Natural resource space planning management method and system based on territorial space element data

Abstract

The invention provides a natural resource space planning management method and system based on territorial space element data, and relates to the technical field of natural resource planning management.The method comprises the steps that firstly, the evolution driving relation of territorial space elements in a planning period is mined, and an evolution driving network is generated; bidirectionally binding the dynamically updated planning rule with an element driving path in a driving network, and constructing a rule response type element configuration guiding model; deriving an element configuration direction based on the model and generating a reference frame; collecting element real-time change signals, fusing into the framework, and optimizing element configuration details to generate a plurality of groups of planning draft plans; and finally, integrating the draft based on the driving relation strength to form a final planning result. According to the method, the scientificity, flexibility and coordination of natural resource space planning are improved.

Description

TECHNICAL FIELD

[0001] The present application relates to the technical field of natural resource planning and management, in particular to a natural resource space planning and management method and system based on land space element data. BACKGROUND

[0002] In the field of natural resource space planning and management, with the continuous deepening of land space development and utilization, the demand for scientific, accurate and dynamic planning and management is increasingly urgent. At present, the traditional natural resource space planning and management method mainly relies on static spatial data and established planning rules. The above method is usually based on limited current data and experience to set the planning scheme at the initial stage of planning, and it is difficult to fully consider the dynamic change characteristics of land space elements in a long planning period.

[0003] For example, in land use planning, it is usually only planned according to the existing land use type, topography and other factors, without in-depth analysis of the evolution driving relationship between different elements in the planning period, such as how population growth, industrial development, ecological environment change and other factors interact and promote the change of land use type. At the same time, the use of historical planning implementation feedback information is also insufficient, and the laws and lessons learned contained therein cannot be fully tapped, resulting in a lack of flexibility and adaptability of the planning scheme in the implementation process, and it is difficult to adjust and optimize in a timely manner according to the actual situation.

[0004] In addition, the existing planning and management method lacks effective constraints and guidance mechanism in element configuration, and often only allocates according to the established indicators without considering the internal relationship and mutual restraint relationship between elements, which is easy to cause unreasonable and waste of resource allocation. SUMMARY

[0005] In view of the above-mentioned problems, in combination with the first aspect of the present application, the present application provides a natural resource space planning and management method based on land space element data, which comprises: Based on the land space element data and the historical planning implementation feedback information, the evolution driving relationship of different elements in the planning period is mined, the trigger factor and transmission path of element evolution are extracted, and the land space element evolution driving network is generated; The dynamically updated space planning rules and the element driving path in the land space element evolution driving network are bidirectionally bound to construct a rule response type element configuration guidance model; Based on the rule response type element configuration guidance model, the configuration direction of the land space element is deduced based on the element evolution driving relationship as a constraint to generate an element configuration benchmark framework; Collect real-time change signals of land and space elements, integrate these signals into the element allocation benchmark framework, optimize element allocation details through the path adjustment mechanism of the rule-responsive element allocation guidance model, and generate multiple sets of natural resource spatial planning drafts. Based on the strength of the driving relationship in the evolution driving network of national land space elements, multiple natural resource spatial planning drafts are integrated in a coordinated manner to form the final natural resource spatial planning results.

[0006] Furthermore, this invention also provides a natural resource spatial planning management system based on land spatial element data, comprising: A processor; a machine-readable storage medium for storing machine-executable instructions of the processor; wherein the processor is configured to execute the above-described method for natural resource spatial planning and management based on territorial spatial element data by executing the machine-executable instructions.

[0007] Based on the above, this study mines the evolutionary driving relationships of different elements within the planning cycle by leveraging land spatial element data and historical planning implementation feedback information, generating a land spatial element evolution driving network. This allows for an understanding of the intrinsic connections and dynamic change patterns among land spatial elements. Next, dynamically updated spatial planning rules are bidirectionally bound to the element driving paths within the land spatial element evolution driving network, constructing a rule-responsive element allocation guidance model. This enables planning rules to respond and adjust in real time according to the dynamic changes of elements, enhancing the flexibility and adaptability of planning and avoiding the problems of fixed rules and lack of flexibility in traditional planning methods. Furthermore, based on the rule-responsive element allocation guidance model, the allocation direction of land spatial elements is derived, generating an element allocation benchmark framework. Real-time change signals of land spatial elements are collected and integrated into the element allocation benchmark framework. Element allocation details are optimized through a path adjustment mechanism, reflecting the actual changes in land spatial elements in a timely manner and achieving dynamic adjustment and optimization of the plan. Finally, based on the driving relationship strength in the land spatial element evolution driving network, multiple natural resource spatial planning drafts are integrated for driving coordination, forming the final natural resource spatial planning outcome, thereby improving the quality and level of natural resource spatial planning. Attached Figure Description

[0008] Figure 1 This is a schematic diagram of the execution flow of the natural resource spatial planning and management method based on land and space element data provided in the embodiments of the present invention. Detailed Implementation

[0009] The present invention will now be described in detail with reference to the accompanying drawings. Figure 1This is a flowchart illustrating a natural resource spatial planning and management method based on territorial spatial element data, provided in one embodiment of the present invention. The following is a detailed description of this natural resource spatial planning and management method based on territorial spatial element data.

[0010] Step S110: Based on land and space element data and historical planning implementation feedback information, explore the evolution driving relationship of different elements within the planning cycle, extract the triggering factors and transmission paths of element evolution, and generate a land and space element evolution driving network.

[0011] This embodiment takes the spatial planning of natural resources in a plain area as a unified application scenario. The plain area includes land space elements such as cultivated land, rivers, forest land, urban construction land, ecological protection areas, and groundwater resource distribution areas, and the planning period is five years.

[0012] Step S111: Collect land space element data, which includes topographic element data, hydrological element data, vegetation element data, construction land element data, ecological protection element data, resource distribution element data, and climate impact element data.

[0013] The collected topographic data includes data on elevation distribution, slope grade, and terrain type. Elevation distribution data covers the elevation information of all plots within the region. Slope grade data is divided into different grades according to slope ranges. Terrain type data indicates the distribution of plains, depressions, and other terrain types within the region. Hydrological data includes data on the runoff changes of major rivers, lake water level changes, and groundwater depth. Runoff change data records river flow values ​​at different time periods. Water level change data records lake water level fluctuations. Groundwater depth data indicates the groundwater depth at different locations. Vegetation data includes data on forest vegetation types, vegetation cover, and vegetation growth cycle within the region. Vegetation type data indicates the distribution of tree and shrub types. Vegetation cover data records the cover status of different plots according to percentage ranges. Vegetation growth cycle data records the growth stages of the vegetation. Construction land data includes information on the area, plot ratio, and land use type of urban construction land. Area data records the size of different urban construction land plots, plot ratio data indicates the plot ratio values ​​for different building plots, and land use type data distinguishes between residential land, commercial land, etc. Ecological protection data includes data on the boundaries of ecological protection zones, the distribution of ecologically sensitive areas, and ecological functional zoning. Boundary data indicates the specific scope of ecological protection zones, data on the distribution of ecologically sensitive areas indicates areas susceptible to disturbance, and data on ecological functional zoning distinguishes between water conservation areas, biodiversity conservation areas, etc. Resource distribution data includes data on the distribution areas of groundwater resources and the distribution locations of mineral resources. Groundwater resource distribution area data indicates the scope of groundwater-rich areas, and mineral resource distribution location data indicates the burial areas of minerals. Climate impact data includes data on regional temperature changes, precipitation distribution, wind speed, and sunshine duration. Temperature change data records temperature values ​​at different times, precipitation distribution data records precipitation in different areas, wind speed data records wind conditions in different areas according to speed ranges, and sunshine duration data records sunshine hours at different times.

[0014] Step S112: Collect historical planning implementation feedback information, which includes records of element adjustments at different planning stages, information on changes in element status after planning implementation, information on the impact of elements on the process of achieving planning goals, and information on element evolution across planning cycles.

[0015] The collected records of element adjustments across different planning phases include the content and timing of adjustments to elements such as arable land area, river protection areas, and forest coverage during the first two five-year planning cycles. The adjustment content records specific numerical values, and the adjustment time records the year and month of the adjustment. Information on changes in element status after planning implementation includes the differences between the actual arable land area and the planned target area, and the differences between the actual and planned target values ​​for river runoff after the implementation of the first two planning cycles. The difference data records specific discrepancies. Information on the impact of elements on achieving planning goals includes the promoting or hindering effect of changes in arable land area on achieving grain production targets, and the impact of changes in forest coverage on achieving ecological and environmental targets. The impact information records the direction and extent of the effect. Information on element evolution across planning cycles includes the continuous changes in arable land area and the annual changes in river runoff during the first two planning cycles. The evolution information records the element status values ​​for different years.

[0016] Step S113: Split the land space element data according to element type to form element data units, record the data attributes and spatial distribution range of each element, and construct an element data classification set.

[0017] The land space element data is broken down into categories such as topographic elements, hydrological elements, vegetation elements, construction land elements, ecological protection elements, resource distribution elements, and climate impact elements. Each element data unit records the data attributes and spatial distribution range of the corresponding element. The topographic element data unit records data attributes such as elevation, slope, and topographic type, as well as the specific distribution range of topographic types within the region; the hydrological element data unit records data attributes such as runoff, water level, and groundwater depth, as well as the distribution range of rivers and lakes within the region; the vegetation element data unit records data attributes such as vegetation type, coverage, and growth cycle, as well as the distribution range of forest land within the region; the construction land element data unit records data attributes such as area, plot ratio, and land use type, as well as the distribution range of urban construction land within the region; the ecological protection element data unit records data attributes such as protected area boundaries, distribution of sensitive areas, and functional zoning, as well as the distribution range of ecological protected areas within the region; the resource distribution element data unit records data attributes such as the distribution area of ​​groundwater resources and the location of mineral resources, as well as the range of resource distribution areas within the region; the climate impact element data unit records data attributes such as temperature, precipitation, wind force, and sunshine duration, as well as the regional range affected by climate elements. The constructed element data classification set contains element data units of the above seven element types.

[0018] Step S114: Break down historical planning implementation feedback information according to the planning cycle, divide the feedback information segments corresponding to each planning cycle, and mark the time range and corresponding planning stage of each feedback information segment.

[0019] The historical planning implementation feedback information is broken down according to the five-year planning cycle. The feedback information for the first two five-year planning cycles is divided into two feedback information segments, each corresponding to one five-year planning cycle. The time range of the first feedback information segment is from the start year to the end year of the first five-year plan, and the corresponding planning stages are the planning stage, the planning implementation stage, and the planning evaluation stage. The time range of the second feedback information segment is from the start year to the end year of the second five-year plan, and the corresponding planning stages are the same as those of the first feedback information segment.

[0020] Step S115: Bind the same type of element data in the element data classification set with the feedback information fragments of the corresponding planning period, track the status change trajectory of a single element in different planning stages, and record the time nodes and manifestations of the element status change.

[0021] The cultivated land data in the element data classification set is linked to the feedback information fragments of the first planning cycle to track the status changes of cultivated land elements during the planning, implementation, and evaluation phases of the first planning cycle. The planned area value of cultivated land elements is recorded during the planning stage, the area reduction due to urban expansion during the implementation stage, and the actual area value during the evaluation stage. Time nodes are recorded as a specific month during the planning stage, the implementation stage, and the evaluation stage, and the format is recorded as changes in area values. Similarly, river element data is linked to the feedback information fragments of the first planning cycle to track the runoff changes of river elements at different planning stages. The planned runoff value during the planning stage, the numerical fluctuations due to precipitation changes during the implementation stage, and the actual value during the evaluation stage are recorded, with time nodes and format recorded in the same way.

[0022] Step S116: Compare the state change trajectories of different elements, locate the element combinations whose change time difference within the same planning period or adjacent planning stages is less than the time synchronization threshold, and record the change order and action path of each element in the element combination.

[0023] Comparing the state change trajectories of cultivated land and urban construction land elements in the first planning cycle, it was found that the time difference between the time point of decrease in cultivated land area and the time point of increase in urban construction land area was less than the time synchronization threshold, thus identifying this element combination as a combination of cultivated land and urban construction land elements. The sequence of change in this element combination—initially an increase in urban construction land area followed by a decrease in cultivated land area—was recorded, indicating that the mechanism was the expansion of urban construction land encroaching on cultivated land. Similarly, comparing the state change trajectories of forest land and river runoff elements in the first planning cycle, it was found that the time difference between the time point of increase in forest cover and the time point of stabilization in river runoff was less than the time synchronization threshold, thus identifying this element combination as a combination of forest land and river runoff elements. The sequence of change in this element combination—initially an increase in forest cover followed by a tendency for river runoff to stabilize—was recorded, indicating that the mechanism was the increase in forest cover conserving water resources and stabilizing river runoff.

[0024] Step S117: Extract the evolutionary driving features of the combination of elements. The evolutionary driving features include the time node of the driving effect, the cycle length of the driving effect, the response pattern of the element state change, and the time span of the driving effect. At the same time, extract the specific factors that trigger the evolution of the elements and determine the correspondence between the factors and the changes in the elements.

[0025] The evolutionary driving characteristics of the combination of cultivated land and urban construction land elements are extracted. The driving point is the month in which urban construction land begins to expand, and the duration of the driving effect is the length of time from the start of urban construction land expansion to the stabilization of cultivated land area. The correlation pattern of element state changes is that the increase in urban construction land area is positively correlated with the decrease in cultivated land area, and the duration of the driving effect is the duration of urban construction land expansion. The specific factor triggering the evolution of this element combination is urban population growth, and the correspondence between urban population growth and the increase in urban construction land area and the decrease in cultivated land area is determined. The evolutionary driving characteristics of the combination of forest land and river runoff elements are also extracted. The driving point is the month in which forest land begins to be planted, and the duration of the driving effect is the length of time from the start of forest land planting to the stabilization of river runoff. The correlation pattern of element state changes is that the increase in forest land coverage is positively correlated with the degree of stability of river runoff, and the duration of the driving effect is the time of forest land growth and maturity. The specific factors that trigger the evolution of this combination of elements are the implementation of ecological protection policies, and the correspondence between the implementation of ecological protection policies and the increase in forest coverage and the stability of river runoff is determined.

[0026] Step S118: Classify the evolutionary driving relationships of all element combinations according to the spatial distribution range of the elements, and group the evolutionary driving relationships of elements within the same spatial region into one category to form a regional element-driven subset.

[0027] Based on the spatial distribution of elements, the evolutionary driving relationships of the combination of cultivated land and urban construction land elements located in the northern part of the region are grouped into one category, forming the northern regional element-driven subset; the evolutionary driving relationships of the combination of forest land and river runoff elements located in the southern part of the region are grouped into another category, forming the southern regional element-driven subset. The evolutionary driving relationships of elements within the same spatial area share the same spatial range attribute, and the regional element-driven subset records the evolutionary driving relationships of all element combinations within that spatial range.

[0028] Step S119: Integrate all regional element-driven subsets according to the time evolution order, construct a networked structure that includes spatial dimension association and time dimension evolution, and form a land space element evolution driving network. Each network member in the land space element evolution driving network corresponds to a land space element, and the connection between network members corresponds to the evolution driving relationship between elements. The member association attributes include driving characteristics, triggering factors and time markers.

[0029] Following the chronological evolution, the factor-driven subsets of the northern and southern regions are integrated to construct a network structure. Each network member corresponds to land space elements such as cultivated land, urban construction land, forest land, and river runoff. The connections between network members correspond to the evolutionary driving relationships between elements; for example, the connection between cultivated land and urban construction land elements represents their evolutionary driving relationship. Member association attributes include driving characteristics (such as the time node of the driving effect and the duration of the driving effect), triggering factors (such as urban population growth and the implementation of ecological protection policies), and time markers (such as the year and month of the driving effect). The resulting land space element evolution driving network covers the evolutionary driving relationships of all land space elements in the region.

[0030] Step S120: Bind the dynamically updated spatial planning rules to the element-driven paths in the land and space element evolution driving network in both directions to construct a rule-responsive element configuration guidance model.

[0031] Dynamically updated spatial planning rules include the latest rules for farmland protection, ecological protection, and urban construction land expansion. The factor-driven path is the interaction path between factors in the land space factor evolution driving network.

[0032] Step S121: Obtain dynamically updated spatial planning rules, which include rules related to ecological protection, rules related to construction land management, rules related to resource development and utilization, rules related to spatial layout coordination, rules related to cross-regional element allocation, and rules related to climate adaptation.

[0033] The acquired rules related to ecological protection include prohibitions on development and construction within ecological protection zones and the requirement for forest coverage to reach a certain percentage; rules related to construction land management include prohibitions on urban construction land expansion from encroaching on basic farmland and the requirement that the plot ratio of construction land not exceed a certain value; rules related to resource development and utilization include prohibitions on groundwater extraction from exceeding the exploitable amount and the requirement that mineral resource development must comply with ecological protection requirements; rules related to spatial layout coordination include the requirement that urban construction land and ecological protection zones maintain a certain distance and that cultivated land and rivers maintain a reasonable spatial layout; rules related to cross-regional resource allocation include the requirement that water resources within a region be allocated in a coordinated manner with adjacent regions and that ecological protection be implemented collaboratively with adjacent regions; and rules related to climate adaptation include the requirement that urban construction land consider responses to rainstorms and flooding and that cultivated land considers drought adaptation measures.

[0034] Step S122: Semantically decompose each spatial planning rule to extract the constraint object, applicable spatial range, specific execution requirements, and preconditions for triggering adjustment.

[0035] The rule "development and construction are prohibited within ecological protection zones" in the relevant ecological protection rules is semantically broken down. It applies to all development and construction activities within ecological protection zones, and its spatial scope is the boundary of the ecological protection zone. The specific enforcement requirement is that any development and construction activities are prohibited. The precondition for adjustment is a change in the boundary of the ecological protection zone or a significant change in the ecological environment. Similarly, the rule "urban construction land expansion shall not encroach on basic farmland" in the relevant construction land management rules is semantically broken down. It applies to the expansion of urban construction land, and its spatial scope is the distribution range of basic farmland within the region. The specific enforcement requirement is that the boundary of urban construction land expansion shall not overlap with the boundary of basic farmland. The precondition for adjustment is a change in the distribution range of basic farmland or a significant change in urban development needs.

[0036] Step S123: Analyze the attribute characteristics of the connections between network members in the land space element evolution driving network, and locate the element evolution driving relationship type corresponding to each spatial planning rule.

[0037] Analyzing the attribute characteristics of the connection between cultivated land and urban construction land in the evolutionary driving network of national land space elements, the characteristic of this connection is that the expansion of urban construction land leads to a reduction in cultivated land area. Therefore, the element evolution driving relationship corresponding to the rule "the expansion of urban construction land shall not occupy basic farmland" is identified as the driving relationship of urban construction land on cultivated land. Analyzing the attribute characteristics of the connection between forest land and river runoff, the characteristic of this connection is that increased forest cover stabilizes river runoff. Therefore, the element evolution driving relationship corresponding to the rule "forest cover must reach a certain percentage" is identified as the driving relationship of forest land on river runoff.

[0038] Step S124: Transform the execution requirements of each spatial planning rule into constraints that are compatible with the factor evolution driving relationship. The form of expression of the constraints is consistent with the attribute characteristics of the factor evolution driving relationship, so that the constraints can be directly applied to the factor driving relationship.

[0039] The implementation requirement of the rule "urban construction land expansion shall not encroach on basic farmland" is transformed into a constraint condition. This constraint condition is stated as follows: in the driving relationship between urban construction land and cultivated land, the spatial scope of urban construction land expansion shall not include the spatial scope of basic farmland. This formulation maintains consistency with the attribute characteristics (spatial scope change relationship) of the driving relationship between urban construction land and cultivated land. Similarly, the implementation requirement of the rule "forest coverage must reach a certain percentage" is transformed into a constraint condition. This constraint condition is stated as follows: in the driving relationship between forest land and river runoff, the forest coverage value must reach a specified percentage. This formulation maintains consistency with the attribute characteristics (numerical change relationship) of the driving relationship between forest land and river runoff.

[0040] Step S125: Based on the triggering adjustment preconditions of each spatial planning rule, set dynamic response standards for constraints. The dynamic response standards correspond to the specific manifestations of element state changes and describe the performance threshold of element state changes. When the element state change reaches the performance threshold, the constraint adjustment is initiated.

[0041] Step S1251: Extract the element status description content from the preconditions for triggering the adjustment of each spatial planning rule, and locate the element status change type and related element status response requirements required to trigger the spatial planning rule adjustment.

[0042] Extracting the element status description from the preconditions for triggering the adjustment of the rule "Prohibition of Development and Construction within Ecological Protection Zones," this element status description indicates a change in the boundary of the ecological protection zone or a significant change in the ecological environment. The required element status change types for triggering this rule adjustment are changes in the boundary of the ecological protection zone and changes in the ecological environment. The requirement for related element status compliance is that development and construction activities within the ecological protection zone must correspond to changes in the state of the ecological protection zone. Similarly, extracting the element status description from the preconditions for triggering the adjustment of the rule "Urban Construction Land Expansion Must Not Occupy Basic Farmland," this element status description indicates a change in the distribution range of basic farmland or a significant change in urban development needs. The required element status change types for triggering this rule adjustment are changes in the distribution range of basic farmland and changes in urban development needs. The requirement for related element status compliance is that urban construction land expansion activities must correspond to changes in the state of basic farmland.

[0043] Step S1252: Filter out feedback records related to the type of change in the status of the element from the historical planning implementation feedback information, and collect the manifestation of the change in the status of the element and the corresponding status response of the related elements.

[0044] Feedback records related to changes in the boundaries of ecological protection zones were selected from historical planning implementation feedback information. These records documented the expansion or contraction of ecological protection zone boundaries due to natural factors or human adjustments, and the corresponding responses to development and construction activities within the ecological protection zones. For example, if the boundaries expanded, the prohibited development and construction area expanded accordingly; if the boundaries contracted, the permitted development and construction area adjusted accordingly. Feedback records related to changes in the distribution range of basic farmland were also selected. These records documented the expansion or contraction of basic farmland distribution range due to land consolidation or urban development, and the corresponding responses to urban construction land expansion activities. For example, if the distribution range of basic farmland expanded, urban construction land expansion could not occupy newly added basic farmland; if the distribution range contracted, urban construction land expansion could be adjusted within the original basic farmland area.

[0045] Step S1253: Classify the feedback records according to the manifestation of the change in the state of the elements, and extract the specific characteristics of the change in the state of the elements and the response patterns of the related elements under each manifestation.

[0046] Feedback records on changes in the boundaries of ecological protection zones are categorized based on their manifestations of expansion and contraction. For expansion, the specific characteristic of the change in element status is an increase in the boundary range value, with the response pattern of related elements being a corresponding expansion of the prohibited area for development and construction activities. For contraction, the specific characteristic is a decrease in the boundary range value, with the response pattern of related elements being a corresponding adjustment of the permitted area for development and construction activities. Similarly, feedback records on changes in the distribution range of basic farmland are categorized based on their manifestations of expansion and contraction. For expansion, the specific characteristic is an increase in the distribution range value, with the response pattern of related elements being a corresponding expansion of the prohibited area for urban construction land expansion. For contraction, the specific characteristic is a decrease in the distribution range value, with the response pattern of related elements being a corresponding adjustment of the permitted area for urban construction land expansion.

[0047] Step S1254: Combine the execution requirements of each spatial planning rule, analyze the degree of deviation of each form of expression from the preset execution target of each spatial planning rule, and determine the adjustment direction of each spatial planning rule based on the degree of deviation. The adjustment direction is related to the influence range of the element state change and the response mode of the associated elements.

[0048] Based on the implementation requirements of the rule "development and construction are prohibited within ecological protection zones," this analysis examines the degree to which the expansion of ecological protection zone boundaries deviates from the pre-set implementation goals of this rule. If the expansion does not deviate from the goals, the adjustment direction is to maintain the original implementation requirements. Conversely, this analysis examines the degree to which the shrinking of ecological protection zone boundaries deviates from the pre-set implementation goals. If this expansion may lead to a reduction in the prohibited development and construction area, it deviates from the goals. The adjustment direction is to redefine the prohibited development and construction area. Similarly, based on the implementation requirements of the rule "urban construction land expansion must not occupy basic farmland," this analysis examines the degree to which the expansion of basic farmland distribution deviates from the pre-set implementation goals of this rule. If this expansion does not deviate from the goals, the adjustment direction is to maintain the original implementation requirements. Conversely, this analysis examines the degree to which the shrinking of basic farmland distribution deviates from the pre-set implementation goals. If this shrinking may lead to an expansion of the permitted area for urban construction land expansion, it deviates from the goals. The adjustment direction is to redefine the permitted area for urban construction land expansion.

[0049] Step S1255: Based on the specific characteristics of the changes in the element's state and the direction of rule adjustment, divide the changes in the element's state into different performance intervals, with each performance interval corresponding to a rule adjustment requirement.

[0050] Based on the specific characteristics of the expansion of ecological protection zone boundaries (the magnitude of the increase in boundary area values) and the direction of rule adjustments (maintaining the original implementation requirements), the expansion of ecological protection zone boundaries is divided into two ranges: a small increase in boundary area values ​​and a large increase in boundary area values. Each range corresponds to the need for rule adjustments to maintain the original implementation requirements. Similarly, based on the specific characteristics of the shrinkage of ecological protection zone boundaries (the magnitude of the decrease in boundary area values) and the direction of rule adjustments (re-clarifying the prohibited development and construction areas), the shrinkage of ecological protection zone boundaries is also divided into two ranges: a small decrease in boundary area values ​​and a large decrease in boundary area values. Each range corresponds to the need for rule adjustments to re-clarify the prohibited development and construction areas. Likewise, corresponding ranges are defined for the manifestations of changes in the distribution range of basic farmland.

[0051] Step S1256: Set a corresponding dynamic response standard for each performance interval. The dynamic response standard describes in detail the performance threshold of the element state change. When the element state change reaches the performance threshold, the corresponding rule adjustment is initiated.

[0052] For the "small increase in boundary range value" interval within the ecological protection zone boundary expansion performance range, dynamic response standards are set. The performance threshold is that the increase in boundary range value is less than a certain percentage; when the change in element status reaches this threshold, the original implementation requirements are maintained. For the "large increase in boundary range value" interval, dynamic response standards are set. The performance threshold is that the increase in boundary range value is greater than or equal to a certain percentage; when the change in element status reaches this threshold, the original implementation requirements are maintained. For the "small decrease in boundary range value" interval within the ecological protection zone boundary shrinkage performance range, dynamic response standards are set. The performance threshold is that the decrease in boundary range value is less than a certain percentage; when the change in element status reaches this threshold, the prohibited development and construction area is redefined, with a smaller adjustment. For the "large decrease in boundary range value" interval, dynamic response standards are set. The performance threshold is that the decrease in boundary range value is greater than or equal to a certain percentage; when the change in element status reaches this threshold, the prohibited development and construction area is redefined, with a larger adjustment. Similarly, corresponding dynamic response standards are set for the performance range of changes in the distribution range of basic farmland.

[0053] Step S1257: Bind the dynamic response standard to the rule adjustment direction, and describe the specific adjustment content and method of the constraint conditions when the change of the element status meets the dynamic response standard.

[0054] The dynamic response standards for expanding the ecological protection zone boundary are linked to the rule adjustment direction of maintaining the original enforcement requirements. This describes that when the increase in the ecological protection zone boundary value is less than a certain percentage, the constraint condition remains unchanged: "development and construction are prohibited within the ecological protection zone." Similarly, when the increase is greater than or equal to a certain percentage, the constraint condition also remains unchanged. The dynamic response standards for shrinking the ecological protection zone boundary are linked to the rule adjustment direction of re-clarifying the prohibited development and construction area. This describes that when the decrease in the ecological protection zone boundary value is less than a certain percentage, the constraint condition is adjusted to prohibit development and construction within the shrunken ecological protection zone boundary. When the decrease is greater than or equal to a certain percentage, the constraint condition is adjusted to prohibit development and construction within the shrunken ecological protection zone boundary, and ecological restoration requirements for the shrunken area are added. Likewise, the dynamic response standards for changes in the distribution range of basic farmland are linked to the corresponding rule adjustment direction.

[0055] Step S1258: Integrate the dynamic response standards, rule adjustment directions, and constraint adjustment contents corresponding to all spatial planning rules to form a dynamic constraint adjustment description, and incorporate it into the rule-responsive element configuration guidance model.

[0056] All spatial planning rules' corresponding dynamic response standards, rule adjustment directions, and constraint adjustment contents are integrated to form a dynamic constraint adjustment specification document. This document is categorized by spatial planning rule type, detailing the dynamic response standards, rule adjustment directions, and constraint adjustment contents for each rule. This dynamic constraint adjustment specification document is then integrated into the rule-responsive element configuration guidance model, serving as the basis for adjusting the model's constraints.

[0057] Step S126: The transformed constraints and dynamic response standards are bidirectionally bound to the corresponding element evolution driving relationships. Constraint labels are added to the corresponding connections in the land space element evolution driving network. The label content of the constraint label includes the constraint conditions and dynamic response standards.

[0058] The constraints and dynamic response standards transformed from the rule "urban construction land expansion shall not occupy basic farmland" are bidirectionally bound to the connection between urban construction land elements and cultivated land elements in the land space element evolution driving network. A constraint label is added to this connection. The label content includes the constraint condition "the spatial range of urban construction land expansion shall not include the spatial range of basic farmland" and the dynamic response standard "when the change range of basic farmland distribution is less than a certain percentage, the constraint condition remains unchanged; when the change range is greater than or equal to a certain percentage, the constraint condition is adjusted to the spatial range of urban construction land expansion shall not include the adjusted spatial range of basic farmland". The constraints and dynamic response standards transformed from the rule "forest coverage must reach a certain percentage" are bidirectionally bound to the connection between forest land elements and river runoff elements in the land space element evolution driving network. A constraint label is added to this connection, with the label content including the constraint "the value of forest coverage must reach the specified percentage" and the dynamic response standard "when the change in the value of forest coverage is less than a certain percentage, the constraint remains unchanged; when the change is greater than or equal to a certain percentage, the constraint is adjusted to the value of forest coverage must reach the adjusted percentage".

[0059] Step S127: Construct a rule transmission path based on the element evolution driving relationship with constraint labels, describing how a rule affects the transmission order and action mode of other elements through the evolution driving relationship between elements.

[0060] Based on the connection between urban construction land elements and cultivated land elements labeled with the constraint "urban construction land expansion must not occupy basic farmland," a rule transmission path is constructed. This path describes how the rule "urban construction land expansion must not occupy basic farmland" first acts on the expansion behavior of urban construction land elements, restricting their expansion scope from including basic farmland; subsequently, this rule influences the runoff status of river elements through the evolutionary driving relationship between cultivated land elements and river elements (changes in cultivated land area affect river runoff); and then, through the evolutionary driving relationship between river elements and forest land elements (changes in river runoff affect forest growth), it influences the coverage status of forest land elements. The transmission order is urban construction land elements → cultivated land elements → river elements → forest land elements, and the mode of action is to restrict the state changes of elements through constraints.

[0061] Step S128: Integrate all land space element evolution driving networks and rule transmission paths with constraint labels to construct a rule-responsive element allocation guidance model.

[0062] By integrating all the evolution-driven networks and rule transmission paths of territorial spatial elements with constraint labels, a rule-responsive element allocation guidance model is formed. This model includes the structure of the evolution-driven network of territorial spatial elements, the constraint labels of each connection, and the rule transmission paths. It can dynamically adjust the allocation direction of elements according to changes in element status and adjustments to spatial planning rules.

[0063] Step S130: Based on the rule-responsive element allocation guidance model, the allocation direction of land space elements is derived by taking the element evolution driving relationship as a constraint, and an element allocation benchmark framework is generated.

[0064] Step S131: Set the core orientation of natural resource spatial planning, which includes ecological protection orientation, spatial utilization efficiency orientation, sustainable resource utilization orientation, regional coordinated development orientation, and climate adaptation orientation.

[0065] The established ecological protection orientation is to maintain the stability of the regional ecosystem and biodiversity; the spatial utilization efficiency orientation is to improve the utilization efficiency of factors such as urban construction land and arable land; the sustainable utilization of resources orientation is to ensure the long-term availability of groundwater resources, mineral resources, etc.; the regional coordinated development orientation is to promote the coordinated development of urban areas, rural areas, ecological protection areas, etc. in the region; and the climate adaptation orientation is to improve the adaptability of factors in the region to climate change.

[0066] Step S132: Decompose the core guidance into configuration requirements that can be implemented in specific elements. The configuration requirements correspond one-to-one with the attribute dimensions of the land and space element data, describing the state characteristics that each element needs to meet under the core guidance.

[0067] The ecological protection orientation is broken down into configuration requirements such as forest coverage reaching a specified percentage, river runoff remaining stable, and ecological protection area maintaining a specified size. These configuration requirements correspond one-to-one with the forest coverage attribute, river runoff attribute, and ecological protection area area attribute, describing the required percentage value for forest coverage, the stable range for river runoff, and the maintained size for ecological protection area under the ecological protection orientation. Similarly, the spatial utilization efficiency orientation is broken down into configuration requirements such as urban construction land plot ratio reaching a specified value and cultivated land multiple cropping index reaching a specified percentage. These requirements correspond one-to-one with the urban construction land plot ratio attribute and cultivated land multiple cropping index attribute, describing the required value for urban construction land plot ratio and the required percentage for cultivated land multiple cropping index.

[0068] Step S133: Input the configuration requirements into the rule-responsive element configuration guidance model, and locate the key elements that affect the achievement of the configuration requirements through the element evolution driving relationship in the rule-responsive element configuration guidance model. The key elements are the elements that play a decisive role in the achievement of the configuration requirements.

[0069] The configuration requirement of "forest coverage must reach a specified percentage" is input into a rule-responsive element allocation guidance model. Through the evolutionary driving relationships between forest land and river runoff elements, and between forest land and ecological protection zone elements, the key elements influencing the achievement of this configuration requirement are identified as forest land, river runoff, and ecological protection zone elements. Specifically, forest land coverage directly affects the achievement of the configuration requirement, the stability of river runoff affects forest growth, and the extent of ecological protection zone elements affects forest distribution; therefore, all are key elements. Similarly, the configuration requirement of "urban construction land plot ratio must reach a specified value" is input into the model. Through the evolutionary driving relationships between urban construction land and cultivated land elements, and between urban construction land and ecological protection zone elements, the key elements influencing the achievement of this configuration requirement are identified as urban construction land, cultivated land, and ecological protection zone elements.

[0070] Step S134: Extract the constraints and rule transmission paths corresponding to the key elements in the rule-responsive element configuration-oriented model, and describe the configuration boundaries and influence scope of the key elements.

[0071] The constraints corresponding to the key element of forest land are extracted, including "forest coverage must reach the specified percentage" and "logging is prohibited in forest land within ecological protection zones." The rule transmission path is that the forest land element affects other elements through its evolutionary driving relationship with river runoff and ecological protection zone elements. The configuration boundary of the forest land element is described as the forest land area within the ecological protection zone and the forest land distribution range within the region, affecting the stability of river runoff and the balance of the ecosystem. The constraints corresponding to the key element of urban construction land are extracted, including "urban construction land expansion must not occupy basic farmland" and "plot ratio must not exceed the specified value." The rule transmission path is that the urban construction land element affects other elements through its evolutionary driving relationship with cultivated land and ecological protection zone elements. The configuration boundary of the urban construction land element is described as the construction land area of ​​urban planning, affecting changes in cultivated land area and the scope of ecological protection zones.

[0072] Step S135: Starting from the configuration requirements corresponding to the core orientation, reverse deduce the state characteristics that the key elements need to possess, and the state characteristics meet the constraints of the conditions and the logical requirements of the rule transmission path.

[0073] Starting with the configuration requirement that "forest coverage must reach a specified percentage," we can deduce the necessary characteristics of the key element, forest land, including a specified percentage of coverage and distribution covering designated areas within ecological protection zones. These characteristics comply with constraints such as "forest coverage must reach a specified percentage" and "logging is prohibited in forest areas within ecological protection zones," and also align with the logical requirements of the evolutionary relationship between forest land, river runoff, and ecological protection zone elements. Similarly, starting with the configuration requirement that "urban construction land plot ratio must reach a specified value," we can deduce the necessary characteristics of the key element, urban construction land, including a specified plot ratio and expansion without encroaching on basic farmland. These characteristics comply with the corresponding constraints and the logical requirements of the rule transmission path.

[0074] Step S136: Based on the state characteristics of the key elements, deduce the adaptation state characteristics of the related elements that have an evolutionary driving relationship with the key elements. The adaptation state characteristics correspond to the state characteristics of the key elements and meet the requirements of the element evolutionary driving relationship.

[0075] Step S1361: Extract all related elements of the key element from the rule-responsive element configuration-oriented model, and describe the evolutionary driving relationship type and action path between the key element and each related element.

[0076] The key element forestry element and its associated elements, including river elements, ecological reserve elements, and cultivated land elements, are extracted from the rule-responsive element allocation-oriented model. The evolutionary driving relationship between forestry and river elements is that forest cover affects river runoff, with the path being: increased forest cover → water conservation → stable river runoff. The evolutionary driving relationship between forestry and ecological reserve elements is that forest cover distribution affects ecological reserve area, with the path being: expanded forest cover → correspondingly expanded ecological reserve area. The evolutionary driving relationship between forestry and cultivated land elements is spatial competition between forestry and cultivated land, with the path being: increased forestry area → correspondingly decreased cultivated land area.

[0077] Step S1362: Based on the rule transmission path, analyze how the changes in the state characteristics of key elements affect each related element, and determine the type of state response that the related elements need to make.

[0078] Based on the rule-based transmission path, the impact of the forest cover reaching a specified percentage on the river element is analyzed in the following way: river runoff will remain stable, and the required state response type for the river element is to maintain runoff within a stable range. The impact of forest cover reaching a specified percentage on the ecological reserve element is analyzed in the following way: the ecological reserve area will maintain a specified size, and the required state response type for the ecological reserve element is to maintain the area at the specified value. The impact of forest cover reaching a specified percentage on the cultivated land element is analyzed in the following way: the cultivated land area will decrease accordingly, and the required state response type for the cultivated land element is to reduce the area to the specified value.

[0079] Step S1363: Based on the constraints corresponding to the associated elements themselves, describe the boundary requirements that the associated elements need to follow when making state responses, and ensure that the state responses of the associated elements do not violate the constraints.

[0080] Based on the constraint "river runoff must remain stable within a specified range" for the river element, the boundary requirement for the river element to maintain a stable runoff range is that the runoff must not be lower than the specified lower limit value or higher than the specified upper limit value. This state response does not violate the constraint. Similarly, based on the constraint "ecological reserve area must maintain a specified size" for the ecological reserve element, the boundary requirement for the ecological reserve element to maintain a specified area is that the area must not be less than the specified lower limit value or higher than the specified upper limit value. This state response does not violate the constraint. Finally, based on the constraint "cultivated land area must maintain a specified size" for the cultivated land element, the boundary requirement for the cultivated land element to reduce its area to a specified value is that the area must not be less than the specified lower limit value. This state response does not violate the constraint.

[0081] Step S1364: If the related element has an evolution-driven relationship with multiple key elements at the same time, determine the comprehensive state response requirements of the related element by comprehensively considering the state characteristics and influence methods of multiple key elements, so as to avoid the mutual conflict of the influences brought by different key elements.

[0082] Assume that the related factor, cultivated land, has an evolutionary driving relationship with both the key factors, forest land and urban construction land. The key factor, forest land, is characterized by reaching a specified percentage of land coverage, and its impact is a reduction in cultivated land area. The key factor, urban construction land, is characterized by expansion that does not encroach on basic farmland, and its impact is a reduction in cultivated land area due to urban expansion. Considering the state characteristics and impact mechanisms of these two key factors, the comprehensive state response requirement for the related factor, cultivated land, is determined to be a reduction in area to simultaneously meet the requirements of forest land coverage and urban expansion, avoiding conflicts arising from excessive or insufficient reduction in cultivated land area due to the influence of these two key factors.

[0083] Step S1365: Based on the state response type, boundary requirements, and comprehensive state response needs of the associated elements, derive the adaptive state characteristics of the associated elements. The adaptive state characteristics are used to represent the attribute performance and spatial state of the associated elements.

[0084] Based on the state response type (runoff volume remains within a stable range), boundary requirements (runoff volume is between specified upper and lower limits), and comprehensive state response requirements (no influence from multiple key elements) of the associated element, the adaptive state characteristics of the river element are deduced as: runoff volume remains within a specified stable range, the attribute is stable runoff volume, and the spatial state is uniform river flow distribution. Based on the state response type (area remains within a specified value), boundary requirements (area is between specified upper and lower limits), and comprehensive state response requirements (no influence from multiple key elements) of the associated element, the adaptive state characteristics of the ecological protection zone element are deduced as: area remains within a specified value, the attribute is stable area value, and the spatial state is fixed boundary range. Based on the state response type (area decreases to a specified value), boundary requirements (area not less than a specified lower limit), and comprehensive state response requirements (meeting the impact of forest land and urban construction land), the adaptive state characteristics of the cultivated land element are deduced as: area decreases to a specified value, the attribute is that the area value meets the requirements, and the spatial state is a corresponding adjustment in distribution range.

[0085] Step S1366: According to the requirements of the element evolution driving relationship, verify whether the adaptation state characteristics of the associated elements and the state characteristics of the key elements meet the preset state correspondence rules; if they meet the requirements, determine that the adaptation state characteristics and the state characteristics of the key elements jointly support the configuration requirements corresponding to the core guidance.

[0086] Based on the evolutionary driving relationship between forest land and river elements (increased forest cover → stable river runoff), this study verifies whether the adaptation characteristics of river elements (runoff maintained within a stable range) and the state characteristics of forest land elements (coverage reaching a specified percentage) satisfy the state correspondence rule. By comparing the state values ​​of the two, if river runoff remains within a stable range when forest cover reaches the specified percentage, the state correspondence rule is satisfied, and it is determined that both jointly support the configuration requirement of "stable river runoff" corresponding to the ecological protection orientation. Similarly, this study verifies whether the adaptation characteristics of ecological protection zone elements and cultivated land elements, and the state characteristics of the key element forest land, satisfy the state correspondence rule.

[0087] Step S1367: If the verification does not meet the preset state response rules, adjust the adaptation state features of the associated elements or the state features of the key elements until the verification meets the state response rules.

[0088] If the verification finds that the river runoff does not remain within a stable range when the forest cover reaches the specified percentage, thus failing to meet the state response rule, then the adaptation state characteristics of the river element will be adjusted, such as expanding the stable range of runoff, or the state characteristics of the forest element will be adjusted, such as increasing the specified percentage of forest cover, until the verification meets the state response rule.

[0089] Step S1368: Integrate the adaptation state features of all related elements to form a set of related element adaptation states. The set of related element adaptation states includes the adaptation state features of each related element, the corresponding key elements, and the evolution driving relationship type.

[0090] The adaptation status characteristics of all related elements are integrated to form a set of related element adaptation statuses. This set of related element adaptation statuses is classified according to the type of related element, and records in detail the adaptation status characteristics of each related element (such as the stable range of river runoff, the area value of ecological protection zone elements, etc.), the corresponding key elements (such as forest land elements, urban construction land elements, etc.), and the type of evolution driving relationship (such as forest coverage affecting river runoff, urban construction land expansion affecting cultivated land area, etc.).

[0091] Step S137: For each element, based on its state characteristics and adaptation state characteristics, determine the configuration scope, configuration form, and configuration priority of the element. The configuration scope is determined based on the spatial distribution attributes of the element, the configuration form is determined based on the attribute characteristics of the element, and the configuration priority is determined based on the contribution of the element to the preset weight indicators of the core guidance. Integrate the configuration scope, configuration form, and configuration priority of all elements to form an element configuration benchmark framework. The element configuration benchmark framework includes the specific configuration requirements of various elements, the coordination configuration relationship between elements, and the rule basis corresponding to the configuration requirements.

[0092] For forest land elements, considering their status characteristics (coverage reaching the specified percentage) and suitability characteristics (distribution range covering ecological protection zones), their allocation range is determined to be the specified areas within ecological protection zones and suitable forest distribution areas within those zones. The allocation form is a mixed planting of trees and shrubs, and the allocation priority is determined as higher priority based on its contribution to ecological protection. For river elements, considering their status characteristics (runoff volume maintained within a stable range) and suitability characteristics (distribution range covering major rivers within the region), their allocation range is determined to be the distribution area of ​​major rivers within the region. The allocation form is a natural river channel, and the allocation priority is determined as higher priority based on its contribution to ecological protection and sustainable resource utilization. For urban construction land elements, considering their status characteristics (plot ratio reaching the specified value, expansion range not occupying basic farmland) and suitability characteristics (distribution range within urban planning areas), their allocation range is determined to be the specified areas within urban planning areas. The allocation form is a high-density building form, and the allocation priority is determined as medium priority based on its contribution to spatial utilization efficiency. Integrating the allocation range, allocation form, and allocation priority of all elements forms a baseline framework for element allocation. This benchmark framework for element allocation includes specific allocation requirements for various elements (such as numerical requirements for forest coverage, river runoff, and urban construction land plot ratio), coordinated allocation relationships between elements (such as spatial distance requirements between forest land and rivers, and spatial layout requirements between urban construction land and cultivated land), and the rules and basis corresponding to the allocation requirements (such as ecological protection rules and construction land management rules).

[0093] Step S140: Collect real-time change signals of land and space elements, integrate the real-time change signals into the element allocation benchmark framework, optimize the element allocation details through the path adjustment mechanism of the rule-responsive element allocation guidance model, and generate multiple sets of natural resource spatial planning drafts.

[0094] Step S141: Construct a real-time data acquisition source for land and space elements, and continuously acquire real-time change signals of land and space elements. The real-time change signals include change signals of element attributes, change signals of element spatial distribution, change signals of element evolution driving relationships, and change signals of elements caused by external environmental influences.

[0095] The constructed real-time data acquisition sources for land and space elements include vegetation cover sensors installed in forest land, runoff monitoring instruments in rivers, plot ratio monitoring equipment in urban construction land, and area monitoring devices in ecological protection zones. Continuously acquired signals of changes in element attributes include real-time numerical changes in forest cover, real-time fluctuations in river runoff, and real-time adjustments to the plot ratio of urban construction land; signals of changes in element spatial distribution include real-time expansion or contraction of forest land distribution, real-time course changes in rivers, and real-time boundary changes in urban construction land expansion; signals of changes in element evolution driving relationships include changes in the intensity of the evolution driving relationship between forest land and rivers, and changes in the type of evolution driving relationship between urban construction land and cultivated land; signals of element changes caused by external environmental influences include surges in river runoff due to heavy rainfall, decreases in forest cover due to drought, and changes in restrictions on urban construction land expansion due to policy adjustments.

[0096] Step S142: Perform type identification on the real-time change signal to locate the type of element that has changed, the dimension of the changed attribute, the spatial range of the change, and the time node of the change.

[0097] The acquired real-time change signals were type-identified. Among the feature attribute change signals, a forest cover decrease signal was identified, pinpointing the affected feature type as forest land, the change attribute dimension as cover, the spatial range as the southern forest area within the region, and the time point as a specific date and time. Similarly, an urban construction land expansion signal was identified among the feature spatial distribution change signals, pinpointing the affected feature type as urban construction land, the change attribute dimension as spatial distribution, the spatial range as the eastern urban planning area within the region, and the time point as a specific date and time. Finally, a surge in river runoff due to heavy rainfall was identified among the feature change signals caused by external environmental influences, pinpointing the affected feature type as river, the change attribute dimension as runoff, the spatial range as the main rivers within the region, and the time point as the date and time of the heavy rainfall.

[0098] Step S143: Input the real-time change signal into the rule-responsive element configuration guidance model, and analyze the influence range and performance of the change element on other related elements through the rule transmission path in the rule-responsive element configuration guidance model.

[0099] Real-time changes in forest cover decline are input into a rule-responsive element allocation guidance model. Analysis of the model's rule transmission paths reveals the following impacts: For the river element, the impact is felt on the main rivers within the region, resulting in reduced river runoff; for the ecological reserve element, the impact is felt on the southern part of the ecological reserve, resulting in a corresponding decrease in the ecological reserve area; and for the cultivated land element, the impact is felt on the southern cultivated land within the region, resulting in a corresponding increase in cultivated land area. Similarly, real-time changes in urban construction land expansion are input into the model. Analysis shows the impact on the cultivated land element is felt on the cultivated land surrounding the eastern urban planning area, resulting in a decrease in cultivated land area; and on the ecological reserve element, the impact is felt on the boundary area of ​​the eastern ecological reserve, resulting in a corresponding decrease in the ecological reserve area.

[0100] Step S144: Extract the configuration requirements of the changed elements and the affected related elements in the element configuration baseline framework, compare the differences between the real-time change signals and the configuration requirements, and locate the configuration content that needs to be adjusted.

[0101] The configuration requirements for the forest land element in the baseline framework for element configuration are as follows: forest land element requires a coverage rate of a specified percentage; river element requires stable runoff; ecological reserve element requires a specified area size; and cultivated land element requires a specified area value. Comparing the real-time change signal of declining forest land coverage with the forest land element configuration requirements reveals that the real-time forest land coverage value is below the specified percentage, indicating that the required adjustment is to adjust the forest land coverage value. Similarly, comparing the expected impact of reduced river runoff with the river element configuration requirements reveals that river runoff will fall below the lower limit of the stable range, indicating that the required adjustment is to adjust the stable range of river runoff. Likewise, the required adjustments are identified for ecological reserve and cultivated land elements.

[0102] Step S145: Based on the constraints and dynamic response standards in the rule-responsive element configuration guidance model, construct an adjustment scheme. The adjustment scheme is used to determine the types of elements to be adjusted, the attribute dimensions to be adjusted, and the specific methods of adjustment. The adjusted configuration content meets the constraints.

[0103] Step S1451: Extract the constraints corresponding to the changing elements and affected related elements in the rule-responsive element configuration-oriented model, and describe the configuration boundaries and prohibition requirements of each element.

[0104] In the rule-based responsive element allocation-oriented model, the constraint for the changing element (forest land) is "forest coverage must reach a specified percentage," with the allocation boundary being the specified percentage value of coverage, and a prohibition requiring that coverage not fall below the lower limit of the specified percentage. The constraint for the affected related element (river) is "river runoff must remain within a stable range," with the allocation boundary being the stable range value of runoff, and a prohibition requiring that runoff not fall below the lower limit of the stable range. The constraint for the ecological protection zone element is "ecological protection zone area must maintain a specified size," with the allocation boundary being the specified area value, and a prohibition requiring that the area not fall below the lower limit of the specified value. The constraint for the cultivated land element is "cultivated land area must maintain a specified value," with the allocation boundary being the specified area value, and a prohibition requiring that the area not fall below the lower limit of the specified value.

[0105] Step S1452: Retrieve the dynamic response standards related to the changing elements in the rule-responsive element configuration guidance model, and locate the adjustment trigger conditions and rule adjustment directions corresponding to the real-time change signals.

[0106] The retrieval rule-based element allocation guidance model establishes a dynamic response standard related to the changing element of forest land. This standard states that "when the decrease in forest land coverage is less than a certain percentage, the adjustment trigger condition is to initiate forest replanting measures; when the decrease is greater than or equal to a certain percentage, the adjustment trigger condition is to initiate forest land expansion measures." The real-time change signal indicating a decrease in forest land coverage corresponds to either initiating forest replanting measures (when the decrease is less than a certain percentage) or initiating forest land expansion measures (when the decrease is greater than or equal to a certain percentage), with the rule adjustment direction being to increase forest land coverage to the specified percentage.

[0107] Step S1453: Combining constraints and dynamic response criteria, analyze the impact of the change magnitude of the changing elements on the configuration requirements, and locate the attribute dimensions that need to be adjusted. The attribute dimensions are consistent with the change attribute dimensions of the elements.

[0108] Combining the constraints of forest land elements (coverage must reach a specified percentage) and dynamic response standards (different adjustment measures are initiated based on the rate of decline), this study analyzes the impact of the rate of decline in forest land cover on allocation requirements. When the decline is less than a certain percentage, the impact is that the coverage does not meet the specified requirements, and the attribute dimension that needs adjustment is the coverage attribute. When the decline is greater than or equal to a certain percentage, the impact is that the coverage is severely below the specified requirements, and the attribute dimension that needs adjustment is also the coverage attribute.

[0109] Step S1454: For each attribute dimension that needs to be adjusted, refer to the original configuration requirements in the feature configuration baseline framework, and combine real-time change signals and rule adjustment directions to propose multiple adjustment alternatives.

[0110] Regarding the forest land element's coverage attribute dimension, and referring to the original configuration requirements (coverage reaching a specified percentage) in the element configuration benchmark framework, this paper proposes several adjustment options based on real-time changes in forest land coverage and the rule-based adjustment direction for increasing coverage. When the decline is less than a certain percentage, adjustment options include replanting suitable arbor species in existing forest land and increasing the planting density of shrubs. When the decline is greater than or equal to a certain percentage, adjustment options include expanding the distribution range of forest land to suitable unused land and converting some plots of cultivated land into forest land.

[0111] Step S1455: Analyze the impact of each adjustment alternative on the driving relationship of factor evolution, and monitor whether adjusting the alternative will cause other factors to violate the constraints.

[0112] This analysis examines the impact of the alternative adjustment, "replanting suitable tree species within existing forest land," on the evolutionary drivers of factors. This approach increases forest cover, thereby affecting the evolutionary drivers between forest land and river factors (increased cover → water conservation → stable river runoff). The analysis monitors whether this approach would cause the river factor to violate the constraint condition (runoff maintaining a stable range). The analysis shows that this approach will not cause the river factor to violate the constraint condition because increased cover will stabilize river runoff within the specified range. The analysis also examines the impact of the alternative adjustment, "expanding the distribution range of forest land to suitable unused land," on the evolutionary drivers of factors. This approach expands the distribution range of forest land, affecting the evolutionary drivers between forest land and cultivated land factors (expanded forest land area → correspondingly reduced cultivated land area). The analysis monitors whether this approach would cause the cultivated land factor to violate the constraint condition (area maintaining a specified value). The analysis shows that if the expanded forest land area is unused land, it will not lead to a reduction in cultivated land area, and therefore will not violate the constraints of the cultivated land factor.

[0113] Step S1456: Select the adjustment options that will not cause other elements to violate the constraints and that conform to the adjustment direction of the rules, and use them as valid adjustment options.

[0114] The following adjustment options were selected: "replanting suitable tree species in existing forest land", "increasing the planting density of shrubs", and "expanding the distribution range of forest land to suitable unused land". These options do not cause other elements to violate the constraints and are in line with the adjustment direction of increasing forest coverage. Therefore, they are considered as effective adjustment options.

[0115] Step S1457: Evaluate and rank the effective adjustment methods, and give priority to the adjustment methods whose negative impact on the evaluation index of the coordination relationship between elements is lower than the preset impact threshold and whose adaptability to real-time change signals is higher than the preset adaptability threshold.

[0116] Effective adjustment methods were evaluated and ranked, with evaluation indicators including the impact on the coordination between forest land and river elements, the impact on the coordination between forest land and cultivated land elements, and adaptability to real-time change signals. The method of "replanting suitable tree species in existing forest land" had a low negative impact on the coordination between elements and a high adaptability to real-time change signals, therefore it was ranked first. The method of "expanding the distribution range of forest land to suitable unused land" had a low negative impact on the coordination between elements and a high adaptability, ranking second. The method of "increasing the planting density of shrubs" had a slightly higher negative impact on the coordination and a slightly lower adaptability, ranking last. The adjustment methods ranked first were given priority.

[0117] Step S1458: Based on the preferred adjustment method, determine the types of elements to be adjusted, the attribute dimensions to be adjusted, and the specific operational content of the adjustment to form an adjustment plan.

[0118] Based on the preferred adjustment method of "replanting suitable arbor species in existing forest land," the adjustment element type is determined to be forest land, the attribute dimension is the coverage attribute, and the specific operation is to replant a specified number of arbor species in the southern forest land of the region. The replanted species must be suitable for local growth, and the replanting time is the current year's planting season. Based on the adjustment method of "expanding the distribution range of forest land to suitable unused land," the adjustment element type is determined to be forest land, the attribute dimension is the spatial distribution attribute, and the specific operation is to designate the unused land in the eastern part of the region as forest land and plant suitable arbor and shrub species.

[0119] Step S1459: Compare the adaptation of the adjustment scheme with the rule-responsive element configuration guidance model. All adjustments in the adjustment scheme meet the constraints and dynamic response standards.

[0120] The compatibility of the adjustment plan "replanting suitable tree species in existing forest land" with the rule-responsive element allocation guidance model was compared, and it was checked whether the adjustment content met the constraints of the forest land element (coverage must reach the specified percentage) and the dynamic response standard (adjustment measures are initiated according to the decline). The check showed that the adjustment plan met the constraints and dynamic response standard, and the compatibility was good. The compatibility of the adjustment plan "expanding the distribution range of forest land to suitable unused land" with the model was also compared, and its compliance with the constraints and dynamic response standard was also checked; the compatibility was good.

[0121] Step S14510: If the adaptation meets the requirements, determine the adjustment plan as the final adjustment plan; if it does not meet the requirements, modify the adjustment method until the adaptation meets the requirements.

[0122] Since both adjustment schemes meet the requirements, they are determined to be the final adjustment schemes. If the suitability of one of the adjustment schemes is not met, such as the replanted tree species being unsuitable for local growth, resulting in the inability to increase forest coverage, the adjustment method will be modified, such as changing the replanted tree species, until the suitability meets the requirements.

[0123] Step S146: Apply the adjustment scheme to the element configuration baseline framework, modify the configuration requirements of the changed elements and the affected related elements, and form the adjusted element configuration scheme.

[0124] The adjustment scheme of "replanting suitable tree species in existing forest land" is applied to the baseline framework for resource allocation. The allocation requirements for forest land are modified to ensure that the coverage reaches a specified percentage after replanting; the allocation requirements for river elements are modified to ensure that runoff remains stable after the forest coverage increases; the allocation requirements for ecological protection zones are modified to ensure that the area remains at a specified size after the forest coverage increases; and the allocation requirements for cultivated land elements are modified to ensure that the area remains at the original specified value. The adjustment scheme of "expanding the distribution range of forest land to suitable unused land" is also applied to the framework. The allocation requirements for forest land elements are modified to expand the distribution range to eastern unused land and ensure that the coverage reaches a specified percentage; the allocation requirements for river elements are modified to ensure that runoff remains stable after the forest land area is expanded; the allocation requirements for ecological protection zones are modified to ensure that the area expands accordingly after the forest land area is expanded; and the allocation requirements for cultivated land elements are modified to ensure that the area remains at the original specified value. This results in two adjusted resource allocation schemes.

[0125] Step S147: Based on the rule-responsive element configuration guidance model, simulate the evolution driving effect of each element in the adjusted element configuration scheme, and monitor the coordination relationship between elements and the fit of the core guidance.

[0126] Based on a rule-responsive element allocation guidance model, this study simulates the evolutionary driving effect of the adjustment scheme of "replanting suitable tree species in existing forest land". The simulation shows that after replanting, forest cover gradually increases to a specified percentage, river runoff gradually recovers to a stable range, the area of ​​ecological protection zones remains at a specified size, and the cultivated land area remains at its original specified value. The study monitors the coordination relationships between elements, such as the coordination between forest land and rivers (the correspondence between cover and runoff), and the coordination between forest land and ecological protection zones (the correspondence between cover and area), and their alignment with ecological protection and sustainable resource utilization guidelines. The study also simulates the evolutionary driving effect of the adjustment scheme of "expanding the distribution range of forest land to suitable unused land", monitoring the alignment of the coordination relationships between elements with the core guidelines.

[0127] Step S148: If the simulation results show that the coordination relationship between elements meets the preset coordination threshold, then the adjusted element configuration scheme is retained; if it does not meet the threshold, then the configuration content is adjusted again based on the rule transmission path until the simulation results meet the coordination threshold.

[0128] A coordination threshold is set when the degree of fit between elements reaches a specified percentage. If the simulation results of the adjustment scheme "replanting suitable tree species in existing forest land" show that the degree of fit between elements reaches the specified percentage, the adjusted element configuration scheme is retained; if not, the configuration content is adjusted again based on the rule transmission path, such as increasing the number of replanted tree species or changing the replanted tree species, until the simulation results meet the coordination threshold. Similarly, the simulation results of the adjustment scheme "expanding the distribution range of forest land to suitable unused land" are processed.

[0129] Step S149: For different types of real-time change signals, repeat the adjustment process to form multiple sets of adjusted element configuration schemes, each set of adjusted element configuration schemes corresponding to a combination of real-time change signals.

[0130] For real-time changes in urban construction land expansion, the above adjustment process is repeated to construct adjustment schemes, which are then applied to the baseline framework for resource allocation to simulate evolutionary effects. Adjustment schemes that meet the coordination threshold are retained. Similarly, for real-time changes in river runoff caused by torrential rain, the adjustment process is repeated to form corresponding adjustment schemes. Ultimately, multiple sets of adjusted resource allocation schemes are formed, each corresponding to a combination of real-time changes, such as the combination of declining forest cover and urban construction land expansion, or the combination of declining forest cover and torrential rain.

[0131] Step S1410: Classify and integrate the multiple sets of adjusted element allocation schemes to form multiple sets of natural resource spatial planning drafts. Each set of natural resource spatial planning drafts contains complete element allocation requirements and descriptions of coordination relationships between elements.

[0132] The adjusted resource allocation schemes were categorized and integrated according to the type of real-time change signal combination. Combinations containing forest cover reduction adjustment schemes were grouped into one category and integrated into a set of natural resource spatial planning drafts; combinations containing urban construction land expansion adjustment schemes were grouped into another category and integrated into a third set of drafts; and combinations containing rainstorm adjustment schemes were grouped into a third set of drafts. Each set of drafts includes complete resource allocation requirements (such as numerical requirements for forest cover, river runoff, and urban construction land plot ratio) and descriptions of the coordination relationships between resources (such as the coordination relationship between forest land and rivers, and the coordination relationship between urban construction land and cultivated land).

[0133] Step S150: Based on the strength of the driving relationship in the evolution driving network of national land space elements, integrate multiple natural resource spatial planning drafts in a coordinated manner to form the final natural resource spatial planning results.

[0134] Step S151: Extract element-driven features from the evolution-driven network of land space elements. The element-driven features include the frequency of the effect of the evolution-driven relationship between elements, the duration of the element-driven relationship, the length of the transmission path of the element-driven relationship, and the spatial distribution of the element-driven relationship.

[0135] The driving characteristics of the elements were extracted from the evolutionary network of land space elements. The frequency of the driving relationship between elements is the number of times the driving relationship between forest land and river elements occurred in the historical planning cycle, and the number of times the driving relationship between urban construction land and cultivated land elements occurred. The duration of the driving relationship is the duration of the driving relationship between forest land and river elements, and the duration of the driving relationship between urban construction land and cultivated land elements. The length of the transmission path of the driving relationship is the number of elements included in the transmission path of forest land → river → ecological protection zone, and the number of elements included in the transmission path of urban construction land → cultivated land → ecological protection zone. The spatial distribution of the driving relationship is that the driving relationship between forest land and river is more obvious in the southern part of the region, and the driving relationship between urban construction land and cultivated land is more obvious in the eastern part of the region.

[0136] Step S152: Perform element configuration-driven coordination analysis on each group of natural resource spatial planning drafts. By calculating the matching degree between the element configuration in the draft and the element-driven features, locate the configuration content with a matching degree higher than the preset matching threshold and the configuration content with a matching degree lower than the preset matching threshold.

[0137] A coordination analysis of factor allocation-driven factors was conducted on the draft natural resource spatial planning that included an adjustment plan for declining forest cover. The matching degree between the forest cover allocation requirements in the draft and the factor-driven characteristics such as the frequency and duration of the driving relationship between forest land and rivers was calculated. If the matching degree was higher than a preset matching threshold, the allocation content was identified as having a high matching degree; if it was lower than the threshold, it was identified as having a low matching degree. Similarly, the draft plans that included adjustments for urban construction land expansion and those that included adjustments for rainstorms were analyzed to identify allocation content with high and low matching degrees.

[0138] Step S153: Classify the configuration content in all natural resource spatial planning drafts according to the frequency of action of the factor-driven relationship, and group the configuration content involving factor-driven relationships that rank in the top preset position in terms of frequency of action into one category to form a core configuration set.

[0139] Based on the frequency of influence of factor-driven relationships from high to low, the configuration content related to the top three factor-driven relationships (such as the relationship between forest land and rivers, the relationship between urban construction land and cultivated land, and the relationship between ecological protection zones and forest land) is grouped into one category, forming a core configuration set. This core configuration set includes requirements for forest land coverage, river runoff, urban construction land plot ratio, cultivated land area, and ecological protection zone area.

[0140] Step S154: Extract the common configuration content of all natural resource spatial planning drafts in the core configuration set as the basic configuration content. The basic configuration content is the configuration requirements that conform to the element-driven characteristics and are consistent in all natural resource spatial planning drafts.

[0141] Extract the common configuration content of all natural resource spatial planning drafts in the core configuration set, such as forest coverage needing to reach the specified percentage, river runoff needing to maintain a stable range, urban construction land plot ratio needing to reach the specified value, cultivated land area needing to maintain the specified size, and ecological protection area needing to maintain the specified value. These contents are the configuration requirements that conform to the factor-driven characteristics and are consistent in all drafts, and are used as the basic configuration content.

[0142] Step S155: Locate configuration content in the core configuration set that differs but all conform to the element-driven characteristics, and use it as optional configuration content. Analyze the supporting role of the optional configuration content in the core guidance.

[0143] The core configuration set includes configurations that differ but all conform to the characteristics of element-driven features. For example, the specific value of forest cover varies across different drafts (some require a certain percentage, others a different percentage, but all conform to the driving relationship between forest and river), and the specific scope of urban construction land expansion varies across different drafts (some require expansion to a certain area in the east, others to a certain area in the west, but all conform to the driving relationship between urban construction land and cultivated land). These are considered optional configurations. The supporting role of optional configurations for the core orientation is analyzed. For example, configurations with higher forest cover strongly support the orientation of ecological protection, while configurations with smaller urban construction land expansion areas strongly support the orientation of spatial utilization efficiency.

[0144] Step S156: Evaluate the optional configuration content based on the duration of the element-driven relationship and the length of the transmission path, select the optional configuration content that supports the core guidance and meets the requirements of the core guidance setting, and integrate it into the basic configuration content.

[0145] For example, step S1561: Extract the continuous periodic information of the factor-driven relationship in the evolution-driven network of land space elements, describe the continuous performance of each factor-driven relationship in different planning cycles, and record the factor-driven relationship whose continuous period covers multiple planning cycles and the factor-driven relationship that only covers a single planning cycle.

[0146] The continuous periodic information of the driving relationships between elements in the evolutionary network of national land space elements is extracted. The driving relationship between forest land and rivers has been observed in the past three planning cycles, with a continuous period covering multiple planning cycles; the driving relationship between urban construction land and cultivated land has been observed in the past two planning cycles, with a continuous period covering multiple planning cycles; the driving relationship between ecological protection zones and forest land has been observed in the past planning cycle, with a continuous period covering only a single planning cycle. This continuous periodic information is recorded.

[0147] Step S1562: Extract the transmission path length information of the element-driven relationship in the evolution-driven network of national spatial elements, and describe the number of network members and path coverage of the transmission path of the evolution-driven effect between elements.

[0148] Extract the path length information of the driving relationships between elements in the evolutionary network of national spatial elements. The path from forest land to river to ecological reserve contains three network members, covering the southern and central regions of the area; the path from urban construction land to cultivated land to ecological reserve contains three network members, covering the eastern and central regions of the area; and the path from ecological reserve to forest land contains two network members, covering the southern region of the area. Describe the path length information of these paths.

[0149] Step S1563: Decompose the optional configuration content and analyze the element-driven relationship type involved in each optional configuration content.

[0150] The optional configuration option "Forest coverage at a relatively high percentage" is broken down, and the driving relationships involved are analyzed as follows: the driving relationship between forest land and rivers, and the driving relationship between forest land and ecological protection zones. Similarly, "Forest coverage at a relatively low percentage" is broken down, and the driving relationships involved are also the same: the driving relationship between forest land and rivers, and the driving relationship between forest land and ecological protection zones. The option "Urban construction land expands to a certain area in the east" is also broken down, and the driving relationships involved are also the same: the driving relationship between urban construction land and cultivated land, and the driving relationship between urban construction land and ecological protection zones. Finally, the option "Urban construction land expands to a certain area in the west" is also broken down, and the driving relationships involved are also the same: the driving relationship between urban construction land and cultivated land, and the driving relationship between urban construction land and ecological protection zones.

[0151] Step S1564: Evaluate the adaptability of optional configuration content for factor-driven relationships that depend on a continuous period covering more than one planning period across multiple periods. If the configuration content meets the core orientation requirements in all planning periods covered by the factor-driven relationship, it is included in the priority consideration.

[0152] The optional configuration "forest coverage at a relatively high percentage" is evaluated because the driving relationship between forest land and rivers, upon which this configuration depends, spans multiple planning cycles. The evaluation examined whether this configuration complies with ecological protection guidelines in the past three planning cycles. The evaluation found that this configuration has ensured stable river runoff in the past three planning cycles, thus meeting the requirements of ecological protection guidelines and is therefore included in the priority consideration scope. The optional configuration "expansion of urban construction land to a certain area in the east" is also evaluated because the driving relationship between urban construction land and cultivated land, upon which this configuration depends, spans multiple planning cycles. The evaluation examined whether this configuration complies with spatial utilization efficiency guidelines in the past two planning cycles. The evaluation found that this configuration can improve the utilization efficiency of urban construction land, meeting the requirements of spatial utilization efficiency guidelines and is therefore included in the priority consideration scope.

[0153] Step S1565: Evaluate the optional configuration content of the element-driven relationship where the number of network members in the dependency transmission path is lower than the system statistical average, and whether its influence diffusion range matches the spatial influence range preset by the core guidance. Include the matching optional configuration content in the priority consideration range.

[0154] In this embodiment, the statistical average is the average number of network members in the transmission path, assumed to be three. The optional configuration "maintaining the area of ​​the ecological protection zone at a relatively large value" is evaluated. The number of network members in the ecological protection zone → forest transmission path, upon which this configuration depends, is two, lower than the system statistical average. Checking whether its impact diffusion range matches the preset spatial impact range of the ecological protection orientation, the evaluation finds that the impact diffusion range of this configuration is the southern area of ​​the ecological protection zone, matching the preset spatial impact range of the ecological protection orientation; therefore, it is included in the priority consideration range. The optional configuration "maintaining the multiple cropping index of arable land at a relatively high percentage" is also evaluated. The number of network members in the arable land → river transmission path, upon which this configuration depends, is two, lower than the system statistical average. Checking whether its impact diffusion range matches the preset spatial impact range of the resource sustainable utilization orientation, the evaluation finds that the impact diffusion range of this configuration is the arable land distribution area within the region, matching the preset spatial impact range of the resource sustainable utilization orientation; therefore, it is included in the priority consideration range.

[0155] Step S1566: Combining the long-term adaptability assessment results and the assessment results of the impact diffusion scope and the alignment with the core orientation, a comprehensive score is given to each optional configuration content according to the preset scoring rules.

[0156] The preset scoring rules are as follows: 60% for the long-term adaptability assessment result, and 40% for the impact diffusion range and core orientation alignment assessment result. For the optional configuration item "forest coverage at a certain high percentage," a comprehensive score is applied. If the long-term adaptability assessment result is "meets the requirements," the score is 90 out of 100; if the impact diffusion range and core orientation alignment assessment result is "matches," the score is also 90. The comprehensive score is 90 multiplied by 60% plus 90 multiplied by 40%, equaling 90. For the optional configuration item "expansion of urban construction land to a certain area in the east," a comprehensive score is applied. If the long-term adaptability assessment result is 80, and the impact diffusion range alignment assessment result is 85, the comprehensive score is 80 multiplied by 60% plus 85 multiplied by 40%, equaling 83. Similarly, other optional configuration items are comprehensively scored.

[0157] Step S1567: Sort the optional configuration content according to the comprehensive scoring results, and select the optional configuration content whose scoring results are higher than the preset support score threshold.

[0158] The preset support score threshold is 80 points. Based on the overall score results, from highest to lowest, the optional configuration items are ordered as follows: "Forest coverage reaches a certain high percentage" (90 points), "Urban construction land expands to a certain area in the east" (83 points), "Ecological protection zone area maintains a certain high value" (87 points), "Cultivated land multiple cropping index maintains a certain high percentage" (84 points), etc. Selecting optional configuration items with a score higher than 80 points includes all of the above.

[0159] Step S1568: Analyze the consistency between the selected optional configuration content and the basic configuration content. When the selected optional configuration content and the basic configuration content do not conflict under the preset rule logic, the selected optional configuration content is integrated into the basic configuration content.

[0160] The consistency between the selected optional configuration "forest coverage at a certain high percentage" and the basic configuration "forest coverage must reach a specified percentage" is analyzed. Under the preset rule logic (forest coverage must conform to the driving relationship between forest land and rivers), there is no conflict between the two. Therefore, this optional configuration is integrated into the basic configuration, and the forest coverage requirement in the basic configuration is modified to a certain high percentage. Similarly, the consistency between the selected optional configuration "urban construction land expansion to a certain area in the east" and the basic configuration "urban construction land plot ratio must reach a specified value" is analyzed. Under the preset rule logic (urban construction land expansion must conform to the driving relationship between urban construction land and cultivated land), there is no conflict between the two. Therefore, this optional configuration is integrated into the basic configuration, and the urban construction land expansion range requirement in the basic configuration is modified to a certain area in the east. Likewise, the consistency between other selected optional configurations and the basic configurations is analyzed, and content without conflict is integrated into the basic configurations.

[0161] Step S1569: If a conflict exists, adjust the conflicting parts based on element-driven features and core orientation so that the selected optional configuration content can be integrated into the basic configuration content.

[0162] If the selected optional configuration "maintain a certain minimum cultivated land area" conflicts with the basic configuration "cultivated land area must be maintained at a specified size" (the minimum cultivated land area is lower than the specified size), the conflicting part will be adjusted based on the factor-driven characteristics (the driving relationship between cultivated land and urban construction land) and the core orientation (spatial utilization efficiency orientation). The optional configuration will be adjusted to maintain the specified cultivated land area, or the basic configuration will be adjusted to allow the cultivated land area to be appropriately reduced but not lower than a certain lower limit, so that the optional configuration can be integrated into the basic configuration.

[0163] Step S15610: Integrate the adjusted optional configuration content with the basic configuration content, update the basic configuration content, and form an integrated configuration set that includes the basic configuration content and the selected optional configuration content.

[0164] The adjusted optional configuration content is integrated with the basic configuration content, and the basic configuration content is updated. The integrated basic configuration content includes forest coverage at a certain high percentage, river runoff maintained within a stable range, urban construction land plot ratio reaching a specified value and expanding to a certain area in the east, cultivated land area maintained at a specified size, and ecological protection area maintained at a certain large value, forming an integrated configuration set.

[0165] Step S157: For the configuration content in the draft natural resource spatial planning that does not conform to the factor-driven characteristics, refer to the factor-driven characteristics in the land spatial factor evolution driving network and the constraints in the rule-responsive factor configuration guidance model, construct a correction scheme, modify the non-conforming configuration content, and make it conform to the factor-driven characteristics.

[0166] To address configuration elements in draft natural resource spatial planning that do not conform to factor-driven characteristics, such as a draft requiring forest coverage to be below a specified percentage (contrary to the driving relationship between forest land and rivers) or a draft requiring urban construction land expansion to encroach on basic farmland (contrary to the driving relationship between urban construction land and arable land), this paper proposes a revised scheme. This scheme references the factor-driven characteristics in the national spatial element evolution driving network (forest coverage must reach a specified percentage to stabilize river runoff, and urban construction land expansion must not encroach on basic farmland to maintain arable land area) and the constraints in the rule-responsive factor allocation guidance model (forest coverage must reach a specified percentage, and urban construction land expansion must not encroach on basic farmland). The revised scheme includes increasing forest coverage to the specified percentage and adjusting the scope of urban construction land expansion to areas that do not encroach on basic farmland. The revised configuration elements are modified to conform to factor-driven characteristics.

[0167] Step S158: Integrate the revised configuration content with the basic configuration content and the selected optional configuration content to form a unified element configuration framework. The element configuration framework includes the configuration requirements of all elements, the coordination relationship between elements, and the element driving basis corresponding to the configuration requirements.

[0168] The revised configuration content (such as increased forest coverage and adjusted urban construction land expansion range) is integrated with the basic configuration content and selected optional configuration content to form a unified element configuration framework. This element configuration framework includes the configuration requirements of all elements (such as numerical requirements for forest coverage, river runoff, urban construction land plot ratio, cultivated land area, and ecological protection zone area), the coordination relationships between elements (such as the coordination relationship between forest land and rivers, urban construction land and cultivated land, and ecological protection zones and forest land), and the element driving basis corresponding to the configuration requirements (such as the driving relationship between forest land and rivers corresponding to forest coverage requirements, and the driving relationship between urban construction land and cultivated land corresponding to urban construction land expansion range requirements).

[0169] Step S159: Structure and integrate the element configuration framework according to spatial region and element type, and describe the configuration requirements and mutual coordination relationships of various elements in each spatial region.

[0170] The resource allocation framework is divided into southern, eastern, central, and western regions based on spatial area, and into forest land, river, urban construction land, arable land, and ecological protection zone elements based on resource type. The requirements for forest land allocation in the southern region are described as achieving a high percentage of coverage; for river allocation, runoff must remain within a stable range; for arable land allocation, area must remain at a specified size; and for ecological protection zone allocation, area must remain at a relatively large value. The interrelationships between these elements are also described (e.g., increased forest coverage → stable river runoff → maintained ecological protection zone area → stable arable land area). Similarly, the requirements for urban construction land allocation in the eastern region are described as achieving a specified plot ratio and expanding to a certain area; for arable land allocation, area must remain at a specified size; and for ecological protection zone allocation, area must remain at a specified value. The interrelationships between these elements are also described (e.g., expansion of urban construction land → stable arable land area → maintained ecological protection zone area). Likewise, the allocation requirements and interrelationships of various elements in the central and western regions are described.

[0171] Step S1510: Transform the structured and integrated element allocation framework into a standardized planning expression form to form the final natural resource spatial planning result. The natural resource spatial planning result includes spatial layout planning, element allocation planning, coordination relationship description, and rule basis description.

[0172] The structured and integrated element allocation framework is transformed into a standardized planning expression, forming the final natural resource spatial planning outcome. The spatial layout planning section describes the distribution range and layout of various elements by spatial region; the element allocation planning section describes the allocation requirements of various elements by element type (such as numerical requirements for coverage, plot ratio, and area); the coordination relationship description section describes the interaction and responsiveness requirements between elements by type of coordination relationship; and the rule basis description section describes the rule basis corresponding to the allocation requirements by type of spatial planning rule (such as ecological protection rules, construction land control rules, etc.). The final natural resource spatial planning outcome is presented in the form of a formal planning text, containing all the above content, and can be used to guide the implementation of natural resource spatial planning in the region.

[0173] In an exemplary embodiment, a natural resource spatial planning and management system based on land spatial element data is provided. This system can be a terminal, server, etc. The system includes a processor, memory, input / output interface, communication interface, display unit, and input device. The processor, memory, and input / output interface are connected via a system bus, and the communication interface, display unit, and input device are also connected to the system bus via the input / output interface. The processor provides computing and control capabilities. The memory includes a non-volatile storage medium and internal memory. The non-volatile storage medium stores an operating system and computer programs. The internal memory provides an environment for the operation of the operating system and computer programs in the non-volatile storage medium. The input / output interface is used for exchanging information between the processor and external devices. The communication interface is used for wired or wireless communication with external terminals; wireless communication can be achieved through Wi-Fi, mobile cellular networks, near-field communication, or other technologies. When the computer program is executed by the processor, it implements a natural resource spatial planning and management method based on land spatial element data. The display unit is used to form a visually visible image and can be a display screen, projection device, or virtual reality imaging device. The display screen can be an LCD screen or an e-ink screen. The input device can be a touch layer covering the display screen, or a button, trackball, or touchpad set on the shell of the natural resources spatial planning management system based on land spatial element data, or an external keyboard, touchpad, or mouse, etc.

[0174] It should be noted that, in order to simplify the description of the present invention and thus help to understand one or more embodiments of the invention, multiple features may sometimes be grouped into one embodiment, drawing or description thereof in the foregoing description of the embodiments of the present invention.

Claims

1. A method for natural resource spatial planning and management based on land and space element data, characterized in that, The method includes: Based on land and space element data and historical planning implementation feedback information, we explore the evolutionary driving relationships of different elements within the planning cycle, extract the triggering factors and transmission paths of element evolution, and generate a land and space element evolution driving network. By bidirectionally binding the dynamically updated spatial planning rules with the element-driven paths in the land and space element evolution driving network, a rule-responsive element allocation guidance model is constructed. Based on the rule-responsive element allocation guidance model, the allocation direction of land space elements is derived by taking the element evolution driving relationship as a constraint, and a benchmark framework for element allocation is generated. Collect real-time change signals of land and space elements, integrate these signals into the element allocation benchmark framework, optimize element allocation details through the path adjustment mechanism of the rule-responsive element allocation guidance model, and generate multiple sets of natural resource spatial planning drafts. Based on the strength of the driving relationship in the evolution driving network of national land space elements, multiple natural resource spatial planning drafts are integrated in a coordinated manner to form the final natural resource spatial planning results.

2. The method for natural resource spatial planning management based on territorial spatial element data according to claim 1, characterized in that, The process, based on land and space element data and historical planning implementation feedback information, mines the evolutionary driving relationships of different elements within the planning cycle, extracts the triggering factors and transmission paths of element evolution, and generates a land and space element evolution driving network, including: Collect land and space element data, which includes topographic element data, hydrological element data, vegetation element data, construction land element data, ecological protection element data, resource distribution element data, and climate impact element data; Collect historical planning implementation feedback information, which includes records of element adjustments at different planning stages, information on changes in element status after planning implementation, information on the impact of elements on the process of achieving planning goals, and information on element evolution across planning cycles. Land space element data is broken down by element type to form element data units. Data attributes and spatial distribution range of each element are recorded to construct a set of element data classifications. Historical planning implementation feedback information is broken down according to planning cycle, and feedback information segments corresponding to each planning cycle are divided, with the time range and corresponding planning stage of each feedback information segment marked. Bind similar element data in the element data classification set with feedback information fragments of the corresponding planning cycle to track the status change trajectory of a single element in different planning stages and record the time nodes and manifestations of element status changes. By comparing the state change trajectories of different elements, we can locate the combination of elements whose change time difference within the same planning period or adjacent planning stages is less than the time synchronization threshold, and record the change order and action path of each element in the combination of elements. The evolutionary driving features of the combination of elements are extracted. These features include the time node of the driving effect, the duration of the driving effect, the response pattern of the changes in the state of the elements, and the duration of the driving effect. At the same time, the specific factors that trigger the evolution of the elements are extracted, and the correspondence between the factors and the changes in the elements is determined. The evolutionary driving relationships of all element combinations are classified according to the spatial distribution range of the elements. The evolutionary driving relationships of elements within the same spatial region are grouped into one category to form a regional element-driven subset. By integrating all regional element-driven subsets in chronological order of evolution, a networked structure containing spatial dimension association and temporal dimension evolution is constructed to form a land space element evolution-driven network. Each network member in the land space element evolution-driven network corresponds to a land space element, and the connections between network members correspond to the evolution-driven relationship between elements. The member association attributes include driving characteristics, triggering factors, and time markers.

3. The method for natural resource spatial planning and management based on territorial spatial element data according to claim 1, characterized in that, The method of bidirectionally binding dynamically updated spatial planning rules with element-driven paths in the land and space element evolution driving network to construct a rule-responsive element allocation guidance model includes: Obtain dynamically updated spatial planning rules, which include rules related to ecological protection, rules related to construction land management, rules related to resource development and utilization, rules related to spatial layout coordination, rules related to cross-regional factor allocation, and rules related to climate adaptation. Each spatial planning rule is semantically decomposed to extract the constraint object it targets, the applicable spatial scope, the specific execution requirements, and the preconditions for triggering adjustments. Analyze the attribute characteristics of the connections between network members in the evolution-driven network of national spatial elements, and locate the element evolution-driven relationship type corresponding to each spatial planning rule; The execution requirements of each spatial planning rule are transformed into constraints that are adapted to the driving relationship of element evolution. The form of expression of the constraints is consistent with the attribute characteristics of the driving relationship of element evolution, so that the constraints can be directly applied to the driving relationship of elements. Based on the triggering adjustment preconditions of each spatial planning rule, dynamic response standards for constraints are set. These dynamic response standards correspond to the specific manifestations of changes in element status and describe the performance thresholds of changes in element status. When the changes in element status reach these performance thresholds, the constraints are adjusted. The transformed constraints and dynamic response standards are bidirectionally bound to the corresponding element evolution driving relationships. Constraint labels are added to the corresponding connections in the land space element evolution driving network. The label content of the constraint label includes the constraint conditions and dynamic response standards. Based on the element evolution driving relationship with constraint labels, a rule transmission path is constructed to describe how a rule affects the transmission order and action mode of other elements through the evolution driving relationship between elements, so that the rule constraint spreads along the element driving link. By integrating all the evolution-driven networks and rule transmission paths of territorial spatial elements with constraint labels, a rule-responsive element allocation guidance model is constructed. This model applies constraints to all relevant elements through rule transmission paths and adjusts the constraint strength of rules through feedback from element-driven relationships.

4. The method for natural resource spatial planning and management based on territorial spatial element data according to claim 3, characterized in that, The dynamic response criteria for setting constraints based on the triggering adjustment preconditions of each spatial planning rule include: Extract the element status description from the preconditions for triggering adjustments to each spatial planning rule, and identify the types of element status changes required to trigger spatial planning rule adjustments and the status response requirements of related elements. Filter feedback records related to the type of change in the state of the element from historical planning implementation feedback information, and collect the manifestations of the change in the state of the element and the corresponding response of the state of related elements. The feedback records are classified according to the manifestation of the changes in the state of the elements, and the specific characteristics of the changes in the state of the elements and the response patterns of the related elements under each manifestation are extracted. Based on the execution requirements of each spatial planning rule, the degree of deviation of each form of expression from the preset execution target of each spatial planning rule is analyzed. The adjustment direction of each spatial planning rule is determined according to the degree of deviation. The adjustment direction is related to the influence range of the change of element status and the response mode of related elements. Based on the specific characteristics of element state changes and the direction of rule adjustment, the different manifestation intervals of element state changes are divided, and each manifestation interval corresponds to a rule adjustment requirement. A corresponding dynamic response standard is set for each performance interval. The dynamic response standard describes in detail the performance threshold of the element state change. When the element state change reaches the performance threshold, the corresponding rule adjustment is initiated. The dynamic response standard is linked to the rule adjustment direction, describing the specific adjustment content and method of the constraint conditions when the change of the element status meets the dynamic response standard; The dynamic response standards, rule adjustment directions, and constraint adjustment contents corresponding to all spatial planning rules are integrated to form a dynamic constraint adjustment specification, which is then incorporated into the rule-responsive element configuration guidance model.

5. The method for natural resource spatial planning management based on territorial spatial element data according to claim 1, characterized in that, The rule-based response-oriented factor allocation guidance model derives the allocation direction of land and space factors based on the factor evolution driving relationship as a constraint, generating a factor allocation benchmark framework, including: The core orientations for spatial planning of natural resources are set, including ecological protection orientation, spatial utilization efficiency orientation, sustainable resource utilization orientation, regional coordinated development orientation, and climate adaptation orientation. The core guidance is broken down into configuration requirements that can be implemented in specific elements. These configuration requirements correspond one-to-one with the attribute dimensions of the land and space element data, describing the state characteristics that each element needs to meet under the core guidance. The configuration requirements are input into the rule-responsive element configuration guidance model. The key elements affecting the achievement of the configuration requirements are located through the element evolution driving relationship in the rule-responsive element configuration guidance model. The key elements are those that play a decisive role in achieving the configuration requirements. Extract the constraints and rule transmission paths corresponding to key elements in the rule-responsive element configuration-oriented model, and describe the configuration boundaries and scope of influence of key elements; Starting from the configuration requirements corresponding to the core orientation, the state characteristics that key elements need to possess are deduced in reverse, and the state characteristics meet the constraints of the conditions and the logical requirements of the rule transmission path; Based on the state characteristics of key elements, the adaptation state characteristics of related elements that have an evolutionary driving relationship with key elements are derived. The adaptation state characteristics correspond to the state characteristics of key elements and meet the requirements of the element evolution driving relationship. For each element, its configuration scope, configuration form, and configuration priority are determined by combining its state characteristics and adaptation state characteristics. The configuration scope is determined based on the spatial distribution attributes of the element, the configuration form is determined based on the attribute characteristics of the element, and the configuration priority is determined based on the contribution of the element to the preset weight indicators of the core guidance. The configuration scope, configuration form, and configuration priority of all elements are integrated to form an element configuration benchmark framework. The element configuration benchmark framework includes the specific configuration requirements of various elements, the coordination configuration relationships between elements, and the rule basis corresponding to the configuration requirements.

6. The method for natural resource spatial planning and management based on territorial spatial element data according to claim 5, characterized in that, The step of deriving the adaptation state characteristics of related elements that have an evolution-driven relationship with the key elements based on the state characteristics of the key elements includes: Extract all related elements of the key elements from the rule-responsive element configuration-oriented model, and describe the evolutionary driving relationship type and action path between the key elements and each related element; Based on the rule transmission path, analyze the impact of changes in the state characteristics of key elements on each related element, and identify the type of state response that related elements need to make. Based on the constraints corresponding to the associated elements themselves, describe the boundary requirements that the associated elements must follow when making state responses, and ensure that the state responses of the associated elements do not violate the constraints. If a related element has an evolution-driven relationship with multiple key elements, the overall state response requirements of the related element should be determined by comprehensively considering the state characteristics and influence methods of the multiple key elements, so as to avoid conflicts between the influences of different key elements. Based on the state response type, boundary requirements, and comprehensive state response needs of the associated elements, the adaptive state characteristics of the associated elements are derived. These adaptive state characteristics are used to represent the attribute performance and spatial state of the associated elements. Based on the requirements of the element evolution driving relationship, verify whether the adaptation state characteristics of the associated elements and the state characteristics of the key elements meet the preset state correspondence rules; if they do, determine that the adaptation state characteristics and the state characteristics of the key elements jointly support the configuration requirements corresponding to the core guidance. If the verification does not meet the preset state response rules, the adaptation state features of the associated elements or the state features of the key elements are adjusted until the verification meets the state response rules. The adaptation state features of all related elements are integrated to form a set of related element adaptation states. The set of related element adaptation states includes the adaptation state features of each related element, the corresponding key elements, and the evolution driving relationship type.

7. The method for natural resource spatial planning management based on territorial spatial element data according to claim 1, characterized in that, The process involves collecting real-time change signals of land and space elements, integrating these signals into the element allocation benchmark framework, and optimizing element allocation details through the path adjustment mechanism of a rule-responsive element allocation guidance model. This generates multiple sets of natural resource spatial planning drafts, including: Construct a real-time data acquisition source for land and space elements to continuously acquire real-time change signals of land and space elements. The real-time change signals include change signals of element attributes, change signals of element spatial distribution, change signals of element evolution driving relationships, and change signals of elements caused by external environmental influences. The real-time change signal is identified by type, and the types of elements that have changed, the dimensions of the changed attributes, the spatial range of the change, and the time points of the change are located. Input real-time change signals into the rule-responsive element configuration guidance model, and analyze the scope and manifestation of the influence of the change elements on other related elements through the rule transmission path in the rule-responsive element configuration guidance model; Extract the configuration requirements of changed elements and affected related elements in the element configuration baseline framework, compare the differences between real-time change signals and configuration requirements, and locate the configuration content that needs to be adjusted. Based on the constraints and dynamic response standards in the rule-responsive element configuration guidance model, an adjustment plan is constructed. The adjustment plan is used to determine the types of elements to be adjusted, the attribute dimensions to be adjusted, and the specific methods of adjustment. The adjusted configuration content meets the constraints. The adjustment scheme is applied to the element configuration baseline framework, and the configuration requirements of the changed elements and the affected related elements are modified to form the adjusted element configuration scheme. Based on a rule-responsive element configuration guidance model, the evolutionary driving effect of each element in the adjusted element configuration scheme is simulated, and the coordination relationship between elements and the fit of the core guidance are monitored. If the simulation results show that the coordination relationship between elements meets the preset coordination threshold, the adjusted element configuration scheme is retained; if it does not meet the threshold, the configuration content is adjusted again based on the rule transmission path until the simulation results meet the coordination threshold. For different types of real-time change signals, the process is repeatedly adjusted to form multiple sets of adjusted element configuration schemes, each set of adjusted element configuration schemes corresponding to a combination of real-time change signals. Multiple sets of adjusted resource allocation schemes were categorized and integrated to form multiple sets of natural resource spatial planning drafts. Each set of natural resource spatial planning drafts includes complete resource allocation requirements and descriptions of the coordination relationships between resources.

8. The method for natural resource spatial planning management based on territorial spatial element data according to claim 7, characterized in that, The adjustment scheme is constructed based on the constraints and dynamic response criteria in the rule-responsive element configuration guidance model, including: Extract the constraints corresponding to the changing elements and affected related elements in the rule-responsive element configuration-oriented model, and describe the configuration boundaries and prohibition requirements of each element; Retrieve the dynamic response standards related to changing elements in the rule-responsive element configuration guidance model, and locate the adjustment trigger conditions and rule adjustment directions corresponding to real-time change signals; By combining constraints and dynamic response standards, the impact of the change magnitude of changing elements on configuration requirements is analyzed, and the attribute dimensions that need to be adjusted are identified. These attribute dimensions are consistent with the change attribute dimensions of the elements. For each attribute dimension that needs adjustment, referencing the original configuration requirements in the feature configuration baseline framework, and combining real-time change signals and rule adjustment directions, multiple adjustment alternatives are proposed. Analyze the impact of each adjustment option on the driving relationship of factor evolution, and monitor whether adjusting the option will cause other factors to violate the constraints; Select the adjustment options that do not cause other elements to violate the constraints and conform to the direction of rule adjustment as valid adjustment methods; Effective adjustment methods are evaluated and ranked, with priority given to those whose negative impact on the evaluation indicators of the coordination relationship between elements is lower than the preset impact threshold and whose adaptability to real-time change signals is higher than the preset adaptability threshold. Based on the preferred adjustment method, determine the types of elements to be adjusted, the attribute dimensions to be adjusted, and the specific operational content of the adjustment to form an adjustment plan; The compatibility of the adjustment plan with the rule-responsive element configuration guidance model was compared, and all the adjustments in the adjustment plan met the constraints and dynamic response standards. If the adaptation meets the requirements, the adjustment plan is determined as the final adjustment plan; if it does not meet the requirements, the adjustment method is modified until the adaptation meets the requirements.

9. The method for natural resource spatial planning management based on territorial spatial element data according to claim 1, characterized in that, The method, based on the strength of driving relationships in the evolutionary driving network of national land space elements, integrates multiple draft natural resource spatial plans in a coordinated manner to form the final natural resource spatial planning outcome, including: Extracting element-driven features from the evolution-driven network of territorial spatial elements, the element-driven features include the frequency of the effect of evolution-driven relationships between elements, the duration of element-driven relationships, the length of the transmission path of element-driven relationships, and the spatial distribution of element-driven relationships. For each group of natural resource spatial planning drafts, an element allocation-driven coordination analysis is performed. By calculating the matching degree between the element allocation in the draft and the element-driven characteristics, configuration content with a matching degree higher than a preset matching threshold and configuration content with a matching degree lower than a preset matching threshold are identified. The configuration content in all natural resource spatial planning drafts is classified according to the frequency of the effect of the factor-driven relationship. The configuration content involving the factor-driven relationship that ranks first in the preset order of the frequency of effect is grouped into one category to form a core configuration set. Extract the common configuration content of all natural resource spatial planning drafts in the core configuration set as the basic configuration content. The basic configuration content is the consistent configuration requirements of all natural resource spatial planning drafts that conform to the element-driven characteristics. The configuration content that differs in the core configuration set but all conforms to the element-driven characteristics is identified as optional configuration content, and the supporting role of the optional configuration content in the core guidance is analyzed. Based on the duration and transmission path length of the factor-driven relationship, the optional configuration content is evaluated, and the optional configuration content that supports the core guidance and meets the requirements of the core guidance setting is selected and integrated into the basic configuration content. For the configuration content in the draft of the natural resources spatial plan that does not conform to the factor-driven characteristics, a correction scheme is constructed by referring to the factor-driven characteristics in the evolution-driven network of national land spatial elements and the constraints in the rule-responsive factor configuration guidance model, and the non-conforming configuration content is modified to conform to the factor-driven characteristics. The revised configuration content is integrated with the basic configuration content and the selected optional configuration content to form a unified element configuration framework. The element configuration framework includes the configuration requirements of all elements, the coordination relationship between elements, and the element driving basis corresponding to the configuration requirements. The element configuration framework is structured and integrated according to spatial regions and element types, describing the configuration requirements and mutual coordination relationships of various elements in each spatial region; The structured and integrated element allocation framework is transformed into a standardized planning expression form, forming the final natural resource spatial planning result. The natural resource spatial planning result includes spatial layout planning, element allocation planning, coordination relationship description, and rule basis description.

10. A natural resource spatial planning management system based on land spatial element data, characterized in that, include: processor; A machine-readable storage medium for storing machine-executable instructions of the processor; The processor is configured to execute the natural resource spatial planning and management method based on territorial spatial element data as described in any one of claims 1 to 9 by executing the machine-executable instructions.

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