CN117192015A - Risk assessment method and system for pesticide residues in medlar - Google Patents

Risk assessment method and system for pesticide residues in medlar Download PDF

Info

Publication number
CN117192015A
CN117192015A CN202311162656.9A CN202311162656A CN117192015A CN 117192015 A CN117192015 A CN 117192015A CN 202311162656 A CN202311162656 A CN 202311162656A CN 117192015 A CN117192015 A CN 117192015A
Authority
CN
China
Prior art keywords
medlar
samples
pesticide
risk
different batches
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN202311162656.9A
Other languages
Chinese (zh)
Inventor
牛艳
吴燕
左忠
杨静
杨春霞
刘霞
苟春林
王晓菁
张萍
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Ningxia Institute of Quality Standards and Testing Technology for Agro Products of Ningxia Agricultural Product Quality Monitoring Center
Original Assignee
Ningxia Institute of Quality Standards and Testing Technology for Agro Products of Ningxia Agricultural Product Quality Monitoring Center
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Ningxia Institute of Quality Standards and Testing Technology for Agro Products of Ningxia Agricultural Product Quality Monitoring Center filed Critical Ningxia Institute of Quality Standards and Testing Technology for Agro Products of Ningxia Agricultural Product Quality Monitoring Center
Priority to CN202311162656.9A priority Critical patent/CN117192015A/en
Publication of CN117192015A publication Critical patent/CN117192015A/en
Pending legal-status Critical Current

Links

Classifications

    • 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
    • Y02PCLIMATE CHANGE MITIGATION TECHNOLOGIES IN THE PRODUCTION OR PROCESSING OF GOODS
    • Y02P90/00Enabling technologies with a potential contribution to greenhouse gas [GHG] emissions mitigation
    • Y02P90/30Computing systems specially adapted for manufacturing

Landscapes

  • Automatic Analysis And Handling Materials Therefor (AREA)

Abstract

The application discloses a risk assessment method and a system for pesticide residues in medlar, relates to the field of agriculture, and solves the problem that the risk of pesticide residues in medlar products cannot be assessed and known in daily purchase, wherein the risk assessment method comprises the following steps: the data acquisition module acquires real-time sample data of the medlar samples in the same batch; the data analysis module performs data analysis on the medlar samples in different batches to obtain product risk values or sample abnormal signals of the medlar samples in different batches; the operation monitoring module monitors pesticide operation conditions of the medlar samples in different batches to obtain operation risk values of the medlar samples in different batches; the intelligent evaluation module evaluates the risk level of pesticide residues in medlar samples in different batches; the user terminal scans the batch code on the medlar packaging bag, and the information comparison module compares the identification information of the medlar packaging bag.

Description

Risk assessment method and system for pesticide residues in medlar
Technical Field
The application belongs to the field of agriculture, relates to a risk assessment technology, and in particular relates to a risk assessment method and a risk assessment system for pesticide residues in medlar.
Background
Lycium barbarum, a perennial woody plant of Lycium of Solanaceae, has weak branches, and is bent or sagged in an arcuate shape, and is light gray; the blade is oval; flowers grow singly or doubly on long branches and are grown on leaf axils; the fruit is oval berry red; the flowering period is 6-7 months; the fruit period is 8-10 months. The medlar needs to be sprayed with pesticide in the daily growth process, so that the residual pesticide dosage in the medlar needs to be detected in the picking and subsequent use processes of the medlar so as to ensure that the medlar can be safely eaten.
When buying medlar products in daily life, although the medlar products put on shelf have been subjected to food safety quality inspection, a part of medlar products still have trace pesticide dosage, and the resistances to pesticides are different due to different ages of medlar audience groups, so how to evaluate and know the pesticide residue risk of the medlar products is important during buying;
therefore, we propose a risk assessment method and system for pesticide residues in medlar.
Disclosure of Invention
The application aims at: in order to solve the above problems, a risk assessment method and a risk assessment system for pesticide residues in wolfberry are provided to solve the problems in the prior art.
In order to achieve the above purpose, the present application adopts the following technical scheme:
a risk assessment method for pesticide residues in medlar is specifically as follows:
step S100, a data acquisition module acquires real-time sample data of medlar samples in different batches, the real-time sample data is sent to a server, and the server sends the real-time sample data to a data analysis module;
step S200, the data analysis module performs data analysis on the medlar samples in different batches to obtain product risk values or sample abnormal signals of the medlar samples in different batches, and feeds back the product risk values or sample abnormal signals to the server, if the server receives the sample abnormal signals, no operation is performed, and if the server receives the product risk values of the medlar samples in different batches, the product risk values are sent to the intelligent evaluation module;
step S300, the storage module sends stored pesticide operation data of different batches of medlar samples to the operation monitoring module, the operation monitoring module monitors pesticide operation conditions of the different batches of medlar samples, operation risk values of the different batches of medlar samples are obtained and fed back to the server, and the server sends the operation risk values of the different batches of medlar samples to the intelligent evaluation module;
step S400, the intelligent evaluation module evaluates the risk levels of pesticide residues in the medlar samples in different batches, the risk levels of the pesticide residues in the medlar samples in different batches are obtained through evaluation and fed back to the server, the server sends the risk levels of the pesticide residues in the medlar samples in different batches to the storage module, and the storage module stores the risk levels of the pesticide residues in the medlar samples in different batches;
step S500, the user terminal scans the batch code on the medlar packaging bag and uploads the batch code to the server, the server sends the batch code to the information comparison module, the information comparison module compares the identification information of the medlar packaging bag to obtain risk grade feedback of the medlar packaging bag to the server, the server sends the risk grade of the medlar packaging bag to the user terminal, and the user terminal checks the risk grade of the medlar packaging bag.
Further, the real-time sample data are slurry real-time weight values of medlar samples in different batches and real-time doses of each residual pesticide.
Further, the data analysis process of the data analysis module is specifically as follows:
acquiring a slurry real-time weight value of any medlar sample in the same batch and a real-time dose of each residual pesticide, and summing and comparing the residual pesticide real-time dose of each residual pesticide with the slurry real-time weight value to obtain a residual pesticide dose ratio of any medlar sample in the same batch;
if the residual pesticide dosage ratio is greater than or equal to the second preset pesticide dosage ratio, generating a sample abnormal signal;
if the residual pesticide dosage ratio is smaller than the second preset pesticide dosage ratio, carrying out the subsequent steps;
putting another wolfberry sample in the same batch into the soaking liquid for soaking, recording the beginning soaking time of the wolfberry sample, then obtaining the real-time dose of each residual pesticide in the soaked wolfberry sample, recording the ending soaking time of the wolfberry sample, and obtaining the soaking pesticide dose ratio of the soaked wolfberry sample by adding and summing the real-time dose of each residual pesticide in the soaked wolfberry sample and comparing the real-time weight value of the slurry; wherein the soaking liquid is salt water, clear water and black tea water;
if the soaking pesticide dosage ratio is smaller than the first preset pesticide dosage ratio, subtracting the soaking starting time from the soaking ending time to obtain the residual pesticide removing duration of the soaked medlar sample; wherein the value of the first preset pesticide dosage ratio is smaller than the value of the second preset pesticide dosage ratio;
and calculating product risk values of different batches of medlar samples.
Further, the pesticide operation data are the pesticide spraying times of the medlar samples in different batches, and the spraying amount and the spraying time of each pesticide spraying.
Further, the monitoring process of the operation monitoring module is specifically as follows:
acquiring pesticide spraying times of medlar samples in the same batch;
then, the spraying quantity of the medlar samples in the same batch is obtained when each pesticide is sprayed, and the spraying quantity of the medlar samples in the same batch is obtained by adding and summing the spraying quantity of each pesticide spraying;
finally, the spraying time of each pesticide spraying of the same batch of medlar samples is obtained, the time intervals of adjacent spraying time are calculated to obtain a plurality of groups of pesticide spraying interval duration, and the pesticide spraying interval duration of the plurality of groups of pesticide spraying interval duration is added and summed to obtain an average value to obtain the pesticide spraying interval average duration of the same batch of medlar samples;
and calculating the operation risk values of the medlar samples in different batches.
Further, the evaluation process of the intelligent evaluation module is specifically as follows;
obtaining product risk values and operation risk values of medlar samples in different batches;
calculating risk assessment values of medlar samples in different batches;
if the risk assessment value is greater than or equal to the second risk assessment threshold, the risk level of pesticide residues in the medlar samples in different batches is the first risk level;
if the risk assessment value is smaller than the second risk assessment threshold value and larger than or equal to the first risk assessment threshold value, the risk level of pesticide residues in the medlar samples in different batches is the second risk level;
and if the risk assessment value is smaller than the first risk assessment threshold, the risk level of pesticide residues in the medlar samples in different batches is a third risk level.
Further, the first risk rating threshold is less than the first risk rating threshold, the degree of risk of the first risk level is greater than the degree of risk of the second risk level, and the degree of risk of the second risk level is greater than the degree of risk of the third risk level.
Further, the comparison process of the information comparison module is specifically as follows:
comparing the batch code on the medlar packaging bag with the batch numbers of medlar samples in different batches of the storage module;
if the batch code is matched with the batch number, acquiring a risk level corresponding to the medlar sample according to the batch number;
and (5) marking the risk level corresponding to the medlar sample as the risk level of the medlar packaging bag.
A risk assessment system for pesticide residues in medlar comprises a data acquisition module, a data analysis module, an intelligent evaluation module, an operation monitoring module, an information comparison module, a storage module, a user terminal and a server;
the data acquisition module is used for acquiring real-time sample data of medlar samples in different batches and sending the real-time sample data to the server, and the server sends the real-time sample data to the data analysis module;
the data analysis module is used for carrying out data analysis on medlar samples in different batches to obtain product risk values of medlar samples in different batches or generating sample abnormal signals and feeding the sample abnormal signals back to the server, if the server receives the sample abnormal signals, no operation is carried out, and if the server receives the product risk values of medlar samples in different batches, the product risk values of medlar samples in different batches are sent to the intelligent evaluation module;
the storage module is used for storing pesticide operation data of medlar samples in different batches and sending the pesticide operation data to the operation monitoring module;
the operation monitoring module is used for monitoring pesticide operation conditions of different batches of medlar samples, obtaining operation risk values of the different batches of medlar samples and feeding back the operation risk values to the server, and the server sends the operation risk values of the different batches of medlar samples to the intelligent evaluation module;
the intelligent evaluation module is used for evaluating the risk levels of pesticide residues in the medlar samples in different batches, obtaining the risk levels of the pesticide residues in the medlar samples in different batches, feeding back the risk levels of the pesticide residues in the medlar samples in different batches to the server, sending the risk levels of the pesticide residues in the medlar samples in different batches to the storage module by the server, and storing the risk levels of the pesticide residues in the medlar samples in different batches by the storage module;
the user terminal is used for scanning the batch code on the medlar packaging bag and uploading the batch code to the server, and the server sends the batch code to the information comparison module;
the information comparison module is used for comparing the identification information of the medlar packaging bags, the risk level of the medlar packaging bags is obtained through comparison and fed back to the server, and the server sends the risk level of the medlar packaging bags to the user terminal;
the user terminal is used for checking the risk level of the medlar packaging bag.
Compared with the prior art, the application has the beneficial effects that:
according to the application, firstly, data analysis is carried out on medlar samples of different batches through a data analysis module to obtain product risk values or sample abnormal signals of the medlar samples of different batches, if the product risk values of the medlar samples of different batches are obtained, the product risk values are sent to an intelligent evaluation module, meanwhile, the pesticide operation conditions of the medlar samples of different batches are monitored by utilizing an operation monitoring module, the operation risk values of the medlar samples of different batches are obtained and sent to the intelligent evaluation module through a server, the intelligent evaluation module evaluates the risk grades of pesticide residues in the medlar samples of different batches, a storage module stores the risk grades of pesticide residues in the medlar samples of different batches, and when the risk grades are actually determined, a user terminal scans the batch codes on medlar packaging bags and sends to an information comparison module, and the information comparison module compares the identification information of the medlar packaging bags to obtain the risk grades of the medlar packaging bags.
Drawings
The present application is further described below with reference to the accompanying drawings for the convenience of understanding by those skilled in the art.
FIG. 1 is a flow chart of the method of the present application;
fig. 2 is an overall system block diagram of the present application.
Detailed Description
The technical solutions of the present application will be clearly and completely described in connection with the embodiments, and it is obvious that the described embodiments are only some embodiments of the present application, not all embodiments. All other embodiments, which can be made by those skilled in the art based on the embodiments of the application without making any inventive effort, are intended to be within the scope of the application.
Example 1
Referring to fig. 1, the present application provides a risk assessment method for pesticide residues in wolfberry, which specifically comprises the following steps:
step S100, a data acquisition module acquires real-time sample data of medlar samples in different batches, the real-time sample data is sent to a server, and the server sends the real-time sample data to a data analysis module;
the real-time sample data are slurry real-time weight values of medlar samples in different batches and real-time doses of each residual pesticide; in actual collection, the medlar samples are required to be ensured to be in the same batch, so that the real-time weight value of the slurry of the medlar samples and the real-time dosage of the residual pesticides are ensured to be on the same starting line, the residual pesticides comprise imidacloprid, acetamiprid, carbendazim, chlorpyrifos, cypermethrin, cyhalothrin, difenoconazole and pyridaben, but are not limited to the same, in practice, 20mL of acetonitrile and crushed medlar can be added into a test tube for centrifugation, then 300 mu L of the centrifuged medlar upper layer is filtered into a 1.5mL of small bottle through a 0.45 mu m polyvinylidene fluoride (PVDF) injector filter, and finally the liquid in the small bottle is detected and analyzed through an ACQUITY ultra-high performance liquid chromatography system and a QT 5500 triple quadrupole mass spectrometer, so that the real-time dosage of the residual pesticides in the medlar samples is obtained;
step S200, the data analysis module performs data analysis on the medlar samples in different batches to obtain product risk values or sample abnormal signals of the medlar samples in different batches, and feeds back the product risk values or sample abnormal signals to the server, if the server receives the sample abnormal signals, no operation is performed, and if the server receives the product risk values of the medlar samples in different batches, the product risk values are sent to the intelligent evaluation module;
in step S200, the data analysis process of the data analysis module specifically includes the following steps:
step S201, obtaining the real-time weight value of the slurry of any medlar sample in the same batch and the real-time dose of each residual pesticide, and obtaining the residual pesticide dose ratio CNi of any medlar sample in the same batch by summing and comparing the real-time weight values of the residual pesticides of each residual pesticide, wherein i is the batch number of medlar samples, the batch number can be composed of pure numbers, can be composed of English, and the like;
step S202, if the residual pesticide dose ratio is greater than or equal to a second preset pesticide dose ratio, generating a sample abnormal signal;
step S203, if the residual pesticide dose ratio is smaller than the second preset pesticide dose ratio, carrying out the subsequent steps;
step S204, another medlar sample in the same batch is put into the soaking liquid for soaking, the beginning soaking time of the medlar sample is recorded, then the real-time dose of each residual pesticide in the soaked medlar sample is obtained, the ending soaking time of the medlar sample is recorded, and the real-time dose of each residual pesticide in the soaked medlar sample is added, summed and compared with the real-time weight value of the slurry to obtain the soaking pesticide dose ratio of the soaked medlar sample; wherein the soaking liquid can be salt water, clear water, black tea water, etc.;
step S205, if the soaked pesticide dose ratio is smaller than the first preset pesticide dose ratio, the soaked time is subtracted from the soaking ending time to obtain the residual pesticide removal duration CTi of the soaked medlar sample; wherein the value of the first preset pesticide dosage ratio is smaller than the value of the second preset pesticide dosage ratio;
step S206, calculating the product risk value CFi of the medlar samples of different batches according to the formula CFi= (CNi×a1+CTi×a2)/(a1+a2); wherein a1 and a2 are proportionality coefficients with fixed values, and the values of a1 and a2 are larger than zero;
the daily removal method of the pesticide residue in the medlar comprises the following steps:
(1) The salt water soaking method is also a simple method. The salt is used for soaking the medlar to remove most pesticide residues. Adding a small spoon of salt into cold water, soaking fructus Lycii in salt water for 5-10 min, and cleaning with clear water; (2) the cold bubble method is a relatively common method. Soaking fructus Lycii in clear water for 30 min, and washing with flowing water for several times, wherein soap or detergent is not suitable for cleaning, which is easy to remain in fructus Lycii; (3) Black tea infusion is also a good method for removing pesticides. The medlar is soaked in the black tea for about 5 minutes, so that most pesticide residues in the medlar can be removed. If green tea or other tea is used for soaking the medlar, other flavors are left on the medlar, and eating is not recommended;
step S300, the storage module sends stored pesticide operation data of different batches of medlar samples to the operation monitoring module, the operation monitoring module monitors pesticide operation conditions of the different batches of medlar samples, operation risk values of the different batches of medlar samples are obtained and fed back to the server, and the server sends the operation risk values of the different batches of medlar samples to the intelligent evaluation module;
the pesticide operation data is the pesticide spraying times of medlar samples in different batches, and the spraying quantity and the spraying time of each pesticide spraying, and the pesticide operation data is related data in the period from planting to picking of medlar;
in step S300, the monitoring process of the job monitoring module specifically includes the following steps:
step S301, acquiring the pesticide spraying times of the medlar samples in the same batch, and marking the pesticide spraying times as PCi;
step S302, the spraying quantity of the same batch of medlar samples when each pesticide is sprayed is obtained, and the spraying quantity of each pesticide is added and summed to obtain the pesticide spraying quantity PLi of the same batch of medlar samples;
step S303, finally, the spraying time of the same batch of medlar samples when each pesticide is sprayed is obtained, the time intervals of adjacent spraying time are calculated to obtain a plurality of groups of pesticide spraying interval duration, and the pesticide spraying interval duration of the plurality of groups of pesticide spraying interval duration are added, summed and averaged to obtain the pesticide spraying interval average duration PJTi of the same batch of medlar samples;
step S305, calculating the operation risk value ZFi of the medlar samples of different batches according to the formula ZFi = (pci+pli)/PJTi;
step S400, the intelligent evaluation module evaluates the risk levels of pesticide residues in the medlar samples in different batches, the risk levels of the pesticide residues in the medlar samples in different batches are obtained through evaluation and fed back to the server, the server sends the risk levels of the pesticide residues in the medlar samples in different batches to the storage module, and the storage module stores the risk levels of the pesticide residues in the medlar samples in different batches;
in this embodiment, the evaluation process of the intelligent evaluation module in the step S400 is specifically as follows;
step S401, obtaining the product risk values CFi and the operation risk values ZFi of the medlar samples in different batches obtained by the calculation;
step S402, calculating risk assessment values FPi for different batches of medlar samples using the formula FPi =cfi×α+ ZFi ×β; wherein, alpha and beta are weight coefficients with fixed values, and alpha+beta=1;
step S403, if the risk assessment value is greater than or equal to the second risk assessment threshold, the risk level of the pesticide residue in the medlar samples of different batches is the first risk level, if the risk assessment value is less than the second risk assessment threshold and greater than or equal to the first risk assessment threshold, the risk level of the pesticide residue in the medlar samples of different batches is the second risk level, and if the risk assessment value is less than the first risk assessment threshold, the risk level of the pesticide residue in the medlar samples of different batches is the third risk level;
the first risk assessment threshold is smaller than the first risk assessment threshold, the risk degree of the first risk level is larger than the risk degree of the second risk level, and the risk degree of the second risk level is larger than the risk degree of the third risk level;
step S500, the user terminal scans the batch code on the medlar packaging bag and uploads the batch code to the server, the server sends the batch code to the information comparison module, the information comparison module compares the identification information of the medlar packaging bag to obtain risk level feedback of the medlar packaging bag to the server, the server sends the risk level of the medlar packaging bag to the user terminal, and the user terminal checks the risk level of the medlar packaging bag;
specifically, the user terminal is configured to input personal information by using a person, and send the personal information to the server, where the personal information is a name, a mobile phone number, etc. of the person;
in step S500, the comparison process of the information comparison module specifically includes the following steps:
step S501, comparing the batch code on the medlar packaging bag with the batch numbers of medlar samples in different batches of the storage module, wherein the comparison method can be used for comparing keywords or contours;
step S502, if the batch code is matched with the batch number, acquiring a risk level corresponding to the medlar sample according to the batch number;
step S503, the risk level corresponding to the medlar sample is marked as the risk level of the medlar packaging bag.
Example two
Based on another concept of the same application, referring to fig. 2, a risk assessment system for pesticide residues in medlar is now provided, which comprises a data acquisition module, a data analysis module, an intelligent assessment module, an operation monitoring module, an information comparison module, a storage module, a user terminal and a server;
in this embodiment, the data acquisition module is configured to acquire real-time sample data of medlar samples in different batches, and send the real-time sample data to the server, where the server sends the real-time sample data to the data analysis module;
the real-time sample data are slurry real-time weight values of medlar samples in different batches and real-time doses of each residual pesticide; in actual collection, the medlar samples are required to be ensured to be in the same batch, so that the real-time weight value of the slurry of the medlar samples and the real-time dosage of the residual pesticides are ensured to be on the same starting line, the residual pesticides comprise imidacloprid, acetamiprid, carbendazim, chlorpyrifos, cypermethrin, cyhalothrin, difenoconazole and pyridaben, but are not limited to the same, in practice, 20mL of acetonitrile and crushed medlar can be added into a test tube for centrifugation, then 300 mu L of the centrifuged medlar upper layer is filtered into a 1.5mL of small bottle through a 0.45 mu m polyvinylidene fluoride (PVDF) injector filter, and finally the liquid in the small bottle is detected and analyzed through an ACQUITY ultra-high performance liquid chromatography system and a QT 5500 triple quadrupole mass spectrometer, so that the real-time dosage of the residual pesticides in the medlar samples is obtained;
the data analysis module is used for carrying out data analysis on medlar samples in different batches, and the data analysis process is specifically as follows:
acquiring a slurry real-time weight value of any medlar sample in the same batch and a real-time dose of each residual pesticide, adding and comparing the real-time doses of each residual pesticide to the slurry real-time weight value to obtain a residual pesticide dose ratio CNi of any medlar sample in the same batch, wherein i is a batch number of medlar samples, and the batch number can be composed of pure numbers, english, and the like;
if the residual pesticide dosage ratio is greater than or equal to the second preset pesticide dosage ratio, generating a sample abnormal signal;
if the residual pesticide dosage ratio is smaller than the second preset pesticide dosage ratio, carrying out the subsequent steps;
putting another wolfberry sample in the same batch into the soaking liquid for soaking, recording the beginning soaking time of the wolfberry sample, then obtaining the real-time dose of each residual pesticide in the soaked wolfberry sample, recording the ending soaking time of the wolfberry sample, and obtaining the soaking pesticide dose ratio of the soaked wolfberry sample by adding and summing the real-time dose of each residual pesticide in the soaked wolfberry sample and comparing the real-time weight value of the slurry; wherein the soaking liquid can be salt water, clear water, black tea water, etc.;
if the soaking pesticide dosage ratio is smaller than the first preset pesticide dosage ratio, subtracting the soaking starting time from the soaking ending time to obtain the residual pesticide removal duration CTi of the soaked medlar sample; wherein the value of the first preset pesticide dosage ratio is smaller than the value of the second preset pesticide dosage ratio;
calculating to obtain product risk values CFi of different batches of medlar samples through a formula CFi= (CNi×a1+CTi×a2)/(a1+a2); wherein a1 and a2 are proportionality coefficients with fixed values, and the values of a1 and a2 are larger than zero;
the daily removal method of the residual pesticide in the medlar comprises the following steps:
(1) The salt water soaking method is also a simple method. The salt is used for soaking the medlar to remove most pesticide residues. Adding a small spoon of salt into cold water, soaking fructus Lycii in salt water for 5-10 min, and cleaning with clear water; (2) the cold bubble method is a relatively common method. Soaking fructus Lycii in clear water for 30 min, and washing with flowing water for several times, wherein soap or detergent is not suitable for cleaning, which is easy to remain in fructus Lycii; (3) Black tea infusion is also a good method for removing pesticides. The medlar is soaked in the black tea for about 5 minutes, so that most pesticide residues in the medlar can be removed. If green tea or other tea is used for soaking the medlar, other flavors are left on the medlar, and eating is not recommended;
the data analysis module feeds back product risk values or sample abnormal signals of the medlar samples in different batches to the server, if the server receives the sample abnormal signals, no operation is performed, and if the server receives the product risk values of the medlar samples in different batches, the product risk values are sent to the intelligent evaluation module;
in this embodiment, the server is connected with a storage module, and the storage module is used for storing pesticide operation data of medlar samples in different batches and sending the pesticide operation data to the operation monitoring module;
the pesticide operation data is the pesticide spraying times of medlar samples in different batches, and the spraying quantity and the spraying time of each pesticide spraying, and the pesticide operation data is related data in the period from planting to picking of medlar;
the operation monitoring module is used for monitoring pesticide operation conditions of medlar samples in different batches, and the monitoring process is specifically as follows:
acquiring pesticide spraying times of the medlar samples in the same batch, and marking the pesticide spraying times as PCi;
then, the spraying quantity of the medlar samples in the same batch is obtained when each pesticide is sprayed, and the spraying quantity of each pesticide is added and summed to obtain the pesticide spraying quantity PLi of the medlar samples in the same batch;
finally, the spraying time of each pesticide spraying of the same batch of medlar samples is obtained, the time intervals of adjacent spraying time are calculated to obtain a plurality of groups of pesticide spraying interval duration, and the pesticide spraying interval duration of the plurality of groups of pesticide spraying interval duration is added and summed to obtain an average value to obtain the pesticide spraying interval average duration PJTi of the same batch of medlar samples;
calculating to obtain operation risk values ZFi of medlar samples in different batches through a formula ZFi = (PCi+PLi)/PJTi;
the operation monitoring module feeds back operation risk values of the medlar samples in different batches to the server, and the server sends the operation risk values of the medlar samples in different batches to the intelligent evaluation module;
the intelligent evaluation module is used for evaluating the risk level of pesticide residues in medlar samples in different batches, and the evaluation process is specifically as follows;
obtaining the product risk values CFi and the operation risk values ZFi of the medlar samples in different batches through calculation;
calculating risk scores FPi for different batches of medlar samples using the formula FPi =cfi×α+ ZFi ×β; wherein, alpha and beta are weight coefficients with fixed values, and alpha+beta=1;
if the risk assessment value is greater than or equal to the second risk assessment threshold, the risk level of pesticide residues in the medlar samples in different batches is the first risk level;
if the risk assessment value is smaller than the second risk assessment threshold value and larger than or equal to the first risk assessment threshold value, the risk level of pesticide residues in the medlar samples in different batches is the second risk level;
if the risk assessment value is smaller than the first risk assessment threshold, the risk level of pesticide residues in the medlar samples in different batches is a third risk level; the first risk assessment threshold is smaller than the first risk assessment threshold, the risk degree of the first risk level is larger than the risk degree of the second risk level, and the risk degree of the second risk level is larger than the risk degree of the third risk level;
the intelligent evaluation module feeds back the risk levels of pesticide residues in the medlar samples in different batches to the server, the server sends the risk levels of the pesticide residues in the medlar samples in different batches to the storage module, and the storage module is used for storing the risk levels of the pesticide residues in the medlar samples in different batches;
specifically, the user terminal is configured to input personal information by using a person, and send the personal information to the server, where the personal information is a name, a mobile phone number, etc. of the person;
in a specific implementation, the user terminal is used for scanning the batch code on the medlar packaging bag and uploading the batch code to the server, the server sends the batch code to the information comparison module, and the information comparison module is used for comparing the identification information of the medlar packaging bag, wherein the comparison process is specifically as follows:
comparing the batch code on the medlar packaging bag with the batch numbers of medlar samples in different batches of the storage module, wherein the comparison method can be used for comparing keywords or contours;
if the batch code is matched with the batch number, acquiring a risk level corresponding to the medlar sample according to the batch number;
the risk level corresponding to the medlar sample is marked as the risk level of the medlar packaging bag;
the information comparison module feeds back the risk level of the medlar packaging bag to the server, the server sends the risk level of the medlar packaging bag to the user terminal, and the user terminal is used for checking the risk level of the medlar packaging bag;
in the application, if a corresponding calculation formula appears, the calculation formulas are all dimensionality-removed and numerical calculation, and the weight coefficient, the proportion coefficient and other coefficients in the formulas are set to be a result value obtained by quantizing each parameter, so long as the proportion relation between the parameter and the result value is not influenced.
The preferred embodiments of the application disclosed above are intended only to assist in the explanation of the application. The preferred embodiments are not intended to be exhaustive or to limit the application to the precise form disclosed. Obviously, many modifications and variations are possible in light of the above teaching. The embodiments were chosen and described in order to best explain the principles of the application and the practical application, to thereby enable others skilled in the art to best understand and utilize the application. The application is limited only by the claims and the full scope and equivalents thereof.

Claims (9)

1. The risk assessment method for pesticide residues in medlar is characterized by comprising the following steps of:
step S100, a data acquisition module acquires real-time sample data of medlar samples in the same batch, and sends the real-time sample data to a data analysis module through a server;
step S200, the data analysis module performs data analysis on the medlar samples in different batches to obtain product risk values or sample abnormal signals of the medlar samples in different batches, if the sample abnormal signals are generated, no operation is performed, and if the product risk values of the medlar samples in different batches are obtained, the product risk values are sent to the intelligent evaluation module;
step S300, the storage module sends stored pesticide operation data of different batches of medlar samples to the operation monitoring module, the operation monitoring module monitors pesticide operation conditions of the different batches of medlar samples, and operation risk values of the different batches of medlar samples are obtained and sent to the intelligent evaluation module through the server;
step S400, the intelligent evaluation module evaluates the risk levels of pesticide residues in the medlar samples in different batches and sends the risk levels to the storage module through the server, and the storage module stores the risk levels of pesticide residues in the medlar samples in different batches;
step S500, the user terminal scans the batch code on the medlar packaging bag and sends the batch code to the information comparison module through the server, the information comparison module compares the identification information of the medlar packaging bag, the obtained risk level of the medlar packaging bag is sent to the user terminal through the server, and the user terminal checks the risk level of the medlar packaging bag.
2. The method for risk assessment of pesticide residues in wolfberry according to claim 1, wherein the real-time sample data is a real-time weight value of slurry of wolfberry samples of different batches, and a real-time dose of each residual pesticide.
3. The risk assessment method for pesticide residues in medlar according to claim 1, wherein the data analysis process of the data analysis module is specifically as follows:
acquiring a slurry real-time weight value of any medlar sample in the same batch and a real-time dose of each residual pesticide, and summing and comparing the residual pesticide real-time dose of each residual pesticide with the slurry real-time weight value to obtain a residual pesticide dose ratio of any medlar sample in the same batch;
if the residual pesticide dosage ratio is greater than or equal to the second preset pesticide dosage ratio, generating a sample abnormal signal;
if the residual pesticide dosage ratio is smaller than the second preset pesticide dosage ratio, carrying out the subsequent steps;
putting another wolfberry sample in the same batch into the soaking liquid for soaking, recording the beginning soaking time of the wolfberry sample, then obtaining the real-time dose of each residual pesticide in the soaked wolfberry sample, recording the ending soaking time of the wolfberry sample, and obtaining the soaking pesticide dose ratio of the soaked wolfberry sample by adding and summing the real-time dose of each residual pesticide in the soaked wolfberry sample and comparing the real-time weight value of the slurry; wherein the soaking liquid is salt water, clear water and black tea water;
if the soaking pesticide dosage ratio is smaller than the first preset pesticide dosage ratio, subtracting the soaking starting time from the soaking ending time to obtain the residual pesticide removing duration of the soaked medlar sample; wherein the value of the first preset pesticide dosage ratio is smaller than the value of the second preset pesticide dosage ratio;
and calculating product risk values of different batches of medlar samples.
4. The method for risk assessment of pesticide residues in wolfberry according to claim 1, wherein the pesticide operation data is the number of pesticide sprays of different batches of wolfberry samples, and the amount and time of each pesticide spray.
5. The method for risk assessment of pesticide residues in wolfberry as set forth in claim 4, wherein the monitoring process of the operation monitoring module is specifically as follows:
acquiring pesticide spraying times of medlar samples in the same batch;
then, the spraying quantity of the medlar samples in the same batch is obtained when each pesticide is sprayed, and the spraying quantity of the medlar samples in the same batch is obtained by adding and summing the spraying quantity of each pesticide spraying;
finally, the spraying time of each pesticide spraying of the same batch of medlar samples is obtained, the time intervals of adjacent spraying time are calculated to obtain a plurality of groups of pesticide spraying interval duration, and the pesticide spraying interval duration of the plurality of groups of pesticide spraying interval duration is added and summed to obtain an average value to obtain the pesticide spraying interval average duration of the same batch of medlar samples;
and calculating the operation risk values of the medlar samples in different batches.
6. The risk assessment method for pesticide residues in medlar according to claim 1, wherein the assessment process of the intelligent assessment module is specifically as follows;
obtaining product risk values and operation risk values of medlar samples in different batches;
calculating risk assessment values of medlar samples in different batches;
if the risk assessment value is greater than or equal to the second risk assessment threshold, the risk level of pesticide residues in the medlar samples in different batches is the first risk level;
if the risk assessment value is smaller than the second risk assessment threshold value and larger than or equal to the first risk assessment threshold value, the risk level of pesticide residues in the medlar samples in different batches is the second risk level;
and if the risk assessment value is smaller than the first risk assessment threshold, the risk level of pesticide residues in the medlar samples in different batches is a third risk level.
7. The method of claim 6, wherein the first risk rating threshold is less than the first risk rating threshold, the first risk level is greater than the second risk level, and the second risk level is greater than the third risk level.
8. The risk assessment method for pesticide residues in medlar according to claim 1, wherein the comparison process of the information comparison module is specifically as follows:
comparing the batch code on the medlar packaging bag with the batch numbers of medlar samples in different batches of the storage module;
if the batch code is matched with the batch number, acquiring a risk level corresponding to the medlar sample according to the batch number;
and (5) marking the risk level corresponding to the medlar sample as the risk level of the medlar packaging bag.
9. The risk assessment system for pesticide residues in medlar is characterized by being suitable for the risk assessment method for pesticide residues in medlar according to any one of claims 1-8, and comprises a data acquisition module, a data analysis module, an intelligent assessment module, a job monitoring module, an information comparison module, a storage module, a user terminal and a server;
the data acquisition module is used for acquiring real-time sample data of medlar samples in different batches and sending the real-time sample data to the data analysis module through the server;
the data analysis module is used for carrying out data analysis on medlar samples in different batches to obtain product risk values of medlar samples in different batches or generating sample abnormal signals and feeding the sample abnormal signals back to the server, if the server receives the sample abnormal signals, no operation is carried out, and if the server receives the product risk values of medlar samples in different batches, the product risk values of medlar samples in different batches are sent to the intelligent evaluation module;
the storage module is used for storing pesticide operation data of medlar samples in different batches and sending the pesticide operation data to the operation monitoring module;
the operation monitoring module is used for monitoring pesticide operation conditions of the medlar samples in different batches, obtaining operation risk values of the medlar samples in different batches and sending the operation risk values to the intelligent evaluation module through the server;
the intelligent evaluation module is used for evaluating the risk grades of pesticide residues in the medlar samples in different batches, the obtained risk grades of the pesticide residues in the medlar samples in different batches are sent to the storage module through the server, and the storage module is used for storing the risk grades of the pesticide residues in the medlar samples in different batches;
the user terminal is used for scanning the batch code on the medlar packaging bag and sending the batch code to the information comparison module through the server;
the information comparison module is used for comparing the identification information of the medlar packaging bags, and the risk level of the medlar packaging bags obtained by comparison is sent to the user terminal through the server;
the user terminal is used for checking the risk level of the medlar packaging bag.
CN202311162656.9A 2023-09-11 2023-09-11 Risk assessment method and system for pesticide residues in medlar Pending CN117192015A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN202311162656.9A CN117192015A (en) 2023-09-11 2023-09-11 Risk assessment method and system for pesticide residues in medlar

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN202311162656.9A CN117192015A (en) 2023-09-11 2023-09-11 Risk assessment method and system for pesticide residues in medlar

Publications (1)

Publication Number Publication Date
CN117192015A true CN117192015A (en) 2023-12-08

Family

ID=88993744

Family Applications (1)

Application Number Title Priority Date Filing Date
CN202311162656.9A Pending CN117192015A (en) 2023-09-11 2023-09-11 Risk assessment method and system for pesticide residues in medlar

Country Status (1)

Country Link
CN (1) CN117192015A (en)

Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107103571A (en) * 2017-04-17 2017-08-29 中国检验检疫科学研究院 Residues of pesticides detecting data platform and detecting report automatic generation method based on high resolution mass spectrum, internet and data science
CN208141590U (en) * 2018-05-04 2018-11-23 安徽大学 Detecting Pesticide tidal data recovering, analysis and early warning system
CN111667122A (en) * 2020-06-16 2020-09-15 国研软件股份有限公司 Risk assessment method for pesticide residue of agricultural product variety
CN111784197A (en) * 2020-07-20 2020-10-16 龙口海关综合技术服务中心 Risk analysis and detection method for plant-derived food chemical pollutants
CN111896513A (en) * 2020-08-13 2020-11-06 广东省林业科学研究院 Big data statistical analysis system for residual detection of toxic and harmful substances
CN111999287A (en) * 2020-08-26 2020-11-27 刘同友 Intelligent agricultural product pesticide residue safety detection management system based on big data
CN112529394A (en) * 2020-12-03 2021-03-19 江苏省农业科学院 Monitoring method and system for pesticide use risk
CN114143352A (en) * 2021-12-03 2022-03-04 江苏省农业科学院 Wisdom pesticide monitoring device
CN115144343A (en) * 2022-02-18 2022-10-04 贵州省生物技术研究所(贵州省生物技术重点实验室、贵州省马铃薯研究所、贵州省食品加工研究所) Tea tree disease intelligent monitoring and analyzing method and system based on distributed data acquisition
CN116300608A (en) * 2023-03-13 2023-06-23 衡阳晟达信息技术有限公司 Intelligent agriculture remote monitoring system based on big data

Patent Citations (10)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107103571A (en) * 2017-04-17 2017-08-29 中国检验检疫科学研究院 Residues of pesticides detecting data platform and detecting report automatic generation method based on high resolution mass spectrum, internet and data science
CN208141590U (en) * 2018-05-04 2018-11-23 安徽大学 Detecting Pesticide tidal data recovering, analysis and early warning system
CN111667122A (en) * 2020-06-16 2020-09-15 国研软件股份有限公司 Risk assessment method for pesticide residue of agricultural product variety
CN111784197A (en) * 2020-07-20 2020-10-16 龙口海关综合技术服务中心 Risk analysis and detection method for plant-derived food chemical pollutants
CN111896513A (en) * 2020-08-13 2020-11-06 广东省林业科学研究院 Big data statistical analysis system for residual detection of toxic and harmful substances
CN111999287A (en) * 2020-08-26 2020-11-27 刘同友 Intelligent agricultural product pesticide residue safety detection management system based on big data
CN112529394A (en) * 2020-12-03 2021-03-19 江苏省农业科学院 Monitoring method and system for pesticide use risk
CN114143352A (en) * 2021-12-03 2022-03-04 江苏省农业科学院 Wisdom pesticide monitoring device
CN115144343A (en) * 2022-02-18 2022-10-04 贵州省生物技术研究所(贵州省生物技术重点实验室、贵州省马铃薯研究所、贵州省食品加工研究所) Tea tree disease intelligent monitoring and analyzing method and system based on distributed data acquisition
CN116300608A (en) * 2023-03-13 2023-06-23 衡阳晟达信息技术有限公司 Intelligent agriculture remote monitoring system based on big data

Similar Documents

Publication Publication Date Title
Pratt et al. Chinese gooseberry: seasonal patterns in fruit growth and maturation, ripening, respiration and the role of ethylene
Williams et al. Validation of a model for the growth and development of the Thompson Seedless grapevine. II. Phenology
Lauenroth et al. Estimating aboveground net primary production in grasslands: a simulation approach
Kieckhefer et al. Losses in Yield in Spring Wheat in South Dakota caused by Cereal Aphidst
Ben-Tal Effects of gibberellin treatments on ripening and berry drop from Thompson Seedless grapes
CN104597217A (en) Fruit maturity evaluating method based on maturation rule
Tancred et al. Heritability and patterns of inheritance of the ripening date of apples
CN117192015A (en) Risk assessment method and system for pesticide residues in medlar
Stover et al. A method for assessing the relationship between cropload and crop value following fruit thinning
Hardegree et al. Predicting variable temperature response of non-dormant seeds from constant-temperature germination data.
Serna‐Saldivar et al. Method to evaluate ease of pericarp removal on lime‐cooked corn kernels
CN111999287A (en) Intelligent agricultural product pesticide residue safety detection management system based on big data
CN108108872B (en) Method for accurately judging fruit maturity of Feizixiao litchi
CN111563635A (en) Pesticide residue detection system and method based on big data
Lavee et al. Effect of fruit size and yield on the fruit-removal-force within and between olive cultivars
Hamann et al. Ripeness sorting of muscadine grapes by use of low‐frequency vibrational energy
CN107228809B (en) A kind of peanut quality evaluation method and device suitable for peanut processing of lying fallow
CN115619586A (en) Ecological agriculture plants risk assessment system based on data analysis
Teague et al. Risk efficient perennial crop selection: a MOTAD approach to citrus production
Pool et al. Effect of Delayed Harvest on Quality of Soft Red Winter Wheat 1
Harris Effect of harvest date, storage period and ripening time on the quality of Chinese gooseberries
Colbert et al. General and specific combining ability estimates for pith cell death in stalk internodes of maize
Albach et al. Limonin content of juice from Marrs and Hamlin oranges [Citrus sinensis (L.) Osbeck]
CN110879953A (en) Plant category identification method and system
Kapse et al. Correlation between bio-chemical parameters and organoleptic evaluation in mango varieties

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination