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Article

Impact of Industrial Structure Upgrading on Green Total Factor Productivity in the Yangtze River Economic Belt

1
School of Law and Business, Sanjiang University, Nanjing 210012, China
2
School of Management Science and Engineering, Nanjing University of Information Science & Technology, Nanjing 210044, China
3
School of Economics and Management, Nanjing University of Science & Technology, Nanjing 210000, China
*
Authors to whom correspondence should be addressed.
Int. J. Environ. Res. Public Health 2022, 19(6), 3718; https://doi.org/10.3390/ijerph19063718
Submission received: 22 February 2022 / Revised: 16 March 2022 / Accepted: 19 March 2022 / Published: 21 March 2022

Abstract

:
The Yangtze River economic belt is an inland river economic belt with international influence composed of 11 provinces and municipalities in the Yangtze River Basin. This paper uses the super-efficiency model to calculate the green total factor productivity of 11 provinces and municipalities in the Yangtze River economic belt (YREB). Then we establish a model to study the impact of industrial structure upgrading, industrial structure rationalization, and environmental regulation on green total factor productivity (GTFP). Empirical analysis shows that the industrial structure upgrading and environmental regulation have a significant impact on GTFP and show regional characteristics. The more developed the economy and the higher the industrial structure, the greater the impact of upgrading and environmental regulation on GTFP. Compared with other control variables, the urbanization rate impacts GTFP, followed by regional economic development.

1. Introduction

Promoting the development and construction of the Yangtze River economic belt (YREB) is an important national strategy of China. That is, it prioritizes regional green development and ecological green development at home and abroad, promoting coordinated, balanced, and innovation-driven high-quality development [1]. The YREB spans Eastern, Central, and Western China, including 11 provinces (municipalities) such as Shanghai, Jiangsu, Zhejiang, Anhui, Jiangxi, Hubei, Hunan, Chongqing, Sichuan, Yunnan, and Guizhou (as shown in Figure 1). It is an important support for China’s economy.
In 2020, the regional GDP exceeded CNY 47 trillion, accounting for 46.5% of the country. Figure 2 shows the proportion and change trend of three industries in the YREB from 2005 to 2020. In 2020, the three industries in the YREB accounted for 7.23%, 38.74%, and 54.02% of the regional GDP, respectively. The industrial structure shows a trend of continuous upgrading.
The YREB has rich natural resources, a strong industrial foundation, significant talent advantages, and strong economic growth potential. However, for a long time, the proportion of iron and steel, petrochemical, cement, and other industries in the industrial structure has been high, and there is great pressure to upgrade the industrial structure. To effectively improve the quality of economic growth, the National Development and Reform Commission, the Ministry of Science and Technology, and the Ministry of Industry and Information Technology of China jointly issued the plan for the YREB’s industrial transformation and upgrading driven by innovation in September 2016. The document proposed that “promoting industrial transformation and upgrading driven by innovation is an important task for the YREB to achieve economic quality, efficiency and green development”. With the slowdown of economic growth, as an important economic belt in China, the sustainable economic growth of the YREB in the future should improve the quality of economic growth [2]. The economic development of 11 provinces (municipalities) in the YREB is very unbalanced. Promoting the green and sustainable development of the YREB is an important issue [3].
This paper aims to study the impact of industrial structure upgrading of the YREB on green total factor productivity (GTFP). We collected the relevant data of 11 provinces (municipalities) in the YREB from 2005 to 2019 for analysis. Firstly, considering the undesirable output such as environmental pollution, we use the super-efficiency SBM model to calculate the value of GTFP in 11 provinces (municipalities). We find that GTFP presents regional characteristics in the YREB. Then, we establish a model to study the impact of the upgrading and rationalization of industrial structure on GTFP. The results show that industrial structure upgrading has a significant positive impact on GTFP, while industrial structure rationalization has no significant impact on GTFP. At the same time, environmental regulation, as a regulatory variable, also has a significant impact on GTFP. After further analysis, it is found that the impact of industrial structure upgrading and environmental regulation on GTFP in the eastern region is significantly higher than that in the western region. At the same time, we also observed that urbanization also promoted the improvement of GTFP. Finally, we review and prospect the analysis. The YREB should promote upgrading industrial structures, protect the environment, and promote urbanization to improve GTFP.
This paper makes contributions to the literature from the following aspects. Firstly, our paper provides new evidence for understanding the relationship between upgrading industrial structure and GTFP. Promoting the upgrading of industrial structure can promote energy conservation and environmental protection to improve GTFP. Secondly, this paper provides suggestions for the development of the YREB. We believe that the economic development of provinces (municipalities) in the YREB is unbalanced, and the industrial structure has different effects on GTFP in different regions. Therefore, provinces and municipalities should adjust measures to local conditions to promote industrial structure upgrading and environmental protection [4,5].

2. Review of Literature

Green total factor productivity (GTFP), which focuses on green growth, includes traditional labor, capital, and economic input and considers energy consumption and environmental pollution [6]. The upgrading of the industrial structure means that in economic growth, the proportion of output value and employment of the primary industry decreases [7]. In contrast, the proportion of output value and employment of the secondary and tertiary industries increases, and there is a trend of unbalanced growth among various industries. For a long time, scholars have believed that the flow of production factors in various industrial sectors promotes the industrial structure upgrading and improves the efficiency of production factors and economic growth.

2.1. GTFP Measurement

Many scholars calculated GFTP through data envelopment analysis (DEA). Kong [8] studied the total factor productivity of ten major industries in Singapore using the nonparametric frontier method of DEA and obtained the Malmquist productivity index at the sectoral level. Kuosmanen et al. [9] analyzed the panel data of 459 Finnish farms from 1992 to 2000 and revealed the driving factors behind productivity changes. Hu [10] used the DEA Malmquist index model to measure the green Malmquist index of 29 provinces in China from 1995 to 2008. Wang [11] selected DEA-BCC and DEA-Malmquist models to conduct empirical measurement and comparative research on temporal and spatial differentiation of green economy efficiency of 285 cities in China from 2004 to 2012. Feng [12] used the SBM-DEA method to study and found that China’s GTFP showed a decreasing trend from the eastern coastal region to the western region. Wang [13] used SBM directional distance function and the global Malmquist–Luenberger index to estimate the change and decomposition of the GTFP of the service industry in various regions of China from 2002 to 2014. Ren [14] used the DEA Malmquist index method to measure China’s provinces’ GTFP and decomposition index from 2007 to 2016 and introduced a spatial Durbin econometric model to analyze the spatial spillover effect and regional influencing factors GTFP. Chen [15] applied a three-stage data envelopment analysis method combined with the slack-based measure model to eliminate the influences of environmental factors and random errors and explore the real agricultural GTFP of 30 provinces in China from 2000 to 2017. Li [16] proposed slack based measure-Malmquist–Luenberger (SBM-ML) model to measure GTFP of the pearl river delta urban agglomeration from 2005 to 2018. Xiao [17] estimated the GTFP of 33 industrial sectors in China from 2002 to 2014 based on the nonparametric DEA-Malmquist method. DAR [18] used nonparametric data envelopment analysis (DEA) technology to analyze the technical efficiency and scale efficiency scores of Indian banks. Zhang [19] calculated one belt, one road, total factor productivity of 36 countries by using the DEA-Malmquist index method and established a dynamic panel model.

2.2. Industrial Structure and GTFP

William Petty [20] was the first to notice the evolution of industrial structure. According to Petty, he believes that “the income of industry is more than that of agriculture, and the income of commerce is more than that of industry”. This income gap between industries will promote the transfer of the labor force from low-income industries to high-income industries and promote economic growth at the same time. Combes [7] analyzed the data of manufacturing and service industries in France. He concluded that different industrial structures have different effects on economic growth. Buera and Kaboski [21] used a standard neoclassical growth model to analyze the agriculture, manufacturing, and service industries in the United States from 1870 to 2000. They believed that the professional and highly skilled labor force had made a significant contribution to economic growth. Noseleit [22] used the data of Germany from 1975 to 2002, and he considered that inter-industry redistribution is an important means to accelerate economic growth. Jebali [23] investigated the environmental productivity of Mediterranean countries from 2009 to 2014. He considered that technological progress and industrial structure upgrading are the main sources of productivity growth. Fukao [24] studied Japan’s structural transformation and found that the commerce and service industry played a driving role in Japan’s GDP growth throughout the 20th century. Li [25], Liu [26], Zhang [27], She [28], and Zhang [29] found that the upgrading of the industrial structure plays a positive role in promoting GTFP through the empirical study. Strengthening the upgrading of industrial structure and effective allocation of resources can promote the improvement of GTFP [30].
Scholars have studied the impact of industrial structure adjustment on economic development through different research methods in the existing research. Most scholars affirm that industrial structure upgrading plays a role in promoting economic growth and explore scientific methods to study the impact of industrial structure upgrading of the YREB across different stages of economic development on GTFP. It can provide suggestions for adjusting the regional industrial structure, promoting optimal allocation of resources among regions, improving regional innovation and development, and supporting green all-around development.

3. Measurement of GTFP

In this section, GTFP will be calculated first.

3.1. Measurement Method

Total factor productivity refers to the utilization efficiency of all production factors input in a certain period [6]. Taking natural resources and ecological environment factors into account, the GTFP is formed. GTFP should consider not only desirable output but also undesirable output such as environmental pollution. Therefore, GTFP is an important performance index to measure regional sustainable development. Data envelopment analysis (DEA) is a commonly used method to calculate GTFP because it can calculate the decision-making units (DMU) with more input and output. In this paper, a non-radial super-efficiency SBM model [31,32], including undesirable output, is established to measure GTFP. Assuming that each province is a decision-making unit (DMU), there are n DMUs in total. The input x, desirable output y g , and undesirable output y b of each DMU are as follows:
x R m
y g R s 1
y b R s 2
Then, there are matrixes:
X = x 1 , x 2 , , x n R m × n
Y g = y 1 g , y 2 g , , y n g R s 1 × n
Y b = y 1 b , y 2 b , , y n b R s 2 × n
SBM model formula is expressed as
ρ = m i n 1 1 m i = 1 m s i x i k 1 + 1 s 1 + s 2 r = 1 s 1 s r g y r k g + r = 1 s 2 s r b y r k b
Subject to
x k = X λ + s
y k g = Y g λ s g
y k b = Y b λ + s b
λ 0 , s 0 , s g 0 , s b 0
where m is the number of input indicators, s 1 and s 2 are the numbers of desirable output indicators and undesirable output indicators, respectively, and k is the number of time. s ,   s g ,   s b are relaxation variables of input, desirable output, and undesirable output, respectively. λ is the coefficient vector of the DMU linear combination. ρ is the efficiency value of DMU. If ρ = 1 that indicates that the DMU is efficient, and ρ < 1 indicates that the DMU is inefficient. Suppose ρ = 1 super-efficiency analysis is carried out to calculate the specific value.
P x 0 , y 0 is an efficient production possibility set.
P x 0 , y 0 = x ¯ , y ¯ | x ¯ j = 1 , 0 n λ j x j , y ¯ j = 1 , 0 n λ j y , y ¯ 0 , λ 0
The super efficiency SBM formula is as follows:
ρ * = m i n 1 m i = 1 m x ¯ i x i 0 1 s 1 + s 2 r = 1 s 1 y ¯ r g y r 0 g + r = 1 s 2 y ¯ r b y r 0 b
Subject to
x ¯ j = 1 , 0 n λ j x j ,
y ¯ g j = 1 , 0 n λ j y j g ,
y ¯ b j = 1 , 0 n λ j y j b ,
x ¯ x 0 , y ¯ g y 0 g , y ¯ b y 0 b , λ 0
The value of ρ and ρ * can be used to represent GTFP.

3.2. Selection of Measurement Variables

According to the super-efficiency SBM model, labor input, capital input, and energy consumption are selected as input indicators based on the scientificity and availability of data. Regional GDP and urban green space area are selected as desirable output indicators, and wastewater emission and industrial sulfur dioxide emission are selected as undesirable output indicators. This paper selects the relevant data from 2008 to 2019 for calculation. The variables are listed in Table 1.

3.3. Measurement Result

According to the aforementioned SBM model, the above variables are used to calculate the GTFP of provinces and municipalities in the YREB. The results are shown in Table 2.
It can be seen from Table 2 that the GTFP of provinces in the YREB is the lowest in the west and the highest in the east. Among them, the GTFP of Shanghai and Jiangsu Province is always higher than 1, indicating that the investment of these two provinces and municipalities is the most efficient. The GTFP of Anhui Province, Hubei Province, Guizhou Province, and Yunnan Province shows a downward trend yearly. From the perspective of efficiency decomposition, it is mainly due to the decline of technological progress efficiency [35].

4. Empirical Research Design

4.1. Model Construction

Based on theoretical analysis, to explore the impact of industrial structure upgrading on GTFP, an econometric model is adopted as follows:
l n G T F P i t = α 0 + β 1 l n I S U + β 2 l n I S R + β i l n C T R L i t + ε i t
where i and t indicate the province and period, α 0 indicates the section effect, β i represents the regression coefficient of each variable, and ε is a random error term.
The regulatory variable environmental regulation is introduced to build the model as follows:
l n G T F P i t = λ 0 + λ 1 l n I S U + λ 2 l n I S R + λ 3 l n E R + λ 2 l n C T R L i t + ε i t
where i and t indicate the province and period, λ 0 indicates the section effect, λ i represents the regression coefficient of each variable, and ε is a random error term.

4.2. Variable Selection

4.2.1. Explained Variable: GTFP

The GTFP of each province (municipality) is calculated according to the above method. The value of GTFP is shown in Table 2.

4.2.2. Explanatory Variables: Industrial Structure

The industrial structure is the composition of various industries in the national economy. The industrial structure can be considered from two aspects: the industrial structure upgrade and the industrial structure rationalization.
The industrial structure upgrade is the upgrading process of industries and the embodiment of the proportional relationship between industries. The upgrading index is determined according to the following formula:
I S U = V i t n × L P i t N
where V i t n is the proportion of the output value of industry i in the regional GDP in the t year of region n and L P i t N represents the standardized labor productivity of industry i in year t of region n. The calculation formula of L P i t N is as follows:
L P i t N = L P i t n L P i b L P i f L P i b
where L P i t n represents the labour productivity of industry i in year t of region n, L P i b represents the labour productivity of industry i at the beginning of industrialization, and L P i f represents the labor productivity of industry i at the completion of industrialization. Referring to Chenery [36] and Liu [37], the labor productivity at the beginning of industrialization is CNY 2570 for the primary industry, CNY 10,755 for the secondary industry, and CNY 12,509 for the tertiary industry. The labor productivity in the completion of industrialization is CNY 53,058 for the primary industry, CNY 141,036 for the secondary industry, and CNY 49,441 for the tertiary industry at the end of industrialization (all calculated at 2005 prices).
Industrial structure rationalization refers to the coupling degree of each industry’s factor input structure and output structure. It is measured by the Theil index. The formula is as follows:
I S R = i = 1 n Y i Y L N Y i L i Y L
where Y i represents the output value of the industry i, Y represents the total output value of the region, L i is the number of employees in the industry i, L is the total number of employees in the province, and n represents the number of industrial sectors. When ISR = 0, the regional industrial structure is reasonable. The larger the index, the worse the degree of industrial structure rationalization.

4.2.3. Regulatory Variable: Environmental Regulation

Environmental regulation is a kind of social regulation [38]. It is a legal policy, and the government adopts its implementation process to restrict economic activities in order to protect the environment [39]. Environmental regulation is measured by the comprehensive index of the discharge of industrial pollutants (industrial wastewater, industrial sulfur dioxide, and industrial solid waste) and the total industrial output value. The formula is as follows [40,41,42]:
E R i , t = 1 1 3 n = 1 3 E n , i t = 1 1 3 n = 1 3 e n , i t Y i t e n , t Y t
where E n , i t refers to the relative position of the n-th pollutant emission intensity in the whole county of province i in t year, e n , i t represents the emission of the nth pollutant of province i in t year, Y i t refers to the total industrial output value of province i in t year, e n , t represents the national emission of the n-th pollutant in t year, and Y t represents the total industrial output value of the country in t year.
The higher the ER value, the stricter the environmental standards implemented by the government and the stronger the environmental regulation.

4.2.4. Control Variables

The control variables selected in this study include (1) economic development level, which is measured by per capita regional GDP, (2) the degree of opening to the outside world, which is measured by the ratio of export trade volume to regional GDP, (3) local government input, which is measured by the ratio of local government financial expenditure to regional GDP, and (4) urbanization rate, which is measured by the proportion of the urban population in the total population.
The variables are listed in Table 3.

4.3. Data Sources and Descriptive Statistics

Taking the panel data of 11 provinces and municipalities in the YREB from 2005 to 2019 as the sample, the data are derived from the statistical yearbook of each province and municipality and the statistical yearbook of China.
The descriptive statistics are shown in Table 4.

5. Empirical Research Results and Analysis

5.1. Main Regression Results

Table 5 shows the main regression results of the impact of industrial structure upgrading on GTFP in 11 provinces and municipalities of the YREB.
From the specific direction and regression results, the explanatory variables, regulatory variables, and control variables show the same direction and significance. The explanatory variable industrial structure upgrading (ISU) is significantly positive at the 1% confidence level. This means that the upgrading of the industrial structure plays a significant role in promoting GTFP [43]. The industrial structure upgrade is the increase in the proportion of secondary industry and tertiary industry. The development of the tertiary industry has driven the increase of more pollution-free enterprises, promoted the reallocation of resources, and reduced the emission of pollution to improve the GTFP. Moreover, after adding the environmental regulation (ER) variable, the coefficient of ISU has increased. This shows that, with the enhancement of environmental awareness and the improvement of environmental protection regulations in various regions, enterprises in various regions have strengthened self-discipline and minimized the emission of pollutants. This indicates that the industrial structure upgrading has a significant spillover effect on GTFP [44]. The explanatory variable industrial structure rationalization (ISR) estimation result is not significant. The industrial structure rationalization measures each industry’s coupling degree of output and input and has no significant promotion or inhibition effect on the GTFP. The regulatory variable environmental regulation (ER) is significantly positive at the 1% confidence level, which shows that with the attention paid to environmental protection in various regions, enterprises pay attention to technology research and development in industry upgrading, update backward technologies and equipment, reduce pollutant emissions, facilitate the growth of economic quality, and promote GTFP. Among the control variables, economic development level (EDL), local government input (INP), and urbanization rate (UR) are significantly correlated with GTFP at the confidence level of 1%.

5.2. Subregional Test

Per the 11 provinces and municipalities of the YREB span from the west to the east of China, the economic development of each region is uneven. The YREB is divided into three regions: west, midland, and east. The results are shown in Table 6.
The results of Table 6 show that the industrial structure has different effects on GTFP in the west, middle, and east of the YREB. Still, ISU has a significant positive impact on GTFP [17], and the coefficient from west to east shows an increasing trend. While ISR does not pass the regression test in the west, it has a significance of 5% and 1% in the middle and east. It indicates that the rationality of the industrial structure in the western region is insufficient. ER also has a significant impact on GTFP, and the higher the degree of economic development, the greater the impact of ER. The urbanization rate in the control variables passed the significance check. Still, the coefficient values in different regions are different, indicating that the role of the urbanization process in GTFP is quite different in different regions.

6. Research Conclusions and Suggestions

6.1. Research Conclusions

Through the study on the GTFP of 11 provinces and municipalities in the YREB from 2005 to 2019, it is found that the GTFP value of Shanghai is the highest, while that of Yunnan is the lowest. The efficiency value of GTFP of provinces and municipalities in the YREB in the east is higher than that in the middle and west (as shown in Figure 3), which is consistent with the level of regional economic development.
The industrial structure upgrading index calculated by formulas (5) and (6) is shown in Figure 4. Shanghai, Jiangsu, and Zhejiang indexes in the east of the YREB are the highest, while those of Yunnan, Sichuan, Guizhou, and Jiangxi in the west are lower. Chongqing in the west ranks fourth after provinces and municipalities in the east, reflecting its role as an economic center and modern manufacturing base in the upper reaches of the Yangtze River.
The empirical analysis of the industrial structure upgrade on GTFP in 11 provinces and municipalities of the YREB from 2005 to 2019 found that the industrial structure upgrade plays a significant role in promoting GTFP [45]. The impact of industrial structure upgrading on GTFP is deepened under environmental regulation. From different regions, compared with underdeveloped regions, the industrial structure upgrade is more conducive to the improvement of GTFP in economically developed regions. Therefore, promoting the advanced development of industrial structures and formulating environmental protection laws and regulations in line with regional development are important ways to promote sustainable economic development and improve GTFP.

6.2. Countermeasures and Suggestions

6.2.1. Promote the Industrial Structure Upgrade in Various Regions of the YREB

The industrial structure upgrade has a significant impact on GTFP. As such, all regions should formulate appropriate industrial policies in combination with the regional resource situation and economic development stage [46]. As a whole, the YREB should pay attention to the complementarity of industrial layout and regional economy according to the carrying capacity of regional resources and environment. The industrial structure of eastern provinces and municipalities should develop to high-tech and intelligent manufacturing industry to explore the demonstration role. The central and western provinces should accelerate the upgrading and transformation of traditional industries, improve the green and intelligent level of industries, promote the development of producer services, extend the manufacturing service chain, and promote the upgrading of the industrial structure of the YREB.

6.2.2. Promote Environmental Protection

The government should formulate perfect environmental protection laws and regulations and strengthen pollution control [46]. Many petrochemical, iron and steel, and non-ferrous metal enterprises in the provinces and municipalities of the YREB have accelerated the technological upgrading and equipment transformation of these enterprises in multiple ways. This has also promoted the application of new technologies, new equipment, and new materials for energy-saving, water-saving, and cleaner production [35]. They should vigorously develop the energy conservation and environmental protection industry, improve the technology R&D and services of energy conservation and environmental protection industry, and promote the centralized development of energy conservation and environmental protection equipment manufacturing industry.

6.2.3. Push Forward the New Urbanization of the YREB

The scale and agglomeration effect of cities have an important impact on GTFP [47]. All provinces and municipalities should make and improve attractive talent introduction policies according to the economic level and development orientation, appropriately control the expansion speed of old urbanization, improve the quality of urbanization, and promote the balanced development of human capital and GTFP [48].

6.3. Limitations and Future Research

Although this paper provides sufficient evidence for the impact of industrial structure upgrading of the YREB on GTFP, it also has limitations for further research. Firstly, this study uses the data envelopment analysis method to measure the GTFP. The result is a static efficiency value, so the result is not comprehensive enough, and it will be improved in future research. Secondly, this study divides industrial structure upgrading into industrial structure upgrading and industrial structure rationalization. In further research, the calculation of industrial structure upgrading can be further expanded. Finally, this paper takes 11 provinces (municipalities) in the YREB as the research object and draws some conclusions. Among these 11 provinces (municipalities), there is a large gap among the constituent cities. Further exploration and research should be made on the adjustment of industrial structure.

Author Contributions

Conceptualization, J.S. and D.T.; methodology, J.S.; software, H.K.; validation, D.T., H.K. and J.S.; formal analysis, J.S.; investigation, H.K.; resources, J.S. and D.T.; data curation, J.S.; writing—original draft preparation, J.S.; writing—review and editing, D.T. and V.B.; visualization, D.T. and V.B.; supervision, D.T. and V.B.; project administration, J.S. and D.T.; funding acquisition, D.T. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by The Open Fund of the China Institute of Manufacturing Development, Nanjing University of Information Science and Technology, China, funding number (SK2021-0090-9).

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

All the original data are from the official websites of China Statistics Bureau (http://www.stats.gov.cn/tjsj/ndsj/, accessed on 15 February 2022); Anhui Statistics Bureau (http://tjj.ah.gov.cn/ssah/qwfbjd/tjnj/index.html, accessed on 15 February 2022); Guizhou Statistics Bureau (http://stjj.guizhou.gov.cn/, accessed on 15 February 2022); Hubei Statistics Bureau (http://tjj.hubei.gov.cn/tjsj/sjkscx/tjnj/qstjnj/, accessed on 15 February 2022); Hunan Statistics Bureau(http://tjj.hunan.gov.cn/tjsj/tjnj/, accessed on 15 February 2022); Jiangsu Statistics Bureau (http://tj.jiangsu.gov.cn/col/col83749/index.html, accessed on 15 February 2022); Jiangxi Statistics Bureau (http://tjj.jiangxi.gov.cn/col/col38595/index.html, accessed on 15 February 2022); Shanghai Statistics Bureau (http://tjj.sh.gov.cn/tjnj/index.html, accessed on 15 February 2022); Sichuan Statistics Bureau (http://tjj.sc.gov.cn/scstjj/c105855/nj.shtml, accessed on 15 February 2022); Yunnan Statistics Bureau (http://stats.yn.gov.cn/tjsj/tjnj/, accessed on 15 February 2022); Zhejiang Statistics Bureau (http://tjj.zj.gov.cn/col/col1525563/index.html, accessed on 15 February 2022); Chongqing Statistics Bureau (http://tjj.cq.gov.cn/zwgk_233/tjnj/, accessed on 15 February 2022); and China’s economic and social big data research platform (https://data.cnki.net/, accessed on 15 February 2022).

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Wu, R.; Possingham, H.P.; Yu, G.; Jin, T.; Wang, J.; Yang, F.; Liu, S.; Ma, J.; Liu, X.; Zhao, H. Strengthening China’s national biodiversity strategy to attain an ecological civilization. Conserv. Lett. 2019, 12, e12660. [Google Scholar] [CrossRef] [Green Version]
  2. Tang, D.C.; Zhang, Y.; Bethel, B.J. A Comprehensive Evaluation of Carbon Emission Reduction Capability in the Yangtze River Economic Belt. Int. J. Environ. Res. Public Health 2020, 17, 545. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  3. Ye, T.; Zheng, H.; Ge, X.; Yang, K. Pathway of Green Development of Yangtze River Economics Belt from the Perspective of Green Technological Innovation and Environmental Regulation. Int. J. Environ. Res. Public Health 2021, 18, 10471. [Google Scholar] [CrossRef] [PubMed]
  4. Kutlu, L. Greenhouse Gas Emission Efficiencies of World Countries. International journal of environmental research and public health. Int. J. Environ. Res. Public Health 2020, 17, 8771. [Google Scholar] [CrossRef] [PubMed]
  5. Kutlu, L.; Wang, R. Greenhouse Gas Emission Inefficiency Spillover Effects in European Countries. Int. J. Environ. Res. Public Health 2021, 18, 4479. [Google Scholar] [CrossRef] [PubMed]
  6. Tang, D.; Tang, J.; Xiao, Z.; Ma, T.; Bethel, B.J. Environmental regulation efficiency and total factor productivity—Effect analysis based on Chinese data from 2003 to 2013. Ecol. Indic. 2017, 73, 312–318. [Google Scholar] [CrossRef]
  7. Combes, P.-P. Economic structure and local growth. France, 1984-1993. J. Urban Econ. 2000, 47, 329–355. [Google Scholar] [CrossRef]
  8. Kong, N.Y.C.; Tongzon, J. Estimating total factor productivity growth in Singapore at sectoral level using data envelopment analysis. Appl. Econ. 2006, 38, 2299–2314. [Google Scholar] [CrossRef]
  9. Kuosmanen, T.; Sipiläinen, T. Exact decomposition of the Fisher ideal total factor productivity index. J. Prod. Anal. 2009, 31, 137–150. [Google Scholar] [CrossRef]
  10. Hu, X.Z.; Yang, L. Analysis on The Difference and Convergence of Regional Green Total Factor Productivity Growth in China. Financ. Res. 2011, 37, 123–134. [Google Scholar]
  11. Wang, X.Y.; Wei, Q.; Hu, X.H. Comprehensive Measurement and Temporal and Spatial Differentiation of Urban Green Economic Efficiency in China—Based on DEA-BCC and Malmquist Model. Ecol. Econ. 2016, 32, 40–45. [Google Scholar]
  12. Feng, J.; Zhang, S.Q. Evaluation of China’s Inter Provincial Green Total Factor Productivity Based on DEA Method—An Analysis of The Differences of Different Model Choices. J. Peking Univ. (Nat. Sci. Ed.) 2017, 53, 151–159. [Google Scholar]
  13. Wang, S.L.; Wang, X.L. Does FDI in Service Industry Improve Green Total Factor Productivity—An Empirical Study Based on China’s Inter Provincial Panel Data. Int. Trade Issues 2017, 12, 83–93. [Google Scholar]
  14. Ren, Y.J.; Wang, C.X.; Yu, C. A Study on The Spatial Spillover Effect of China’s Regional Green Total Factor Productivity. Soft Sci. 2019, 33, 40–43. [Google Scholar]
  15. Chen, Y.; Miao, J.; Zhu, Z. Measuring green total factor productivity of China’s agricultural sector: A three-stage SBM-DEA model with non-point source pollution and CO2 emissions. J. Clean. Prod. 2021, 318. [Google Scholar] [CrossRef]
  16. Li, Y.; Chen, Y. Development of an SBM-ML model for the measurement of green total factor productivity: The case of pearl river delta urban agglomeration. Renew. Sustain. Energy Rev. 2021, 145, 111131. [Google Scholar] [CrossRef]
  17. Xiao, Y.; Ma, D.; Cheng, Y.; Wang, L. Effect of Labor Cost and Industrial Structure on the Development Mode Transformation of China’s Industrial Economy. Emerg. Mark. Financ. Trade 2020, 56, 1677–1690. [Google Scholar] [CrossRef]
  18. Dar, A.H.; Mathur, S.K. The Efficiency of Indian Banks. A Non-Pparametric DEA Approach with Panel Regression Based Feedback. Prajnan 2021, 49, 407–427. [Google Scholar]
  19. Zhang, X.; Huang, Z.; Jiang, S. The impact of two-way FDI on total factor productivity in China and countries of the belt and road initiative. Econ. Res. -Ekon. Istraz. 2021, 1–21. [Google Scholar] [CrossRef]
  20. Roncaglia, A. William Petty and the Ambitions of Political Arithmetick. Eur. J. Hist. Econ. Thought 2013, 20, 532–536. [Google Scholar] [CrossRef]
  21. Buera, F.J.; Kaboski, J.P. Can Traditional Theories of Structural Change Fit the Data? J. Eur. Econ. Assoc. 2009, 7, 469–477. [Google Scholar] [CrossRef] [Green Version]
  22. Noseleit, F. Entrepreneurship, structural change, and economic growth. J. Evol. Econ. 2013, 23, 735–766. [Google Scholar] [CrossRef] [Green Version]
  23. Jebali, E.; Essid, H. Total Factor Environmental Productivity in the Mediterranean Countries. A Malmquist-Luenberger Index Approach. Int. J. Appl. Manag. Technol. 2020, 19, 62–76. [Google Scholar] [CrossRef]
  24. Fukao, K.; Paul, S. Baumol, Engel, and beyond. accounting for a century of structural transformation in Japan, 1885–1985†. Econ. Hist. Rev. 2021, 74, 164–180. [Google Scholar] [CrossRef]
  25. Li, Q.; Wei, W. Study on The Coupling Coordination Degree of Economic Growth Quality and Ecological Environment Optimization in The Yangtze River Economic Belt. Soft Sci. 2019, 33, 117–122. [Google Scholar]
  26. Liu, Y.; Tian, Y.; Luo, Y. Industrial Structure Upgrading, Energy Efficiency and Green Total Factor Productivity. Financ. Theory Pract. 2018, 39, 118–126. [Google Scholar]
  27. Zhang, S.; Wang, C.; Ren, Y. Spatial Spillover Effect of Producer Services Agglomeration on Green Total Factor Productivity. Soft Sci. 2019, 33, 11–15. [Google Scholar]
  28. She, S.; Wang, Q.; Zhang, A. Technological Innovation, Industrial Structure and Urban Green Total Factor Productivity—An Impact Channel Test Based on The National Low Carbon City Pilot. Econ. Manag. Res. 2020, 41, 44–61. [Google Scholar]
  29. Zhang, H.; Wang, Y. Changes of Economic System, Evolution of Industrial Structure and High-Quality Development of China’s Economy. Econ. Syst. Reform 2020, 2, 31–37. [Google Scholar]
  30. Zhang, R.; Wang, G.; Sun, X. Fiscal Decentralization, Industrial Structure and High Quality Development Of The Yellow River Basin. Econ. Issues 2020, 9, 1–11. [Google Scholar] [CrossRef]
  31. Tone, K.; Toloo, M.; Izadikhah, M. A modified slacks-based measure of efficiency in data envelopment analysis. Eur. J. Oper. Res. 2020, 287, 560–571. [Google Scholar] [CrossRef]
  32. Cantor, V.J.M.; Poh, K.L. Efficiency measurement for general network systems. A slacks-based measure model. J. Product. Anal. 2020, 54, 43–57. [Google Scholar] [CrossRef]
  33. Zhang, J.; Wu, G.; Zhang, J. Estimation of China’s Inter Provincial Physical Capital Stock. 1952–2000. Econ. Res. 2004, 10, 35–44. [Google Scholar] [CrossRef]
  34. Zhang, J.; Zhang, Y. Re-Estimation of China’s Capital Stock K. Econ. Res. 2003, 7, 35–43. [Google Scholar]
  35. Tao, F.; Zhang, H.; Hu, Y.; Duncan, A.A. Growth of Green Total Factor Productivity and Its Determinants of Cities in China. A Spatial Econometric Approach. Emerg. Mark. Financ. Trade 2017, 53, 2123–2140. [Google Scholar] [CrossRef]
  36. Chenery, H.B.; Syrquin, M. Patterns of Development. 1955–1975; Oxford University Press: London, UK, 1977. [Google Scholar]
  37. Liu, W.; Zhang, H. Industrial Structure in China’s Economic Growth. Soc. Sci. Chin. Univ. 2013, 1, 98–118. [Google Scholar]
  38. Zhang, H.; Zhou, F.; Yang, H.; Guo, Q. Empirical Analysis of Regulation Performance of Win-Win Between Environmental Protection and Economic Development. Econ. Res. 2009, 44, 14–26. [Google Scholar]
  39. Ma, J.; Wang, J.; Shen, X. Economic policy uncertainty and green economy efficiency. power or resistance?—Empirical evidence from Chinese major urban agglomerations. Econ. Res.-Ekon. Istraz. 2021, 1–19. [Google Scholar] [CrossRef]
  40. Li, B.; Wu, S. Effects of local and civil environmental regulation on green total factor productivity in China. A spatial Durbin econometric analysis. J. Clean. Prod. 2017, 153, 342–353. [Google Scholar] [CrossRef]
  41. Sun, Y.; Du, J.; Wang, S. Environmental regulations, enterprise productivity, and green technological progress. large-scale data analysis in China. Ann. Oper. Res. 2020, 290, 369–384. [Google Scholar] [CrossRef]
  42. Hu, W.; Xiong, Z. Do stringent environmental regulations help improve the total factor carbon productivity? Empirical evidence from China’s industrial sectors. Appl. Econ. 2021, 53, 6398–6411. [Google Scholar] [CrossRef]
  43. Tang, D.; Wang, L.; Bethel, B.J. An Evaluation of the Yangtze River Economic Belt Manufacturing Industry Level of Intelligentization and Influencing Factors. Evidence from China. Sustainability 2021, 13, 8913. [Google Scholar] [CrossRef]
  44. He, J.; Wang, L.; Tang, D. Research on Green Total Factor Productivity of Yangtze River Economic Belt Based on Environmental Regulation. Int. J. Environ. Res. Public Health 2021, 18, 12242. [Google Scholar] [CrossRef] [PubMed]
  45. Tang, D.; Bethel, B.J. Yangtze River Economic Belt environmental remediation efficiency based on an input-output optimization analysis. Environ. Sci. Pollut. Res. 2021, 1, 04. [Google Scholar] [CrossRef]
  46. Lin, B.; Zhu, J. Fiscal spending and green economic growth. Evidence from China. Energy Econ. 2019, 83, 264–271. [Google Scholar] [CrossRef]
  47. Qiu, S.; Wang, Z.; Liu, S. The policy outcomes of low-carbon city construction on urban green development: Evidence from a quasi-natural experiment conducted in China. Sustain. Cities Soc. 2021, 66, 102699. [Google Scholar] [CrossRef]
  48. Bai, Y.; Deng, X.; Jiang, S.; Zhang, Q.; Wang, Z. Exploring the Relationship between Urbanization and Urban Eco-efficiency. Evidence from Prefecture-level Cities in China. J. Clean. Prod. 2018, 195, 1487–1496. [Google Scholar] [CrossRef]
Figure 1. The Yangtze River economic belt research area (dark green).
Figure 1. The Yangtze River economic belt research area (dark green).
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Figure 2. Three industries’ output value (CNY billion) and structure (%) of YREB (data source: Statistical Yearbooks of provinces and municipalities).
Figure 2. Three industries’ output value (CNY billion) and structure (%) of YREB (data source: Statistical Yearbooks of provinces and municipalities).
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Figure 3. GTFP value.
Figure 3. GTFP value.
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Figure 4. Industrial structure upgrading index.
Figure 4. Industrial structure upgrading index.
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Table 1. GTFP measurement variables.
Table 1. GTFP measurement variables.
Primary IndexSecondary IndexVariable Description
InputLabor inputNumber of employed persons in the region (104 persons)
Capital inputCalculate the capital stock by using the perpetual inventory method (CNY 108) 1
Energy consumptionElectricity consumption (100 million kwh)
Desirable outputRegional GDPRegional GDP (CNY 108)
The urban green space areaUrban green space area (104 hectares)
Undesirable output indexWastewater emissionTotal industrial wastewater discharge (100 million tons)
Industrial sulfur dioxide emissionIndustrial sulfur dioxide emission (100 million tons)
1 The capital input adopts the perpetual inventory method to calculate the capital stock, and the formula is K i , t = K i , t 1 1 δ i , t + I i , t , where K i , t represents the capital stock of province i in year t, δ i , t   represents the depreciation rate of province i in year t, and I i , t refers to the total investment in fixed assets of province i in year t. The capital stock in the base period is 2004, and the calculation formula is K i , 2004 = I i , 2005 g i , 2005 2019 + δ . The fixed asset investment amount in each year is reduced to the constant price in 2005 by using the fixed asset investment price index of each province, and δ   is supposed to 9.6% (Zhang [33,34]).
Table 2. GTFP in all provinces/municipalities of the YREB.
Table 2. GTFP in all provinces/municipalities of the YREB.
YearWest
YunanGuizhouSichuanChongqingMean
20050.5460.4360.5440.5850.528
20060.450.4160.4980.4730.459
20070.4110.4110.4560.4540.433
20080.4050.4270.4690.4760.444
20090.3670.3930.4310.4620.413
20100.3470.3710.4310.4640.403
20110.330.3570.4520.5080.412
20120.3380.3670.4821.010.549
20130.350.4060.5060.5630.456
20140.3210.3730.4720.5340.425
20150.3150.3890.460.5750.435
20160.2950.3950.4510.6650.452
20170.3280.3480.4221.0080.527
20180.3160.3320.4110.4580.379
20190.3290.3440.5410.4830.424
mean0.3630.3840.4680.5810.449
YearMidland
HubeiHunanAnhuiJiangxiMean
20050.5991.0270.611.0150.813
20060.571.0320.5891.010.800
20070.5121.0330.470.5080.631
20080.5231.030.4531.0030.752
20090.5130.5360.4210.4560.482
20100.5191.0010.4240.6720.654
20110.5171.0090.4310.4510.602
20120.5371.0170.4310.4540.610
20130.5561.0280.4330.4680.621
20140.5361.0250.4060.4360.601
20150.5271.0320.3850.410.589
20160.5581.0270.3790.3860.588
20170.4840.5080.3650.350.427
20180.4630.4690.3540.3390.406
20190.4581.0380.3530.3540.551
mean0.5250.9210.4340.5540.608
YearEast
JiangsuShanghaiZhejiangMean
20051.0431.2230.7511.006
20061.0321.2370.6830.984
20071.0111.2410.6130.955
20081.0011.2410.6110.951
20091.0191.2540.5770.950
20101.0181.2620.5980.959
20111.0231.2170.5970.946
20121.0291.1850.5960.937
20131.0441.1920.7330.990
20141.0451.2060.6850.979
20151.0511.2680.6280.982
20161.0571.2110.5560.941
20171.0391.4130.4530.968
20181.0291.4170.4350.960
20191.0451.4120.4560.971
mean1.0321.2650.5980.965
Table 3. Variable description.
Table 3. Variable description.
Variable TypeNameCodeDescription
Explained variableGreen total factor productivityGTFPAccording to 3.3 measurement result
Explanatory variablesIndustry structure upgradeISUCalculated according to formula (5)
Industry structure rationalizationISRCalculated according to formula (7)
Regulatory variableEnvironmental regulationERCalculated according to formula (8)
Control variableEconomic development levelEDLEDL = Per capita GDP (CNY 104)
Degree of opennessEXPESP = Regional export trade volume/regional GDP
Local government inputINPINP = Regional government expenditure/regional GDP
Urbanization rateURUR = Regional urban population/total population
Table 4. Descriptive statistics.
Table 4. Descriptive statistics.
VariableObsMeanStd. Dev.MinMax
GTFP1650.6240.2950.2061.417
ISU1650.9780.6330.1543.142
ISR1650.2070.1780.0010.819
ER1651.3310.8590.3525.772
EDL1654.2902.9990.50515.659
EXP1650.1870.2060.0200.899
INP1650.2070.0710.0900.402
UR1650.5240.1480.2690.893
Table 5. Regression results of industrial structure affecting GTFP.
Table 5. Regression results of industrial structure affecting GTFP.
VariablesModel 1Model 2Model 3Model 4
Ln ISU0.154 ***0.203 *0.282 ***0.328 ***
(4.773)(1.935)(7.661)(3.039)
Ln ISR−0.047−0.002−0.030−0.005
(−1.135)(−0.059)(−0.806)(−0.119)
Ln ER 0.511 ***0.319 ***
(6.018)(3.275)
Ln EDL 0.687 *** 0.571 ***
(4.136) (3.434)
Ln EXP 0.117 *** 0.054
(2.732) (1.181)
Ln INP −0.528 *** −0.405 ***
(−4.390) (−3.280)
Ln UR −1.406 *** −0.998 ***
(−4.188) (−2.792)
Constant−0.667 ***−2.778 ***−0.725 ***−2.406 ***
(−5.165)(−6.376)(−6.627)(−5.376)
Observations165165165165
Number of DMU11111111
Z-statistics in parentheses: *** p < 0.01, ** p < 0.05, * p < 0.1.
Table 6. Regression results of the impact of subregional industrial structure on GTFP.
Table 6. Regression results of the impact of subregional industrial structure on GTFP.
VARIABLESWestMidlandEast
Ln ISU0.309 ***0.690 **2.327 ***
(3.083)(1.943)(3.533)
Ln ISR−0.1370.065 **0.772 ***
(−1.065)(2.503)(4.860)
Ln ER0.412 ***0.039 *0.691 ***
(3.208)(0.212)(3.219)
Ln EDL−0.723 ***0.072 *−3.273 ***
(−2.868)(1.034)(−3.885)
Ln EXP0.068−0.268 *−0.409
(1.062)(−1.878)(−1.507)
Ln INP−0.126−0.134−0.528
(−0.669)(−0.446)(−1.300)
Ln UR0.478−3.975 ***2.272 ***
(1.215)(−3.362)(2.915)
Constant0.076−3.907 ***5.405 ***
(0.137)(−3.393)(3.631)
Observations606045
Number of DMU443
Z-statistics in parentheses: *** p < 0.01, ** p < 0.05, * p < 0.1.
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Sun, J.; Tang, D.; Kong, H.; Boamah, V. Impact of Industrial Structure Upgrading on Green Total Factor Productivity in the Yangtze River Economic Belt. Int. J. Environ. Res. Public Health 2022, 19, 3718. https://doi.org/10.3390/ijerph19063718

AMA Style

Sun J, Tang D, Kong H, Boamah V. Impact of Industrial Structure Upgrading on Green Total Factor Productivity in the Yangtze River Economic Belt. International Journal of Environmental Research and Public Health. 2022; 19(6):3718. https://doi.org/10.3390/ijerph19063718

Chicago/Turabian Style

Sun, Jinhua, Decai Tang, Haojia Kong, and Valentina Boamah. 2022. "Impact of Industrial Structure Upgrading on Green Total Factor Productivity in the Yangtze River Economic Belt" International Journal of Environmental Research and Public Health 19, no. 6: 3718. https://doi.org/10.3390/ijerph19063718

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