Next Article in Journal
Forests, Farms, and Fallows: The Dynamics of Tree Cover Transition in the Southern Part of the Uluguru Mountains, Tanzania
Next Article in Special Issue
Analysis of Replicability of Conservation Actions across Mediterranean Europe
Previous Article in Journal
Spatial Distribution, Environmental Risk and Safe Utilization Zoning of Soil Heavy Metals in Farmland, Subtropical China
Previous Article in Special Issue
Impact of Sustainable Cultural Contact, Natural Atmospherics, and Risk Perception on Rural Destination Involvement and Traveler Behavior in Inner Mongolia
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Comprehensive Evaluation and Quantitative Research on the Living Protection of Traditional Villages from the Perspective of “Production–Living–Ecology”

School of Architecture, Southeast University, Nanjing 210096, China
*
Author to whom correspondence should be addressed.
Submission received: 27 April 2021 / Revised: 21 May 2021 / Accepted: 21 May 2021 / Published: 28 May 2021
(This article belongs to the Special Issue Ecosystem Services, Sustainable Rural Development and Protected Areas)

Abstract

:
Aiming at the current isolated, static protection method of traditional villages, a comprehensive evaluation system for the living protection of traditional villages has been constructed based on the land use function integration concept in “Production–Living–Ecology” (PLE). By combining the “horizontal” PLE coupling coordination analysis with the “vertical” correlation analysis of the elements at each layer, the comprehensive evaluation and quantitative analysis of six traditional villages of different types and grades in the Taihu Lake area are carried out to quantitatively reflect the interactive relationship and integration mechanism of PLE in traditional villages. The results show that: (1) The PLE development of traditional villages is a dynamic process. Even if the villages are close in the PLE score, they may be in different stages of PLE development and coupling coordination type. (2) The “living” function has the highest correlation with the coupling coordination degree of PLE, and it acts as the engine and bridge of benign interaction between the PLE. (3) Even if the national traditional villages have a favorable ecology background, they may not get high scores, or even fail in the PLE score. (4) Among the sub-indicators, the natural environmental characteristics, the ecological vitality of political organizations, and the level of human settlement facilities show a significant linear correlation with the PLE score. Additionally, the ecological vitality of political organizations is the strongest. It can be therefore concluded that a positive policy organization is an important guarantee for realizing the PLE integration of traditional villages.

1. Introduction

Both the countryside and the city are the formal manifestations of human activities of production, living, and ecology, and the two have an isomorphic relationship; traditional Chinese cities dominate rural areas politically, but rely on them economically for survival [1,2]. Villages vastly outnumber cities. Countless villages are scattered on the vast land of China, where hundreds of millions of people live, giving birth to a world-famous agricultural civilization [3]. Traditional villages are one type of village. In the past, it used to be called “ancient village”, which means that the village formed earlier. It has rich cultural and natural resources, and has certain historical, cultural, scientific, artistic, economic, and social values. Compared with general villages, they reflect the wisdom of the overall spatial pattern and engineering construction, and the harmonious state of integration and symbiosis between humankind and the original ecological environment during the farming period. They are of high artistic and scientific value, and are the living fossils of China’s thousand-year agricultural civilization. With rapid urbanization, a large amount of intangible rural cultural heritage has failed to be handed down from past generations, so the intangible culture in traditional villages is endangered and lacks vitality [4]. Doubts and reflections have been aroused on the conventional way of preserving traditional villages by making them into “museums”, which is only a preservation of the lifeless remains. At present, the previous research on the protection and utilization of traditional villages is mostly based on a one-sided, static protection, which has encountered many difficulties and resistance in practice, and the effect is not ideal [5,6]. It is therefore urgent to carry out research on the living protection of traditional villages.
The concept of Production–Living–Ecology (PLE) was first put forward in “Our Common Future” by the World Commission on environment and development in 1987. Under the promotion of the report, countries (regions) worldwide have reached a consensus on “sustainable development”. After that, the “Rio Declaration on environment and development” and “Convention on biological diversity” signed in the 1990s and “transforming our world: the 2030 agenda for sustainable development” was signed in the 21st century, and they all expressed their continuous concern for sustainable development. As rural agricultural production is a part of rural life and ecological environment, and the food, energy, and resources of rural life come from agricultural production and ecological environment, respectively, the sustainable development of rural areas is considered as the integrated development of PLE [7]. It is an inexorable trend to integrate the development concept of PLE into the living protection of traditional villages.
Rural policies in Europe all show concern for PLE, with the introduction of the Agenda 2000 reforms, rural development was established in the European Union as the so-called second pillar of the Common Agricultural Policy (CAP), aiming at sustainably developing the rural area as a whole [8]. Based on Council Regulations 1257/1999 and 1698/2005, rural development plans (RDP) require Member States to pay more attention to maintaining the diversity of the ecosystem and ensuring the vitality of the village and the quality of the village’s living environment in addition to strengthening the development of rural economy. In terms of funding, more funds are invested in sustainable ecological economic development, improvement of rural living quality, characteristic economy, and rural tourism [9]. In addition, many countries have their own unique plans, such as Poland’s “Rural Renewal Programs” in the Warmia and Mazury Region, promoting the quality of production, living and ecology of the village systematically through “small grants”, which then stimulate the comprehensive vitality of the village [10]. As for Germany, according to the German Territorial Order Act, the primary principle of territorial planning includes the construction of high-quality and healthy living and working environments throughout the country. Starting from the important significance of agriculture to production, living, and ecology, the principle of saving cultivated land resources and making better use of cultivated land resources is emphasized [11]. In addition, in the Weyarn Municipality, a rural area of upper Bavaria in southern Germany, village renewal under the framework of the Federal Land Consolidation Act provided a broad range of instruments: the local government makes full use of the land resources, actively develops the village economy, and, at the same time, takes into account the sustainable ecological development and the improvement of people’s living quality, so that the village can be revitalized [12]. In China, 2017, the rural revitalization strategy emphasized the new requirements of thriving industries, a pleasant living environment, and a prosperous life in its overall development route, pushing the development concept of PLE to a new height. The living protection of traditional villages characterized by the development concept of PLE integration is a new practice. The basic connotation of PLE integration covers the material and spiritual achievements from the harmonious coexistence of humankind and nature, and from the construction of better human settlements. For traditional villages, ecological space is their natural foundation, while living space and production space are products derived from the environment where human beings live. In the long-term process of human activities, they react on the ecological space, thus forming a relatively stable overall pattern.
Domestic and foreign research on evaluation methods of traditional villages in related fields has yielded certain results, and the quantitative methods are increasingly concerned. For example, Yang et al. constructed an evaluation system and comprehensive evaluation function of cultural inheritance from the aspects of preservation and acceptance, and put forward corresponding protection strategies and suggestions [13]. Zou et al. constructed an index system for evaluating the vitality level of traditional villages from the three aspects of material heritage, intangible heritage, and village residents. They obtained data through field surveys, literature review, questionnaires, and other methods, and then quantitatively evaluated the vitality level of three types of traditional villages in West Hunan, China [14]. Ipekoglu proposed a grading system-based approach to evaluate the external and internal characteristics of traditional buildings in Odunpazari, Turkey, by their architectural, historical, environmental, visual, and aesthetic features, and divided these buildings into four groups of different values, A, B, C, and D, which would help make better decisions on cultural heritage [15]. Hu et al. constructed a multi-dimensional framework to understand the spatial reconstruction of traditional villages from the three levels of material space, social space, and cultural space. They preliminarily analyzed the spatial reconstruction mechanism of traditional villages under the interaction of social, political, and capital forces [16]. Guo et al. analyzed the Dang Village, a traditional village in Shaanxi Province, by combining qualitative and quantitative methods from social, economic, and environmental perspectives [17].
The current research results have the following shortcomings: First, the evaluation framework is relatively one-sided. Due to different research perspectives and evaluation objectives, the organic integrity of the village and the complexity of its internal system are ignored. To explore the influence mechanism of internal factors, a more comprehensive evaluation system is needed. Second, the quantitative evaluation research is relatively weak, and the reliability judgment of parameter compound operation lacks a systematic approach and accuracy of data processing. Third, the biggest feature of traditional villages is that the boundaries of PLE spaces are indistinct, and the degree of coupling coordination is high. During the integrative development of PLE in traditional villages, their interaction and integration mechanism is still vague [18].
In view of this, this paper attempts to construct a PLE comprehensive evaluation system of traditional villages. Taking the traditional villages around Taihu Lake as the research object, this paper quantitatively evaluates the PLE development levels of various traditional villages. By combining the horizontal PLE coupling coordination analysis with the vertical correlation analysis of indicators at different layers, the internal mechanism between PLE during the living protection of traditional villages is thoroughly analyzed, and appropriate multiple paths and strategies are proposed.

2. Materials and Methods

2.1. Study Area

The research team selected six traditional villages with typical characteristics in the Taihu Lake area for case study, covering different grades (national grade and provincial grade) and different types (mountainous, urban-suburbs, and water-network intensive). The basic information of these villages is shown in Figure 1 and Table 1.
The research data was obtained mainly through field surveys, on-site surveys, questionnaires, and a literature review. In August 2020, the research team conducted field surveys, on-site interviews, and questionnaire surveys for more than 20 days. Indicators D8–18 were from field surveys; D22, D30, and D38 from questionnaire surveys; and D1–2, D5–7, D19–20, and D23–25 from the literature review. Some indicators came from multiple sources. For example, D3–4, D26–30, and D36–37 were obtained through on-site interviews supplemented by literature review, whereas D21 and D32–35 were obtained through a questionnaire survey and field survey.

2.2. Methods

A comprehensive evaluation system was constructed based on the PLE integration with the principles of high feasibility and strong operability. The major steps were as follows: preliminary screening of indicators, expert consultation, determination of weights, determination of scoring standards, distribution of survey questionnaires, fuzzy comprehensive evaluation, correlation analysis of internal factors, etc. In terms of quantitative methods, the statistical method of “reliability analysis and Z-score unified standardization” was adopted to ensure the objectivity of scale analysis. By combining the horizontal PLE coupling coordination analysis with the vertical correlation analysis of the indicators at different layers, the interaction and integration of PLE of traditional villages are quantitatively reflected.

2.2.1. Construction of the Proposed Comprehensive Evaluation System

The specific evaluation process is shown in Figure 2 below.

2.2.2. Index Screening and Expert Consultation

Preliminary screening of indicators: Analyze and sort out relevant evaluation indicators for village economic production [19,20,21,22,23], human settlement environment [15,24,25,26,27], village ecological and cultural value [28,29,30], diversity of traditional village [31,32,33,34], policy efficiency index [35,36], and adaptability of rural tourism [17,32,37,38,39] from available literature. Finally, a total of 52 evaluation indicators were selected according to the objectives and principles mentioned above.
Expert consultation: The consulting experts were composed of four parts: experts in the field of traditional village protection, representatives of villagers, managers of village-related administrative organizations, and tourists, at a proportion of 4:3:2:1. By distributing the index consultation forms after the preliminary screening and analyzing the collected consultation forms and questionnaires [40], 38 key indicators were singled out (see Table A1 in Appendix A). These indicators were from 3 major categories (layer B), 8 medium categories (layer C), and 38 small categories (layer D).
  • Production B1
Comprehensive economic vitality C1 can roughly reflect the overall economic development level of the village [41]. A higher villagers’ annual income per capital D1 and village collective annual average income D2 means better economic development. A strong industry means an economy of scale but not necessarily with distinctive features. As a result, the landscape and cultural characteristics of the village have not been fully explored. Therefore, the indexes D3 and D4 in the characteristic industry vitality C2 need to be treated differently. The deeper the future industrial development of the village integrates with the local characteristics [42], the higher the vitality level of its production field. Generally, the number of tourists reflects the real vitality of the tourism industry in the village. D6 and D7 reflect the talent leadership in the field of village production; the larger the number of leaders and the higher their income, the better the economic production vitality of the village [43].
2.
Ecology B2
The products of the interaction between human beings and the environment include material ecology as well as spiritual ecology, such as society and humanities. Ecological civilization is the sum of material and spiritual results produced in the process of long-term coexistence and mutual influence between humans and the environment [44]. Academics have put forward the “pan-ecology” viewpoint which refers to the generalization of ecology in a broader sense. It is the sum of the material and spiritual achievements made by human beings in the interaction with the original ecological environment. Thus, the ecology B2 includes two major parts: material ecology and spiritual ecology [45].
Specifically, material ecology herein consists of the characteristics of natural environment C3 and the spatial characteristics of the village C4; the higher the scores of D8, D9, and D10, the better the natural environment of the village [46]. The material heritage features can be divided into three layers: overall layout, public space, and single building. The indexes in each layer are evaluated according to their quantity and quality. The larger the quantity of material heritages and the more distinctive and the more diversified the village, the higher the score for the ecology of the village [47].
The spiritual ecology is composed of political organization ecology C5 and cultural ecology C6 [48]. In addition to the evaluation of system management, the former index also includes the government’s execution power and villagers’ participation in protection work, thus forming a systematic evaluation system from top-level management to personnel implementation to villagers’ cooperation and participation. The more complete the system, the higher the degree of implementation and the better the villagers’ awareness and participation, the more effective the political organization ecology of the village. The latter is selected according to principle of “quantity + quality”. The score of cultural ecology C6 is higher if the sub-indexes—history (D23–24), influence of historic figures and events (D25), cultural features (D26), villagers’ participation in cultural activities (D27), and cultural inheritance—have higher scores.
3.
Living B3
As for the layer of human settlement facilities (C7) [31], the higher the scores of such sub-indexes such as traffic (D32), living facilities (D33), and service facilities (D34), the better the living environment of the village, the stronger its attraction, and the more conducive it is to the living protection of the village. Meanwhile, it is necessary to pay more attention to the actual returned population and talent attraction of the village [49], especially the returned young population (D36), the attractiveness to foreign entrepreneurs (D37), and social inclusiveness (D38).

2.2.3. Analytic Hierarchy Process and Weight Determination

The weights are determined by the classical Analytic Hierarchy Process (AHP) [50]. That is, a tree hierarchical structure is constructed according to the comprehensive evaluation framework of PLE integration, and then Yaahp program distributes the score questionnaire to experts and scholars in the field. After experts determine the weight scores, the software will generate a judgment matrix to obtain the weight of each index in the comprehensive evaluation index system (see Table A1 in Appendix A).

2.2.4. Determination of Scoring Standards and Survey Questionnaire Design

Comprehensive evaluation includes qualitative and quantitative indicators. The graded scoring method for qualitative indicators [51]. There are five grades of evaluation scores (I, II, III, IV, and V), and each grade is assigned 20 points, that is, the scores of the grades are in the interval of 0–20, 21–40, 41–60, 61–80, and 81–100, respectively [52]. For quantitative indicators, a five-grade centesimal system similar to the above method is developed in combination with relevant standards for scoring. For the types of questionnaire and interview indicators, the majority opinion results of questionnaire interview are the final evaluation results. Copies of the survey questionnaire formulated by experts were distributed to local villagers. The collected valid questionnaires for each village were ensured to be more than 50.

2.2.5. Fuzzy Comprehensive Evaluation

Experts in the field were invited to score according to the above criteria. In the evaluation layer domain U, in order to obtain the index membership degree, it was necessary to uniformly sort and analyze the indexes of each layer to form a fuzzy evaluation matrix R.
Then, compound operation was carried out for the fuzzy matrix. According to the weight of each index w   = ( w 1 , w 2 , …, w n ) [53] and fuzzy evaluation matrix R obtained in the above steps by AHP [54], the following operations are started:
B = W · R = w 1 , w 2 , , w n · r 11 r 12 r 1 n r 21 r 22 r 2 n r m 1 r m 2 r m n = B 1 , B 2 , , B n
Similarly, a complete resulting score scale for groups A, B, C, and D of the comprehensive evaluation index system for traditional village living protection can be obtained.

2.2.6. Reliability Analysis

The reliability analysis—Cronbach reliability analysis—was performed on the PLE comprehensive score scale to estimate the internal consistency of the test.
α = K K 1 1 S i 2 S x 2
α is the reliability coefficient, K is the number of test items, S i 2 is the score variation of all subjects on the i-th question, and S x 2 is the variance of the total scores obtained by all subjects.
In the above analysis, if the reliability coefficient is less than 0.35, it is considered to be low reliability, indicating the unreliability of the scale data. A reliability coefficient larger than 0.8 is acceptable. If the value is above 0.9, the scale is of high reliability. If the comprehensive evaluation scale fails to have high reliability, adjustments should be made on the related indexes according to the modification suggestions of experts.

2.2.7. Weight Calculation Based on Entropy Weighting Method and PLE Coupling Coordination Model

The process of the horizontal PLE coupling coordination model is shown in Figure 3.
The range method is adopted in this paper normalize the dimensionless data:
x = x x min x max x i
where x i = x 1 , x 2 , …, x n ; x max and x min respectively are the maximum and minimum of the index i.
The index weight is determined by calculating information entropy and information entropy redundancy. After the weights are determined, the comprehensive scores of PLE system can be calculated [55].
f ( x ) = i = 1 m a i x i
g ( y ) = i = 1 n b i y i
h ( z ) = i = 1 k c i z i
Here, f ( x ) , g ( y ) , and h ( z ) are the comprehensive scores of production, living, and ecology, respectively. a i , b i , and c i are the weights of the production, living, and ecology system, respectively, and they are dimensionless values.
C = f ( x ) × g ( y ) × h ( z ) f ( x ) + g ( y ) + h ( z ) 3 3 1 3
The value of the coupling degree C ranges within (0, 1). The closer C is to 1, the greater the coupling degree between the systems; the closer C is to 0, the smaller the coupling degree between systems, and the order parameters are in a state of independent and disorderly development.
D = C × T
T = f ( x ) + β g ( y ) + δ h ( z )
D is the coordination degree of the interaction coupling between the PLE functions, C is the coupling degree, and T is the comprehensive evaluation index of the coupling coordination degree. , β , and δ are the weights of the PLE systems, which are assigned to 1/3, 1/3, and 1/3, respectively. Similarly, the pairwise mutual influence between production, living, and ecology can be calculated, respectively, such as ecology–production (E–P), living–ecology (L–E) and production–living (P–L) [56,57,58,59].
The lower the coordination ( D value), the weaker the interaction among the three functions, and the greater the conflict among them. With reference to relevant research results and the actual development stage of the village, the results are divided into 4 categories and 10 subcategories [56] (see Table 2).

2.2.8. Z-Score Normalization and the Vertical Correlation Analysis Model

The process of the vertical correlation analysis model is shown in Figure 4.
To ensure the results of different dimensions or layers of the fuzzy comprehensive evaluation [60] are comparable, it is necessary to normalize the evaluation vector results in the SPSS software. Z-score processing method is used to convert the data so that they have a mean value of 0 and a standard deviation of 1. The conversion formula is:
x * = x x ¯ σ
where x * is the Z-score, x is the score of the indicator, x ¯ is the mean of the original data, and σ is the standard deviation of the original data.
Finally, the Pearson correlation analysis is adopted to measure the closeness of two or more variables in the PLE systems, so as to explore the mutual influence mechanism of the internal factors [61].
The Pearson’s correlation coefficient is defined as:
r = i = 1 n X i X ¯ Y i Y ¯ i = 1 n X i X ¯ 2 i = 1 n Y i Y ¯ 2
Obviously, −1 ≤ r ≤ 1. When r < 0, the two variables are negatively correlated; when r ≥ 0.8, the two variables are highly correlated; when 0.8 > r ≥ 0.5, they are moderately correlated; when 0.5 > r ≥ 0.3, they are slightly correlated; and when r < 0.3, they are roughly independent. The significance test results show that when the significance is less than 0.05, the samples have a relatively significant linear correlation; when the significance is below 0.01, the samples have an extreme significant linear correlation [62].

3. Results

3.1. Evaluation Results

According to the operation process of the comprehensive evaluation index system constructed above, the fuzzy evaluation is carried out, and the scores are shown in Table 3. In this table, village names are abbreviated, such as Yangfeng (YF), Erdu (ED), Shazhang (SZ), Yanjiaqiao (YJQ), Yangqiao (YQ), Tangli (TL).

3.2. Reliability Analysis

The Cronbach reliability analysis results show that the average value of the Alpha index of the evaluation scale for the above-mentioned villages reach 0.952, and the Alpha index of each indicator is above 0.94, indicating that the scale has high consistency and strong reliability (Table 4).

3.3. Horizontal Analysis: PLE Score and Coupling Coordination Analysis Results

Through the comparison of the PLE score and coupling coordination degree (CCD) scores, the CCD contain PLE CCD and pairwise mutual CCDs of production, living and ecology, respectively, Pearson correlation analysis method is adopted to explore the evaluation content such as the integration and correlation of PLE, so as to quantitatively express the interaction and integration mechanism of PLE of traditional villages.
As shown in Table 5 and Figure 5, the PLE score and the PLE CCD are not strongly correlated. Yangfeng Village (61.88), Erdu Village (62.35) and Yanjiaqiao Village (62.71) have similar PLE scores. Among them, Yangfeng Village is the lowest, but it has reached coordination and integration period in PLE development stage (0.76), higher than the other two villages’ 0.63 and 0.68 (Running-in and adjustment period).
The internal mechanism reason for that scoring performance can be found from the pairwise mutual CCDs, as shown in Figure 6. Erdu village and Yanjiaqiao village show Type Ⅱ adjustment performance, respectively in the pairwise mutual CCDs on L–E (0.56) and P–L (0.51). Even though they show a relatively high score on other CCDs, their scores of PLE coordination will be affected by the buckets effect. It thus can be concluded that the PLE development of village is a dynamic process, the coordination among PLE functions constrain and contribute each other. In Yangfeng Village, the three functions of space begin to balance and cooperate with each other, which shows the characteristics of benign coupling coordination. Different from Yangfeng Village, Erdu village and Yanjiaqiao village face the problem of antagonism at CCD in L–E and P–L. Their dominant function become stronger and occupy the space for the development of disadvantaged functions. Consequently, these disadvantaged functions would become weaker and weaker.
After Z-score processing, the relationships among the CCDs of PLE, L–E, P–L, and E–P can be seen more intuitively (Figure 7). Figure 8 shows the significance of Pearson results between the PLE score, PLE CCD, and pairwise mutual CCDs. When the significance is less than 0.05, the samples have a relatively significant linear correlation (light red); when the significance is below 0.01, the samples have an extreme significant linear correlation (bright red). Specifically, the PLE CCD shows a strong linear relationship with P–L (0.002) and L–E (0.003), respectively, as shown in Table A2 of Appendix A. Moreover, P–L shows a strong correlation of 0.005 with L–E. It can be seen that the living function acts as a bridge for the interaction between the production and ecology functions. It has demonstrated that the living protection for traditional villages is a key link to realize the coordinated development of PLE, which is inconsistent with the general belief that the better the production or ecology, the better the PLE development of village. In addition, PLE CCD shows a strong correlation of 0.006 with PLE score, demonstrating that the comprehensive development of three aspects is an effective way to realize the living development trend of “seeing people, things, and living” in traditional villages.

3.4. Vertical Analysis: PLE Score (Layer A) and Analysis Results of PLE Dimensions (Layer B)

Overall, the average score of the six studied villages only reached 57.26. This indicates that although they are located around the Taihu Lake, a developed region covering Zhejiang and Jiangsu provinces, their PLE development is not ideal. Among them, only Tangli Village scores over 70, and three villages (Yangfeng, Erdu, and Yanjiaqiao) score a little over 60. Furthermore, among the villages with scores below 60 points, Yangqiao only achieves 54.08, while Shazhang shows the lowest score of 29.37. In addition to Erdu, which is a provincial grade traditional village, the others are all at the national grade. This shows that the villages may score low even if they have a fine ecology, and that their development strategy should be adapted to the concept of PLE integration.
The difference among the studied villages in terms of production, living, and ecology can be directly seen after Z-score normalization (Table 6). To better show the difference, the villages’ Z-scores of production, living, and ecology at layer B can be transformed and put into a coordinate system (Figure 9). The larger the circular area in the figure, the higher the village’s Z-score in the production.
  • Production dimension
In terms of production, provincial grade traditional village Erdu has the highest score (16.4 points), followed by the national grade traditional villages, Yanjiaqiao, Tangli and Yangfeng, ranking 2nd, 3rd, and 4th, respectively. There are not many historical sites and features in Erdu Village, and its score for spatial and environmental characteristics (C4) are not high. However, Erdu has benefited greatly from large projects and events nearby, such as the Xiazhu Lake Wetland Park completed in 2013 and the pastoral expo held in 2019. Yanjiaqiao is a traditional suburban village, 4 km away from Yangjian Industrial Park in Wuxi City, 12 km from East Railway Station, and 20 km from the downtown. In recent years, it has developed an economy through suburban tourism and urban industry, so the villagers’ income and the collective income of the village are both high. In addition, Tangli Village is located in the Xishan Island Scenic Spot, with high artificial and natural ecological values. The development of tourism helps the village score relatively high in the production dimension. Moreover, Yangfeng is a mountainous type of village with a forest coverage rate of more than 80%. This village develops forestry and mining industries based on its own superior natural conditions and sees a sound economic boost. It shows that the rational use of their own and surrounding environmental resources is the key to maintaining the economic vitality of traditional villages.
The villages with lower scores are Yangqiao and Shazhang. Yangqiao Village has a favorable material ecology (C3 and C4), yet the lack of large-scale development projects in its surrounding area and the poor planning and management of the political organization ecology (C5) have resulted in a low production score. In contrast, the economy of Shazhang is more sluggish, and the low score of political organization is one of the main reasons for the decline in its production. According to the on-site interview, the local government organized the aborigines to move out for the protection of historic sites. There were more than 200 households, more than 180 of which have moved out. Those still live there are mostly the elderly. Shazhang village is almost an empty village where only some lonely elderly villagers visit each other during the day. As most of the residents have moved out, many century-old houses in the village are worn down by the years without repair, and even collapsed, showing a dilapidated scene.
2.
Living dimension
As can be seen in Figure 9, Shazhang, Yangqiao, and Erdu have relatively low scores for the living dimension. Although Erdu sees an outstanding economic increase, as well as a trend of labor returning (a subindicator at layer D), its social amenities are insufficient. As a result, the livability is poor, which partly affects the progress in its living protection. For Shazhang and Yangqiao, as mentioned above, in addition to regional differences, the quality of policy organization plays a crucial role in their development. Despite a large number of material ecological remains and various historical sites, Yangqiao is poor in livability and living protection owing to the lagged policy and organization.
The villages with relatively high scores in the living dimension, such as Yangfeng, Yanjiaqiao, and Tangli, also face the same issues. The living facilities are relatively complete, and a certain number of migrants come to the village to start businesses, such as opening homestays, restaurants, and studios. However, the indicator D36 shows that only a small proportion of young people in Tangli have returned to the village. Additionally, this figure for the other two villages is almost zero.
3.
Ecology dimension
In this dimension, except for the relatively weak Shazhang and Yangqiao, the remaining four villages all show high scores. Comparison between Yangqiao and Yanjiaqiao shows that, under the same material ecology (natural environment and material heritage), the villages with better spiritual ecology (political organization ecology and cultural ecology) have a higher level in production and living dimensions.
It can also be found that the material ecology and cultural ecology of Erdu (a provincial grade traditional village) are significantly inferior to Yangqiao (a national grade traditional village), whereas Erdu’s scores for the production dimension are significantly higher. This further confirms the importance of organizational ecology mentioned above in Pearson correlation analysis. Thus, the local government should appropriately develop and utilize the resources of the village and those nearby, which is a necessary guarantee for the village to achieve a sustainable development of PLE integration. The production, living and ecology are closely related and complement each other, the absence of any of which will impact the sound, sustainable development of the whole system.

3.5. Vertical Analysis: Analysis Results of Sub-Indicators (Layer C and Layer D)

The indicators of layer C are standardized by Z-score processing mentioned above, and the results are shown in Table 7. The data are visualized to analyze the differences between specific indicators, as shown in Figure 10.
From the score of indicator C1 (overall economic vitality), it can be observed that all the other villages are at or above the mean, except for Shazhang. This shows that the traditional villages in the affluent area around Taihu Lake in Jiangsu and Zhejiang provinces have excellent economic performance.
The indicators C2 (characteristic industrial vitality), C5 (ecological vitality of political organizations), C6 (cultural ecological vitality), and C7 (the level of human settlement facilities) exhibit consistent characteristics in their standardized images That is, except Yangqiao and Shazhang, the scores of other villages are close to each other. These indicators are closely related to the administration level of government.
Shazhang Village has been unmanaged in recent years, so the surrounding environment is overgrown with weeds, and its natural features have been seriously damaged. Consequently, this village scores low at the natural environment features C3 and spatial environment features C4. Erdu Village, a provincial grade traditional village, is not comparable to the other five national grade traditional villages in terms of material heritage characteristics due to fewer historical sites and cultural relics. Nevertheless, the outstanding characteristic industries, political organizations, and the human settlement environment have contributed to Erdu’s PLE score above the average level.
Through the standardization of Z-score and Pearson analysis, the correlation results between the PLE scores and the C-layer indicators are obtained (Table A3 in Appendix A). In order to make the data more intuitive, the significance of correlation results between the PLE scores and the C-layer indicators table is drawn (Figure 11). When the significance is less than 0.05, the samples have a relatively significant linear correlation (light red); when the significance is below 0.01, the samples have an extreme significant linear correlation (bright red).
Natural environment features, ecological vitality of political organizations, and the level of human settlement facilities show a linear correlation with the PLE score. Among them, the significance between the ecological vitality of political organizations and the score is 0.002, indicating the strongest correlation. This indicates that positive policy organization is the key factor a key factor in realizing the PLE integration of villages. In addition, in C5 column, the number of bright red color blocks is the most, indicating that the index has the strongest correlation with other elements.
In addition, the correlation value of the PLE score with spatial environmental features and population vitality of the village is 0.696 and 0.161, respectively, showing a weak linear correlation. It is thus can be concluded that the village can still find a suitable path for PLE integration based on its own strengths even if its spatial environment is not excellent. Moreover, there is a certain correlation between spatial environment and population vitality (0.137). This indicates that a favorable natural environment is the foundation of the village’s development and population increase.

4. Discussions

Figure 12 shows the visualization results of the indicators at layer C. Then, each quadrant in the z-score coordinate system (Figure 9) of each village is classified and summarized, and the influence mechanism and related issues of the village are explored from the perspective of PLE, so that the suitable strategy can be proposed.
(1) The villages in the first quadrant are Yangfeng, Yanjiaqiao, and Tangli, all national grade villages. They score above the average in the PLE dimensions and have achieved all-around progress in PLE integration. These villages all make full use of natural and cultural resources, forming unique village characteristics, and providing a high-class ecological and cultural foundation for further living protection (Figure 9).
For such traditional villages, we should adhere to the strategy of “inheritance first”. Moreover, they should actively promote local culture and characteristic industries, and develop tourism, which can in turn contribute to heritage preservation. Furthermore, it is necessary to guide villagers to participate in the village protection, ensure they are the masters of the village, and expand the cultural heritage team to achieve internal improvement. It is suggested to attract young people to return and inject vitality into the sustainable development of the village by creating more employment opportunities. In addition, it is also suggested to adhere to continuous protection plan of villages and unify the historic style of traditional villages from the overall spatial environment, individual buildings, and interior space. At the same time, multiple functional spaces for photography, painting, and cultural experience can be constructed.
(2) The villages in the second (fourth) quadrant are those with above-average scores in one of the ecology and living functions and below-average scores in the other. These villages have a single characteristic. Only Erdu is in this quadrant, and it is a provincial grade traditional village. Thanks to the major projects nearby, this village boosts its economy by developing corresponding service industry. However, Erdu is weak in preservation of historical characteristics. Many of the traditional features are not well conserved, and there are few traditional buildings left (Figure 9).
Such traditional villages should adopt the strategy of “development first”. They should promote the construction of “one village and one featured product”, explore the diversified value of traditional villages according to local conditions, clarify the major characteristics, establish their own brands, and actively develop tourism and its surrounding industries. They need to improve infrastructure and enhance the overall livability and tourism service quality in the village, so as to attract talents to return. Furthermore, they also need to restore the traditional buildings and unify the traditional style. To ensure the living protection of traditional villages does not deviate from the masses, the government should play a leading role in establishing a long-term preservation mechanism. Meanwhile, the government should provide more opportunities for villagers to fully express their opinions so that they can better participate in the development of villages.
(3) In the third quadrant, there are Shazhang and Yangqiao. Their scores of ecology and living dimensions are lower than the average, so they belong to the villages with lagged PLE development. The common problems these villages face are as follows: First, the village characteristics are not distinct, the exploration of connotative values is limited, and the economy is sluggish. Second, a large number of villagers go out to work, which makes it more difficult to protect and inherit the culture and building technology of traditional villages. Additionally, the architectural heritage with cultural and historical value have not received enough attention (Figure 9).
Therefore, such traditional villages should adhere to the strategy of “protection first”. With low productivity and serious population loss, these villages should not take tourism as their leading industry. Instead, they should preserve the main historical remains of traditional villages and meanwhile develop agriculture as a basic industry while protecting the heritage. In addition, they should actively expand their diversified and compound functions, and integrate them with industries such as culture, tourism, and education. Furthermore, they are suggested to extend the industrial chain and develop related service industries based on the natural and cultural resources and historic remains of traditional villages. In general, the key to a virtuous revival of traditional villages lies in enhancing infrastructure construction and retaining villagers. In terms of material ecology, the priority should be given to its protection, and the heritages at different spatial levels should be properly preserved. As for political ecology, the social capital should play a leading role in the development of rural tourism based on government guidance and public participation.

5. Conclusions

Based on the development concept of PL integration, this paper conducts a comprehensive evaluation and quantitative study of the living protection of traditional villages. The case study is based on a number of traditional villages of different grades and types in the Taihu Lake area. The evaluation research in this paper is based on quantitative evaluation and supplemented by qualitative evaluation. In data processing, the reliability analysis is combined with Z-score normalization to ensure that the evaluation indicators are comparable. Through the horizontal PLE coupling coordination analysis with the vertical correlation analysis of the elements at each layer, the relationship between the internal factors of the living protection of traditional villages and the mutual influence mechanism are thoroughly analyzed. The major preliminary conclusions can be drawn as follows:
(1) The PLE development of traditional villages is a dynamic process. Even if the villages are close in the PLE score, they may be in different stages of PLE development and coupling coordination type. For example, in the coupling coordination stage, the villages’ production, living, and ecology functions restrict and contribute to each other, showing a benign coupling. However, the villages in the adjustment stage would have confrontation between different dimensions. The stronger the predominant function of traditional villages, the less space for the development of other functions. As a result, these disadvantaged functions would be weakened.
(2) The living function serves as a bridge between production and ecology functions. This is inconsistent with the general belief that the better the production or ecology, the better the PLE development of villages. It has also demonstrated that the living protection of traditional villages is a key link to realizing the coordinated development of PLE. The PLE integration development is an effective way to practice the living protection of traditional villages.
(3) Villages may score low even if they are national grade traditional villages with a high-quality ecological environment. Thus, their development strategy should be adapted to the concept of PLE integration. By contrast, even if the spatial and environmental characteristics of the villages are not distinct, they can still pursue suitable PLE integration according to the local conditions.
(4) There is a significant linear correlation between the ecological vitality of political organizations and PLE score. This shows that a positive policy organization is the fundamental guarantee for the PLE integration of traditional villages.
The evaluation results can clarify the interaction mechanism of the internal factors of the village, pinpoint problems, and provide a research reference for formulating targeted optimization measures. The comprehensive evaluation system established based on the PLE perspectives breaks through the traditional isolated, static protection method. For China and other countries and regions, it is of positive significance to discuss the quantitative evaluation of traditional villages’ living protection in terms of methods. In theory, it can broaden the ideas of traditional villages’ activation and protection, and in practice, it can provide basis and reference for the activation of traditional villages.
As it is still exploratory research, the interaction mechanism between the internal elements of traditional villages may be more complex network structure or composite structure, and even need more than two multi factor correlation comparative study. Follow up studies need to continue to optimize the traditional mechanism analysis methods. For example, the way of AHP, Pearson correlation analysis of paired comparison, the construction of evaluation index system and the selection of case villages need to be further improved.

Author Contributions

Conceptualization, L.K. and X.X.; Data curation, W.W.; Formal analysis, L.K.; Funding acquisition, X.X.; Methodology, L.K. and W.W.; Project administration, M.Z.; Visualization, J.W.; Writing–original draft, L.K. All authors have read and agreed to the published version of the manuscript.

Funding

This research was supported by National Key R&D Program of China, grant number: 2019YFD1100904, Demonstration of Integration of Key Techniques for the Living Protection and Utilization of Traditional Villages.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Data sharing not applicable.

Acknowledgments

We sincerely thank Haining Wang from the school of architecture, Southeast University, for his efforts in the research process and the students’ participation in the investigation and survey.

Conflicts of Interest

The authors declare no conflict of interest.

Appendix A

Table A1. The comprehensive evaluation system for the living protection of traditional villages.
Table A1. The comprehensive evaluation system for the living protection of traditional villages.
Layer ALayer BWeightOrderLayer CWeightOrderLayer CWeightOrder
The comprehensive evaluation system for the living protection of traditional villagesProduction B10.20002Comprehensive economic vitality C10.06672Villagers’ annual income per capital D10.02222
Village collective annual average income D20.04441
Characteristic industry vitality C20.13331Development of strong industries D30.02763
Development of characteristic industries D40.04501
Daily average number of tourists in Tourism D50.01854
Number of rich leaders D60.01385
Annual output value of rich leaders D70.02852
Ecology B20.40001Material ecologyCharacteristics of landscape and natural environment C30.05001Water green area coverage D80.00593
Landscape environmental quality and overall continuity D90.01342
Uniqueness of ecological environment D100.03071
Characteristics of village space environment
C4
0.15002characteristics of traditional village pattern D110.01236
Landform adaptability D120.01435
Overall features of the village D130.02123
Public space and the number of important nodes D140.01047
Public space and quality of important nodes D150.00748
Types of ancient buildings and cultural relics D160.02064
Number of ancient buildings and cultural relics D170.03191
Characteristics of ancient buildings and cultural relics D180.03182
Spiritual ecologyEcological vitality of political organizations
C5
0.05001Integrity of village management system D190.00674
Integrity of traditional village protection system D200.00883
Implementation of traditional village protection measures D210.01532
Villagers’ participation in protection work D220.01921
Cultural ecological vitality
C6
0.15002Historical value and importance of villages D230.01196
Number of important historical events and figures D240.01245
Important historical events and influence of figures D250.01823
Quantity of traditional intangible culture D260.00767
Characteristics of traditional intangible culture D270.01644
Quantity of traditional products D280.00489
Characteristics of traditional products D290.00798
Participation in Villagers’ cultural life D300.03961
Number of cultural inheritors D310.03122
Living B30.40001The level of human settlement facilities C70.13332Traffic convenience in the village D320.02243
Living infrastructure D330.04382
Integrated service facilities D340.05111
Recreational facilities D350.01604
Village popularity and vitality C80.26671The number of young people returning to villages D360.13161
Number of foreign talents D370.08292
Social Inclusiveness D380.05223
Table A2. Pearson correlation analysis Z-score results between PLE score, PLE CCD and pairwise mutual CCDs.
Table A2. Pearson correlation analysis Z-score results between PLE score, PLE CCD and pairwise mutual CCDs.
Z-Score
(PLE Score)
Z-Score
(PLE CCD)
Z-Score
(E–P CCD)
Z-Score
(P–L CCD)
Z-Score
(L–E CCD)
Z-score
(PLE Score)
Pearson correlation10.937 **0.864 *0.884 *0.893 *
Significance (2- tailed) 0.0060.0260.0190.017
Number of cases66666
Z-score
(PLE CCD)
Pearson correlation0.937 **10.7660.961 **0.958 **
Significance (2- tailed)0.006 0.0760.0020.003
Number of cases66666
Z-score
(E–P CCD)
Pearson correlation0.864 *0.77610.6000.658
Significance (2- tailed)0.0260.076 0.2080.156
Number of cases66666
Z-score
(P–L CCD)
Pearson correlation0.884 *0.961 **0.60010.924 **
Significance (2- tailed)0.0190.0020.208 0.005
Number of cases66666
Z-score
(L–E CCD)
Pearson correlation0.893 *0.958 *0.6580.924 **1
Significance (2- tailed)0.0170.0030.1560.005
Number of cases66666
Note: **, at 0.01 level (2-tailed), the correlation is strong significant; *, at 0.05 level (2-tailed), the correlation is significant.
Table A3. Pearson correlation analysis Z-score results between PLE scores and the C-layer indicators.
Table A3. Pearson correlation analysis Z-score results between PLE scores and the C-layer indicators.
Z-Score
(PLE Score)
Z-Score
(C1)
Z-Score
(C2)
Z-Score
(C3)
Z-Score
(C4)
Z-Score
(C5)
Z-Score
(C6)
Z-Score
(C7)
Z-Score
(C8)
Z-score
(“PLE” Score)
Pearson correlation10.904 *0.919 *0.958 **0.2060.968 **0.937 **0.955 **0.652
Significance (2- tailed) 0.0130.0100.0030.6960.0020.0060.0030.161
Number of cases666666666
Z-score
(C1)
Pearson correlation0.904 *10.916 *0.921 **0.0910.956 **0.812 *0.886 *0.434
Significance(2- tailed)0.013 0.0100.0090.8650.0030.0500.0190.390
Number of cases666666666
Z-score
(C2)
Pearson correlation0.919 **0.916 *10.919 **−0.1280.975 **0.922 **0.960 **0.437
Significance(2- tailed)0.0100.010 0.0100.8080.0010.0090.0020.386
Number of cases666666666
Z-score
(C3)
Pearson correlation0.958 **0.921 **0.919 **10.0110.970 **0.845 *0.917 *0.680
Significance(2- tailed)0.0030.0090.010 0.9840.0010.0340.0100.137
Number of cases666666666
Z-score
(C4)
Pearson correlation0.2060.091−0.1280.01110.0230.1430.0550.170
Significance(2- tailed)0.6960.8650.8080.984 0.9660.7880.9170.747
Number of cases666666666
Z-score
(C5)
Pearson correlation0.968 **0.956 **0.975 **0.970 **0.02310.924 **0.975 **0.519
Significance(2- tailed)0.0020.0030.0010.0010.966 0.0090.0010.291
Number of cases666666666
Z-score
(C6)
Pearson correlation0.937 **0.812 *0.922 **0.845 *0.1430.924 **10.978 **0.428
Significance(2- tailed)0.0060.0500.0090.0340.7880.009 0.0010.397
Number of cases666666666
Z-score
(C7)
Pearson correlation0.955 **0.886 *0.960 **0.917 *0.0550.975 **0.978 **10.443
Significance(2- tailed)0.0030.0190.0020.0100.9170.0010.001 0.379
Number of cases666666666
Z-score
(C8)
Pearson correlation0.6520.4340.4370.6800.1700.5190.4280.4431
Significance(2- tailed)0.1610.3900.3860.1370.7470.2910.3970.379
Number of cases666666666
Note: **, at 0.01 level (2-tailed), the correlation is strong significant; *, at 0.05 level (2-tailed), the correlation is significant.

References

  1. Ye, C.; Ma, X.; Gao, Y.; Johnson, L. The lost countryside: Spatial production of rural culture in Tangwan village in Shanghai. Habitat Int. 2020, 98, 102137. [Google Scholar] [CrossRef]
  2. Ye, C.; Liu, Z. Rural-urban co-governance: Multi-scale practice. Sci. Bull. 2020, 65, 778–780. [Google Scholar] [CrossRef]
  3. Chen, M.; Zhou, Y.; Huang, X.; Ye, C. The Integration of New-Type Urbanization and Rural Revitalization Strategies in China: Origin, Reality and Future Trends. Land 2021, 10, 207. [Google Scholar] [CrossRef]
  4. Yu, B.; Lu, Y.; Zeng, J.; Zhu, Y. Progress and Prospect on Rural Living Space. Scientia Geographica Sinica 2017, 37, 375–385. [Google Scholar]
  5. Long, H.; Zou, J.; Pykett, J.; Li, Y. Analysis of rural transformation development in China since the turn of the new millennium. Appl. Geogr. 2011, 31, 1094–1105. [Google Scholar] [CrossRef]
  6. Xu, J.; Lu, Z.; Huo, X. The evolution and adaptive development of traditional dwelling in Southern Shaanxi, China. Environ. Sci. Pollut. Res. 2019, 26, 13914–13930. [Google Scholar] [CrossRef]
  7. Lennon, B. What next for sustainable development? Our Common Future at Thirty. Eurasian Geogr. Econ. 2019, 61, 338–340. [Google Scholar] [CrossRef]
  8. Zasada, I.; Piorr, A. The role of local framework conditions for the adoption of rural development policy: An example of diversification, tourism development and village renewal in Brandenburg, Germany. Ecol. Indic. 2015, 59, 82–93. [Google Scholar] [CrossRef]
  9. Ilbery, B. Book Review: Geographies of agriculture: Globalisation, restructuring and sustainability. Prog. Hum. Geogr. 2005, 29, 803–805. [Google Scholar] [CrossRef]
  10. Jaszczak, A.; Žukovskis, J.; Antolak, M. The role of rural renewal program in planning of the village public spaces: Systematic approach. Manag. Theory Stud. Rural. Bus. Infrastruct. Dev. 2017, 39, 432–441. [Google Scholar] [CrossRef] [Green Version]
  11. Liu, C.-Z. The Village Renewal in Germany and Its Implications for Taiwan. J. Agric. Econ. 2001, 69, 129–165. [Google Scholar] [CrossRef]
  12. Chigbu, U. Village renewal as an instrument of rural development: Evidence from Weyarn, Germany. Community Dev. 2012, 43, 209–224. [Google Scholar] [CrossRef]
  13. Yang, L.; Liu, P. The Inheritance and Its Evaluation System of Traditional Village Culture: A Case Study of Traditional Village in Hunan Province. Econ. Geogr. 2017, 37, 203–210. [Google Scholar]
  14. Zou, J.; Liu, Y.; Tan, F.; Liu, P. Landscape Vulnerability and Quantitative Evaluation of Traditional Villages: A Case Study of Xintian County, Hunan Province. Sci. Geogr. Sin. 2018, 38, 1292–1300. [Google Scholar]
  15. Ipekoğlu, B. An architectural evaluation method for conservation of traditional dwellings. Build. Environ. 2006, 41, 386–394. [Google Scholar] [CrossRef] [Green Version]
  16. Hu, X.; Li, H.; Zhang, X.; Chen, X.; Yuan, Y. Multi-dimensionality and the totality of rural spatial restructuring from the perspective of the rural space system: A case study of traditional villages in the ancient Huizhou region, China. Habitat Int. 2019, 94, 102062. [Google Scholar] [CrossRef]
  17. Guo, Z.; Sun, L. The planning, development and management of tourism: The case of Dangjia, an ancient village in China. Tour. Manag. 2016, 56, 52–62. [Google Scholar] [CrossRef]
  18. Sun, C.; Zhang, S.; Song, C.; Xu, J.; Fan, F. Investigation of Dynamic Coupling Coordination between Urbanization and the Eco-Environment—A Case Study in the Pearl River Delta Area. Land 2021, 10, 190. [Google Scholar] [CrossRef]
  19. Rosner, A.; Wesołowska, M. Deagrarianisation of the Economic Structure and the Evolution of Rural Settlement Patterns in Poland. Land 2020, 9, 523. [Google Scholar] [CrossRef]
  20. Martínez, P.F.; De Castro-Pardo, M.; Barroso, V.M.; Azevedo, J.C. Assessing Sustainable Rural Development Based on Ecosystem Services Vulnerability. Land 2020, 9, 222. [Google Scholar] [CrossRef]
  21. Chen, Q.; Xie, H. Temporal-Spatial Differentiation and Optimization Analysis of Cultivated Land Green Utilization Efficiency in China. Land 2019, 8, 158. [Google Scholar] [CrossRef] [Green Version]
  22. Perchinunno, P.; Rotondo, F.; Torre, C.M. The Evidence of Links between Landscape and Economy in a Rural Park. Int. J. Agric. Environ. Inf. Syst. 2012, 3, 72–85. [Google Scholar] [CrossRef] [Green Version]
  23. Cerreta, M.; Poli, G. A Complex Values Map of Marginal Urban Landscapes. Int. J. Agric. Environ. Inf. Syst. 2013, 4, 41–62. [Google Scholar] [CrossRef] [Green Version]
  24. Renes, H.; Centeri, C.; Kruse, A.; Kučera, Z. The Future of Traditional Landscapes: Discussions and Visions. Land 2019, 8, 98. [Google Scholar] [CrossRef] [Green Version]
  25. Guo, R.; Bai, Y. Simulation of an Urban-Rural Spatial Structure on the Basis of Green Infrastructure Assessment: The Case of Harbin, China. Land 2019, 8, 196. [Google Scholar] [CrossRef] [Green Version]
  26. Duan, Z.; Lyu, H.; Yang, X.; Yang, Y. Green Improvement Technology of Wind Environment of Traditional Courtyard House A Case Study of Fang Zhaotu House in Fangding Village, Zhengzhou. Build. Sci. 2019, 35, 25–31. [Google Scholar]
  27. Shao, T.; Zheng, W.; Jin, H. Analysis of the Indoor Thermal Environment and Passive Energy-Saving Optimization Design of Rural Dwellings in Zhalantun, Inner Mongolia, China. Sustainability 2020, 12, 1103. [Google Scholar] [CrossRef] [Green Version]
  28. Xu, M.; Hu, W.-Q. A research on coordination between economy, society and environment in China: A case study of Jiangsu. J. Clean. Prod. 2020, 258, 120641. [Google Scholar] [CrossRef]
  29. Mitchell, C.J.A.; VanderWerf, J. Creative Destruction and Trial by Space in a Historic Canadian Village. Geogr. Rev. 2010, 100, 356–374. [Google Scholar] [CrossRef]
  30. Martellozzo, F. Forecasting High Correlation Transition of Agricultural Landscapes into Urban Areas. Int. J. Agric. Environ. Inf. Syst. 2012, 3, 22–34. [Google Scholar] [CrossRef] [Green Version]
  31. Tong, W.; Lo, K.; Zhang, P. Land Consolidation in Rural China: Life Satisfaction among Resettlers and Its Determinants. Land 2020, 9, 118. [Google Scholar] [CrossRef] [Green Version]
  32. Makhzoumi, J.M. Unfolding Landscape in a Lebanese Village: Rural Heritage in a Globalising World. Int. J. Herit. Stud. 2009, 15, 317–337. [Google Scholar] [CrossRef]
  33. Yu, H.; Luo, Y.; Li, P.; Dong, W.; Yu, S.; Gao, X. Water-Facing Distribution and Suitability Space for Rural Mountain Settlements Based on Fractal Theory, South-Western China. Land 2021, 10, 96. [Google Scholar] [CrossRef]
  34. Long, H.; Tu, S.; Ge, D.; Li, T.; Liu, Y. The allocation and management of critical resources in rural China under restructuring: Problems and prospects. J. Rural. Stud. 2016, 47, 392–412. [Google Scholar] [CrossRef] [Green Version]
  35. Attardi, R.; Cerreta, M.; Sannicandro, V.; Torre, C.M. Non-compensatory composite indicators for the evaluation of urban planning policy: The Land-Use Policy Efficiency Index (LUPEI). Eur. J. Oper. Res. 2018, 264, 491–507. [Google Scholar] [CrossRef]
  36. Torre, C.M.; Morano, P.; Tajani, F. Saving Soil for Sustainable Land Use. Sustainability 2017, 9, 350. [Google Scholar] [CrossRef] [Green Version]
  37. Li, W.; Zhou, Y.; Zhang, Z. Strategies of Landscape Planning in Peri-Urban Rural Tourism: A Comparison between Two Villages in China. Land 2021, 10, 277. [Google Scholar] [CrossRef]
  38. Tang, C.; Zheng, Q.; Wang, X.; Zou, Z. Discussion on the model of green development of tourism in traditional village. J. Arid Land Resour. Environ. 2019, 33, 203–208. [Google Scholar]
  39. Liu, T.; Liu, P.; Wang, L. The protection and tourism development path of ancient villages and old towns under the background of new-type urbanization:A case study of old town of Xuanzhou in Hunan province. Geogr. Res. 2019, 38, 133–145. [Google Scholar]
  40. Yu, S.-H.; Deng, W.; Xu, Y.-X.; Zhang, X.; Xiang, H.-L. Evaluation of the production-living-ecology space function suitability of Pingshan County in the Taihang mountainous area, China. J. Mt. Sci. 2020, 17, 2562–2576. [Google Scholar] [CrossRef]
  41. Yang, F.; Chi, G.; Wang, G.; Tang, S.; Li, Y.; Ju, C. Untangle the Complex Stakeholder Relationships in Rural Settlement Consolidation in China: A Social Network Approach. Land 2020, 9, 210. [Google Scholar] [CrossRef]
  42. Dharmawan, A.H.; Mardiyaningsih, D.I.; Komarudin, H.; Ghazoul, J.; Pacheco, P.; Rahmadian, F. Dynamics of Rural Economy: A Socio-Economic Understanding of Oil Palm Expansion and Landscape Changes in East Kalimantan, Indonesia. Land 2020, 9, 213. [Google Scholar] [CrossRef]
  43. Tu, S.; Long, H.; Zhang, Y.; Ge, D.; Qu, Y. Rural restructuring at village level under rapid urbanization in metropolitan suburbs of China and its implications for innovations in land use policy. Habitat Int. 2018, 77, 143–152. [Google Scholar] [CrossRef]
  44. Yu, Z.; Xu, E.; Zhang, H.; Shang, E. Spatio-Temporal Coordination and Conflict of Production-Living-Ecology Land Functions in the Beijing-Tianjin-Hebei Region, China. Land 2020, 9, 170. [Google Scholar] [CrossRef]
  45. Meng, F.; Guo, J.; Guo, Z.; Lee, J.C.; Liu, G.; Wang, N. Urban ecological transition: The practice of ecological civilization construction in China. Sci. Total. Environ. 2021, 755, 142633. [Google Scholar] [CrossRef]
  46. Salvia, R.; Egidi, G.; Vinci, S.; Salvati, L. Desertification Risk and Rural Development in Southern Europe: Permanent Assessment and Implications for Sustainable Land Management and Mitigation Policies. Land 2019, 8, 191. [Google Scholar] [CrossRef] [Green Version]
  47. Li, Y.; Fan, P.; Liu, Y. What makes better village development in traditional agricultural areas of China? Evidence from long-term observation of typical villages. Habitat Int. 2019, 83, 111–124. [Google Scholar] [CrossRef]
  48. Head, L. Cultural ecology: Adaptation-retrofitting a concept? Prog. Hum. Geogr. 2010, 34, 234–242. [Google Scholar] [CrossRef]
  49. Qiu, L.; Zeng, W.; Kant, S.; Wang, S. The Role of Social Capital in Rural Households’ Perceptions toward the Benefits of Forest Carbon Sequestration Projects: Evidence from a Rural Household Survey in Sichuan and Yunnan Provinces, China. Land 2021, 10, 91. [Google Scholar] [CrossRef]
  50. Long, Y.; Xu, G.; Ma, C.; Chen, L. Emergency control system based on the analytical hierarchy process and coordinated development degree model for sudden water pollution accidents in the Middle Route of the South-to-North Water Transfer Project in China. Environ. Sci. Pollut. Res. 2016, 23, 12332–12342. [Google Scholar] [CrossRef]
  51. Chand, B.; Kaushik, H.B.; Das, S. Lateral Load Behavior of Traditional Assam-Type Wooden House. J. Struct. Eng. 2019, 145, 04019072. [Google Scholar] [CrossRef]
  52. Bu, X.; Pu, L.; Shen, C.; Xie, X.; Xu, C. Study on the Spatial Restructuring of the Village System at the County Level Oriented toward the Rural Revitalization Strategy: A Case of Jintan District, Jiangsu Province. Land 2020, 9, 478. [Google Scholar] [CrossRef]
  53. Long, Y.; Yang, Y.; Lei, X.; Tian, Y.; Li, Y. Integrated Assessment Method of Emergency Plan for Sudden Water Pollution Accidents Based on Improved TOPSIS, Shannon Entropy and a Coordinated Development Degree Model. Sustainability 2019, 11, 510. [Google Scholar] [CrossRef] [Green Version]
  54. Fu, J.; Zhou, J.; Deng, Y. Heritage values of ancient vernacular residences in traditional villages in Western Hunan, China: Spatial patterns and influencing factors. Build. Environ. 2021, 188, 107473. [Google Scholar] [CrossRef]
  55. Gong, W.; Wang, N.; Zhang, N.; Han, W.; Qiao, H. Water resistance and a comprehensive evaluation model of magnesium oxychloride cement concrete based on Taguchi and entropy weight method. Constr. Build. Mater. 2020, 260, 119817. [Google Scholar] [CrossRef]
  56. Wang, D.; Jiang, D.; Fu, J.; Lin, G.; Zhang, J. Comprehensive Assessment of Production–Living–Ecological Space Based on the Coupling Coordination Degree Model. Sustainability 2020, 12, 2009. [Google Scholar] [CrossRef] [Green Version]
  57. Wang, H. Regional Ecological Risk Assessment with Respect to Human Disturbance in the Poyang Lake Region (PYLR) Using Production–Living–Ecology Analysis. J. Indian Soc. Remote. Sens. 2021, 49, 449–460. [Google Scholar] [CrossRef]
  58. Wei, C.; Lin, Q.; Yu, L.; Zhang, H.; Ye, S.; Zhang, D. Research on Sustainable Land Use Based on Production-Living-Ecological Function: A Case Study of Hubei Province, China. Sustainability 2021, 13, 996. [Google Scholar] [CrossRef]
  59. Lin, J.; Song, G.; Zhang, Y. Synergistic Evolution Mechanism of Production-Living-Ecology Functions in Spatial Planning System: A Case Study of Fuxin City. China Land Sci. 2019, 33, 9–17. [Google Scholar]
  60. Geng, Y.; Zhang, H. Coordination assessment of environment and urbanization: Hunan case. Environ. Monit. Assess. 2020, 192, 637. [Google Scholar] [CrossRef]
  61. Qiao, W.; Hu, Y.; Jia, K.; He, T.; Wang, Y. Dynamic modes and ecological effects of salt field utilization in the Weifang coastal area, China: Implications for territorial spatial planning. Land Use Policy 2020, 99, 104952. [Google Scholar] [CrossRef]
  62. Zhai, R.; Liu, Y. Dynamic evolvement of agricultural system and typical patterns of modern agriculture in coastal China: A case of Suzhou. Chin. Geogr. Sci. 2009, 19, 249–257. [Google Scholar] [CrossRef] [Green Version]
Figure 1. Distribution of typical traditional villages around Taihu Lake.
Figure 1. Distribution of typical traditional villages around Taihu Lake.
Land 10 00570 g001
Figure 2. Flowchart for the comprehensive evaluation system.
Figure 2. Flowchart for the comprehensive evaluation system.
Land 10 00570 g002
Figure 3. Process of the horizontal PLE coupling coordination model.
Figure 3. Process of the horizontal PLE coupling coordination model.
Land 10 00570 g003
Figure 4. Process of the vertical correlation analysis model.
Figure 4. Process of the vertical correlation analysis model.
Land 10 00570 g004
Figure 5. The relationship between PLE score with PLE CCD.
Figure 5. The relationship between PLE score with PLE CCD.
Land 10 00570 g005
Figure 6. The relationship among pairwise mutual CCDs.
Figure 6. The relationship among pairwise mutual CCDs.
Land 10 00570 g006
Figure 7. The relationship of PLE CCD with pairwise mutual CCDs.
Figure 7. The relationship of PLE CCD with pairwise mutual CCDs.
Land 10 00570 g007
Figure 8. The significance of Pearson results between the PLE score, PLE CCD, and pairwise mutual CCDs.
Figure 8. The significance of Pearson results between the PLE score, PLE CCD, and pairwise mutual CCDs.
Land 10 00570 g008
Figure 9. Z-scores of production, living, and ecology after normalization.
Figure 9. Z-scores of production, living, and ecology after normalization.
Land 10 00570 g009
Figure 10. The Z-score of each index in C layer.
Figure 10. The Z-score of each index in C layer.
Land 10 00570 g010
Figure 11. The significance of Pearson results between the PLE scores and the C-layer indicators.
Figure 11. The significance of Pearson results between the PLE scores and the C-layer indicators.
Land 10 00570 g011
Figure 12. Normalized Z-scores of villages’ indicators at layer C.
Figure 12. Normalized Z-scores of villages’ indicators at layer C.
Land 10 00570 g012
Table 1. Basic information of villages.
Table 1. Basic information of villages.
Village NameGeographical PositionTypeGradeBasic Information and Characteristics
YangfengHuaikan Township, Changxing Countymountainous typenational gradeA population of 1453 (2019); the main industries are forestry, mining resources development, and tourism; a forest coverage rate of more than 80%. Yangfeng village has a large number of historical sites of the Communist Party, known as “little Yanan in the south of the Yangtze River”.
ErduXiazhuhu street, Deqing Countywater-network intensive typeprovincial gradeA population of 1775 (2019), the main industries are ecological agriculture, aquaculture, and tourism services. It is known as the most beautiful wetland in China and an important part of Xiazhu Lake National Wetland Park.
ShazhangKunlun Street, Liyang Cityurban-suburbs typenational gradeA population of 1014 (most of which have moved to the New Village), the main industry is concentrated aquaculture. Shazhang Village Lane presents a structure of two horizontal and six vertical, which is famous for its features of “ancient village, ancient water, ancient tomb and ancient trees”.
YanjiaqiaoYangjian Town, Xishan Districturban-suburbs typenational gradeA population of 5770 (2019), the main industries are ecological agriculture, processing and manufacturing, and eco-tourism. In the 1920s and 1930s, the village was a famous trading dock for rice, books, cloth, and medicine in Wuxi, and also a famous birthplace of Xi opera.
YangqiaoQianhuang Town, Wujin Districtwater-network intensive typenational gradeA population of 5211 (2019), the main industries are traditional cultivation, aquaculture, and tourism services. There are about 13,000 square meters of ancient buildings from the Ming and Qing Dynasties and the Republic of China. About 1000 square meters of stone revetments have been well preserved.
TangliJinting Town, Wuzhong Districtmountainous typenational gradeA population of 2991 (2019); the main industries are traditional planting and tourism. There are more than 30 single buildings and cultural relics, among which Diaohua hall, Rongde hall, and Qinyuan hall are typical.
Table 2. Classification of PLE coupling coordination degree.
Table 2. Classification of PLE coupling coordination degree.
PLE Development StageCoupling Coordination TypeCoupling
Coordination
Degree
Coordination and
integration period
Type I integration0.9~1.0
Type II integration0.8~0.9
Type Ш integration0.7~0.8
Running-in and
adjustment period
Type I adjustment0.6~0.7
Type II adjustment0.5~0.6
Antagonistic and
contradictory period
Type I contradiction0.4~0.5
Type II contradiction0.3~0.4
Declining and
maladjusted period
Type I maladjustment0.2~0.3
Type II maladjustment
Type Ш maladjustment
0.1~0.2
0~0.1
Table 3. Comprehensive evaluation index result.
Table 3. Comprehensive evaluation index result.
Layer CScoreAverage ScoreLayer DScoreAverage Score
YFEDSZYJQYQTLYFEDSZYJQYQTL
C13.754.660.664.354.634.713.78D11.531.550.221.111.521.591.24
D22.223.100.443.243.113.122.53
C29.3111.732.7710.398.0110.118.72D31.932.480.822.481.381.941.84
D43.154.021.354.053.154.053.29
D51.291.660.180.920.551.290.98
D60.960.960.130.960.960.960.82
D71.992.560.281.991.991.991.81
C33.894.271.893.513.624.513.62D80.530.290.290.410.530.530.43
D91.211.200.670.930.931.221.02
D102.142.760.922.142.122.762.14
C49.725.469.0310.8610.4411.769.55D111.110.611.110.860.860.860.90
D121.281.001.131.281.001.561.09
D131.481.061.471.481.901.921.55
D140.720.520.720.750.720.520.66
D150.660.370.070.370.660.510.44
D160.610.611.441.031.441.851.16
D170.950.952.212.272.232.231.80
D182.860.310.952.861.592.861.90
C54.124.511.474.123.734.513.74D190.600.610.210.610.630.660.53
D200.790.790.610.790.790.790.76
D211.391.340.451.331.311.371.21
D221.341.720.191.340.961.721.21
C69.869.324.8710.347.449.898.62D230.830.830.590.830.590.590.71
D240.620.370.860.620.620.620.62
D251.270.910.911.270.540.910.97
D260.220.380.380.220.380.530.35
D271.141.140.491.470.491.140.98
D280.240.140.040.240.240.240.19
D290.390.390.070.070.230.710.31
D303.563.511.182.772.773.562.89
D311.561.560.312.811.561.551.55
C712.1111.651.3111.718.2311.739.46D322.012.010.222.012.012.011.71
D333.943.940.433.943.063.943.21
D344.594.590.514.592.554.593.57
D351.441.120.161.440.821.461.07
C89.1210.757.377.427.9815.999.77D361.311.313.941.311.316.582.63
D374.145.800.822.482.485.823.59
D383.213.652.613.853.673.593.43
Amount61.8862.3529.3762.7154.0873.2157.26 61.8862.3529.3762.7154.0873.2157.26
Table 4. Comprehensive evaluation index result.
Table 4. Comprehensive evaluation index result.
Layer DCronbach’s AlphaLayer DCronbach’s Alpha
D10.949D200.951
D20.949D210.954
D30.950D220.953
D40.948D230.952
D50.950D240.952
D60.949D250.949
D70.949D260.951
D80.953D270.949
D90.953D280.949
D100.950D290.952
D110.950D300.955
D120.949D310.953
D130.955D320.953
D140.952D330.951
D150.952D340.949
D160.954D350.951
D170.949D360.949
D180.955D370.949
D190.955D380.950
Table 5. The score of PLE, coupling coordination degree scores and Z-score processing results.
Table 5. The score of PLE, coupling coordination degree scores and Z-score processing results.
Village NamePLE ScorePLE
CCD
L–E CCDP–L
CCD
E–P
CCD
Z-Score
PLE Score
Z-Score
PLE CCD
Z-Score
L–E CCD
Z-Score
P–L CCD
Z-Score
E–P CCD
Yangfeng61.880.760.740.710.770.308330.650110.370470.696160.32223
Erdu62.350.630.820.840.560.339750.079890.28871−0.401510.91481
Shazhang29.370.280.310.290.19−1.86449−1.52665−1.38747−1.45669−1.61181
Yanjiaqiao62.710.680.820.510.760.363810.291190.683750.65367−0.56392
Yangqiao54.080.450.390.610.42−0.21298−0.75418−1.06993−0.661160.12344
Tangli73.210.890.920.870.891.065581.259651.114481.169531.06212
Table 6. Z-score normalization results of production, living, and ecology.
Table 6. Z-score normalization results of production, living, and ecology.
Village NameProductionLivingEcologyZ-Score
(Production)
Z-Score
(Living)
Z-Score
(Ecology)
Yangfeng13.127.621.10.122630.442730.28009
Erdu16.423.522.40.83674−0.414840.47871
Shazhang3.517.28.7−1.95480−1.73256−1.61436
Yanjiaqiao14.628.818.40.447220.693720.02037
Yangqiao12.725.215.90.03607−0.05926−0.51435
Tangli14.930.628.10.512141.070221.34954
Table 7. Normalized results of Z-scores for sub-indicators at layer C.
Table 7. Normalized results of Z-scores for sub-indicators at layer C.
Layer CZ-Score
(Yangfeng)
Z-Score
(Erdu)
Z-Score (Shazhang)Z-Score (Yanjiaqiao)Z-Score (Yangqiao)Z-Score (Tangli)
C1−0.027490.54987−1.987990.353190.530840.58159
C20.186510.95150−1.880880.52791−0.224440.43940
C30.296800.70693−1.86177−0.113330.005400.96596
C40.07919−1.84845−0.233040.595030.404991.00228
C50.327160.66591−1.974570.32716−0.011580.66591
C60.590430.33330−1.785560.81898−0.561860.60471
C70.625500.51706−1.920510.53121−0.289180.53592
C8−0.197280.29617−0.72706−0.71192−0.542391.88248
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Kong, L.; Xu, X.; Wang, W.; Wu, J.; Zhang, M. Comprehensive Evaluation and Quantitative Research on the Living Protection of Traditional Villages from the Perspective of “Production–Living–Ecology”. Land 2021, 10, 570. https://0-doi-org.brum.beds.ac.uk/10.3390/land10060570

AMA Style

Kong L, Xu X, Wang W, Wu J, Zhang M. Comprehensive Evaluation and Quantitative Research on the Living Protection of Traditional Villages from the Perspective of “Production–Living–Ecology”. Land. 2021; 10(6):570. https://0-doi-org.brum.beds.ac.uk/10.3390/land10060570

Chicago/Turabian Style

Kong, Lingyu, Xiaodong Xu, Wei Wang, Jinxiu Wu, and Meiying Zhang. 2021. "Comprehensive Evaluation and Quantitative Research on the Living Protection of Traditional Villages from the Perspective of “Production–Living–Ecology”" Land 10, no. 6: 570. https://0-doi-org.brum.beds.ac.uk/10.3390/land10060570

Note that from the first issue of 2016, this journal uses article numbers instead of page numbers. See further details here.

Article Metrics

Back to TopTop