calculating module 314, a control module 315, a sterilization intensity grading regulating module 316, an ultraviolet sterilization power regulating module 321, a water pump variable frequency motor and other flow control modules 322. The water environment monitoring module 311, the model module 312, the maximum bearable concentration calculating module 313, the concentration killing amount calculating module 314, the control module 315 and the sterilization intensity grading regulation module 316 belong to the weak current part 310, and the ultraviolet sterilization power regulating module 321, the water pump variable frequency motor and other flow control modules 322 belong to the strong current part 320.
Specifically, in the self-adaptive sterilization intensity regulating device, each module has the following functions:
the power supply module 330 provides the required electric energy for the self-adaptive sterilization intensity regulating device to execute the operation;
The water environment monitoring module 311 is used for monitoring and acquiring a plurality of water quality index parameters of the aquaculture water environment in a preset time period and an actual concentration value of target pathogenic microorganisms at the current moment;
The model module 312 is used for storing various index values such as an immune balance equation, an inactivation rate and a function of ultraviolet dose of target pathogenic microorganisms on target aquatic products under water quality parameters, an infection activity in the immune balance equation, constants determined by the structures of the target aquatic products in anti-infection capability, and the like, and an optimal intermittent time T value and a preset safe concentration threshold value The method also comprises the steps of storing the water treatment amount, the treatment time, the pathogen species and concentration prevention (which are different along with the time period of seasons) and the structural parameters of the ultraviolet sterilization device, and completing the corresponding updating. Wherein parameters such as the water treatment amount, the treatment time, the pathogen prevention type and concentration (which are different along with the time period of seasons) can be manually and remotely input, and the remote input value can be generated by a numerical variation simulation model based on the approximate input concentration, and the optimal intermittent time T value and the preset safe concentration threshold valueCan be obtained through experiments according to actual conditions;
The maximum bearable concentration calculation module 313 is configured to calculate and determine a maximum bearable concentration value of the target pathogenic microorganism based on an immune balance equation of the target pathogenic microorganism to the target aquatic product in the environment corresponding to the plurality of water quality index parameters within the preset time period;
The concentration killing amount calculation module 314 is configured to calculate according to the water quality parameter space and the concentration value of the target pathogenic microorganism obtained by the water body environment monitoring module, and the maximum bearing concentration value calculated by the maximum bearable concentration calculation module, so as to obtain the concentration killing amount of the target pathogenic microorganism.
The control module 315 is configured to perform the above method to complete the adaptive sterilization process.
And the sterilization intensity grading regulation and control module 316 is used for dynamically regulating and controlling sterilization process parameters in a grading manner based on the concentration sterilization amount, and guiding the ultraviolet sterilization power regulation module, the water pump variable frequency motor and other flow control modules to sterilize the aquaculture water environment.
The specific using steps of the device are that the control module 315 is used for executing the regulation and control method, the water environment monitoring module 311 is used for monitoring and acquiring water quality parameter indexes and the actual concentration value of the current target pathogenic microorganisms, the acquired parameters are input into the model module 312, a related model is called, the maximum bearable concentration calculation module 313 is used for calculating the maximum bearable concentration value of the target aquatic product on the target pathogenic microorganisms under the current water quality condition, the concentration killing amount calculation module 314 is used for calculating and determining the concentration killing amount, then the sterilization intensity classification is carried out according to the concentration killing amount calculated by the concentration killing amount calculation module 314, and the sterilization intensity classification regulation and control module 316 is guided to regulate the parameters of the flow control module 322 such as the ultraviolet sterilization power regulation module 321, the water pump variable frequency motor and the like, so as to sterilize the water.
It should be noted that, when the adaptive sterilization intensity control device provided by the present invention is specifically operated, the adaptive sterilization intensity control method described in any one of the above embodiments may be executed, and this embodiment will not be described in detail.
In addition, the self-adaptive sterilization intensity regulating device has two typical application forms. The device is used as an independent device for integrated use, such as in relatively independent closed water bodies of traditional pond culture and the like, sterilization intensity control based on the water body environment is realized through in-situ deployment of the device, and the device is used as a dispersion mode, such as in open/semi-open scenes of semi-open industrial culture, culture engineering and the like, and can be dispersed into other facility equipment to be matched with other equipment through main components.
Specifically, in an embodiment, for the closed application scenarios such as in-water circulation and traditional pit culture in facility culture such as factory, because the water treatment capacity is relatively fixed, an in-situ sterilization treatment device in an independent form is used in the scenario, and sterilization regulation and control are performed according to the internal water quality index parameters of the device. According to the method, the device dynamically monitors the water quality change and the immune balance of the concentration of pathogenic microorganisms to realize the control of the concentration of the pathogenic microorganisms so as to reduce the occurrence of diseases.
Specifically, in another embodiment, the method is used in an open/semi-open application scenario in which the water quality index parameter is inconvenient to adjust and the concentration of the water quality index parameter and the target pathogenic microorganism is in a relatively fixed large water surface containment mode, a deep sea net cage, a work ship and the like, and the culture is performed by using environmental water. Because the water quality index parameters are difficult to control, the concentration of the target pathogenic microorganisms in the water body needs to be adjusted at the water inlet according to the water quality conditions in the cultivation facilities. In this scenario, the background concentration of pathogenic microorganisms is the biggest influencing factor for disease occurrence, especially in situations where insufficient energy supply or complete killing is not feasible, whereas traditional complete killing consumes huge energy. The reasonable pathogen concentration is particularly important based on water quality reduction, so that energy consumption can be saved, and the disease prevention effect generated by unit energy consumption can be improved. It will be appreciated that at this point the body of water is divided into an inner and an outer portion, the outer body of water is defined as a first body of water, the inner body of water is defined as a second body of water, the actual concentration of the target pathogenic microorganism can be determined in the first body of water, and the water quality index parameter can be determined in the second body of water. The water body in the water inlet process is treated by the rapid sterilization mode formed by the device to construct a barrier, the second water area has a large culture density, and the internal and external environments have tiny but obvious water quality index parameter differences, so that the tolerance of the target aquatic product to the target pathogenic microorganism is reduced, and the sterilization treatment is required according to the water quality parameters of the second water body.
Fig. 4 is a schematic structural diagram of an electronic device according to the present invention, as shown in fig. 4, the electronic device may include a processor (processor) 410, a communication interface (Communications Interface) 420, a memory (memory) 430, and a communication bus 440, where the processor 410, the communication interface 420, and the memory 430 perform communication with each other through the communication bus 440. Processor 410 may invoke logic instructions in memory 430 to perform the adaptive sterilization intensity control method, the specific method content being described above.
Further, the logic instructions in the memory 430 described above may be implemented in the form of software functional units and may be stored in a computer-readable storage medium when sold or used as a stand-alone product. Based on this understanding, the technical solution of the present invention may be embodied essentially or in a part contributing to the prior art or in a part of the technical solution, in the form of a software product stored in a storage medium, comprising several instructions for causing a computer device (which may be a personal computer, a server, a network device, etc.) to perform all or part of the steps of the method according to the embodiments of the present invention. The storage medium includes a U disk, a removable hard disk, a Read-Only Memory (ROM), a random access Memory (RAM, random Access Memory), a magnetic disk, an optical disk, or other various media capable of storing program codes.
In another aspect, the present invention also provides a computer program product, which includes a computer program stored on a non-transitory computer readable storage medium, the computer program including program instructions, which when executed by a computer, can perform the adaptive sterilization intensity control method provided in the above embodiments, and the specific method content is as described above.
In yet another aspect, the present invention further provides a non-transitory computer readable storage medium, on which a computer program is stored, which when executed by a processor is implemented to perform the adaptive sterilization intensity control method provided in the above embodiments, where the specific method content is as described above.
The embodiments of the apparatus described above are merely illustrative, wherein the elements illustrated as separate elements may or may not be physically separate, and the elements shown as elements may or may not be physical elements. Some or all of the modules may be selected according to actual needs to achieve the purpose of the solution of this embodiment. Those of ordinary skill in the art will understand and implement the present invention without undue burden.
From the above description of the embodiments, it will be apparent to those skilled in the art that the embodiments may be implemented by means of software plus necessary general hardware platforms, or of course may be implemented by means of hardware. Based on this understanding, the foregoing technical solution may be embodied essentially or in a part contributing to the prior art in the form of a software product, which may be stored in a computer readable storage medium, such as ROM/RAM, a magnetic disk, an optical disk, etc., including several instructions for causing a computer device (which may be a personal computer, a server, or a network device, etc.) to execute the method described in the respective embodiments or some parts of the embodiments.
It should be noted that the above-mentioned embodiments are merely for illustrating the technical solution of the present invention, and not for limiting the same, and although the present invention has been described in detail with reference to the above-mentioned embodiments, it should be understood by those skilled in the art that the technical solution described in the above-mentioned embodiments may be modified or some technical features may be equivalently replaced, and these modifications or substitutions do not make the essence of the corresponding technical solution deviate from the spirit and scope of the technical solution of the embodiments of the present invention.

Claims (10)

1.一种自适应杀菌强度调控方法,其特征在于,包括:1. A method for adaptively controlling sterilization intensity, comprising: 步骤110、获取预设时间段内养殖水环境的多个水质指标参数以及当前时刻目标病原微生物的实际浓度值;Step 110, obtaining a plurality of water quality index parameters of the aquaculture water environment within a preset time period and the actual concentration value of the target pathogenic microorganism at the current moment; 步骤120、基于目标病原微生物在所述预设时间段内所述多个水质指标参数的环境下对目标水产品的免疫平衡方程,确定所述目标病原微生物的最大承受浓度值;Step 120: determining the maximum tolerance concentration value of the target pathogenic microorganism based on the immune balance equation of the target pathogenic microorganism to the target aquatic product under the environment of the multiple water quality index parameters within the preset time period; 步骤130、基于所述目标病原微生物的预设安全浓度阈值、所述最大承受浓度值和所述实际浓度值,确定所述目标病原微生物的浓度杀灭量;Step 130: determining a concentration killing amount of the target pathogenic microorganism based on a preset safety concentration threshold of the target pathogenic microorganism, the maximum tolerance concentration value, and the actual concentration value; 步骤140、基于所述浓度杀灭量,分级动态调控杀菌过程参数,对所述养殖水环境进行杀菌;Step 140, based on the concentration killing amount, dynamically regulating the sterilization process parameters in a graded manner to sterilize the aquaculture water environment; 步骤150、重复步骤110-步骤140,完成自适应杀菌过程。Step 150, repeat steps 110-140 to complete the adaptive sterilization process. 2.根据权利要求1所述的自适应杀菌强度调控方法,其特征在于,所述基于目标病原微生物在所述预设时间段内所述多个水质指标参数的环境下对目标水产品的免疫平衡方程,确定所述目标病原微生物的最大承受浓度值:2. The adaptive sterilization intensity control method according to claim 1 is characterized in that the maximum tolerance concentration value of the target pathogenic microorganism is determined based on the immune balance equation of the target pathogenic microorganism to the target aquatic product under the environment of the multiple water quality index parameters within the preset time period: 将随水质条件变化的免疫平衡方程为零的时刻确定为所述目标病原微生物对所述目标水产品存在免疫平衡的时刻;Determine the moment when the immune balance equation that changes with water quality conditions is zero as the moment when the target pathogenic microorganism has immune balance with the target aquatic product; 基于免疫平衡方程的平衡时刻对应的目标病原微生物浓度值,确定为所述目标病原微生物的最大承受浓度值。The target pathogenic microorganism concentration value corresponding to the equilibrium moment based on the immune equilibrium equation is determined as the maximum tolerable concentration value of the target pathogenic microorganism. 3.根据权利要求1所述的自适应杀菌强度调控方法,其特征在于,所述基于所述目标病原微生物的预设安全浓度阈值、所述最大承受浓度值和所述实际浓度值,确定所述目标病原微生物的浓度杀灭量,包括:3. The adaptive sterilization intensity control method according to claim 1 is characterized in that the concentration killing amount of the target pathogenic microorganism is determined based on the preset safety concentration threshold of the target pathogenic microorganism, the maximum tolerance concentration value and the actual concentration value, comprising: 对所述最大承受浓度值与预设安全浓度阈值进行差值计算,得到所述目标病原微生物的实际浓度控制目标值;Calculate the difference between the maximum tolerance concentration value and the preset safety concentration threshold to obtain the actual concentration control target value of the target pathogenic microorganism; 对所述实际浓度值与所述实际浓度控制目标值进行差值计算,得到所述目标病原微生物实际的浓度杀灭量。The difference between the actual concentration value and the actual concentration control target value is calculated to obtain the actual concentration killing amount of the target pathogenic microorganism. 4.根据权利要求1所述的自适应杀菌强度调控方法,其特征在于,所述基于所述浓度杀灭量,分级动态调控杀菌过程参数,对所述养殖水环境进行杀菌,包括:4. The adaptive sterilization intensity control method according to claim 1 is characterized in that the sterilization process parameters are dynamically controlled in stages based on the concentration killing amount to sterilize the aquaculture water environment, comprising: 若所述浓度杀灭量大于零,则基于所述浓度杀灭量与所述预设安全浓度阈值,确定杀菌强度等级;If the concentration killing amount is greater than zero, determining the sterilization intensity level based on the concentration killing amount and the preset safety concentration threshold; 基于灭活率和紫外线剂量之间的函数,确定不同杀菌强度等级下的杀菌功率和进水流量;Based on the function between inactivation rate and UV dose, the sterilization power and water flow rate under different sterilization intensity levels are determined; 基于所述不同杀菌强度等级下的杀菌功率和进水速度,对所述养殖水环境进行动态杀菌。Based on the sterilization power and water inlet speed under the different sterilization intensity levels, the aquaculture water environment is dynamically sterilized. 5.根据权利要求2所述的自适应杀菌强度调控方法,其特征在于,所述目标病原微生物在所述预设时间段内所述多个水质指标参数的环境下对目标水产品的免疫平衡方程及其各项参数是预先设定的,是通过如下方式确定的:5. The adaptive sterilization intensity control method according to claim 2 is characterized in that the immune balance equation and its parameters of the target pathogenic microorganisms to the target aquatic product under the environment of the multiple water quality index parameters within the preset time period are pre-set and determined in the following manner: 基于所述多个水质指标参数,确定目标病原微生物在所述预设时间段内的侵染活性;Based on the multiple water quality index parameters, determining the infection activity of the target pathogenic microorganism within the preset time period; 基于所述多个水质指标参数,确定目标水产品在所述预设时间段内的抗感染能力;Based on the multiple water quality index parameters, determining the anti-infection ability of the target aquatic product within the preset time period; 根据基于所述多个水质指标参数侵染活性和所述抗感染能力,预先确定所述目标病原微生物在所述预设时间段内所述多个水质指标参数的环境下对目标水产品的免疫平衡方程及各项参数。According to the infection activity based on the multiple water quality index parameters and the anti-infection ability, the immune balance equation and various parameters of the target pathogenic microorganisms to the target aquatic product under the environment of the multiple water quality index parameters within the preset time period are predetermined. 6.根据权利要求4所述的自适应杀菌强度调控方法,其特征在于,所述基于所述浓度杀灭量与所述预设安全浓度阈值,确定杀菌强度等级,包括:6. The adaptive sterilization intensity control method according to claim 4, characterized in that the sterilization intensity level is determined based on the concentration killing amount and the preset safety concentration threshold, comprising: 若所述浓度杀灭量大于第一预设倍的所述预设安全浓度阈值,则确定所述杀菌强度等级为一级杀菌强度等级;If the concentration killing amount is greater than the first preset times of the preset safety concentration threshold, the sterilization intensity level is determined to be the first level sterilization intensity level; 若所述浓度杀灭量小于所述第一预设倍的所述预设安全浓度阈值,且大于第二预设倍的所述预设安全浓度阈值,则确定所述杀菌强度等级为二级杀菌强度等级;If the concentration killing amount is less than the first preset times of the preset safety concentration threshold, and greater than the second preset times of the preset safety concentration threshold, the sterilization intensity level is determined to be the secondary sterilization intensity level; 若所述浓度杀灭量小于所述第二预设倍的所述预设安全浓度阈值,则确定所述杀菌强度等级为三级杀菌强度等级。If the concentration killing amount is less than the second preset times of the preset safety concentration threshold, the sterilization intensity level is determined to be the third sterilization intensity level. 7.根据权利要求4所述的自适应杀菌强度调控方法,其特征在于,所述基于灭活率和紫外线剂量之间的函数,确定不同杀菌强度等级下的杀菌功率和进水流量,包括:7. The adaptive sterilization intensity control method according to claim 4 is characterized in that the function between the inactivation rate and the ultraviolet dose is used to determine the sterilization power and water flow rate at different sterilization intensity levels, including: 若所述杀菌强度等级为所述一级杀菌强度等级,则根据所述灭活率和紫外线剂量之间的函数,依序确定第一杀菌功率和第一进水流量,分别使用相应加大的杀菌辐照对应的功率值和减小的水泵进水速度值为第一杀菌功率和第一进水流量;If the sterilization intensity level is the first sterilization intensity level, then according to the function between the inactivation rate and the ultraviolet dose, the first sterilization power and the first water inlet flow rate are determined in sequence, and the power value corresponding to the corresponding increased sterilization irradiation and the reduced water pump water inlet speed value are used as the first sterilization power and the first water inlet flow rate respectively; 若所述杀菌强度等级为所述二级杀菌强度等级,则根据所述灭活率和紫外线剂量之间的函数,依序确定第二杀菌功率和第二进水流量,分别使用正常的杀菌辐照量值对应的功率值和正常的水泵进水速度值为第二杀菌功率和第二进水流量;If the sterilization intensity level is the secondary sterilization intensity level, the second sterilization power and the second water inlet flow rate are determined in sequence according to the function between the inactivation rate and the ultraviolet dose, and the power value corresponding to the normal sterilization irradiation value and the normal water pump water inlet speed value are used as the second sterilization power and the second water inlet flow rate respectively; 若所述杀菌强度等级为所述三级杀菌强度等级,则根据所述灭活率和紫外线剂量之间的函数,依序确定第三杀菌功率和第三进水流量,分别使用相应减小的杀菌辐照对应的功率值和加快的水泵进水速度值为第三杀菌功率和第三进水流量;If the sterilization intensity level is the third sterilization intensity level, the third sterilization power and the third water inlet flow rate are determined in sequence according to the function between the inactivation rate and the ultraviolet dose, and the power value corresponding to the corresponding reduced sterilization irradiation and the accelerated water pump water inlet speed value are used as the third sterilization power and the third water inlet flow rate respectively; 所述灭活率和紫外线剂量的函数是基于紫外线剂量-灭活率曲线预先构建的。The function of the inactivation rate and the UV dose is pre-constructed based on the UV dose-inactivation rate curve. 8.根据权利要求4所述的自适应杀菌强度调控方法,其特征在于,在基于所述不同杀菌强度等级下的杀菌功率和进水速度,对所述养殖水环境进行动态杀菌时,针对杀菌功率和进水速度执行如下步骤:8. The adaptive sterilization intensity control method according to claim 4 is characterized in that when the aquaculture water environment is dynamically sterilized based on the sterilization power and water inlet speed at different sterilization intensity levels, the following steps are performed with respect to the sterilization power and water inlet speed: 若所述杀菌强度等级为所述一级杀菌强度等级,则根据第一杀菌功率和第一进水流量,对所述养殖水环境进行杀菌;所述第一杀菌功率是在所述一级杀菌强度等级下的杀菌功率,所述第一进水流量是在所述一级杀菌强度等级下的进水流量;If the sterilization intensity level is the first sterilization intensity level, the aquaculture water environment is sterilized according to the first sterilization power and the first water inlet flow rate; the first sterilization power is the sterilization power at the first sterilization intensity level, and the first water inlet flow rate is the water inlet flow rate at the first sterilization intensity level; 若所述杀菌强度等级为所述二级杀菌强度等级,则根据第二杀菌功率和第二进水流量,对所述养殖水环境进行杀菌;所述第二杀菌功率是在所述二级杀菌强度等级下的杀菌功率,所述第二进水流量是在所述二级杀菌强度等级下的进水流量;If the sterilization intensity level is the secondary sterilization intensity level, the aquaculture water environment is sterilized according to the second sterilization power and the second water inlet flow rate; the second sterilization power is the sterilization power at the secondary sterilization intensity level, and the second water inlet flow rate is the water inlet flow rate at the secondary sterilization intensity level; 若所述杀菌强度等级为所述三级杀菌强度等级,则根据第三杀菌功率和第三进水流量,对所述养殖水环境进行杀菌;所述第三杀菌功率是在所述三级杀菌强度等级下的杀菌功率,所述第三进水流量是在所述三级杀菌强度等级下的进水流量。If the sterilization intensity level is the third sterilization intensity level, the aquaculture water environment is sterilized according to the third sterilization power and the third water inlet flow rate; the third sterilization power is the sterilization power at the third sterilization intensity level, and the third water inlet flow rate is the water inlet flow rate at the third sterilization intensity level. 9.一种自适应杀菌强度调控装置,其特征在于,包括供电模块、水体环境监测模块、模型模块、最大可承受浓度计算模块、浓度杀灭量计算模块、控制模块、杀菌强度分级调控模块、紫外线杀菌功率调节模组和水泵变频电机等流量控制模组;其中:9. An adaptive sterilization intensity control device, characterized in that it includes a power supply module, a water environment monitoring module, a model module, a maximum tolerable concentration calculation module, a concentration killing amount calculation module, a control module, a sterilization intensity classification control module, an ultraviolet sterilization power adjustment module and a water pump variable frequency motor and other flow control modules; wherein: 水体环境监测模块,用于监测并获取预设时间段内养殖水环境的多个水质指标参数以及当前时刻目标病原微生物的实际浓度值;The water environment monitoring module is used to monitor and obtain multiple water quality index parameters of the aquaculture water environment within a preset time period and the actual concentration value of the target pathogenic microorganism at the current moment; 模型模块,用于存储目标病原微生物在水质参数下对目标水产品的免疫平衡方程、灭活率和紫外线剂量的函数以及免疫平衡方程中的侵染活性、抗感染能力中由目标水产品的结构所决定的常数各项指标值;最优的间歇时间值、预设安全浓度阈值,还包括处理水量、处理时间、预防病原种类以及紫外线杀菌装置的结构参数的存储,并完成相应的更新。The model module is used to store the immune balance equation of the target pathogenic microorganisms to the target aquatic products under water quality parameters, the function of the inactivation rate and ultraviolet dose, and the infection activity and anti-infection ability in the immune balance equation, and the constant index values determined by the structure of the target aquatic products; the optimal intermittent time value, the preset safety concentration threshold, and also includes the storage of the treated water volume, treatment time, prevented pathogen types and structural parameters of the ultraviolet disinfection device, and completes the corresponding updates. 最大可承受浓度计算模块,用于基于目标病原微生物在所述预设时间段内所述多个水质指标参数对应环境下对目标水产品的免疫平衡方程,计算并确定所述目标病原微生物的最大承受浓度值;A maximum tolerable concentration calculation module, for calculating and determining a maximum tolerable concentration value of the target pathogenic microorganism based on an immune balance equation of the target pathogenic microorganism to the target aquatic product under the environment corresponding to the multiple water quality index parameters within the preset time period; 浓度杀灭量计算模块,用于根据水体环境监测模块获取到的水质参数空间和目标病原微生物的浓度值以及最大可承受浓度计算模块计算出的最大承受浓度值进行计算,得到目标病原微生物的浓度杀灭量。The concentration killing amount calculation module is used to calculate the concentration killing amount of the target pathogenic microorganism based on the water quality parameter space and the concentration value of the target pathogenic microorganism obtained by the water environment monitoring module and the maximum tolerable concentration value calculated by the maximum tolerable concentration calculation module, so as to obtain the concentration killing amount of the target pathogenic microorganism. 控制模块,用于执行上述的方法,完成自适应杀菌过程。The control module is used to execute the above method to complete the adaptive sterilization process. 杀菌强度分级调控模块,用于基于所述浓度杀灭量,分级动态调控杀菌过程参数,指导紫外线杀菌功率调节模组和水泵变频电机等流量控制模组对所述养殖水环境进行杀菌。The sterilization intensity graded control module is used to dynamically control the sterilization process parameters based on the concentration killing amount, and guide the ultraviolet sterilization power adjustment module and the flow control modules such as the water pump variable frequency motor to sterilize the aquaculture water environment. 10.一种设备,所述设备包括电子设备,所述电子设备包括存储器、处理器及存储在所述存储器上并可在所述处理器上运行的计算机程序,其特征在于,所述处理器执行所述计算机程序时实现如权利要求1至8任一项所述自适应杀菌强度调控方法的步骤。10. A device, comprising an electronic device, wherein the electronic device comprises a memory, a processor, and a computer program stored in the memory and executable on the processor, wherein when the processor executes the computer program, the steps of the adaptive sterilization intensity control method as described in any one of claims 1 to 8 are implemented.
CN202411284420.7A 2024-09-13 2024-09-13 A self-adaptive sterilization intensity control method, device and electronic equipment Pending CN119059608A (en)

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