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Article

Measurement and Coupling Coordination of High-Quality Development in Guangdong Province of China: A Spatiotemporal Analysis

1
School of Public Administration, Guangzhou University, Guangzhou 510006, China
2
Guangdong Provincial Key Laboratory of Urbanization and Geo-Simulation, School of Geography and Planning, Sun Yat-sen University, Guangzhou 510275, China
*
Author to whom correspondence should be addressed.
These authors contributed equally to this work.
Int. J. Environ. Res. Public Health 2023, 20(5), 4305; https://doi.org/10.3390/ijerph20054305
Submission received: 21 January 2023 / Revised: 20 February 2023 / Accepted: 23 February 2023 / Published: 28 February 2023

Abstract

:
Regional high-quality coordination plays a crucial role in promoting high-quality national development. Guangdong province is a trailblazer in China’s reform and opening-up policies and high-quality development. This study analyzes the high-quality development of the economic, social, and ecological environments from 2010 to 2019 in Guangdong with the entropy weight TOPSIS model. Meanwhile, the coupling coordination degree model is used to investigate the spatial-temporal pattern of the coupling and coordinated development of the three-dimensional system in 21 prefecture-level cities. The results show that the high-quality development index of Guangdong increased from 0.32 to 0.39, a 21.9% increase during 2010–2019. The Pearl River Delta had the highest value of the high-quality development index, whereas Western Guangdong had the lowest level in 2019. Guangzhou, Shenzhen, Zhuhai, and Dongguan are the core cities in the high-quality development of Guangdong, with the index decreasing from the Pearl River Delta estuary cities to the province’s edge. We also found that the coupling degree and coupling coordination of high-quality development of the three-dimensional system grew slowly during the study period. Half of the cities in Guangdong entered the stage of benign coupling. Except for Zhaoqing, all cities in the Pearl River Delta have a high coupling coordination degree of high-quality development of the three-dimensional system. This study provides valuable references for the high-quality, coordinated development of Guangdong province and some policy suggestions for other regions.

1. Introduction

The 19th CPC National Congress states that China’s economy has been transitioning from a phase of rapid growth to a stage of high-quality development [1]. It is a pivotal stage for adapting to the principal contradiction facing Chinese society and ecological conservation. The 2022 Central Economic Work Conference also emphasizes that China must make high-quality development a top priority to make China a modern socialist country in all respects. Therefore, the current resource- and investment-driven economy should be transformed into an innovation-driven economy. More efficient use of advanced factors of production, lower ecological costs, and greener technology are helping China’s economy moves towards a stage of high-quality development.
Existing studies have different understandings of high-quality development since it was proposed. Some literature focuses on a single evaluation index, such as total factor productivity [2], economic growth rate [3], or labor productivity [4,5,6], to quantify high-quality development. For instance, Beugelsdijk et al. assessed European development with the total factor productivity [7]. Others constructed a multi-dimensional evaluation index system of high-quality development [8,9,10,11]. Chen and Huo created an evaluation index system to assess the high-quality development of China’s economy, involving innovation, coordination, green, openness, and sharing development [12].
Previous studies attached great significance to high-quality economic development, whereas some of them ignored the fact that high-quality development is part of a complex organic whole involving the economy, society, culture, and ecology [13]. Although most scholars analyze the coupling coordination of just two systems, the coupling coordination of high-quality development is multi-dimensional [14,15]. The existing studies are more concerned with the coupling coordination of two systems from the province, city, basin, and city-cluster levels, such as the ecological economy environment [16,17,18,19], demographic economy [20,21,22], and industrial economy [23,24,25]. These studies pay attention to scientific and technological innovation, industrial structure, urbanization, social development, and ecological environments, whereas the coupling coordination of multiple dimensions receives little research attention.
China’s high-quality development, which regional growth poles are responsible for pursuing, sets a higher requirement for regional coordination. Taking advantage of being adjacent to Hong Kong and Macao and having the longest coastlines, Guangdong province is a pioneer in reform and opening-up policies. As a strong economic province in China, a cascade of development issues caused by rapid urbanization and economic transformation, such as unreasonable economic structure, a significant income gap between urban and rural areas, unbalanced regional development, and ecological damage, have become common, affecting the high-quality coordination of its economic, social, and ecological environment systems. Therefore, this study attempts to build a three-dimensional (3D) system of economy, society, and ecological environments, as well as analyze the coupling coordination of these systems, aiming to promote high-quality regional development.
The existing literature mainly focuses on building an evaluation index system, coupling coordination, and empirical analysis regarding high-quality development. Nevertheless, these studies are limited in several ways. First, many studies use the single index, such as total factor productivity, to measure high-quality development, while this substitution does not fully recognize the multi-dimensional characteristics. Second, some scholars analyze the interactions between high-quality economic development and other influencing factors, including demographic structure, environmental regulation, and urbanization. However, a comprehensive assessment of coupling coordination among economic, social, and ecological systems is important to realize high-quality development, and few studies examine the relationship among them. This study makes up for enriching the existing literature. From the scale of a prefecture-level city, this study aims to establish a comprehensive evaluation index system of the economy, society, and ecological environments. The results of this analysis depict an overview of current high-quality development in different cities in the Guangdong province, helping us design differentiated policies to promote high-quality development at the city level. Further, we seek to analyze the coupling and coordinated development of the 3D system in different regions of Guangdong province during 2010–2019 with the coupling coordination degree model. It not only helps to theoretically understand the coupling coordination mechanism among economic, social, and ecological systems to achieve sustainable development but also helps the government to enact more rational and diversified strategies for rural revitalization, the new type of urbanization, and coordinated urban and rural development.
The structure of this paper is as follows. First, we present the study area and establish evaluation indexes for high-quality development. Second, we introduce the entropy weight TOPSIS method and coupling coordination degree model to analyze the interactions among economic, social, and ecological systems. Third, explain the results and discuss our main findings. Lastly, policy implications, limitations, and suggestions for future research are provided in the Conclusions.

2. Materials and Methodology

2.1. Study Area

Guangdong province, lying between 20°09′ N–25°31′ N and 109°45′ E–117°20′ E, is situated in the southernmost part of mainland China. It borders Hong Kong and Macao Special Administrative Regions to the south, and Fujian to the east, Jiangxi and Hunan to the north, and the Zhuang Autonomous Region of Guangxi to the west (Figure 1). There are 21 prefectural-level cities with a total area of 179,725 km2. The northern part of Guangdong is covered with mountains and hills with a higher terrain, whereas the southern region is dominated by plains with a lower terrain. Located in the East Asian monsoon region, Guangdong has a subtropical monsoon climate with an average annual temperature of 21.8 °C and an average annual precipitation of 1789.3 mm. As the most economically developed province in China, Guangdong’s GDP has a 1.9% year-over-year growth rate, reaching 1291.19 trillion yuan in 2022. The population ranks first nationwide, with a total permanent resident population of 126.24 million in the seventh national census in 2020.

2.2. Evaluation Index System of High-Quality Development

In terms of multi-dimensional nature, integrity, and coordination, this study follows the principles of science and comparability and constructs a comprehensive evaluation index system of high-quality development in the 3D system [26,27,28]. Table 1 reports different indicators of each system.
The high-quality development of economic systems includes upgrades to economic structure, technological innovation, and improvements to total factor productivity [29,30]. Social systems involve the coordinated and shared development of urban and rural areas, improved infrastructure, education and culture, social harmony, and stability [31,32,33]. The indicators of ecological environment system development originate from the 2015 Technical Criterion for Ecosystem Status Evaluation published by the Ministry of Ecology and Environment [34], covering vegetation coverage, water density, pollution load, and biological abundance.
Table 1. Comprehensive evaluation index system of high-quality development in the three-dimensional system during 2010–2019.
Table 1. Comprehensive evaluation index system of high-quality development in the three-dimensional system during 2010–2019.
SystemDimensionCriterion LayerIndicatorAttributesWeightSource
EconomyEconomic structure upgradingEconomic structureIndustrial structure rationalization index0.0303Wang et al., 2022 [31]
Industrial structure upgrading index+0.0430Wang et al., 2022 [31]
Investment structureNumber of start-ups+0.0451Wang et al., 2022 [31]
Ratio of investment in the tertiary industry+0.0315Wang et al., 2022 [31]
Number of VCPE investments+0.0509Wang et al., 2022 [31]
Consumption structureConsumer Price Index0.0203Wang et al., 2022 [31]
Ratio of local government budgetary expenditure0.0081Wang et al., 2022 [31]
Trade structureNumber of new foreign projects for the year+0.0269Wang et al., 2022 [31]
Foreign investment in actual use/GDP+0.1043Song et al., 2022 [27]
Total import and export of goods/GDP+0.1169Song et al., 2022 [27]
Innovation-drivenInnovation inputR&D expenditures of industrial enterprises above designated size/Gross industrial output value+0.0629Song et al., 2022 [27]
R&D employees of industrial enterprises above designated size/employees of secondary industry+0.0943Song et al., 2022 [27]
Innovation outputNumber of invention patent grants+0.0245Wang et al., 2022 [31]
Number of published utility model patents+0.0546Wang et al., 2022 [31]
Number of published design patents+0.0148Wang et al., 2022 [31]
New product sales revenue of large and medium-sized industrial enterprises/Gross industrial output value+0.0814Wang et al., 2022 [31]
Efficient resource allocationCapital productivityGDP/Total investment in fixed assets+0.0364Wang et al., 2022 [31]
Labor productivityGDP/All employees+0.0632Wang et al., 2022 [31]
Energy productivityGDP/million tce+0.0647Fang et al., 2020 [33]
Land productivityTotal grain production/Total arable area+0.0260Wang et al., 2022 [31]
SocietyCoordinated and shared developmentRegional revenue sharingCities’ GDP per capita/Guangdong’s GDP per capita+0.0636Wang et al., 2022 [31]
Regional consumption sharingCities’ household consumption level/Guangdong’s average household consumption level+0.0442Wang et al., 2022 [31]
Urban and rural income coordinationUrban-rural income ratio0.0043Song et al., 2022 [27]
Urban and rural consumption coordinationUrban-rural consumption ratio0.0072Song et al., 2022 [27]
Improved infrastructurePublic transportNumber of buses for every 10,000 people+0.1659Wong et al., 2013 [32]
Transportation facilityPer capita urban road area+0.1331Song et al., 2022 [27]
Medical facilityNumber of beds in hospitals and health centers (pieces) per capita+0.0139Song et al., 2022 [27]
Basic old-age facilityRatio of basic endowment insurance+0.0224Wong et al., 2013 [32]
Education and cultureEducation facilityNumber of colleges and universities+0.2102Fang et al., 2020 [33]
Cultural facilityPublic library holdings per capita+0.1248Song et al., 2022 [27]
Internet penetration rateCapita Internet broadband access port+0.0656Fang et al., 2020 [33]
Teacher-student ratio of elementary educationTeacher-student ratio of secondary schools+0.0196Wong et al., 2013 [32]
Social harmony and stabilityThe emphasis of the service industryValue-added of tertiary industry/GDP+0.0174Wang et al., 2022 [31]
Advance of service productDensity of starred hotels (five-star and four-star)+0.0661Wang et al., 2022 [31]
Optimization of service consumptionTotal revenue of tourism/number of tourists+0.0314Wang et al., 2022 [31]
Stability of social employmentCities’ registered urban unemployed population0.0044Wang et al., 2022 [31]
Safety production accident rateCities’ death rate of production safety accidents with a GDP of RMB 100 million0.0060Wang et al., 2022 [31]
Ecological environmentBiological abundanceBiological abundance indexBiodiversity index, ecological environment quality index (forestry, grassland, water wetland, cropland, construction land, unused land) /0.35Ministry of Ecology and Environment, 2015 [34]
Vegetation coverageVegetation coverage indexNormalized Difference Vegetation Index (NDVI)/0.25Ministry of Ecology and Environment, 2015 [34]
Water densityWater density indexRiver length, water area, water resources/0.15Ministry of Ecology and Environment, 2015 [34]
Land stressLand stress indexSevere erosion intensity, moderate erosion intensity, construction land, other land stress/0.15Ministry of Ecology and Environment, 2015 [34]
Pollution loadPollution load indexSO2 emission, ammonia-nitrogen emission, dust emission, amount of solid waste discarded, chemical oxygen demand/0.10Ministry of Ecology and Environment, 2015 [34]
Environmental constraintsEnvironmental constraints indexEmergent environmental incidents, environmental pollution/ObligatoryMinistry of Ecology and Environment, 2015 [34]
Notes: “+” and “−” represent the positive and negative indexes, respectively. A higher positive index indicates a more remarkable improvement. Source: arranged by the authors.

2.3. The Entropy Weight TOPSIS Method

The entropy weight TOPSIS method is an objective approach that reveals the utility of each indicator and avoids the disturbance of subjective elements [35]. Firstly, the extremum method is selected as the data standardization method. Then, the entropy weight method is applied to calculate the weight of each indicator. Lastly, the TOPSIS method is used to measure and rank the index of high-quality development. The entropy weight TOPSIS approach is suitable for evaluating emerging new objects [36]. This paper calculates the level of high-quality development in Guangdong province based on the entropy weight TOPSIS method, as follows:

2.3.1. Standardization and Processing

Dimensionless processing is performed on the matrix to eliminate the influence of the index dimension. The extremum method is a data standardization method used to calculate economic and social high-quality development in Guangdong province:
Positive   indicator :   Z i j = ( X i j X m i n ) ( X m a x X m i n )
Negative   indicator :   Z i j = ( X m a x X i j ) ( X m a x X m i n )
where Z i j is the value after standardization; i and j represent a city and an indicator, respectively; X m a x and X m i n are the maximum and minimum of X i j ; X i j is the value before standardization with a positive shift (0.0001); and Z i j [ 0.0001 ,   1.0001 ] .

2.3.2. Calculation of Index Weight

The entropy weight method is applied to define each indicator’s weight and avoid the impact of human interference on the indicators:
Normalization :   P i j = Z i j i = 1 n Z i j
P i j is the normalized value of Z i j .
Information   entropy   value :   E j = k i = 1 n P i j ln P i j
where k = 1 / ln n ; E j is the entropy value of indicator j.
Weight :   W j = 1 E j j = 1 m D j
W j is the weight of various indicators in Table 1.

2.3.3. TOPSIS Method

The positive and negative ideal solutions are defined according to the weighted matrix of the high-quality development index. We also calculated the Euclidean distance between the solutions, the closeness of the evaluated target object, and the optimal solution.
The   weighted   matrix :   R = ( r i j ) n × m
where r i j = ( W j × Z i j ) .
The positive and negative ideal solutions are Q j + and Q j :
Q j + = ( Q 1 + , Q 2 + ,   Q m + )
Q j = ( Q 1 , Q 2 ,   Q m )
The Euclidean distance between the positive and negative ideal solutions is calculated as d i + and d i :
d i + = j = 1 m ( Q j + r i j ) 2
d i = j = 1 m ( Q j r i j ) 2
Ci is the closeness of the evaluated target object and the optimal solution:
C i = d i d i + + d i
Ci is between 0 and 1, representing the high-quality development level of city i in various systems.

2.4. Coupling Coordination Degree Model

The high-quality development index of the economic and social systems of Guangdong province is calculated with the entropy weight TOPSIS approach. Furthermore, this paper utilized the coupling coordination degree model to analyze the interactions among economic, social, and ecological environment systems with a high-quality development index.

2.4.1. Types of Coupling Degree Models

Coupling is a concept encountered in physical electronics [37] that can help in analyzing the interactions of two or more systems [38,39]. This study applies the coupling degree model to analyze the reciprocity of the 3D system of economy, society, and ecological environments. A higher coupling value implies a more positive effect on high-quality development and vice versa. Table 2 summarizes four types of coupling degree models:
C = 3 { ( U 1 × U 2 × U 3 ) ( U 1 + U 2 + U 3 ) 3 } 1 / 3
where C is the coupling degree of the high-quality development of the 3D system of economy, society, and ecological environments; C [ 0 ,   1 ] ; and U 1 , U 2 , and U 3 indicate the high-quality development indexes of the economic, social, and ecological environments systems, respectively.

2.4.2. Types of Coupling Coordination Degree Models

The coupling coordination degree model is widely used in the study of the interactions and coordinated development between systems, reflecting various states of coordination between the systems [41]. The formula is as follows:
D = C × T
T = a U 1 + b U 2 + c U 3
where U 1 , U 2 , and U 3 represent the high-quality development indexes of the economic, social, and ecological environment systems, respectively; D represents the coupling coordinated degree of the three systems; T represents the coupling degree of three systems; and a, b, and c are undetermined coefficients, defined as the contribution of each system to national development. Referring to Fan et al. (2019) [42] and Lv et al. (2019) [43], we consider all three coefficients to be equally important, and they are assumed to be 0.3333.
T 1 = a U 1 + b U 2
T 2 = a U 1 + c U 3
T 3 = b U 2 + c U 3
Table 3 shows five levels of coupling coordination degree for high-quality development [44,45].

2.5. Data Sources

The data used in this study mainly come from the Guangdong Statistical Yearbook, the China City Statistical Yearbook, and the Statistical Yearbook of various municipalities for 2010–2019. The ecological index is derived from the Department of Ecology and Environment of Guangdong Province. Given the different criteria and missing values, this study collects data from Guangdong’s science and technology statistics data, environment bulletin, and other data platforms, such as the Guangzhou Municipal Government Data Platform. The interpolation method is used to fill in any missing data. Figure 2 illustrates the flowchart of methods in this study.

3. Results

3.1. Measurement of High-Quality Development of Economic, Social, and Ecologic Environment Systems

As illustrated in Table 4, the economic system’s high-quality development score averaged between 0.32 and 0.35. Nevertheless, there was considerable heterogeneity in the high-quality development level of the economic system between cities. Shenzhen and Zhuhai had the highest mean of 0.61, whereas Jieyang, Maoming, and Yangjiang had the lowest mean. Regionally, the Pearl River Delta was a mid-high-level region with a maximum value of 0.48. Eastern Guangdong was a middle-level region with a mean of 0.25.
Regarding the social system, Table 5 shows that Guangdong’s high-quality development scores averaged between 0.13 and 0.16, indicating a relatively slow rise in high-quality development during 2010–2019. The uneven distribution of social resources centered on developed cities resulted in a considerable regional income gap and a significant infrastructure disparity. However, there is a massive divergence within the province concerning the social system. Guangzhou and Shenzhen had the highest score of over 0.50, whereas Jiangmen, Shantou, Zhanjiang, and Shaoguan had the lowest scores of less than 0.10. It is supported by unbalanced regional and urban-rural development, leading to more public service resources in Guangzhou, Shenzhen, and other cities in Pearl River Delta, such as higher education, medical resources, and libraries. Table 5 also reveals a slight increase in the value of high-quality development of the social system, except for the low score of less than 0.10. The high-quality development score of the social system in the Pearl River Delta averaged 0.26 during 2010–2019, implying a higher-quality development of the social system than in other regions.
As can be seen from Table 6, the high-quality development score of the ecological environment system averaged between 0.68 and 0.75, showing a steady rise during 2010–2019. Shaoguan, Qingyuan, and Heyuan ranked the highest, with scores of more than 0.80, whereas Guangzhou, Foshan, Dongguan, Zhongshan, Shantou, and Zhanjiang ranked the lowest, with scores of less than 0.67. These results suggest that hilly cities have a higher-quality development of the ecological environment compared with coastal cities. In addition, Northern Guangdong had the highest score for the ecological environment index, reaching 0.79. In contrast, the scores of Pearl River Delta, Eastern, and Western Guangdong ranged from 0.69 to 0.72. These data demonstrate that Northern Guangdong is in a better ecological environment development situation than other regions, with more wildlife habitats and green agricultural products.

3.2. Measurement of High-Quality Development in Guangdong Province

Table 7 shows the comprehensive development index of 21 cities in Guangdong during 2010–2019. Guangdong’s high-quality development experienced a slow increase, with the mean ranging from 0.31 to 0.40. The comprehensive development index was lower than 0.35 during 2010–2015 owing to the influx of the cheap labor force, which led to increased environmental awareness, severe air pollution, and appropriated land resources. Thus, the local ecosystem was confronted by a series of environmental issues, exerting an indirect and adverse impact on the high-quality development of Guangdong province. However, the comprehensive development index has increased since 2015, which is attributed to enhanced scientific and technological innovation ability, enterprise transformation, and environmental regulation. All these actions led to economic restructuring, increased environmental awareness, and improved new infrastructure. Nonetheless, Shenzhen, Guangzhou, Zhuhai, and Dongguan ranked in the top four cities in terms of the comprehensive development index, with scores higher than 0.56. In contrast, Chaozhou, Jieyang, Zhanjiang, Maoming, and Yunfu ranked relatively low, with scores lower than 0.19.
During 2010–2019, the high-quality development of nine cities in the Pearl River Delta was more convergent. The first-echelon cities comprised Shenzhen, Guangzhou, Zhuhai, and Dongguan; the second-echelon cities comprised Foshan and Huizhou in 2010 and then also Jiangmen in 2018; and the third-echelon cities comprised Zhaoqing and Zhongshan. It should be noted that there needs to be more high-quality development in cities. In 2010, the high-quality development scores of Guangzhou, Zhuhai, and Dongguan were 0.61, 0.58, and 0.52, rising slowly to 0.71, 0.65, and 0.57 in 2019, respectively. Shenzhen showed a downward trend from 0.85 to 0.78 during 2010–2019 and was confronted with growing environmental stress due to economic slowdown, industrial structure upgrading, and labor inflow. The high-quality development of Foshan and Huizhou exhibited steady growth from 2010–2019, reaching 0.46 and 0.49 in 2019, respectively. Jiangmen experienced rapid growth in high-quality development from 0.31 in 2010 to 0.43 in 2019. It is worth mentioning that the high-quality development score of Zhongshan was more than 0.40 in most years but experienced a lower-volatility growth because the city was under tremendous pressure from industrial structure upgrading, social development, and environmental protection. Zhaoqing had a better ecological environment, but its economic and social development showed slow growth scaling from 0.27 to 0.37.
The spatial patterns of high-quality development in 2010, 2015, and 2019 are depicted in Figure 3. There was a vast difference in high-quality development among the cities over five different periods. It is generally agreed that regional coordination development is under tremendous pressure. Shenzhen, Guangzhou, Zhuhai, and Dongguan were high-level cities, implying that estuary cities succeeded in economic transition, technological innovation, and industrial agglomeration, leading to higher-quality development of the economy. More importantly, better infrastructure, high-quality workers, social stability, and higher environmental standards contribute to social harmony and environmental restoration. Foshan and Huizhou were high-level cities in 2010, as was Jiangmen in 2019. The mid-level cities were Zhongshan, Zhaoqing, Qingyuan, Shaoguan, Heyuan, and Meizhou in 2019, whereas the others were mid-low-level cities. Zhanjiang was a low-level city due to a higher proportion of the population being in Northern Guangdong, more significant pressure from economic transition, and poorer public facilities.
Guangzhou, Shenzhen, Zhuhai, and Dongguan were the core cities of high-quality development in Guangdong province. Guangdong’s high-quality development index decreased from the Pearl River Delta estuary cities to its edge. The high-quality development of Guangdong shows a spatial distribution pattern of high values in the Pearl River Delta and low values in other regions. Northern, Eastern, and Western Guangdong should adjust their development strategies to promote high-quality regional development, including the continuation of the industry transfer from the Pearl River Delta and rural revitalization. As the core region of Guangdong, the Pearl River Delta is divided into three metropolitan areas. Shenzhen, Dongguan, and Huizhou are eastern megalopolis; Guangzhou, Foshan, and Zhaoqing are central megalopolis; and Zhuhai, Zhongshan and Jiangmen are western megalopolis. High-quality economic development depends on technology innovation and factor productivity. Higher-quality labor force, infrastructure, and public services (i.e., education and health care) contribute to social harmony and stability. In addition, environmental protection and restoration receive more attention while promoting economic and social development.

3.3. Coupling Degree Analysis of High-Quality Development of Three Dimensions

Table 8 shows that the coupling degree of three dimensions demonstrated a slow growth, ranging from 0.55 to 1.00. In 2010, Guangzhou, Shenzhen, Foshan, and Dongguan were the top four in terms of the coupling degrees of the three dimensions. These cities were in a period of coordinated coupling, with a value of over 0.90. On the other hand, Zhuhai, Zhongshan, Huizhou, Shantou, Jiangmen, and Zhaoqing were in a period of benign coupling. Additionally, Shaoguan, Heyuan, Meizhou, Shanwei, Yangjiang, Zhanjiang, Maoming, Jieyang, Yunfu, Chaozhou, and Qingyuan were in a period of low coupling, with a value of less than 0.70. In 2019, Zhuhai became the city with the higher coupling degree among the three dimensions, whereas the cities with low coupling degrees were Heyuan, Meizhou, Shanwei, Jieyang, and Yunfu. More importantly, there were 11 cities with benign coupling, implying a mutual promotion among the economic, social, and ecological environment systems.
Figure 4 provides an overview of the spatial distribution of the three dimensions’ coupling degree in 21 cities in 2010, 2015, and 2019. In 2010, Guangzhou, Shenzhen, Foshan, and Dongguan were inner-circle cities of coupling degree; Zhongshan, Zhuhai, Jiangmen, Huizhou, and Zhaoqing were middle-circle cities. In Eastern Guangdong, Shantou was a middle-circle city, whereas others were outer-circle cities. In 2015, Zhuhai was an inner-circle city, and peripheral cities of the Pearl River Delta mainly stayed in the middle circle. Zhanjiang and Shaoguan were central cities of Western and Northern Guangdong, respectively. In 2019, the estuary cities of the Pearl River Delta still remained in the inner circle. However, more cities in the period of benign coupling expanded the scope of the middle circle and narrowed the range of the outer circle. Spatially, the coupling degree took Guangzhou, Shenzhen, Foshan, Dongguan, and Zhuhai as the core, other cities in Pearl River Delta, Shantou, Zhanjiang, and Shaoguan as the sub-core, and still other cities as the edge.

3.4. Coupling Coordination Analysis of High-Quality Development of Three Dimensions

Table 9 presents the classification of the coupling coordination degree of the three studied dimensions in 21 cities in Guangdong based on Formulas (13) and (14), which ranged from 0.43 to 0.81 during 2010–2019. The coupling coordination degree of most cities gradually increased, with means of 0.46 and 0.80, which represented the basic coordination and moderate coordination stages, whereas Shenzhen first decreased and then increased. Guangzhou, Shenzhen, Foshan, Dongguan, Zhuhai, and Zhongshan were in moderate coordination in 2010, and Huizhou and Jiangmen joined them in 2019. Guangzhou, Shenzhen, and Zhuhai were the pillar cities in coupling coordination of high-quality regional development. Nonetheless, the number of cities in basic coordination showed a downward trend, declining from 15 to 13 during 2010–2019. Additionally, the most remarkable result to emerge from the data is that the coupling coordination degree of each city grew slowly, implying higher-quality development during the study period.
As shown in Figure 5, the Pearl River Delta had a higher degree of coupling coordination of the three studied dimensions in 2010, 2015, and 2019. The increase in the number of cities with a higher degree of coupling coordination demonstrates that it has witnessed rapid growth. Meanwhile, the coupling coordination of 12 cities in Eastern, Western, and Northern Guangdong has remained the same for over ten years. These cities were in the basic coordination stage, but there were significant gaps in high-quality coordination between the Pearl River Delta and other regions in Guangdong. Spatially, the coupling coordination of the three dimensions took the Pearl River Delta (except Zhaoqing) as the core and others as the edge.

4. Discussion

High-quality development is conducive to increasing living standards, addressing issues of social justice, and achieving sustainable development. It involves the coordination development of economic, social, and ecological environments. Nonetheless, existing studies pay attention to the relationship between the two systems. This study established a high-quality development index system covering economic, social, and ecological systems. Then this study applied the TOPSIS method to calculate the level of high-quality development in Guangdong province and used the coupling coordination model to analyze the interactions among economic, social, and ecological systems from 2010–2019. Our results suggest that there was a slow increase in Guangdong’s high-quality development from 2010–2019. The Pearl River Delta had the highest level of high-quality development, whereas Eastern Guangdong had the lowest level. There was a significant divergence in the level of high-quality development at the city level. The coupling degree of high-quality development in Guangdong grew slowly, with more cities entering the stage of benign coupling. The coupling coordination degree of high-quality development in Guangdong remained stable, and the Pearl River Delta had a higher degree of coupling coordination degree of the three studied systems.
The results demonstrate that Guangzhou, Shenzhen, Foshan, Dongguan, and Zhuhai have higher-quality development of economic and social systems than other cities. In comparison, Northern Guangdong has higher-quality development of the ecological system. The ecological space is mainly distributed in hilly areas and mountains in Northern Guangdong, which is an important area for protecting and restoring key ecosystems in Guangdong [46]. Previous literature argued that the development of the economy is advancing in the direction of high ecological carrying capacity [47,48]. These findings are consistent with our analysis in that frequent human activities make ecosystem restoration more difficult. The highest level of high-quality development in the Pearl River Delta receives benefits from preferential policies, the rapid growth of high-tech industries, and improved infrastructure facilities [49,50]. More importantly, the divergence of high-quality development among cities in Guangdong implies an imbalance of regional development concerning the economy, society, and ecology in the Guangdong province.
Moreover, the data of coupling degree indicates that Guangdong takes Guangzhou, Shenzhen, Foshan, Dongguan, and Zhuhai as the core, and Shantou, Zhanjiang, Shaoguan, and other cities in the Pearl River Delta as the sub-core, as well as other cities in Guangdong as the edge. Temporally, the coupling coordination of each city shows an upward trend, implying that Guangdong is inclined to enhance the high-quality regional development of the three dimensions. Wang et al. supports the notion that Guangdong takes the lead in entering the high-coupling stage [51]. Our data demonstrates that economic growth and innovation-driven economy in estuary cities of the Pearl River Delta contribute to the spatial pattern described above. Population agglomeration, improving infrastructure, and strict environmental regulations result in mutual promotion and better coupling among the three dimensions in Guangdong province. Shantou, Zhanjiang, and Shaoguan take advantage of a complete industry foundation and enormous economic potential, setting a solid foundation for promoting high-quality development.
The coupling coordination analysis of high-quality development suggests that Guangdong, especially the Pearl River Delta, experienced a slight growth in high-quality development. The findings match those observed in previous studies, but they discovered the coupling coordination between the economy and eco-environment in the Pearl River Delta [52]. Guangzhou, Shenzhen, and Zhuhai play a crucial role in leading high-quality provincial development due to a reasonable economic structure and attach great significance to technology, talents, and capital [53,54]. As a result, local governments and people realize the significance of environmental protection and take a series of measures to restore the ecosystem. In the long run, these actions contribute to building an economic structure conducive to green, low-carbon, and circular development. These results are well in line with previous studies concerning the coupling coordination between two systems [47,51], whereas our study further investigates the interactions among three systems.
The sensitivity analysis performed in this section validates the robustness of the entropy method [55,56,57,58]. The variation coefficient is selected to test whether the different values of the index weight led to a substantial change in the evaluation results [59,60]. According to the results, we found that the sensitivity fluctuation of the results obtained by this method was quite small and relatively stable. Therefore, the evaluation results are objective and reliable.

5. Conclusions

As the most economically developed province in China, Guangdong province is expected to play a significant role in boosting high-quality regional development. In this study, the entropy weight TOPSIS model was used to assess the high-quality development of the 21 cities in Guangdong. The coupling coordination pattern of the three-dimensional system was analyzed using the coupling coordination degree model.
The main findings of the paper are as follows. First, the high-quality development of most cities shows slow growth. Guangzhou and Shenzhen have higher-quality development of economic and social systems than other cities, whereas Northern Guangdong has higher-quality development of the ecological environment, which can be attributed to rapid economic growth in the Pearl River Delta and less anthropogenic activities in Northern Guangdong. Second, the coupling degree of high-quality development of the three-dimensional system in Guangdong Province mainly presents three periods: low coupling, benign coupling, and coordinated coupling; and the degree of coupling coordination is in two stages: basic and moderate. Half of the cities in Guangdong province entered the stage of benign coupling during 2010–2019. Finally, except Zhaoqing, all cities in the Pearl River Delta have a high coupling coordination degree of high-quality development of the three-dimensional system. In contrast, the scores of other cities in Guangdong are low. During the study period, Guangdong transformed from a low coupling period to a coordinated coupling period, indicating Guangdong’s high-quality development entered a higher level of the regional development stage.
This study puts forward some suggestions for Guangdong’s high-quality development and coordination development. Firstly, it is necessary to differentiate economic development strategies and reinforce technological innovations at the city level for regional economic structure improvement. Our results indicate a low degree of high-quality development of economic and social systems in Northern and Eastern Guangdong. In response to the regional development pattern of “one core, one belt, and one zone”, a differentiated economic transformation strategy should be implemented to optimize industrial structures. We discovered that Northern Guangdong has a higher-quality development in terms of ecological environment compared with other regions. Therefore, cities should place emphasis on clean production technology by increasing the funds for scientific innovation, building up a diversified financing support system, and creating an environment of the rational and orderly flow of innovation elements.
Secondly, a stable and harmonious society could be maintained through a better social security network, equal access to public service, and higher-quality employment. Guangdong’s urbanization rate has experienced rapid growth with the growing economy. Thus, a basic public service system should be established to serve population mobility. In addition, compared with other regions, Northern Guangdong has a lower coupling coordination degree of high-quality development, which can be attributed to the poor access to public service and low educational level. Thus, improving infrastructures brings about high-quality employment, helping local people get rid of poverty.
Finally, distinguished environmental regulations and tools aid in the cooperative governance of the local environment. Various environmental regulation tools should be comprehensively applied, including pollution discharge fees, environmental subsidies, and emission reduction control. Enterprises are encouraged to carry out green production, reduce the production cost of green transformation, and get more ecological, social, and environmental benefits.
There are still several limitations to this study. Firstly, the evaluation system should consider more soft power indexes, such as enterprise vitality, resident satisfaction, and market mechanisms. However, it is not easy to quantify these subjective indicators. It is hoped that more subjective indicators will be incorporated into the high-quality development system. Secondly, the data of this study mainly reflects the urban area, ignoring rural development. It may not be sufficient to fully reflect the actual high-quality development of Guangdong province. Future research should attach great importance to urban and rural coordination development with more rural data, considering the high-quality development of rural areas. Lastly, the classic TOPSIS technique is insufficient to cope with subjectivity and incomplete information. If we consider more subjective indicators in the future, the TOPSIS method should be integrated with other theories, such as the fuzzy set theory.

Author Contributions

Conceptualization, S.W.; Investigation, J.H., J.L. and L.T.; Writing—original draft, J.H. and J.L.; Visualization, S.W. All authors have read and agreed to the published version of the manuscript.

Funding

This work was supported by the National Natural Science Foundation of China (Grant No. 41901194).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

All the data used are reflected in the article. If you need other relevant data, please contact the authors.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Xi, J. Secure a Decisive Victory in Building a Moderately Prosperous Society in All Respects and Strive for the Great Success of Socialism with Chinese Characteristics for a New Era. In Proceedings of the 19th National Congress of the Communist Party of China, Beijing, China, 18 October 2017. [Google Scholar]
  2. Wang, Y.; Sun, X.; Guo, X. Environmental regulation and green productivity growth: Empirical evidence on the Porter Hypothesis from OECD industrial sectors. Energy Policy 2019, 132, 611–619. [Google Scholar] [CrossRef]
  3. Luo, S.; Shi, Y.; Sun, Y.; Zhao, Z.; Zhou, G. Can FDI and ODI two-way flows improve the quality of economic growth? Empirical Evidence from China. Appl. Econ. 2021, 53, 5028–5050. [Google Scholar] [CrossRef]
  4. Ma, Y.; Zhang, Q.; Yin, H. Environmental management and labor productivity: The moderating role of quality management. J. Environ. Manag. 2019, 255, 109795. [Google Scholar] [CrossRef] [PubMed]
  5. Hua, X.; Lv, H.; Jin, X. Research on High-Quality Development Efficiency and Total Factor Productivity of Regional Economies in China. Sustainability 2021, 13, 8287. [Google Scholar] [CrossRef]
  6. Li, Y.; Zhong, R.; Wang, Z.; Yu, M.; Wu, Y.; Irfan, M.; Hao, Y. Would the inequality of environmental quality affect labor productivity and the income gap? Evidence from China. J. Environ. Plan. Manag. 2022, 1–34. [Google Scholar] [CrossRef]
  7. Beugelsdijk, S.; Klasing, M.J.; Milionis, P. Regional economic development in Europe: The role of total factor productivity. Reg. Stud. 2017, 52, 461–476. [Google Scholar] [CrossRef] [Green Version]
  8. Cui, X.; Fang, C.; Liu, H.; Liu, X. Assessing sustainability of urbanization by a coordinated development index for an Urbanization-Resources-Environment complex system: A case study of Jing-Jin-Ji region, China. Ecol. Indic. 2019, 96, 383–391. [Google Scholar] [CrossRef]
  9. He, L.; Sun, Y.; Xia, Y.; Zhong, Z. Construction of a green development performance index of industrial enterprises: Based on the empirical study of 458 listed industrial enterprises in China. Ecol. Indic. 2021, 132, 108239. [Google Scholar] [CrossRef]
  10. Liu, K.; Qiao, Y.; Shi, T.; Zhou, Q. Study on coupling coordination and spatiotemporal heterogeneity between economic development and ecological environment of cities along the Yellow River Basin. Environ. Sci. Pollut. Res. 2021, 28, 6898–6912. [Google Scholar] [CrossRef] [PubMed]
  11. Zhang, X.; Huang, R.; Yang, Y. On the Landscape Activity Measure Coupling Ecological Index and Public Vitality Index of UGI: The Case Study of Zhongshan, China. Land 2022, 11, 1879. [Google Scholar] [CrossRef]
  12. Chen, L.; Huo, C. The Measurement and Influencing Factors of High-Quality Economic Development in China. Sustainability 2022, 14, 9293. [Google Scholar] [CrossRef]
  13. Li, W.; Yi, P. Assessment of city sustainability—Coupling coordinated development among economy, society and environment. J. Clean. Prod. 2020, 256, 120453. [Google Scholar] [CrossRef]
  14. Li, J.; Lei, J.; Li, S.; Yang, Z.; Tong, Y.; Zhang, S.; Duan, Z. Spatiotemporal analysis of the relationship between urbanization and the eco-environment in the Kashgar metropolitan area, China. Ecol. Indic. 2022, 135, 108524. [Google Scholar] [CrossRef]
  15. Ariken, M.; Zhang, F.; Liu, K.; Fang, C.; Kung, H.-T. Coupling coordination analysis of urbanization and eco-environment in Yanqi Basin based on multi-source remote sensing data. Ecol. Indic. 2020, 114, 106331. [Google Scholar] [CrossRef]
  16. Liu, X.; Guo, P.; Yue, X.; Zhong, S.; Cao, X. Urban transition in China: Examining the coordination between urbanization and the eco-environment using a multi-model evaluation method. Ecol. Indic. 2021, 130, 108056. [Google Scholar] [CrossRef]
  17. Fu, S.; Zhuo, H.; Song, H.; Wang, J.; Ren, L. Examination of a coupling coordination relationship between urbanization and the eco-environment: A case study in Qingdao, China. Environ. Sci. Pollut. Res. 2020, 27, 23981–23993. [Google Scholar] [CrossRef]
  18. Shi, T.; Yang, S.; Zhang, W.; Zhou, Q. Coupling coordination degree measurement and spatiotemporal heterogeneity between economic development and ecological environment—Empirical evidence from tropical and subtropical regions of China. J. Clean. Prod. 2019, 244, 118739. [Google Scholar] [CrossRef]
  19. Zheng, X.; Zhang, Y.L. Coupling coordination and spatiotemporal dynamic evolution between urbanization and geological hazards–A case study from China. Sci. Total Environ. 2020, 728, 138825. [Google Scholar] [CrossRef]
  20. Zhao, J.; Xiao, Y.; Sun, S.; Sang, W.; Axmacher, J.C. Does China’s increasing coupling of ‘urban population’ and ‘urban area’ growth indicators reflect a growing social and economic sustainability? J. Environ. Manag. 2022, 301, 113932. [Google Scholar] [CrossRef]
  21. Tang, H.; Chen, Y.; Ao, R.; Shen, X.; Shi, G. Spatial–Temporal Characteristics and Driving Factors of the Coupling Coordination between Population Health and Economic Development in China. Sustainability 2022, 14, 10513. [Google Scholar] [CrossRef]
  22. Chu, N.; Zhang, P.; Wu, X. Spatiotemporal evolution characteristics of urbanization and its coupling coordination degree in Russia—Perspectives from the population, economy, society, and eco-environment. Environ. Sci. Pollut. Res. 2022, 29, 61334–61351. [Google Scholar] [CrossRef]
  23. Yan, B.-R.; Dong, Q.-L.; Li, Q.; Amin, F.U.; Wu, J.-N. A Study on the Coupling and Coordination between Logistics Industry and Economy in the Background of High-Quality Development. Sustainability 2021, 13, 10360. [Google Scholar] [CrossRef]
  24. Lai, Z.; Ge, D.; Xia, H.; Yue, Y.; Wang, Z. Coupling coordination between environment, economy and tourism: A case study of China. PLoS ONE 2020, 15, e0228426. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  25. Liu, Y.; Sadiq, F.; Ali, W.; Kumail, T. Does tourism development, energy consumption, trade openness and economic growth matters for ecological footprint: Testing the Environmental Kuznets Curve and pollution haven hypothesis for Pakistan. Energy 2022, 245, 123208. [Google Scholar] [CrossRef]
  26. Hu, W.; Tian, J.; Chen, L. An industrial structure adjustment model to facilitate high-quality development of an eco-industrial park. Sci. Total Environ. 2021, 766, 142502. [Google Scholar] [CrossRef]
  27. Song, M.; Tao, W.; Shen, Z. Improving high-quality development with environmental regulation and industrial structure in China. J. Clean. Prod. 2022, 366. [Google Scholar] [CrossRef]
  28. Li, T.; Li, Y.; An, D.; Han, Y.; Xu, S.; Lu, Z.; Crittenden, J. Mining of the association rules between industrialization level and air quality to inform high-quality development in China. J. Environ. Manag. 2019, 246, 564–574. [Google Scholar] [CrossRef]
  29. Liu, P.; Zhu, B.; Yang, M. Has marine technology innovation promoted the high-quality development of the marine economy?—Evidence from coastal regions in China. Ocean Coast. Manag. 2021, 209, 105695. [Google Scholar] [CrossRef]
  30. Zhou, B.; Zeng, X.; Jiang, L.; Xue, B. High-quality Economic Growth under the Influence of Technological Innovation Preference in China: A Numerical Simulation from the Government Financial Perspective. Struct. Chang. Econ. Dyn. 2020, 54, 163–172. [Google Scholar] [CrossRef]
  31. Wang, X.; Dong, F.; Pan, Y.; Liu, Y. Transport Infrastructure, High-Quality Development and Industrial Pollution: Fresh Evidence from China. Int. J. Environ. Res. Public Health 2022, 19, 9494. [Google Scholar] [CrossRef] [PubMed]
  32. Wong, H.L.; Luo, R.; Zhang, L.; Rozelle, S. Providing quality infrastructure in rural villages: The case of rural roads in China. J. Dev. Econ. 2013, 103, 262–274. [Google Scholar] [CrossRef]
  33. Fang, C.; Wang, Z.; Liu, H. Beautiful China Initiative: Human-nature harmony theory, evaluation index system and application. J. Geogr. Sci. 2020, 30, 691–704. [Google Scholar] [CrossRef]
  34. Technical Criterion for Ecosystem Status Evaluation; Ministry of Ecology and Environment of the People’s Republic of China: Beijing, China, 2015.
  35. Tutak, M.; Brodny, J. Evaluating differences in the Level of Working Conditions between the European Union Member States using TOPSIS method. Decis. Mak. Appl. Manag. Eng. 2022, 5, 1–29. [Google Scholar] [CrossRef]
  36. Liu, X.; Zhou, X.; Zhu, B.; He, K.; Wang, P. Measuring the maturity of carbon market in China: An entropy-based TOPSIS approach. J. Clean. Prod. 2019, 229, 94–103. [Google Scholar] [CrossRef]
  37. Ruehli, A. Equivalent Circuit Models for Three-Dimensional Multiconductor Systems. IEEE Trans. Microw. Theory Tech. 1974, 22, 216–221. [Google Scholar] [CrossRef]
  38. Liu, Y.; Li, R.; Song, X. Association analysis of the coupling between regional urbanization and ecological environment in China. Acta Geogr. Sin. 2005, 2, 237–247. [Google Scholar]
  39. Li, Y.; Li, Y.; Zhou, Y.; Shi, Y.; Zhu, X. Investigation of a coupling model of coordination between urbanization and the environment. J. Environ. Manag. 2012, 98, 127–133. [Google Scholar] [CrossRef] [PubMed]
  40. Wang, C.; Tang, N. Spatio-temporal characteristics and evolution of rural production-living- ecological space function coupling coordination in Chongqing Municipality. Geo. Res. 2018, 37, 1100–1114. (In Chinese) [Google Scholar]
  41. Yu, F.; Hu, W.; Rong, H. Coordinated development about tourism economy and transportation in medium and small cities: Chizhou as example. Sci. Geogr. Sin. 2015, 35, 1116–1122. [Google Scholar]
  42. Fan, Y.; Fang, C.; Zhang, Q. Coupling coordinated development between social economy and ecological environment in Chinese provincial capital cities-assessment and policy implications. J. Clean. Prod. 2019, 229, 289–298. [Google Scholar] [CrossRef]
  43. Lv, T.; Wang, L.; Zhang, X.; Xie, H.; Lu, H.; Li, H.; Liu, W.; Zhang, Y. Coupling Coordinated Development and Exploring Its Influencing Factors in Nanchang, China: From the Perspectives of Land Urbanization and Population Urbanization. Land 2019, 8, 178. [Google Scholar] [CrossRef] [Green Version]
  44. Dong, L.; Shang, J.; Ali, R.; Rehman, R.U. The Coupling Coordinated Relationship Between New-type Urbanization, Eco-Environment and its Driving Mechanism: A Case of Guanzhong, China. Front. Environ. Sci. 2021, 9, 638891. [Google Scholar] [CrossRef]
  45. Fang, X.; Shi, X.; Phillips, T.K.; Du, P.; Gao, W. The coupling coordinated development of urban environment towards sustainable urbanization: An empirical study of Shandong Peninsula, China. Ecol. Indic. 2021, 129, 107864. [Google Scholar] [CrossRef]
  46. Deng, Y.; Yang, R. Influence mechanism of production-living-ecological space changes in the urbanization process of Guangdong province, China. Land 2021, 10, 1357. [Google Scholar] [CrossRef]
  47. Wu, M.; Wu, J.; Zang, C. A comprehensive evaluation of the eco-carrying capacity and green economy in the Guangdong-Hong Kong-Macao Greater Bay Area, China. J. Clean. Prod. 2020, 281, 124945. [Google Scholar] [CrossRef]
  48. Qiao, G.; Chen, F.; Wang, N.; Zhang, D. Spatio-temporal evolution analysis of the coupling situation of economic-social-ecological system in Guangdong. Environ. Sci. Pollut. Res. 2022, 1–21. [Google Scholar] [CrossRef] [PubMed]
  49. Lang, W.; Deng, J.; Li, X. Identification of “growth” and “shrinkage” pattern and planning strategies for shrinking cities based on a spatial perspective of the Pearl River Delta Region. J. Urban Plan. Dev. 2020, 146, 05020020. [Google Scholar] [CrossRef]
  50. Li, X.; Li, Y.; Huang, G.; Lv, J.; Ma, Y. A multi-scenario input-output economy-energy-environment nexus management model for Pearl River Delta urban agglomeration. J. Clean. Prod. 2021, 317, 128402. [Google Scholar] [CrossRef]
  51. Wang, J.; Wang, S.; Li, S.; Feng, K. Coupling analysis of urbanization and energy-environment efficiency: Evidence from Guangdong province. Appl. Energy 2019, 254, 113650. [Google Scholar] [CrossRef]
  52. Sun, C.; Zhang, S.; Song, C.; Xu, J.; Fan, F. Investigation of Dynamic Coupling Coordination between Urbanization and the EcoEnvironment—A Case Study in the Pearl River Delta Area. Land 2021, 10, 190. [Google Scholar] [CrossRef]
  53. Wu, J.; Li, X.; Luo, Y.; Zhang, D. Spatiotemporal effects of urban sprawl on habitat quality in the Pearl River Delta from 1990 to 2018. Sci. Rep. 2021, 11, 1–15. [Google Scholar] [CrossRef] [PubMed]
  54. Liu, T.; Li, Y. Green development of China’s Pan-Pearl River Delta mega-urban agglomeration. Sci. Rep. 2021, 11, 1–11. [Google Scholar] [CrossRef] [PubMed]
  55. Wang, S.; Cui, Z.; Lin, J.; Xie, J.; Su, K. The coupling relationship between urbanization and ecological resilience in the Pearl River Delta. J. Geogr. Sci. 2022, 32, 44–64. [Google Scholar] [CrossRef]
  56. Xie, Z.; Wu, R.; Wang, S. How technological progress affects the carbon emission efficiency? Evidence from national panel quantile regression. J. Clean. Prod. 2021, 307, 127133. [Google Scholar] [CrossRef]
  57. Wang, S.; Gao, S.; Li, S.; Feng, K. Strategizing the relation between urbanization and air pollution: Empirical evidence from global countries. J. Clean. Prod. 2020, 243, 118615. [Google Scholar] [CrossRef]
  58. Wang, S.; Zeng, J.; Liu, X. Examining the multiple impacts of technological progress on CO2 emissions in China: A panel quantile regression approach. Renew. Sustain. Energy. Rev. 2019, 103, 140–150. [Google Scholar] [CrossRef]
  59. Wang, S.; Shi, C.; Fang, C.; Feng, K. Examining the spatial variations of determinants of energy-related CO2 emissions in China at the city level using Geographically Weighted Regression Model. App. Energy. 2019, 235, 95–105. [Google Scholar] [CrossRef]
  60. Wang, S.; Wang, J.; Fang, C.; Li, S. Estimating the impacts of urban form on CO2 emission efficiency in the Pearl River Delta, China. Cities 2019, 85, 117–129. [Google Scholar] [CrossRef]
Figure 1. Administrative divisions and population distribution in the Guangdong province of China. The dark blue area in the upper left picture represents the Guangdong province in China. The unit of the population in the upper right table is a thousand people. The population data originates from the seventh national census.
Figure 1. Administrative divisions and population distribution in the Guangdong province of China. The dark blue area in the upper left picture represents the Guangdong province in China. The unit of the population in the upper right table is a thousand people. The population data originates from the seventh national census.
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Figure 2. Flowchart of methodology.
Figure 2. Flowchart of methodology.
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Figure 3. Spatial distribution of high-quality development in Guangdong.
Figure 3. Spatial distribution of high-quality development in Guangdong.
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Figure 4. Spatial distribution of coupling degree of high-quality development of three dimensions in Guangdong.
Figure 4. Spatial distribution of coupling degree of high-quality development of three dimensions in Guangdong.
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Figure 5. Spatial distribution of coupling coordination degree of high-quality development of three dimensions in Guangdong.
Figure 5. Spatial distribution of coupling coordination degree of high-quality development of three dimensions in Guangdong.
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Table 2. The classification of coupling degree models.
Table 2. The classification of coupling degree models.
Coupling (C)CategoryCharacteristics
0.00 ≤ C ≤ 0.50low couplingThere is a game between the economy, society, and ecological environments, but the interactions with each other are weak. When C = 0, there is no interaction among the three dimensions.
0.50 < C ≤ 0.70lower couplingThere is a strong interaction between the economy, society, and ecological environments. The system with higher-quality development dominates the development, whereas other systems show a downward trend.
0.70 < C ≤ 0.90benign couplingThere is a better balance between each dimension, and the coupling of the three dimensions becomes benign.
0.90 < C ≤ 1.00coordinated couplingThere is a stronger coupling among the three dimensions. When C = 1.0, the two systems have a higher coupling coordination degree of high-quality development.
Source: based on the study of Wang & Tang (2018) [40].
Table 3. The classification of coupling coordination degree.
Table 3. The classification of coupling coordination degree.
Coupling Coordination Degree (D)StageCategoryCharacteristics
0.00 ≤ D ≤ 0.20No coordinationLow-level cityOnly one system develops better, but the others are restricted. There is no coordination.
0.20 < D ≤ 0.40Low coordinationLower-level cityOnly one system takes the leading role, and the others develop slowly. Thus, a series of issues arise.
0.40 < D ≤ 0.60Basic coordinationAverage-level cityOnly one system develops slowly and is more concerned about high-quality development.
0.60 < D ≤ 0.80Moderate coordinationHigher-level cityThe city makes excellent progress in coping with issues of high-quality development and improving the coordination of the three dimensions.
0.80 < D ≤ 1.00Excellent coordinationHigh-level cityThere is excellent coordination among the three dimensions. As a result, various human needs could be satisfied.
Source: based on the study of Dong et al. (2021) [44] and Fang et al. (2021) [45].
Table 4. High-quality development score of the economic system during 2010–2019.
Table 4. High-quality development score of the economic system during 2010–2019.
RegionCity2010201120122013201420152016201720182019Mean
Pearl River DeltaGuangzhou0.440.440.450.460.460.470.480.510.500.500.47
Shenzhen0.630.620.640.620.610.600.610.610.600.600.61
Foshan0.410.410.430.430.440.420.420.450.430.430.43
Dongguan0.510.480.490.500.510.520.520.490.510.510.51
Zhuhai0.600.610.610.610.620.600.600.620.610.610.61
Huizhou0.490.480.510.510.490.450.460.480.500.490.49
Zhaoqing0.400.370.370.370.360.360.290.290.310.290.34
Jiangmen0.380.340.370.350.350.360.340.380.420.440.37
Zhongshan0.400.410.420.420.420.410.410.460.440.420.42
Mean0.470.460.480.470.470.470.460.480.480.48-
Eastern GuangdongShantou0.270.270.260.230.250.260.260.290.290.290.27
Chaozhou0.240.220.220.210.210.170.200.200.210.190.21
Jieyang0.180.180.160.160.170.170.190.190.230.220.19
Shanwei0.320.320.300.260.240.250.230.260.270.250.27
Mean0.250.250.240.220.220.210.220.240.250.24-
Western GuangdongZhanjiang0.200.190.170.180.210.190.190.220.240.240.20
Maoming0.190.180.180.170.190.180.170.200.210.200.19
Yangjiang0.210.200.170.170.160.160.170.170.190.180.18
Mean0.200.190.170.170.190.180.180.200.210.21-
Northern GuangdongShaoguan0.350.330.290.290.280.240.260.270.320.320.30
Qingyuan0.280.280.270.260.240.250.260.280.300.330.28
Meizhou0.220.200.210.200.230.240.240.260.260.240.23
Heyuan0.230.220.200.190.200.200.210.240.230.270.22
Yunfu0.210.200.200.220.200.190.170.180.200.210.20
Mean0.260.250.230.230.230.220.230.250.260.27-
Mean0.340.330.330.330.330.320.320.340.350.34-
Source: Based on the authors’ calculation.
Table 5. High-quality development score of the social system during 2010–2019.
Table 5. High-quality development score of the social system during 2010–2019.
RegionCity2010201120122013201420152016201720182019Mean
Pearl River DeltaGuangzhou0.490.500.510.520.520.520.520.520.530.530.52
Shenzhen0.510.510.510.510.510.510.500.490.480.460.50
Foshan0.210.230.220.170.190.200.190.210.220.220.20
Dongguan0.310.340.350.330.370.390.390.360.360.370.36
Zhuhai0.230.240.240.270.310.330.300.300.300.300.28
Huizhou0.100.100.100.110.110.120.110.120.120.120.11
Zhaoqing0.080.080.080.090.090.090.080.110.130.130.10
Jiangmen0.080.080.090.080.080.100.100.110.110.100.09
Zhongshan0.150.150.150.150.160.160.150.150.150.160.15
Mean0.240.250.250.250.260.270.260.260.270.27-
Eastern GuangdongShantou0.070.070.070.070.070.080.080.090.090.090.08
Chaozhou0.060.060.070.070.060.070.070.070.070.110.07
Jieyang0.060.060.050.050.050.060.060.070.070.070.06
Shanwei0.070.050.050.040.040.060.070.070.070.060.06
Mean0.070.060.060.060.060.070.070.080.080.08-
Western GuangdongZhanjiang0.060.070.070.060.060.070.070.080.090.080.07
Maoming0.060.060.060.060.060.070.080.090.090.090.07
Yangjiang0.050.050.060.060.060.080.080.080.080.080.07
Mean0.060.060.060.060.060.070.080.080.090.08-
Northern GuangdongShaoguan0.060.060.060.060.070.080.090.090.100.080.07
Qingyuan0.050.050.050.050.060.070.070.080.080.070.06
Meizhou0.040.050.050.050.050.070.070.080.080.070.06
Heyuan0.040.040.040.040.050.060.070.080.080.070.06
Yunfu0.050.050.050.050.050.070.070.070.070.070.06
Mean0.050.050.050.050.060.070.070.080.080.07-
Mean0.130.140.140.140.140.150.150.160.160.16-
Source: based on the authors’ calculation.
Table 6. High-quality development score of the ecological environment system during 2010–2019.
Table 6. High-quality development score of the ecological environment system during 2010–2019.
RegionCity2010201120122013201420152016201720182019Mean
Pearl River DeltaGuangzhou0.630.610.620.630.620.630.640.620.620.630.62
Shenzhen0.740.730.720.730.650.660.670.690.690.680.70
Foshan0.580.560.580.590.620.630.630.610.620.620.60
Dongguan0.610.580.600.610.600.600.620.600.600.610.60
Zhuhai0.750.720.730.730.700.690.690.710.710.710.72
Huizhou0.740.750.760.780.810.810.830.810.810.820.79
Zhaoqing0.730.720.740.740.800.800.800.820.830.820.78
Jiangmen0.720.690.720.720.750.740.750.770.770.770.74
Zhongshan0.680.650.670.680.670.660.670.640.630.630.66
Mean0.690.670.680.690.690.690.700.700.700.70-
Eastern GuangdongShantou0.660.660.670.680.660.660.680.670.680.680.67
Chaozhou0.680.660.670.690.700.710.740.770.760.770.71
Jieyang0.700.680.690.720.710.710.740.740.740.740.72
Shanwei0.670.650.670.670.730.720.740.820.830.820.73
Mean0.680.660.680.690.700.700.730.750.750.75-
Western GuangdongZhanjiang0.630.630.640.640.650.640.660.670.680.670.65
Maoming0.680.660.680.700.720.720.750.780.780.780.72
Yangjiang0.760.740.760.760.770.770.780.820.830.820.78
Mean0.690.680.690.700.710.710.730.760.760.76-
Northern GuangdongShaoguan0.780.770.790.790.820.830.840.850.850.850.82
Qingyuan0.760.740.760.780.810.820.830.840.850.850.80
Meizhou0.750.730.740.770.790.800.830.840.830.840.79
Heyuan0.780.760.770.780.800.810.830.830.830.840.80
Yunfu0.670.650.670.670.730.720.740.820.830.820.73
Mean0.750.730.750.760.790.800.810.840.840.84-
Mean0.700.680.700.710.720.720.740.750.750.75-
Source: based on the authors’ calculation.
Table 7. Comprehensive development index of 21 cities in Guangdong during 2010–2019.
Table 7. Comprehensive development index of 21 cities in Guangdong during 2010–2019.
RegionCity2010201120122013201420152016201720182019Mean
Pearl River DeltaGuangzhou0.610.620.650.670.680.680.690.710.710.710.67
Shenzhen0.850.840.850.850.790.790.800.810.800.780.82
Foshan0.400.410.430.400.440.440.430.480.470.460.44
Dongguan0.520.500.530.540.570.600.600.560.570.570.56
Zhuhai0.580.580.600.620.650.660.630.660.650.650.63
Huizhou0.410.420.450.470.470.460.470.490.500.490.46
Zhaoqing0.300.270.290.300.330.340.320.350.370.350.32
Jiangmen0.310.270.320.320.330.350.340.390.420.430.35
Zhongshan0.370.370.400.410.410.400.400.430.420.390.40
Mean0.480.480.500.510.520.520.520.540.550.54-
Eastern GuangdongShantou0.190.200.200.190.190.210.220.250.260.260.22
Chaozhou0.160.130.150.170.180.170.200.240.240.240.19
Jieyang0.160.140.150.170.170.170.200.210.230.220.18
Shanwei0.270.250.260.270.250.260.260.290.290.280.27
Mean0.200.180.190.200.200.200.220.250.260.25-
Western GuangdongZhanjiang0.110.100.100.110.130.120.140.170.200.190.14
Maoming0.140.120.150.160.190.190.210.260.260.250.19
Yangjiang0.220.200.210.210.220.230.240.270.290.270.24
Mean0.160.140.150.160.180.180.200.230.250.24-
Northern GuangdongShaoguan0.320.290.300.300.320.310.330.340.380.370.32
Qingyuan0.240.230.260.270.280.300.310.340.360.370.30
Meizhou0.210.200.210.230.260.270.300.330.320.310.27
Heyuan0.230.220.220.230.250.260.290.300.300.320.26
Yunfu0.130.100.130.150.190.180.190.270.280.280.19
Mean0.230.210.220.240.260.260.280.320.330.33-
Mean0.320.310.330.340.350.350.360.390.400.39-
Source: based on the authors’ calculation.
Table 8. Classification of coupling of three dimensions in 21 cities in Guangdong.
Table 8. Classification of coupling of three dimensions in 21 cities in Guangdong.
10-Year Mean20102019
Coordinated couplingGuangzhou, Shenzhen, Foshan, Dongguan, ZhuhaiGuangzhou, Shenzhen, Foshan, DongguanGuangzhou, Shenzhen, Foshan, Dongguan, Zhuhai
Benign couplingHuizhou, Zhaoqing, Jiangmen, Zhongshan, Shantou, Zhanjiang, Shaoguan Zhuhai, Zhongshan, Huizhou, Shantou, Jiangmen, ZhaoqingZhongshan, Huizhou, Shantou, Jiangmen, Zhaoqing, Shaoguan, Yangjiang, Zhanjiang, Maoming, Chaozhou, Qingyuan
Lower couplingChaozhou, Jieyang, Shanwei, Maoming, Yangjiang, Qingyuan, Meizhou, Heyuan, YunfuShaoguan, Heyuan, Meizhou, Shanwei, Yangjiang, Zhanjiang, Maoming, Jieyang, Yunfu, Chaozhou, QingyuanHeyuan, Meizhou, Shanwei, Jieyang, Yunfu
Low coupling---
Source: based on the authors’ calculation.
Table 9. Classification of coupling coordination of three dimensions in 21 cities in Guangdong.
Table 9. Classification of coupling coordination of three dimensions in 21 cities in Guangdong.
Category10-Year Mean20102019
High coordination---
Moderate coordinationGuangzhou, Shenzhen, Foshan, Dongguan, Zhuhai, Zhongshan, HuizhouGuangzhou, Shenzhen, Foshan, Dongguan, Zhuhai, ZhongshanGuangzhou, Shenzhen, Foshan, Dongguan, Zhuhai, Zhongshan, Huizhou, Jiangmen
Basic coordinationShantou, Jiangmen, Zhaoqing, Shaoguan, Yangjiang, Zhanjiang, Maoming, Chaozhou, Qingyuan, Heyuan, Meizhou, Shanwei, Jieyang, YunfuHuizhou, Shantou, Jiangmen, Zhaoqing, Shaoguan, Yangjiang, Zhanjiang, Maoming, Chaozhou, Qingyuan, Heyuan, Meizhou, Shanwei, Jieyang, YunfuShantou, Zhaoqing, Shaoguan, Yangjiang, Zhanjiang, Maoming, Chaozhou, Qingyuan, Heyuan, Meizhou, Shanwei, Jieyang, Yunfu
Low coordination---
No coordination---
Source: based on the authors’ calculation.
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Hu, J.; Liang, J.; Tian, L.; Wang, S. Measurement and Coupling Coordination of High-Quality Development in Guangdong Province of China: A Spatiotemporal Analysis. Int. J. Environ. Res. Public Health 2023, 20, 4305. https://doi.org/10.3390/ijerph20054305

AMA Style

Hu J, Liang J, Tian L, Wang S. Measurement and Coupling Coordination of High-Quality Development in Guangdong Province of China: A Spatiotemporal Analysis. International Journal of Environmental Research and Public Health. 2023; 20(5):4305. https://doi.org/10.3390/ijerph20054305

Chicago/Turabian Style

Hu, Jincan, Junyi Liang, Litao Tian, and Shaojian Wang. 2023. "Measurement and Coupling Coordination of High-Quality Development in Guangdong Province of China: A Spatiotemporal Analysis" International Journal of Environmental Research and Public Health 20, no. 5: 4305. https://doi.org/10.3390/ijerph20054305

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