Water conservancy scenic spot supervision service system

Abstract

The invention relates to the technical field of scenic spot supervision, and discloses a water conservancy scenic spot supervision service system, which comprises a data acquisition unit, a hierarchical supervision unit, a water quality supervision unit and a result output unit, the scenic spot management station can monitor tourist flow and perform early warning and flow limiting, the regional management center can deploy resources to balance regional experience, and the scenic spot management headquarters can divide regions to formulate strategies so as to improve tourist comfort, satisfaction and scenic spot operation benefits; by monitoring water quality parameters in real time, calculating evaluation indexes and comparing threshold values, pollution is early warned in time, improvement measures are prompted to be taken, the ecological balance of a scenic area and the safety of tourists in contact with water are maintained, and the ecological image is improved; the tourist flow and water quality supervision system is combined, comprehensive information is provided through data acquisition, fine and effective hierarchical supervision is ensured, result output facilitates decision making, the scientific, systematic and intelligent levels of scenic spot management are improved, competitiveness is enhanced, and coordinated development of tourism industry and ecological protection is promoted.

Description

Technical Field

[0001] The present invention relates to the technical field of scenic area supervision, and particularly relates to a supervision service system for water conservancy scenic areas. Background Art

[0002] With the booming development of the tourism industry in water conservancy scenic areas, the number of tourists has been continuously increasing, and the scale of the scenic area has been continuously expanding. The traditional management mode has been difficult to meet the growing supervision needs. In terms of tourist flow management, there is a lack of effective hierarchical monitoring and allocation mechanisms, resulting in overcrowding of tourists at some scenic spots beyond the carrying capacity, which not only affects the tourists' visiting experience but may also lead to safety accidents; while at some scenic spots, there are few tourists and the resources are not fully utilized, causing waste and uneven distribution of resources.

[0003] In terms of water quality supervision, the water quality status of water conservancy scenic areas is crucial for the scenic area's ecological environment and tourists' health. However, the existing supervision means are often relatively single and lagging, unable to monitor the changes in water quality parameters in real time, comprehensively and accurately. It is impossible to detect water pollution hazards in time and give early warnings. When the water quality deteriorates, it may cause irreversible damage to the water ecosystem in the scenic area, such as fish death, withering of aquatic plants, etc. At the same time, it will also reduce the tourists' satisfaction with the scenic area, affecting the reputation and sustainable development of the scenic area.

[0004] In addition, after the scenic area management department obtains the comprehensive supervision data of the scenic area, there is a lack of an efficient data integration and analysis system, making it difficult to make decisions quickly and accurately, formulate targeted management strategies and resource allocation plans, and unable to achieve refined management and optimized operation of the scenic area, thus restricting the improvement of the overall management level of water conservancy scenic areas and the healthy development of the tourism industry. Therefore, it is particularly urgent to develop a system that can comprehensively, accurately and efficiently supervise and serve water conservancy scenic areas. Summary of the Invention

[0005] The purpose of the present invention is to provide a supervision service system for water conservancy scenic areas, which solves the technical problems mentioned in the background art.

[0006] The purpose of the present invention can be achieved through the following technical solutions:

[0007] A supervision service system for water conservancy scenic areas, comprising:

[0008] A data acquisition unit, used to deploy various types of sensors at key positions in the scenic area and obtain target data related to the supervision of water conservancy scenic areas;

[0009] The hierarchical supervision unit is used to conduct hierarchical supervision and analysis on scenic spots. The scenic spot supervision system is divided into multiple levels, including the scenic spot management headquarters, regional management center, and scenic spot management station. Specifically, the scenic spot management station collects tourist flow and compares it with the maximum carrying capacity to generate a flow warning signal. The regional management center receives scenic spot data to perform resource allocation analysis and coordinate abnormal situations. The scenic spot management headquarters receives regional data for comparative analysis to find out popular and unpopular areas.

[0010] Water quality monitoring unit, used to dynamically monitor and analyze water quality in combination with water quality parameter data:

[0011] The result output unit is used to display the results obtained by the grading supervision unit and the water quality supervision unit to relevant personnel.

[0012] As a further solution of the present invention: the target data includes:

[0013] The water quality sensor measures the water quality parameter data of corresponding attributes such as pH value, dissolved oxygen content, ammonia nitrogen content, etc.

[0014] Data corresponding to tourist flow counted by flow sensors.

[0015] As a further solution of the present invention: the supervision and analysis method of the scenic spot management station in the hierarchical supervision unit is as follows:

[0016] The scenic spot management station obtains the tourist flow of the corresponding scenic spot and conducts dynamic monitoring and analysis of the passenger flow of the corresponding scenic spot:

[0017] The specific method is as follows:

[0018] At the corresponding scenic spots, the tourist flow within the predetermined specified time period is collected in real time and recorded as YK;

[0019] Then the maximum carrying capacity of the corresponding scenic spot is extracted and recorded as YKC max ;

[0020] Among them, the maximum load-bearing capacity refers to the maximum number of tourists received by the corresponding scenic spot;

[0021] Then through PYK = YK / YKC max , calculate the ratio of tourist flow to maximum carrying capacity within a specified time period PYK:

[0022] Then the ratio value PYK is compared with the preset passenger flow warning threshold PYK y For comparison:

[0023] When PYK>PYK y When , it means that the number of tourists at the corresponding scenic spot is too large, and a tourist flow warning signal is generated;

[0024] When PYK ≤ PYK y no tourist flow warning signal is generated;

[0025] Among them, the tourist flow warning signal is used to trigger the tourist flow warning and notify the scenic spot management station to take flow-limiting measures.

[0026] As a further solution of the present invention: the supervision and analysis method of the regional management center in the hierarchical supervision unit is as follows:

[0027] The regional management center receives data from multiple scenic spot management stations within the region, and conducts regional resource allocation analysis according to the tourist flow distribution and resource usage conditions among the scenic spots;

[0028] The specific method is as follows:

[0029] Extract the number of all scenic spots within the specified area and record it as m;

[0030] Then count the tourist flow of each scenic spot and record it as YK j At the same time, extract the maximum carrying capacity of each scenic spot and record it as YKC max，j ;

[0031] Among them, j = 1, 2,..., m, YK j is the tourist flow of the jth scenic spot, and YKC max，j is the maximum carrying capacity of the jth scenic spot;

[0032] After that, through:

[0033] X1 j = YK j / YKC max,j

[0034] Calculate the resource allocation coefficient X1 of each scenic spot j ;

[0035] Then, by comparing the resource allocation coefficients of different scenic spots, determine the resource allocation direction;

[0036] The comparison method is as follows:

[0037] Select the resource allocation coefficients X1 k1 and X1 k2 of two different scenic spots, where k1 ∈ j, k2 ∈ j, and when comparing, k1 ≠ k2; k1 and k2 respectively represent the number of the scenic spot;

[0038] At the same time, select the tourist flows YK k1 and YK k2 of two different scenic spots, and select the maximum carrying capacities YKC of two different scenic spotsmax，k1 and YKC max，k2 ;

[0039] Followed by:

[0040] KTP k1 = YK k1 - YKC max,k1

[0041] KTP k2 = YK k2 - YKC max,k2

[0042] Calculate the resource allocation values KTP of two different scenic spots k1 and KTP k2 ;

[0043] When X1 k1 > X1 k2 , and KTP k1 < KTPy and KTP k2 >|KTPy|; then generate a scenic spot scheduling signal, which is used to allocate the tourist flow of the k2th scenic spot and select KTP k1 the number of tourists to the k1th scenic spot to balance the resource utilization efficiency and tourist experience in the area;

[0044] Among them, KTPy is a preset resource allocation threshold, and its value is negative, || represents the absolute value, and the value of |KTPy| is positive.

[0045] As a further solution of the present invention: The supervision and analysis method of the scenic spot management headquarters in the hierarchical supervision unit is as follows:

[0046] The scenic spot management headquarters receives data from each regional management center, compares and analyzes the tourist flow data of different regions, and finds out the popular regions and unpopular regions of the tourist flow;

[0047] The specific method is as follows:

[0048] Extract the tourist flow of each scenic spot in the corresponding area within each area of the scenic spot and mark it as YK r，j ;

[0049] Among them, r = 1, 2,... g, YK r，j is the tourist flow of the jth scenic spot in the rth area, and g is the number of each area in the scenic spot;

[0050] Followed by:

[0051]

[0052] Calculate the tourist flow heat index H of each area in the scenic spotr ;

[0053] Subsequently, the tourist flow heat index H of each area in the scenic area r is compared with the preset heat threshold range [H min , H max :

[0054] Among them, H min is the minimum value of the heat threshold range, and H max is the maximum value of the heat threshold range;

[0055] When H r < H min , the corresponding area is determined as a cold area;

[0056] When H r > H max , the corresponding area is determined as a popular area;

[0057] When H min ≤ H r ≤ H max , the corresponding area is determined as an average area;

[0058] The scenic area management headquarters divides the popular area and the cold area through the tourist flow heat index, and formulates the overall marketing promotion strategy and resource optimization configuration plan for the scenic area.

[0059] As a further solution of the present invention: the water quality dynamic monitoring and analysis method is as follows:

[0060] StepA1. Mark the water quality parameter data of each attribute as SZ i , i = 1, 2,... n, where n represents the number of attributes of the water quality parameter data;

[0061] StepA2. Extract the preset normal range of water quality parameters corresponding to the attribute, and record it as [SZY i，min , SZY i,max ;

[0062] Among them, when i = 1, [SZY 1，min , SZY 1,max is the normal range of pH value; when i = 2, [SZY 2，min , SZY 2,max is the normal range of dissolved oxygen content; when i = 3, [SZY 3，min , SZY 3,max is the normal range of ammonia nitrogen content;

[0063] StepA3. Through:

[0064]

[0065] Calculate the deviation degree value PL of the water quality parameter data corresponding to the attribute from the normal range i ;

[0066] Among them, when i = 1, PL1 is the deviation degree value of the pH value from the normal range; when i = 2, PL2 is the deviation degree value of the dissolved oxygen content from the normal range; when i = 3, PL3 is the deviation degree value of the ammonia nitrogen content from the normal range;

[0067] StepA4. Extract the deviation degree value PL of the water quality parameter data of all attributes from the normal range i ;

[0068] And through:

[0069] HSZ = PL i ×β i

[0070] Calculate the water quality comprehensive evaluation index HSZ;

[0071] In the formula, βi is the preset weight coefficient corresponding to the water quality parameter data of various attributes, and the weight coefficient is determined according to the importance of the water quality parameter data of the attribute to the water quality;

[0072] StepA5. Compare the water quality comprehensive evaluation index HSZ with the preset water quality comprehensive evaluation threshold HSZy:

[0073] If HSZ > HSZy, it means that the water quality is seriously polluted, and a water quality pollution warning signal is generated. The water quality pollution warning signal is used to notify the scenic spot management station to take water quality improvement measures, such as strengthening water purification treatment;

[0074] If HSZ ≤ HSZy, no water quality pollution warning signal is generated.

[0075] Advantages of the present invention:

[0076] In the present invention, the data acquisition unit deploys a variety of sensors at key positions in the scenic area to obtain target data related to the supervision of the water conservancy scenic area, including water quality parameter data and tourist flow data, etc., providing comprehensive data support for subsequent supervision.

[0077] In the present invention, the hierarchical supervision unit conducts hierarchical supervision of the scenic area with the help of the multi-level system of the scenic area management headquarters, regional management centers and scenic spot management stations. The scenic spot management station can effectively monitor the tourist flow and give early warnings in a timely manner. The regional management center can allocate resources according to the situation of each scenic spot to balance the resource utilization efficiency and tourist experience within the region. The scenic area management headquarters can divide popular and unpopular areas and formulate overall marketing promotion and resource optimization allocation plans, realizing all-round and multi-level refined management of the scenic area.

[0078] In the present invention, the water quality supervision unit combines water quality parameter data for dynamic monitoring and analysis, can accurately calculate the comprehensive water quality evaluation index and compare it with the threshold value, timely detect serious water pollution situations and generate warning signals, notify the scenic spot management station to take water quality improvement measures, ensure the water quality safety of the scenic area, improve the management level, resource utilization efficiency, tourist experience, and sustainable development ability of the water conservancy scenic area, and at the same time ensure the stability and health of the ecological environment of the scenic area. BRIEF DESCRIPTION OF THE DRAWINGS

[0079] The present invention will be further described below in conjunction with the accompanying drawings.

[0080] Figure 1 It is a system block diagram of a water conservancy scenic area supervision service system of the present invention.

[0081] Figure 2 It is a schematic flow chart of the hierarchical supervision unit in a water conservancy scenic area supervision service system of the present invention. DETAILED DESCRIPTION OF THE EMBODIMENTS

[0082] The technical solutions in the embodiments of the present invention will be clearly and completely described below in conjunction with the accompanying drawings in the embodiments of the present invention. Obviously, the described embodiments are only a part of the embodiments of the present invention, rather than all of the embodiments. All other embodiments obtained by those of ordinary skill in the art based on the embodiments of the present invention without creative efforts shall fall within the protection scope of the present invention.

[0083] Embodiment 1

[0084] Please refer to Figure 1 and Figure 2 As shown, the present invention is a water conservancy scenic area supervision service system, including:

[0085] A data acquisition unit, configured to deploy various types of sensors at key positions in the scenic area and obtain target data related to the supervision of the water conservancy scenic area;

[0086] The target data includes:

[0087] Data corresponding to the tourist flow statistics by the flow sensor;

[0088] A hierarchical supervision unit, configured to perform hierarchical supervision and analysis on the scenic area;

[0089] Among them, the scenic area supervision system is divided into multiple levels corresponding to the scenic area management headquarters, regional management centers, and scenic spot management stations;

[0090] Step 1. Scenic spot management station supervision and analysis

[0091] The scenic spot management station obtains the tourist flow of the corresponding scenic spot and conducts dynamic monitoring and analysis of the passenger flow of the corresponding scenic spot:

[0092] The specific method is as follows:

[0093] At the corresponding scenic spots, the tourist flow within the predetermined specified time period is collected in real time and recorded as YK;

[0094] Then the maximum carrying capacity of the corresponding scenic spot is extracted and recorded as YKC max ;

[0095] Among them, the maximum load-bearing capacity refers to the maximum number of tourists received by the corresponding scenic spot;

[0096] Then through PYK = YK / YKC max , calculate the ratio of tourist flow to maximum carrying capacity within a specified time period PYK:

[0097] Then the ratio value PYK is compared with the preset passenger flow warning threshold PYK y For comparison:

[0098] When PYK>PYK y When , it means that the number of tourists at the corresponding scenic spot is too large, and a tourist flow warning signal is generated;

[0099] When PYK≤PYK y When , no tourist flow warning signal is generated;

[0100] Among them, the tourist flow warning signal is used to trigger the tourist flow warning and notify the scenic spot management station to take flow control measures, such as guiding tourists to areas with fewer tourists through broadcasting and electronic display screens, or suspending ticket sales, etc.

[0101] Step 2: Regional Management Center Supervision Analysis

[0102] The regional management center receives data from multiple scenic spot management stations in the region and conducts regional resource allocation analysis based on the distribution of tourist flow and resource usage among various scenic spots;

[0103] The specific method is as follows:

[0104] Extract the number of all scenic spots in the specified area and record it as m;

[0105] Then the tourist flow of each scenic spot is counted and recorded as YK j , and extract the maximum carrying capacity of each scenic spot and record it as YKC max，j ;

[0106] Where j = 1, 2, ..., m, YK j is the tourist flow of the jth attraction, YKCmax，j is the maximum carrying capacity of the j-th scenic spot;

[0107] After that, through:

[0108] X1 j = YK j / YKC max,j

[0109] Calculate the resource allocation coefficient X1 of each scenic spot j ;

[0110] Then, by comparing the resource allocation coefficients of different scenic spots, determine the resource allocation direction;

[0111] The comparison method is as follows:

[0112] Select the resource allocation coefficients X1 of two different scenic spots k1 and X1 k2 , where k1 ∈ j, k2 ∈ j, and when comparing, k1 ≠ k2; k1 and k2 respectively represent which scenic spot;

[0113] At the same time, select the tourist flow YK of two different scenic spots k1 and YK k2 , as well as select the maximum carrying capacity YKC of two different scenic spots max，k1 and YKC max，k2 ;

[0114] Then, through:

[0115] KTP k1 = YK k1 -YKC max,k1

[0116] KTP k2 = YK k2 -YKC max,k2

[0117] Calculate the resource allocable values KTP of two different scenic spots k1 and KTP k2 ;

[0118] When X1 k1 > X1 k2 , and KTP k1 < KTPy and KTP k2 > |KTPy|; then generate a scenic spot scheduling signal, and the scenic spot scheduling signal is used to select KTP k1 tourists from the k2-th scenic spot and allocate them to the k1-th scenic spot to balance the resource utilization efficiency and tourist experience in the area;

[0119] Among them, KTPy is the preset threshold for allocating resources, and its value is negative. || represents the absolute value, and the value of |KTPy| is positive;

[0120] In this embodiment, when an abnormal situation of tourist congestion occurs at a certain scenic spot in the area and it cannot be self-dispersed, the area management center coordinates the resources of other scenic spots in the area for support and collaborative processing, and reports to the scenic area management headquarters;

[0121] Step 3. Supervision and analysis by the scenic area management headquarters

[0122] The scenic area management headquarters receives data from each area management center, compares and analyzes the tourist flow data of different areas, and finds out the popular areas and unpopular areas of tourist flow;

[0123] The specific method is as follows:

[0124] Extract the tourist flow of each scenic spot in the corresponding area within each area of the scenic area, and mark it as YK r，j ;

[0125] Among them, r = 1, 2,... g, YK r，j is the tourist flow of the jth scenic spot in the rth area, and g is the number of areas in the scenic area;

[0126] Then through:

[0127]

[0128] Calculate the tourist flow heat index H of each area in the scenic area r ;

[0129] Then compare the tourist flow heat index H of each area in the scenic area r with the preset heat threshold range [H min , H max :

[0130] Among them, H min is the minimum value of the heat threshold range, and H max is the maximum value of the heat threshold range;

[0131] When H r <H min , then the corresponding area is determined as an unpopular area;

[0132] When H r >H max , then the corresponding area is determined as a popular area;

[0133] When H min ≤H r ≤H max, the corresponding area is determined as a general area;

[0134] The scenic area management headquarters divides popular areas and unpopular areas through the tourist flow heat index, and formulates the overall marketing promotion strategy and resource optimization allocation plan for the scenic area;

[0135] The result output unit is used to display the results obtained by the hierarchical supervision unit to relevant personnel.

[0136] In the first embodiment, through the real-time collection of the tourist flow by the scenic spot management station and the comparative analysis with the maximum carrying capacity, the tourist flow conditions of each scenic spot can be accurately grasped. Once the proportion of the tourist flow exceeds the preset threshold, an early warning signal is generated in time and the flow-limiting measures are triggered, effectively avoiding the safety hazards and the decline of the tourist experience caused by the excessive aggregation of tourists, and ensuring the comfort and safety of tourists in the scenic area. The regional management center conducts resource allocation analysis based on the tourist flow distribution and resource usage of each scenic spot. By calculating the resource allocation coefficient and the resource allocable value, a reasonable allocation direction is determined to achieve the dynamic balance of the tourist flow within the region. For example, transferring tourists from crowded scenic spots to relatively loose scenic spots not only improves the resource utilization efficiency, but also enables tourists to experience each scenic spot in the region more evenly, improving the overall tourist satisfaction. At the same time, when a scenic spot is congested and cannot be self-regulated, the resources within the region can be quickly coordinated for support and collaborative processing, and reported in time, enhancing the emergency response ability and coordination of the regional management. The scenic area management headquarters divides popular, unpopular and general areas by comparing and analyzing the tourist flow data of different regions. Based on this, the formulated marketing promotion strategy can target the unpopular areas for publicity and promotion to attract more tourists and enhance the overall attraction of the scenic area; the resource optimization allocation plan can reasonably allocate human, material and other resources according to the regional popularity. For example, increasing service facilities and personnel allocation in popular areas, and optimizing and upgrading facilities or developing characteristic projects in unpopular areas, so as to promote the balanced development of each area of the scenic area, improve the overall operation efficiency and management level of the scenic area, and achieve the sustainable development of the scenic area.

[0137] Embodiment 2

[0138] As the second embodiment of the present invention, when the present application is specifically implemented, compared with the first embodiment, the difference between the technical solution of this embodiment and that of the first embodiment is only that in this embodiment, the target data includes:

[0139] Water quality parameter data of corresponding attributes such as pH value, dissolved oxygen content, ammonia nitrogen content, etc. measured by a water quality sensor;

[0140] The water quality supervision unit is used to conduct dynamic water quality monitoring and analysis in combination with the water quality parameter data: The specific method is as follows:

[0141] StepA1. Mark the water quality parameter data of each attribute as SZi , where \(i = 1, 2, \cdots, n\), and \(n\) represents the number of attributes of water quality parameter data;

[0142] For example: when \(i = 1\), \(SZ1\) is the pH value; when \(i = 2\), \(SZ2\) is the dissolved oxygen content; when \(i = 3\), \(SZ3\) is the ammonia nitrogen content;

[0143] StepA2. Extract the preset normal range of water quality parameters corresponding to the attributes, and denote it as \([SZY i，min , SZY i,max ;

[0144] For example: when \(i = 1\), \([SZY 1，min , SZY 1,max is the normal range of the pH value; when \(i = 2\), \([SZY 2，min , SZY 2,max is the normal range of the dissolved oxygen content; when \(i = 3\), \([SZY 3，min , SZY 3,max is the normal range of the ammonia nitrogen content;

[0145] StepA3. Calculate the deviation degree value \(PL\) of the water quality parameter data corresponding to the attributes from the normal range through:

[0146]

[0147] ; i ;

[0148] For example: when \(i = 1\), \(PL1\) is the deviation degree value of the pH value from the normal range; when \(i = 2\), \(PL2\) is the deviation degree value of the dissolved oxygen content from the normal range; when \(i = 3\), \(PL3\) is the deviation degree value of the ammonia nitrogen content from the normal range;

[0149] StepA4. Extract the deviation degree values \(PL\) of the water quality parameter data of all attributes from the normal range i ;

[0150] And calculate the water quality comprehensive evaluation index \(HSZ\) through:

[0151] HSZ = PL i ×β i

[0152] ;

[0153] In the formula, \(\beta_i\) is the preset weight coefficient corresponding to the water quality parameter data of various attributes, and the weight coefficient is determined according to the importance of the water quality parameter data of the attributes to the water quality;

[0154] StepA5. Compare the water quality comprehensive evaluation index \(HSZ\) with the preset water quality comprehensive evaluation threshold \(HSZy\):

[0155] If HSZ > HSZy, it indicates serious water quality pollution and generates a water quality pollution warning signal, which is used to notify the scenic spot management station to take water quality improvement measures, such as strengthening water purification treatment;

[0156] If HSZ ≤ HSZy, no water quality pollution warning signal is generated;

[0157] The result output unit is also used to display the results obtained by the water quality supervision unit to relevant personnel.

[0158] In this embodiment, through the collection and analysis of key water quality parameter data such as pH value, dissolved oxygen content, and ammonia nitrogen content by water quality sensors, the water quality status of the water bodies in the scenic area can be grasped in real time. Calculate the comprehensive water quality evaluation index and compare it with the threshold. When the water quality pollution is serious, a warning signal is generated in time and the scenic spot management station is notified to take water quality improvement measures, such as strengthening water purification treatment, etc. This effectively prevents the damage caused by water quality deterioration to the water ecosystem in the scenic area, protects the living environment of aquatic organisms, maintains the ecological balance of the scenic area, and at the same time ensures the safety of tourists coming into contact with the water bodies, improves the ecological image of the scenic area and the trust of tourists in the water quality environment of the scenic area.

[0159] Embodiment Three

[0160] As Embodiment Three of the present invention, in the specific implementation of this application, compared with Embodiment One and Embodiment Two, the technical solution of this embodiment lies in the combined implementation of the solutions of the above-mentioned Embodiment One and Embodiment Two.

[0161] This embodiment combines the tourist flow supervision system of Embodiment One with the water quality supervision system of Embodiment Two to achieve comprehensive all-round supervision of the water conservancy scenic area. It not only ensures the tour order and safety of tourists in the scenic area, but also maintains the ecological environment quality of the scenic area. The multi-source data obtained by the data collection unit provides a rich and comprehensive information basis for scenic area management. The multi-level architecture of the hierarchical supervision unit ensures the refinement and effectiveness of supervision. The result output unit displays the supervision results in all aspects to relevant personnel, facilitating timely decision-making and taking targeted measures. This collaborative management mode improves the scientific, systematic and intelligent level of overall scenic area management, helps to create a high-quality and sustainable water conservancy scenic area, meets the diverse needs of tourists, enhances the competitiveness of the scenic area in the tourism market, and promotes the coordinated progress of the scenic area tourism industry and ecological protection.

[0162] The above formulas are all dimensionless and take their numerical values for calculation. The formulas are obtained by software simulation of collecting a large amount of data to get a formula closest to the real situation. The preset parameters and threshold selection in the formulas are set by those skilled in the art according to the actual situation.

[0163] As described above, it is only the specific implementation manner of the present application, but the protection scope of the present application is not limited thereto. Any person skilled in the art within the technical scope disclosed by the present application can easily think of changes or substitutions, which should all be covered within the protection scope of the present application. Therefore, the protection scope of the present application shall be subject to the protection scope of the claims described above.

Claims

1. A water conservancy scenic area supervision and service system, characterized in that, include: Data collection unit, used to deploy various types of sensors at key locations in the scenic area and obtain target data related to the supervision of water conservancy scenic areas; The hierarchical supervision unit is used to conduct hierarchical supervision and analysis on scenic spots. The scenic spot supervision system is divided into multiple levels, including the scenic spot management headquarters, regional management center, and scenic spot management station. Specifically, the scenic spot management station collects tourist flow and compares it with the maximum carrying capacity to generate a flow warning signal. The regional management center receives scenic spot data to perform resource allocation analysis and coordinate abnormal situations. The scenic spot management headquarters receives regional data for comparative analysis to find out popular and unpopular areas. Water quality monitoring unit, used to dynamically monitor and analyze water quality in combination with water quality parameter data: The result output unit is used to display the results obtained by the grading supervision unit and the water quality supervision unit to relevant personnel.

2. The water conservancy scenic area supervision service system according to claim 1, wherein The supervision analysis method of scenic spot management stations in the hierarchical supervision unit is as follows: The scenic spot management station obtains the tourist flow of the corresponding scenic spot and conducts dynamic monitoring and analysis of the passenger flow of the corresponding scenic spot: The specific method is as follows: At the corresponding scenic spots, the tourist flow within the predetermined specified time period is collected in real time and recorded as YK; Then extract the maximum carrying capacity of the corresponding scenic spot and denote it as YKC max ; Among them, the maximum load-bearing capacity refers to the maximum number of tourists received by the corresponding scenic spot; Next, calculate the ratio value PYK of the tourist flow to the maximum carrying capacity within a specified time period through PYK = YK / YKC max , where PYK represents the ratio of the tourist flow to the maximum carrying capacity within a specified time period Subsequently, the ratio value PYK is compared with a preset passenger flow warning threshold PYK y for comparison: When PYK > PYK y it indicates that the tourist volume of the corresponding scenic spot is too large, and a tourist flow warning signal is generated; When PYK ≤ PYK y no tourist flow warning signal is generated.

3. The regulatory service system for a water conservancy scenic area according to claim 1, characterized in that, The supervision analysis method of the regional management center in the hierarchical supervision unit is as follows: The regional management center receives data from multiple scenic spot management stations in the region and conducts regional resource allocation analysis based on the distribution of tourist flow and resource usage among various scenic spots; The specific method is as follows: Extract the number of all scenic spots in the specified area and record it as m; Subsequently, count the tourist flow of each scenic spot and record it as YK j , and at the same time extract the maximum carrying capacity of each scenic spot and record it as YKC max，j ; where j = 1, 2,..., m, and YK j is the tourist flow of the j-th scenic spot, and YKC max，j is the maximum carrying capacity of the j-th scenic spot; Afterwards via: X1 j = YK j / YKC max,j Calculate the resource allocation coefficient X1 for each scenic spot j ; Then, the resource allocation direction is determined by comparing the resource allocation coefficients of different scenic spots.

4. The water conservancy scenic area supervision service system according to claim 3, characterized in that, The comparison method in the intra-regional resource allocation analysis is as follows: Select the resource allocation coefficients X1 of two different scenic spots k1 and X1 k2 , where k1 ∈ j, k2 ∈ j, and when comparing, k1 ≠ k2; k1 and k2 respectively represent which scenic spot; The tourist flows YK of two different scenic spots are selected simultaneously k1 and YK k2 , and the maximum carrying capacities YKC of two different scenic spots max，k1 and YKC max，k2 ; Then through: KTP k1 = YK k1 - YKC max,k1 KTP k2 = YK k2 - YKC max,k2 Calculate the resource allocation values KTP for two different scenic spots k1 and KTP k2 ; When X1 k1 > X1 k2 , and KTP k1 < KTPy and KTP k2 > |KTPy|; then a scenic spot scheduling signal is generated, and the scenic spot scheduling signal is used to select KTP k1 tourists from the k2th scenic spot and allocate them to the k1th scenic spot; Among them, KTPy is the preset resource allocation threshold, and its value is a negative number, || represents the absolute value, and the value of |KTPy| is a positive number.

5. The regulatory service system for a water conservancy scenic area according to claim 1, characterized in that, The supervision and analysis methods of the scenic area management headquarters in the hierarchical supervision unit are as follows: The scenic area management headquarters receives data from various regional management centers, conducts comparative analysis on tourist flow data in different regions, and identifies popular and unpopular areas of tourist flow; The specific method is as follows: Extract the tourist flow of each scenic spot in the corresponding area within each area of the scenic area and mark it as YK r，j ; where r = 1, 2, …… g, YK r，j is the tourist flow of the j-th scenic spot in the r-th area, and g is the number of areas in the scenic area; Then through: Calculate the tourist flow heat index H for each area within the scenic spot r ; Subsequently, the tourist flow heat index H of each area in the scenic area r is compared with the preset heat threshold range [H min , H max , and based on the comparison results, popular areas and unpopular areas are determined.

6. The water conservancy scenic area supervision service system according to claim 5, characterized in that in, The heat threshold range is marked by [H min , H max , and H min is the minimum value of the heat threshold range, and H max is the maximum value of the heat threshold range; When H r <H min , the corresponding area is determined as a cold area; When H r > H max , the corresponding area is determined as a popular area.

7. The regulatory service system for a water conservancy scenic area according to claim 1, wherein The dynamic monitoring and analysis methods of water quality are as follows: Step A1. Mark the water quality parameter data of each attribute as SZ i , where i = 1, 2,..., n, and n represents the number of attributes of the water quality parameter data; Step A2. Extract the preset normal range of water quality parameters corresponding to the attributes, and denote it as [SZY i，min , SZY i,max ; StepA3, through: Calculate the deviation degree value PL of the water quality parameter data corresponding to the attribute deviating from the normal range i ; Step A4. Extract the deviation degree value PL of the water quality parameter data of all attributes deviating from the normal range i ; And through: HSZ = PL i ×β i Calculate the comprehensive water quality evaluation index HSZ; In the formula, βi is the preset weight coefficient corresponding to various attribute water quality parameter data, and the weight coefficient is determined according to the importance of the attribute water quality parameter data on water quality; StepA5, compare the comprehensive water quality evaluation index HSZ with the preset comprehensive water quality evaluation threshold HSZy, and determine whether the corresponding scenic spot has water pollution based on the comparison result, and if there is water pollution, generate a water pollution warning signal and transmit it to the result output unit.

8. The water conservancy scenic area supervision service system according to claim 7, characterized in that, In StepA5, the comparison is as follows: If HSZ>HSZy, it means that the water pollution is serious and a water pollution warning signal is generated; If HSZ≤HSZy, no water pollution warning signal will be generated.

9. The water conservancy scenic area supervision service system according to claim 7, characterized in that, Target data includes: Water quality parameter data of corresponding attributes such as pH value, dissolved oxygen content, ammonia nitrogen content, etc. measured by a water quality sensor; Data corresponding to the tourist flow rate counted by a flow sensor.

10. The water conservancy scenic area supervision service system according to claim 9, wherein Among them, When i = 1, [SZY 1，min , SZY 1,max is the normal range of pH value, and PL1 is the deviation degree value of the pH value from the normal range; when i = 2, [SZY 2，min , SZY 2,max is the normal range of dissolved oxygen content, and PL2 is the deviation degree value of the dissolved oxygen content from the normal range; when i = 3, [SZY 3，min , SZY 3,max is the normal range of ammonia nitrogen content, and PL3 is the deviation degree value of the ammonia nitrogen content from the normal range.

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