A water treatment status assessment method for landscaping

Abstract

The present invention provides a water treatment status assessment method for gardening and greening, which belongs to the field of separation technology, and specifically comprises: utilizing different purification treatment abnormal time periods to determine the index intervals of water quality indicators of concern in different dimensions, determining water purification treatment abnormality coefficients and concerned abnormal time periods of different water purification treatment abnormal time periods, utilizing historical irrigation data to determine distribution data of concerned abnormal time periods at different historical irrigation times, and when determining that the operating status of the water purification equipment meets the requirements through the distribution data of concerned abnormal time periods at different historical irrigation times, taking the irrigation treatment time of the gardening and greening area as the unit assessment time, determining the distribution data of different concerned abnormal time periods within the unit assessment time, and determining whether the operating status of the water treatment equipment meets the requirements in combination with the water purification treatment abnormality coefficients of different concerned abnormal time periods, thereby realizing accurate assessment of the operating status of the water treatment equipment.

Description

Technical Field

[0001] The invention belongs to the field of separation technology, and in particular relates to a water treatment state assessment method for landscaping. Background Art

[0002] In order to evaluate the operating status of the water purification equipment in the water source purification process of the landscaping irrigation treatment, the invention patent application CN201811311037.0 "Water purification equipment and its safety self-test method and device" determines whether the parameter value of the specified parameter is within the preset range, and determines the status of the water purification equipment according to the judgment result, which ensures the reliability of the water purification data. However, it is not difficult to find the following technical problems through analysis:

[0003] The water quality indicators of irrigation water sources in garden greening areas are not static, but will be affected by the water purification equipment and delivery pipelines. Therefore, when the water quality indicators of the water source change, even the same water purification equipment cannot guarantee the reliability of the irrigation water quality. Therefore, if the change data of the water quality indicators of the irrigation water source cannot be combined, it is impossible to accurately evaluate the operating status of the water treatment equipment.

[0004] In view of the above technical problems, the present invention provides a water treatment status assessment method for landscaping. Summary of the invention

[0005] To achieve the purpose of the present invention, the present invention adopts the following technical solutions:

[0006] According to one aspect of the present invention, a method for evaluating water treatment status for landscaping is provided.

[0007] A water treatment status assessment method for landscaping, specifically comprising:

[0008] S1, based on the plant types and planting data of the garden greening area, determining the water quality index of concern in the garden greening area and the index range of concern for the water quality index of concern;

[0009] S2 determines the purification treatment period when the water quality index of concern is in the indicator range of concern through the analysis results of the historical purification data of the water purification equipment, and uses it as the purification treatment abnormal period. By using the indicator range of the water quality index of concern in different dimensions in different purification treatment abnormal periods, the water purification treatment abnormality coefficient and the concerned abnormal period are determined for different water purification treatment abnormal periods;

[0010] S3 uses the historical irrigation data to determine the distribution data of the abnormal periods of concern at different historical irrigation times, and when it is determined that the operating state of the water purification equipment meets the requirements through the distribution data of the abnormal periods of concern at different historical irrigation times, proceed to the next step;

[0011] S4 takes the irrigation treatment time of the garden greening area as the unit evaluation time, determines the distribution data of different abnormal time periods of concern within the unit evaluation time, and determines whether the operating status of the water treatment equipment meets the requirements in combination with the water purification abnormality coefficients of different abnormal time periods of concern.

[0012] The beneficial effects of the present invention are:

[0013] By using the distribution data of abnormal periods of interest in different historical irrigation times, it is determined whether the operating status of the water purification equipment meets the requirements, thereby realizing the distribution of abnormal periods of interest in the historical irrigation process. This avoids the technical problem of inaccurate operating status evaluation results caused by solely considering the water purification effect of the water purification equipment while ignoring the water quality data of the water source, and also lays the foundation for further improving the reliability of irrigation treatment in landscaping.

[0014] By combining the distribution data of different abnormal periods of concern within the unit evaluation time and the water purification treatment abnormality coefficients of different abnormal periods of concern to determine whether the operating status of the water treatment equipment meets the requirements, it is possible to accurately evaluate the operating status of the water treatment equipment from the perspective of the distribution data of the abnormal periods of concern within the unit evaluation time. Taking into account the historical distribution of abnormal periods of concern within the irrigation treatment time, it is possible to evaluate the operating status of the water purification equipment from the perspective of water quality indicators of the water source, thereby ensuring the requirements of water quality indicators during the irrigation process of plant types in the landscaping area.

[0015] A further technical solution is that the water quality index of concern is a water quality index that has an impact on the growth of plant types in the garden greening area.

[0016] A further technical solution is that the planting data includes planting areas of different plant types.

[0017] A further technical solution is that the method for determining the concerned indicator interval of the concerned water quality indicator is:

[0018] Determining growth influence coefficients of different plant types based on the effects of the water quality index of concern within a specific index range on the growth of different plant types;

[0019] Determine the importance of different plant types based on their planting area;

[0020] The water quality impact degree of the concerned water quality index within a specific index interval is determined based on the importance and growth impact coefficient of different plant types, and whether the specific index interval is a concerned index interval is determined based on the water quality impact degree.

[0021] A further technical solution is to determine whether the operating state of the water treatment equipment meets the requirements by combining the water treatment abnormality coefficients of different abnormal time periods, specifically including:

[0022] Using the distribution data of the concerned abnormal time period of the unit evaluation time, determine the unit evaluation time period with concerned abnormal time period, and use it as the abnormal corresponding time period, and determine the equipment abnormality coefficient of the water purification equipment through the number of the abnormal corresponding time periods and the distribution data of the abnormal corresponding time periods on different dates;

[0023] Based on the number of concerned abnormal time periods of different abnormal corresponding time periods and the water purification abnormality coefficients of different concerned abnormal time periods, the irrigation abnormality coefficients of different abnormal corresponding time periods are determined;

[0024] The abnormal value of the operating state of the water purification equipment is determined by the irrigation abnormality coefficient of different abnormal corresponding time periods and the equipment abnormality coefficient of the water purification equipment, and the abnormal value of the operating state is used to determine whether the operating state of the water purification equipment meets the requirements.

[0025] Other features and advantages will be described in the following description. The objects and other advantages of the present invention are realized and obtained by the structures particularly pointed out in the description and drawings.

[0026] In order to make the above-mentioned objects, features and advantages of the present invention more obvious and easy to understand, preferred embodiments are given below and described in detail with reference to the accompanying drawings. BRIEF DESCRIPTION OF THE DRAWINGS

[0027] The above and other features and advantages of the present invention will become more apparent by describing in detail exemplary embodiments thereof with reference to the attached drawings.

[0028] Figure 1 is a flow chart of a method for assessing the state of water treatment used in landscaping;

[0029] Figure 2 is a flow chart of a method for determining a focus index interval of a focus water quality index;

[0030] Figure 3 It is a flow chart of a method for determining a water purification abnormality coefficient during a water purification abnormality period;

[0031] Figure 4 It is a flow chart of a method for determining whether the operating status of a water purification device meets the requirements. DETAILED DESCRIPTION

[0032] In order to enable those skilled in the art to better understand the technical solutions in this specification, the technical solutions in the embodiments of this specification will be clearly and completely described below in conjunction with the drawings in the embodiments of this specification. Obviously, the described embodiments are only part of the embodiments of this specification, not all of the embodiments. Based on the embodiments of this specification, all other embodiments obtained by ordinary technicians in this field without creative work should fall within the scope of protection of this specification.

[0033] Traditionally, when evaluating the operating status of water treatment equipment, the specific data of water quality indicators in different dimensions of the water treatment equipment are often used for evaluation. However, during the operation, since the water quality indicators of the water source are not static, the distribution data of the water quality indicators of the water source after purification in the period corresponding to the irrigation treatment time of the garden area is used in this application to evaluate the operating status of the water treatment equipment. This can comprehensively consider the changes in the water quality of the water source and improve the accuracy of the evaluation results of the operating status.

[0034] To solve the above problems, according to one aspect of the present invention, Figure 1 As shown, a water treatment status assessment method for landscaping is provided, which specifically includes:

[0035] S1, based on the plant types and planting data of the garden greening area, determining the water quality index of concern in the garden greening area and the index range of concern for the water quality index of concern;

[0036] Furthermore, the water quality index of concern in the garden greening area is determined based on the water quality index that has an impact on the production of plant types in the garden greening area.

[0037] It can be understood that the indicator interval is divided into equal intervals according to the historical range of the indicator data of the water quality indicator of interest and according to the preset interval length.

[0038] It should be noted that if Figure 2 As shown, the method for determining the concerned index interval of the concerned water quality index is:

[0039] Determining the growth impact of different plant types when the water quality index of concern is within a specific index range, and determining the growth impact coefficients of different plant types based on the growth impact of different plant types;

[0040] Determining the planting areas of different plant types based on the planting data of different plant types, and using the planting areas to determine the importance of different plant types;

[0041] The water quality impact degree of the concerned water quality index within a specific index interval is determined based on the importance and growth impact coefficient of different plant types, and whether the specific index interval is a concerned index interval is determined based on the water quality impact degree.

[0042] It can be understood that when the water quality impact level does not meet the requirements, the specific indicator interval is determined as the focus indicator interval.

[0043] It should also be noted that the method for determining the concerned index interval of the concerned water quality index is:

[0044] S11 determines the growth impact of different plant types when the concerned water quality index is within a specific index interval, and determines whether there is a growth-affected plant type within the specific index interval based on the growth impact of different plant types. If so, proceed to the next step; if not, determine that the specific index interval does not belong to the concerned index interval;

[0045] S12 determines the growth influence coefficients of different production-influencing plant types based on the production influence conditions of different production-influencing plant types, and determines whether there are production-influencing plant types whose growth influence coefficients do not meet the requirements. If not, proceed to step S15; if yes, proceed to the next step;

[0046] S13 determines whether the planting area of ​​the growth-influencing plant type whose growth-influencing coefficient does not meet the requirement meets the requirement, if so, proceeds to the next step, if not, determines that the specific indicator interval belongs to the concerned indicator interval;

[0047] S14 determines the abnormal influence coefficient by using the planting area of ​​the growth-influencing plant type whose growth influence coefficient does not meet the requirement and the growth influence coefficient, and judges whether the abnormal influence coefficient meets the requirement, if so, proceeds to the next step, if not, determines that the specific indicator interval belongs to the concerned indicator interval;

[0048] S15 determines the growth influence coefficients of different plant types based on the growth influence conditions of different plant types, determines the planting areas of different plant types based on the planting data of different plant types, and uses the planting areas to determine the importance of different plant types, determines the water quality influence degree of the concerned water quality index within a specific index interval based on the importance of different plant types and the growth influence coefficients, and determines whether the specific index interval is a concerned index interval based on the water quality influence degree.

[0049] S2 determines the purification treatment period when the water quality index of concern is in the indicator range of concern through the analysis results of the historical purification data of the water purification equipment, and uses it as the purification treatment abnormal period. By using the indicator range of the water quality index of concern in different dimensions in different purification treatment abnormal periods, the water purification treatment abnormality coefficient and the concerned abnormal period are determined for different water purification treatment abnormal periods;

[0050] Specifically, it should be noted that Figure 3 As shown, the method for determining the water purification abnormality coefficient during the water purification abnormality period is:

[0051] The index intervals where the index data of different concerned water quality indexes are located are taken as corresponding index intervals, and the index abnormality coefficients of different concerned water quality indexes are determined based on the water quality impact degrees of different corresponding index intervals;

[0052] Determine the abnormal water quality index among the water quality indexes of concern in the purification treatment period by using the index abnormality coefficients of different water quality indexes of concern;

[0053] The water purification abnormality coefficient of the water purification abnormality period is determined according to the indicator abnormality coefficients of different abnormal water quality indicators.

[0054] Furthermore, the value range of the water purification anomaly coefficient during the water purification anomaly period is between 0 and 1, wherein the larger the water purification anomaly coefficient during the water purification anomaly period is, the higher the degree of water quality anomaly during the water purification anomaly period is.

[0055] It should also be noted that the method for determining the abnormal time period is:

[0056] Taking the index intervals of the index data of different concerned water quality indexes as corresponding index intervals, and determining the abnormal water quality index in the concerned water quality index based on the water quality impact degree of different corresponding index intervals;

[0057] Determining the indicator importance of the abnormal water quality indicator by the planting area of ​​the plant type affected by the abnormal water quality indicator;

[0058] Based on the weights of the index abnormality coefficients of different abnormal water quality indicators, the water purification abnormality coefficient of the water purification abnormality period is obtained, and whether the water purification abnormality period is a concerned abnormality period is determined by the water purification abnormality coefficient.

[0059] It should also be noted that the method for determining the concerned abnormal period in the abnormal period of water purification treatment is:

[0060] S21 takes the index intervals of the index data of different concerned water quality indexes as corresponding index intervals, and determines whether there are abnormal water quality indexes in the concerned water quality indexes based on the water quality impact degrees of different corresponding index intervals. If yes, proceed to the next step; if no, determine that the abnormal water treatment period does not belong to the concerned abnormal period;

[0061] S22 determines whether the number of the abnormal water quality indicators meets the requirements, if so, proceeds to the next step, if not, determines that the abnormal period of water purification treatment is a concerned abnormal period;

[0062] S23 determines the index abnormality coefficients of different concerned water quality indicators based on the water quality impact degrees of different corresponding index intervals, and judges whether the index abnormality coefficients of different abnormal water quality indicators are all within the preset interval. If so, proceed to the next step; if not, proceed to step S25;

[0063] S24 determines whether the planting area of ​​the plant type affected by the abnormal water quality index is within a preset area range. If so, it is determined that the abnormal water treatment period does not belong to the concerned abnormal period. If not, proceed to the next step.

[0064] S25 determines the index importance of the abnormal water quality index by the planting area of ​​the plant type affected by the abnormal water quality index, and determines the corrected abnormal coefficients of different abnormal water quality indexes in combination with the index abnormal coefficients of different abnormal water quality indexes, and judges whether the number of abnormal water quality indexes whose corrected abnormal coefficients do not meet the requirements meets the requirements, if so, proceeds to the next step, if not, determines that the abnormal period of water purification treatment belongs to the abnormal period of concern;

[0065] S26 obtains the index coefficient abnormal value of the abnormal water treatment period based on the weight of the corrected abnormal coefficient of different abnormal water quality indicators, and determines whether the abnormal water treatment period is a concerned abnormal period through the index coefficient abnormal value.

[0066] S3 uses the historical irrigation data to determine the distribution data of the abnormal periods of concern at different historical irrigation times, and when it is determined that the operating state of the water purification equipment meets the requirements through the distribution data of the abnormal periods of concern at different historical irrigation times, proceed to the next step;

[0067] Specifically, Figure 4 As shown, determining that the operating status of the water purification equipment meets the requirements specifically includes:

[0068] Using the distribution data of the abnormal time period of the historical irrigation times, the historical irrigation times with the abnormal time period of concern are determined, and the times are used as the abnormal irrigation times, and the basic abnormal coefficient of the water purification equipment is determined by the proportion of the abnormal irrigation times in the historical irrigation times;

[0069] Based on the number of concerned abnormal time periods of different abnormal irrigation times and the abnormal coefficients of purified water treatment in different concerned abnormal time periods, determining the irrigation abnormal coefficients of different abnormal irrigation times;

[0070] The operation status value of the water purification device is determined by the irrigation abnormality coefficients of different abnormal irrigation times and the basic abnormality coefficient of the water purification device, and the operation status value is used to determine whether the operation status of the water purification device meets the requirements.

[0071] Furthermore, when the operating state of the water purification device does not meet the requirements, an abnormal reminder signal of the operating state of the water purification device is directly output.

[0072] S4 takes the irrigation treatment time of the garden greening area as the unit evaluation time, determines the distribution data of different abnormal time periods of concern within the unit evaluation time, and determines whether the operating status of the water treatment equipment meets the requirements in combination with the water purification abnormality coefficients of different abnormal time periods of concern.

[0073] It should be noted that the determination of whether the operating state of the water treatment equipment meets the requirements is carried out in combination with the water treatment abnormality coefficients of different abnormal periods of concern, specifically including:

[0074] Using the distribution data of the concerned abnormal time period of the unit evaluation time, determine the unit evaluation time period with concerned abnormal time period, and use it as the abnormal corresponding time period, and determine the equipment abnormality coefficient of the water purification equipment through the number of the abnormal corresponding time periods and the distribution data of the abnormal corresponding time periods on different dates;

[0075] Based on the number of concerned abnormal time periods of different abnormal corresponding time periods and the water purification abnormality coefficients of different concerned abnormal time periods, the irrigation abnormality coefficients of different abnormal corresponding time periods are determined;

[0076] The abnormal value of the operating state of the water purification equipment is determined by the irrigation abnormality coefficient of different abnormal corresponding time periods and the equipment abnormality coefficient of the water purification equipment, and the abnormal value of the operating state is used to determine whether the operating state of the water purification equipment meets the requirements.

[0077] A further technical solution is that, when the abnormal value of the operating status is no longer within a preset interval, it is determined that the operating status of the water purification device does not meet the requirements.

[0078] It should also be noted that the determination of whether the operating status of the water treatment equipment meets the requirements is carried out in combination with the water treatment abnormality coefficients of different abnormal periods of concern, specifically including:

[0079] S41 uses the distribution data of the concerned abnormal time periods of the unit evaluation time to determine the unit evaluation time periods with concerned abnormal time periods, and uses them as the abnormal corresponding time periods to determine whether the number of the abnormal corresponding time periods meets the requirements, if so, proceed to the next step, if not, determine that the operating state of the water treatment equipment does not meet the requirements;

[0080] S42 determines the date when the abnormal corresponding period exists based on the distribution data of different abnormal corresponding periods on different dates, and judges whether the number of dates when the abnormal corresponding period exists meets the requirement, if so, proceeds to the next step, if not, determines that the operating state of the water treatment equipment does not meet the requirement;

[0081] S43 determines the irrigation abnormality coefficients of different abnormal corresponding time periods based on the number of concerned abnormal time periods of different abnormal corresponding time periods and the water purification abnormality coefficients of different concerned abnormal time periods, and determines whether there is an abnormal corresponding time period whose irrigation abnormality coefficient does not meet the requirements. If yes, proceed to the next step, if not, proceed to step S45;

[0082] S44 determines whether the number of abnormal corresponding time periods in which the irrigation abnormality coefficient does not meet the requirement meets the requirement, if so, proceeds to the next step, if not, determines that the operating state of the water treatment equipment does not meet the requirement;

[0083] S45 determines the equipment abnormality coefficient of the water purification equipment through the number of abnormal corresponding time periods and the distribution data of the abnormal corresponding time periods on different dates, determines the operating status abnormal value of the water purification equipment through the irrigation abnormality coefficients of different abnormal corresponding time periods and the equipment abnormality coefficient of the water purification equipment, and uses the operating status abnormal value to determine whether the operating status of the water purification equipment meets the requirements.

[0084] Each embodiment in this specification is described in a progressive manner, and the same or similar parts between the embodiments can be referred to each other, and each embodiment focuses on the differences from other embodiments. In particular, for the device, equipment, and non-volatile computer storage medium embodiments, since they are basically similar to the method embodiments, the description is relatively simple, and the relevant parts can be referred to the partial description of the method embodiment.

[0085] The above is a description of a specific embodiment of the specification. Other embodiments are within the scope of the appended claims. In some cases, the actions or steps recorded in the claims can be performed in an order different from that in the embodiments and still achieve the desired results. In addition, the processes depicted in the drawings do not necessarily require the specific order or continuous order shown to achieve the desired results. In some embodiments, multitasking and parallel processing are also possible or may be advantageous.

[0086] The above description is only one or more embodiments of this specification and is not intended to limit this specification. For those skilled in the art, one or more embodiments of this specification may have various changes and variations. Any modification, equivalent replacement, improvement, etc. made within the spirit and principle of one or more embodiments of this specification shall be included in the scope of the claims of this specification.

Claims

1. A method for evaluating water treatment status for landscaping, characterized in that: Specifically include: Based on the plant types and planting data of the garden greening area, determining the water quality index of concern and the index range of concern of the water quality index of concern in the garden greening area; Through the analysis results of the historical purification data of the water purification equipment, the purification treatment period when the water quality index of concern is in the indicator range of concern is determined, and it is used as the purification treatment abnormal period. The water quality index of concern in different dimensions in different purification treatment abnormal periods is used to determine the water purification treatment abnormality coefficient and the abnormal period of concern in different water purification treatment abnormal periods; Determine the distribution data of abnormal periods of concern at different historical irrigation times by using the historical irrigation data, and proceed to the next step when it is determined that the operating state of the water purification device meets the requirements by using the distribution data of abnormal periods of concern at different historical irrigation times; Determining that the operating status of the water purification equipment meets the requirements, specifically includes: Using the distribution data of the abnormal time period of the historical irrigation times, the historical irrigation times with the abnormal time period of concern are determined, and the times are used as the abnormal irrigation times, and the basic abnormal coefficient of the water purification equipment is determined by the proportion of the abnormal irrigation times in the historical irrigation times; Based on the number of concerned abnormal time periods of different abnormal irrigation times and the abnormal coefficients of purified water treatment in different concerned abnormal time periods, determining the irrigation abnormal coefficients of different abnormal irrigation times; Determine the operation status value of the water purification device through the irrigation abnormality coefficients of different abnormal irrigation times and the basic abnormality coefficient of the water purification device, and use the operation status value to determine whether the operation status of the water purification device meets the requirements; Taking the irrigation treatment time of the garden greening area as the unit evaluation time, determining the distribution data of different abnormal periods of concern within the unit evaluation time, and combining the water purification treatment abnormality coefficients of different abnormal periods of concern to determine whether the operating status of the water purification equipment meets the requirements; Determining whether the operating status of the water purification equipment meets the requirements in combination with the water purification treatment abnormality coefficients of different abnormal periods of concern includes: Using the distribution data of the concerned abnormal time period of the unit evaluation time, determine the unit evaluation time period with concerned abnormal time period, and use it as the abnormal corresponding time period, and determine the equipment abnormality coefficient of the water purification equipment through the number of the abnormal corresponding time periods and the distribution data of the abnormal corresponding time periods on different dates; Based on the number of concerned abnormal time periods of different abnormal corresponding time periods and the water purification abnormality coefficients of different concerned abnormal time periods, the irrigation abnormality coefficients of different abnormal corresponding time periods are determined; The abnormal value of the operating state of the water purification equipment is determined by the irrigation abnormality coefficient of different abnormal corresponding time periods and the equipment abnormality coefficient of the water purification equipment, and the abnormal value of the operating state is used to determine whether the operating state of the water purification equipment meets the requirements.

2. The water treatment status assessment method for landscaping as claimed in claim 1, characterized in that: The water quality index of concern is a water quality index that has an impact on the growth of plant types in the garden greening area.

3. The water treatment status assessment method for landscaping as claimed in claim 1, characterized in that: The planting data includes planting areas of different plant types.

4. The water treatment status assessment method for landscaping as claimed in claim 1, characterized in that: The method for determining the concerned index interval of the concerned water quality index is: Determining growth influence coefficients of different plant types based on the effects of the water quality index of concern within a specific index range on the growth of different plant types; Determine the importance of different plant types based on their planting area; The water quality impact degree of the concerned water quality index within a specific index interval is determined based on the importance and growth impact coefficient of different plant types, and whether the specific index interval is a concerned index interval is determined based on the water quality impact degree.

5. The water treatment status assessment method for landscaping as claimed in claim 4, characterized in that: The value range of the water quality impact degree of the concerned water quality index within a specific index interval is between 0 and 1, wherein the greater the water quality impact degree, the higher the impact of the concerned water quality index on the garden greening area within the specific index interval.

6. The water treatment status assessment method for landscaping as claimed in claim 1, characterized in that: The method for determining the water purification abnormality coefficient during the water purification abnormality period is as follows: The index intervals where the index data of different water quality indexes of concern are located are taken as corresponding index intervals, and the index abnormality coefficients of different water quality indexes of concern are determined based on the water quality impact degrees of different corresponding index intervals; Determine the abnormal water quality index among the water quality indexes of concern in the purification treatment period by using the index abnormality coefficients of different water quality indexes of concern; The water purification abnormality coefficient of the water purification abnormality period is determined according to the indicator abnormality coefficients of different abnormal water quality indicators.

7. The water treatment status assessment method for landscaping as claimed in claim 1, characterized in that: When the operating state of the water purification device does not meet the requirements, an abnormal reminder signal of the operating state of the water purification device is directly output.

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