Next Article in Journal
A New Spatial Criteria Method to Delimit Rural Settlements towards Boundaries Equity: Land Use Optimization for Decision Making in Galicia, NW Spain
Previous Article in Journal
The Identification of Stakeholders’ Living Contexts in Stakeholder Participation Data: A Semantic, Spatial and Temporal Analysis
Previous Article in Special Issue
Urban Land Monetization-Driven Land Use Orientations: An Insight from Land Lease Prices in Addis Ababa
 
 
Font Type:
Arial Georgia Verdana
Font Size:
Aa Aa Aa
Line Spacing:
Column Width:
Background:
Article

Rethinking the Contribution of Land Element to Urban Economic Growth: Evidence from 30 Provinces in China

1
School of Tourism and Urban Management, Jiangxi University of Finance and Economics, Nanchang 330013, China
2
School of Public Policy and Administration, Chongqing University, Chongqing 430044, China
3
Shandong Jianzhu University Design Group Co., Ltd., Jinan 250014, China
*
Author to whom correspondence should be addressed.
Land 2022, 11(6), 801; https://doi.org/10.3390/land11060801
Submission received: 29 March 2022 / Revised: 25 May 2022 / Accepted: 26 May 2022 / Published: 28 May 2022
(This article belongs to the Special Issue Efficient Land Use and Sustainable Urban Development)

Abstract

:
In China, disputes regarding the benefits and drawbacks of land finance have been heated, but the role of land in urban economic growth has received insufficient attention, particularly on a macro scale. This research used the Cobb–Douglas production function model to investigate the role of land in urban economic growth. Then, we conducted an empirical test using panel data from 30 provinces from 2000 to 2019, with the goal of revealing the role of land in urban growth and spatio-temporal inequalities in China. Furthermore, to find the spatial steady-state level of land contributions, σ convergence, absolute β convergence, and condition β convergence tests were applied. The results show that: (1) China’s urban economic development was influenced by the combined element of land, capital, and labor; (2) the contribution of land to China’s urban economy experienced a turning point during the “12th Five-Year Plan”; (3) the spatio-temporal convergence of the contribution of land showed convergence in the east but nonconvergence in the central and western regions; and (4) β convergence demonstrated convergence in eastern, central, and western China. Given the complex and turbulent international political and economic context, the Chinese government should think about how to foster continuous energy by supporting land-supply policies that are adapted to local needs.

1. Introduction

China has made significant progress in terms of urbanization during the last few decades. The urbanization rate climbed significantly from 17.9% in 1978 to 61.43% in 2020, while GDP increased from RMB 0.15 trillion to RMB 14.72 trillion 1. In urban economic growth, the central and municipal governments frequently serve as managers [1]. According to city management, the government wants to achieve three goals: increasing the value of urban resources, increasing the competitiveness of the urban system, and increasing capacity for long-term development [2]. The object of city management is to put the concept of urban entrepreneurialism into practice [3], while aspects like labor [4,5] and capital [6,7] become commonplace.
Local governments generate fiscal revenue through land premiums and land tax revenues, this fiscal revenue strategy is generally referred to as “land finance”. Land finance becomes an important tool to combine diverse resources dedicated to city management [8], whether driven by a huge quantity of capital for city construction or to achieve relative advantages in rivalry with other cities [9]. The urban built-up area expanded from 7538 km2 in 1980 to 60,312 km2 in 2019 [10]. Sustainable urban growth cannot continue without a certain amount of urban land investment, and undoubtedly, land finance was a key factor to support the rapid development of China in the past 30 years [11,12].
However, throughout the years, land financing has earned its share of criticism for the hazards it presents to sustainable urban expansion [13]. Popular criticisms of land finance rely on the fact that local government frequently relied on selling land to bridge the gap between revenues and expenditures; in other words, land became an important source for local government to ease financial pressure and increase revenues outside of the traditional budget [14]. The share of land transfer fees to municipal financial receipts climbed from 28.4 per cent in 2002 to 56.91 per cent in 2017 [12]. Such development sparked questions about the future of sustainable urban expansion. For example, Liu (2020) likened land supply to the engine, which not only propelled quick economic expansion but also governed the rhythm of economic development; however, the role of the engine seems to have been diminishing since 2010 [12]. The high dependence on land-generated financial risks to sustainable urbanization, and underinvestment in land hampered economic development in several areas, especially in eastern China.
In any way, it would be arbitrary to estimate the merits and downsides of land financing if we overlook regional diversity in China. A further empirical investigation is important to explain the driving mechanism of land in urban economic growth, as well as the present perilous economic position both at home and abroad to reinforce the uncertain future [15]. Therefore, understanding how to properly examine the effect of land investment on urban economic development is an essential topic that must be tackled.
The main objectives of this study are to analyze the mechanistic role of land-element inputs on urban economic growth in China based on the Cobb–Douglas production function. It uses economic, social, and construction land-panel data from 30 provinces and municipalities (districts) across the country from 2000 to 2019 as a sample, and analyzes the spatial and temporal differences. Then we conduct a convergence analysis on the contribution of the land element.
This study makes the following contributions. First, we construct a production function model that includes the land element on the basis of the concept of urban management and then demonstrate its national applicability. Second, according to the empirical test, we argue that the Chinese government should think about how to foster continuous energy by supporting land-supply policies that are adapted to local needs.

2. Literature Review

The land has long provided a solid foundation for human productivity and daily activities, and social development has always been accompanied by land-use change [16]. The limited exploitation of land resources creates significant asymmetry with the rate of social development [17], and ecologically fragile regions of the world are characterized by severe constraints on regional economic development and unsustainable economic development dynamics because of the scarcity of land resources [18,19,20]. Overall, along with the steep increase in the real demands of world population growth and urbanization, this has triggered a continuous increase in the demand for land resources for development [21]. The increase or decrease in land demand is mainly influenced by changes in population size and the progress of urbanization [22], while land supply is constrained by factors such as land-resource endowment and land-use planning [23,24]. There is a different historical context for the development of China’s economy compared to the West. China’s unique reform and opening up brought about the rapid development of manufacturing and service industries, and the country entered a more rapid urbanization phase, which can be described as a “take-off” phase of economic development. The development process that accompanied this phase was a huge migration of the rural labor force to the cities: from just 17.9% of the entire population in 1978 to 59.6% in 2018—just four decades. This rate of urbanization meant that there was a huge demand for urban housing, which was accompanied by the implementation of the “housing reform” policy, resulting in the formation of a vast, stable, and inevitable value-added real estate market in China. This played a key role in the development of the entire national economy, and it has been the main driving force in China’s economic take-off phase. Against the backdrop of explosive economic growth, China’s economic development has always maintained a high demand for land resources [25].
As a basic means of production, the importance of land to socio-economic development is self-evident, and most studies have analyzed the impact of land factors on economic growth from the perspectives of land-use efficiency and land input quantity [26,27]. Studies have found that land-use efficiency significantly contributes to economic growth, while changes in land-use efficiency significantly influence the rate of economic growth [28]. The growth of land input was studied as a fundamental element of urban economic development, and it was found that continuous land input contributed significantly to urban economic growth [29], which required the implementation of different land-use plans in different cities to respond to the needs of economic development [30]. Further studies focused on the impact of land factors on the development of secondary and tertiary industries from the perspective of land input in time and space [31]. Meanwhile, other research provided analytical arguments on the influence of land policy on macroeconomic factors and the correlation between land input cycles and economic development cycles [32]. Some scholars focused on the development of the Shanghai metropolitan area and found that there is geospatial variation in land’s contribution to Shanghai’s urbanization progress [33]. Others showed that land input can promote coordinated urban economic development in Wuhan [34], but due to the different stages of development across regions, the contribution of land factors varies, and urban economic growth shows significant spatial correlation, indicating that there is a spillover effect of land factors on economic growth [35]. It is also important to note that land resources are consumed in productive activities and their quality decreases with the frequent occurrence of such activities [36]. Excessive demand for land for socio-economic development can create unsustainable patterns of economic growth, and land changes that squeeze out other factors that drive economic development will eliminate mechanisms for diversified economic growth [37].
Does land represent a factor of production or a package of economic levers? In China, the land is seen as a production factor not only for economic growth but also as a tool for implementing economic development strategies [29]. The importance of land in urban and regional development has long been recognized by Chinese scholars and policymakers [38,39]. Studies indicate that land development has two effects on urban growth. One is the expansion of urban building land, and the other is the significant increase in land revenue from urban construction [40,41]. More effective use of urban land is a reflection of the efficiency of urban administration, and urban growth necessitates the rational use of every inch of urban land [42]. Unrestricted expansion of urban land may pose financial, ecological, and administrative risks [16,43], especially in China where local governments may rely excessively on land revenues to promote economic growth [44]. Some studies suggest that some Chinese cities are being exposed to a certain degree of financial risk that is due to the expansion of urban land areas [45]. Urban land is bought and sold more frequently [46], and frequent transactions in the primary land market are likely to undermine the original urban land plan, resulting in the blind expansion of urban land [47]. Padeiro argues that changes in land plans are not beneficial for urban management and urban development [48].
The classical Cobb–Douglas production function is commonly used in the analysis of industrial development and resource endowment [49,50], and it contains three major elements: technology, capital, and labor. Some scholars have already used the Cobb–Douglas production function to analyze the role of urban land on the urban economy and showed that the expansion of urban land has a positive impact on the urban economy [51]. Stewart [52] uses the Cobb–Douglas model to assess the influence of the land element on urban housing prices and concludes that the land element has little impact. Liu et al. (2018) employ this model to assess the contribution of the land factor input to nonagricultural GDP growth in China, focusing on the differences between the eastern, central, and western areas of the country [53]. Montalbano and Nenci’s (2022) study also shows that selecting the land component as the key variable in the Cobb–Douglas output analysis is an acceptable choice that does not undervalue the amount to which the land factor contributes to output outcomes [54].
Many studies have been conducted on the role of the land element in shaping urban economic growth, which has laid a strong foundation for proposing the rational use of land resources for the orderly promotion of sustainable urban economic growth policies. However, there is a relative lack of studies that theorize the mechanism of the land element on urban economic development at the national level, so it is necessary to re-examine this relationship.

3. Methodology and Variable Selection

3.1. Methodology

The Cobb–Douglas production function model was created by mathematician Cobb and economist Douglas. The Cobb–Douglas production function model has been widely applied in the research of economics [55], environmental sciences [56], management [57], and so on.
Following the literature, we introduce land resources as an element of production distinct from capital and labor in the economic growth model when analyzing the relationship between land and economic growth. According to the classical analysis of the Cobb–Douglas production function in economic growth, we introduce land as an element of production independent of labor and capital and construct a three-element Cobb–Douglas production function where S is the amount of land-element input. The production function including the land element is expressed as:
Y = A K α L β S γ ( A 0 , α > 0 , β > 0 , γ > 0 )
We take the natural logarithm of both sides of Equation (1):
l n Y = l n A + α l n K + β l n L + γ l n S
If the other input element is constant, the rate of change in the quantity of output caused by a 1% increase in the element is the output elasticity of the element, and if the output elasticity of the land element is denoted by ES, then we have:
E S = Δ Y Δ S × S Y Y S × S Y
We take the partial derivative of the land element S in Equation (2):
1 Y × Y S = γ × 1 S γ = Δ Y Δ S × S Y
From Equations (3) and (4), we obtain γ as the output elasticity of the land element. The simultaneous derivation of both sides of Equation (4) with respect to t yields:
1 Y × Y t = α × 1 K × K t + β × 1 L × L t + γ × 1 S × S t
In Equation (5), 1 Y × Y t is the economic growth rate; α × 1 K × K t is the contribution of capital input to economic growth; β × 1 L × L t is the contribution of labour input to economic growth; and γ × 1 S × S t is the contribution rate of construction land input to economic growth.

3.2. Variable Selection and Data Sources

Urban economic development is influenced by various factors and it is impossible to exhaust all the elements that contribute to it [58,59]. We choose data for 30 provinces (cities and districts, excluding Tibet, Hong Kong, Macao, and Taiwan because of missing data) across China from 2000 to 2019 to construct a panel-data econometric model. We then empirically analyze the effects of capital, labor, and urban construction land on economic development using the following model:
l n G D P i t = i t + α l n K i t + β l n L i t + γ l n S i t + μ i t i = 1 , , N ; t = 1 , , T
where lnGDPit represents the natural logarithm of GDP at time t in region I, which quantifies the real output of the national economy in that region.
Furthermore, lnGDPit is the only explained variable in this study, and the rest of the variables are explanatory variables.
The lnLit represents the natural logarithm of the number of employees in secondary and tertiary industries at time t in region i. It is used to quantify the labor factor input of the region in that year.
The lnSit index expresses the natural logarithm of urban construction land area in the ith region at time t. It is designed to identify the input of the land element in the region. Notably, considering that we want to identify the actual economic contribution of urban construction land to cities, the area of urban built-up areas is thus chosen as the variable to measure land-element inputs in this work. The urban built-up area is the area within a city administrative district that has been developed and constructed in a piecemeal manner, which may better represent the actual input of the land element in urban development.
Likewise, lnKit represents the natural logarithm of fixed asset inputs at moment t in the ith region to quantify the number of capital factor inputs in the region. In economics, capital refers to the amount of investment that plays a role in the process of national production creation, and capital data are generally quantified using capital stock. Since there are no aggregate capital stock statistics in China, we adopt the perpetual inventory method pioneered by Goldsmith in 1951 and integrate the research and applications of other Chinese scholars [60] to calculate the physical capital stock based on capital flow data. The expressions are as follows:
K t = 1 δ K t 1 + I t
where Kt and It are the capital stock in period t and current-year investment, respectively; Kt1 is the capital stock in period t−1; and δ is the geometric depreciation rate. The current-year investment in fixed assets is chosen as the current-year investment, and the geometric depreciation rate is estimated for the provincial physical capital stock, which we set at δ = 9.6% [60]. The capital stock in the base period is based on the international common method:
K 0 = I 0 / g + δ
where g is the average annual growth rate of real investment in the sample period.
All data in this report are from the China Urban Statistical Yearbook 2000–2019, the China Urban Construction Statistical Yearbook 2000–2019, and the provincial statistical yearbooks; the descriptive statistics are shown in Table 1.

4. Empirical Analysis and Results

4.1. Data Tests

Since the time-series data may lead to the pseudo-regression phenomenon, it is necessary to conduct smoothness tests on the data. There are many methods for testing the unit root of panel data, including the LLC test, IPS test, Fisher–ADF test, and Fisher-P test. To overcome the bias of using a single test method and to ensure the robustness of the results, we used the LLC, IPS, and Fisher–ADF tests to conduct unit root tests on the data for the following variables: lnYit, lnKit, lnLit, and lnS. The results show that the variables lnYit, lnKit, lnLit, and lnSit can be regressed for the analysis. The specific results are shown in Table 2.

4.2. Results

4.2.1. Element Output Elasticity Analysis

The output elasticity of element of production is the degree to which changes in element of production respond to changes in output. This reflects the demand for different elements of production for output and the importance of different elements in the production. Before estimating the panel model, it is necessary to determine the form of impact and the model form. The Hausman test results were used to determine the form of impact by choosing a random-effects model or a fixed-effects model. The original hypothesis of the Hausman test is that individual effects are not correlated with the explanatory variables in the random-effects model; if the original hypothesis is accepted, then the random-effects model should be chosen; otherwise, the fixed-effects model is used. The cardinality statistic value of the Hausman test is 94.877, and the corresponding p-value is 0.0001; therefore, the test results reject the original hypothesis and it is more appropriate to use a fixed-effects model. Next, it was essential to determine the correct form of the model. There are three forms of panel models: variable coefficient models, variable intercept models, and mixed models. The specific model to be selected can be judged by calculating the F-statistic. The sum of squared residuals obtained after estimating the variable coefficient model, variable intercept model, and mixed regression model are S1, S2, and S3, respectively; N is the number of cross-sections; T is the number of periods, and k is the number of explanatory variables. The models are as follows:
F 1 = S 2 S 1 / N 1 k S 1 / N T N k + 1 ~ F [ N 1 k , N T k 1
F 2 = S 3 S 1 / [ N 1 k + 1 S 1 / N T N k + 1 ~ F [ N 1 k + 1 , N T k 1
The regression estimation of each model yields S1 = 0.268, S2 = 1.985, and S3 = 8.568, where N = 30, T = 20, and k = 3. This results in the calculation of F1 = 5.576 and F2 = 23.885. The values of F1 and F2 are greater than the critical values corresponding to the 5% significance level; thus, the variable coefficient model should be selected for estimation.
Considering the regional differences in the estimation results, we divide the 30 provinces and administrative regions of China into three major regions—the eastern, central, and western regions—based on the National Bureau of Statistics. We then use Eviews to analyze the elemental output elasticity of the regions by applying the variable coefficient model.
Considering that the eastern, central, and western regions of China have varying degrees of economic development and notably diverse resources, we propose that the amount to which land-element inputs impact economic growth may vary among areas. For this reason, we further investigate the land-element contribution rates of the three main regions in China based on the study of the national rate. The results reveal that the output elasticities of all three elements are positive. Therefore, all elements can effectively promote the city’s economic growth. The capital element has the largest output elasticity (i.e., every 1% of capital input can create 0.482% of overall economic growth). Capital plays an important role in economic growth, mainly because China has always considered investment as the primary means to drive economic growth, which contributes to the large output elasticity coefficient of capital. The land has the smallest output elasticity coefficient (i.e., for every 1% increase in the land element, the entire economy will grow by 0.306%). Against the background of larger land finance, the contribution of land is minimal; we believe this is due to the lower share of land-factor inputs compared to total capital inputs in economic and social development.
We observed regional variations in the impact of land-element inputs on urban economic expansion. The results for the eastern region show the lowest land-element elasticity coefficient, and land sprawl is no longer efficient for economic growth. The highest land-element elasticity coefficient is found in the central region of China, where every 1% increase in land-element input is associated with 0.229% growth in the entire central economy. Consequently, when combining internal and external factors, the central region needs a large amount of land to achieve economic expansion. The western region has the lowest output elasticity; each 1% increase in land-element input can only create 0.155% economic growth (Table 3).

4.2.2. Contribution Rate Analysis of Production Element

The contribution rate of element of production is measured as the share of output derived from the inputs of element of production to the volume of total economic output. We estimate the output elasticity coefficients of each productive factor to further calculate the contribution of different factors to economic growth in eastern, central, and western China from 2000 to 2019.
We were surprised to find that, nationally, the contribution of capital input to economic growth reached 52.389%, the highest factor contribution, followed by the contribution of labor input, at 16.715%. The lowest contribution of land input was 6.835%, consistent with the output elasticity coefficients of the three elements.
In the eastern, central, and western regions of China, consistent with our initial hypothesis, there are substantial differences in the contributions of capital, labor, and the land element to the economy. The main underlying reasons for these differences are the different levels of economic development in the three major regions. Nevertheless, in terms of development dynamics, we believe that China’s development status fits the investment-based growth model, which means that the capital element makes the highest contribution to urban economic development.
It was surprising to find that the central region has the highest land-element contribution rate, at 9.135%. The eastern region has the lowest; each 1% increase in land input drives only 4.431% of economic growth. The western region ranks in the middle, with a land contribution rate of 6.337%, a result that also exceeds our expectations. This indicates that the impact of land on economic growth is influenced by the level of regional economic development. The eastern region has the highest level of development and a high degree of utilization of the land element, so land has ceased to be the main driver of economic development. The central region, by its own development and undertaking the industrial transfer from the east, is characterized by the rapid advancement of industrialization and urbanization, so the demand for the land element in the central region is larger. With the deepening of the western development strategy and the undertaking of related industries in central and western regions, it is not difficult to find that the land element plays an increasingly important role in the economic growth of the western region (Table 4).

4.2.3. Land-Element Contribution Rate Analysis

In China, there are historical disparities in urban land use planning and policies, which indicates that the reality of various historical times has put distinct constraints on policies. For example, during the 12th Five-Year Plan period, Shanghai banned the growth of new construction land. To facilitate a comparative analysis of the time variation of land input, we divide the planning period from the 10th Five-Year Plan to the 13th Five-Year Plan and calculate the land-element contribution rate of each province (city) at different time periods.
Over the entire planning period, we observed that cities with generally high contribution rates of land inputs to economic growth include Beijing, Shanxi, Jilin, Heilongjiang, and Henan; the contribution rates in Qinghai, Ningxia, Xinjiang, and Yunnan are generally low. For most provinces (cities) in the eastern region, the contribution rate of the land element to economic growth first rises, then falls, with the turning point appearing during the 11th Five-Year Plan. In the past two decades, the eastern region has been fighting to achieve rapid growth of the national economy, but due to the insufficient national control of the rational use of urban land, most cities rely on large and disorderly urban expansion to achieve high economic growth. Consequently, the contribution of land to urban economic growth is relatively high. However, we also notice that the expansion of urban land has offered room for economic development but, unhappily, it has also given birth to exceptional human–land conflicts. [61]. When we concentrate on the central and western areas, we discover that the land-element contribution rate shows a tendency of varying yearly, and the growth rate is not constant. Specifically, the contribution of the land element in the central region has increased quicker than in western regions. We were shocked to see that, throughout the 12th Five-Year Plan period, the contribution of the land element to urban economic development in most provinces in the central area was even larger than in the eastern region. As for the western area, the efficiency of the land element in driving urban economic growth has progressively been evident, demonstrating a slightly increasing trend from the 10th Five-Year Plan to the 13th Five-Year Plan (Table 5).
We conclude from the research findings that the land element has contributed to the growth of China’s urban economy from the beginning of the 21st century to the present. Previous research has found that Chinese cities are overly reliant on land for development and economic growth [62], that collecting property transaction fees provides the government with rapid economic benefits, and that land financing accounts for the majority of local fiscal revenue [63]. However, our findings show that prior research overestimated the role of urban land in city development to some extent. The maximum contribution value of land to urban growth is 9.651, implying that capital and labor, rather than land, drove China’s city development. The spatial–temporal inconsistencies imply that land, whether undeveloped or developed, plays an equal role in city growth. Without a doubt, the increased contribution across comparable underdeveloped provinces demonstrates a growing interest for land. Furthermore, the declining trend in developed provinces does not mean that land contributes less, but rather that it has contributed more.

4.2.4. The Convergence Analysis of the Contribution Rates of the Land Element

It is worth exploring whether the differences in the land-element contribution rates of different regions show a decreasing trend along with national economic development. Therefore, this paper conducts a convergence analysis of land-element contribution rates in different regions of China. There are usually three types of convergence analyses: σ convergence, absolute β convergence, and conditional β convergence [64]. σ convergence is used to judge whether there is a convergent effect based on the trend of land-element contribution rates in each region; if the standard deviation has a decreasing trend, this indicates the existence of σ convergence; otherwise, it is divergence. Absolute β convergence means that the land-element contribution rate in each region will converge to the same steady-state level. Over time, the less developed regions gradually catch up with the developed regions and reach the convergence state of stable development at the same rate. Conditional β convergence means that the land-element contribution rate of each region will converge to different steady-state levels. In short, both absolute β convergence and conditional β convergence meet the steady-state level, but the land-element contribution rate of each region in absolute β convergence is the same, while in conditional β convergence it differs.
(1)
σ convergence test. We know from existing research [64,65,66] that the standard deviation is used to calculate whether there is convergence in the whole country and the eastern, central, and western regions. The statistical method from Lichtenberg (1997) is used to test the σ convergence as follows:
σ ^ T 0 2 σ ^ T 2 ~ F N 2 , N 2
where the numerator is the variance of the land-element contribution at the beginning, the denominator is the variance at the end, and N is the number of cross-sections in the sample. Table 6 shows the test results.
The results in Table 6 show that there is a σ convergence trend in the land-element contribution rate in the eastern region, but none at the national level or in the central and western regions. Its standard deviation fluctuates widely, indicating that the development levels of provinces and cities (regions) are not stable. This non-stability of economic development suggests that there are cognitive differences in the sustainability of land-element utilization in different regions. The variability of geographic policies, the different degrees of utilization of land resources, and the benefits of utilization lead to fluctuations in the contribution rate of the land element across the country. Although there are differences in economic bases and in resource and environmental endowments, as well as inconsistent development patterns and rates among provinces and municipalities (regions), such differences have not stabilized over time, and differences across provinces still exist. The development synergy among the provinces (cities) in the eastern region is high, the regional linkage is strong, and the contribution of the land element is in a more balanced development state.
(2)
Absolute β convergence test. In this paper, absolute β convergence is invoked to investigate whether the land-element contribution rates of different regions converge to the same steady-state level. At present, the contribution rates of the land element in the whole country and in the eastern, central, and western regions are different. When the absolute β convergence of land-element contribution rates across regions is measured, we observe a “catching-up effect” [67] from provinces with low land-element contribution rates to provinces with high land-element contribution rates. This “catching-up effect” will eventually lead to the same steady-state equilibrium level of land-element contribution across regions. We measure the absolute β convergence of land-element contribution rates in the three major regions and set the model as follows:
1 T ln S i , t S i , 0 = α + β ln S i , 0 + ε
where Si,0 and Si,t denote the contribution of the land element in the base and end periods of province i, respectively, and T represents the time span; α is a constant, β is the absolute convergence coefficient, and ε is the random error term. If β < 0 and significant, there is absolute convergence, which further indicates that provinces with lower land-element contribution rates have a “catch-up effect” on provinces with higher land-element contribution rates. Moreover, the land-element contribution rates of all regions converge toward the same growth rate.
The results in Table 7 show that from the national perspective, the β values of provincial land-element contribution is less than zero, which indicates that there is absolute β convergence in the national provincial land-element contribution (i.e., the growth gap between provinces/municipalities is narrowing). For the three major regions, the β values of the eastern and central regions are less than zero, so there is an absolute β convergence effect in the eastern and central regions, but not in the western region. Thus, there is a “catch-up effect” of convergence of land-element contribution rates from lower provinces to higher provinces, as well as in the eastern and central regions. The “catch-up effect” among provinces is weaker in the western region because of the weak development foundation, the large differences in resource endowments, and the different development patterns across provinces. At the same time, although there are differences in the contribution rates of the land element across the country and the three regions, such differences will tend to advance together in different stages of urban economic development. Although there are still differences among provinces and cities, along with the continuous promotion of the national economic development strategy, the synergy among regions is increasing, which is bound to further reduce the inter-regional differences. This explains the absolute β convergence in the national, eastern, and central regions.
(3)
Conditional β convergence test. According to existing research, the conditional β convergence model is set as follows:
d i t = ln S i t ln S i t 1 = α + β l n S i t 1 + ε i
For ease of analysis, Equation (13) is presented as:
ln S i t = α + β + 1 ln S i t 1 + ε i
where α is the constant term; lnSit is the logarithm of the land-element contribution rate of the ith province (city) in period t, and εit is the error term. The equation indicates the existence of conditional β convergence if (β + 1) is negative and significant.
The conditional β convergence model used is the panel-data model, and the Hausman test results for the panel data have no significant p-values, indicating that the fixed-effects model is better than the random-effects model. Therefore, this paper uses the fixed-effects model for analysis when conducting the panel-data regression; the results are shown in Table 8.
The findings show that the β + 1 coefficient of all regions is negative and significant (p < 0.01). This indicates that there is a significant conditional β convergence effect on the land-element contribution rates of the country and the three regions. It also suggests that the land-element contribution rates of the east, central, and west will converge toward their steady-state levels over time. It is because of the different steady-state levels in each region that the contribution rates of the land element across regions remain continuously differentiated.

5. Conclusions and Discussion

5.1. Conclusions

In summary, based on the Cobb–Douglas production function, we analyze the contribution of land-element inputs to urban economic growth and its spatial and temporal evolution in the urban expansion of Chinese provinces (cities) during the period from the 10th to the 13th Five-Year Plan. We also conduct a convergence analysis on the contribution of the land element. The following conclusions are drawn.
The model of urban economic development including the land element has strong theoretical and practical explanatory power. China’s urban economic development is the result of the joint actions of capital, labor, and land. From the perspective of “city management” theory, the land element, together with the capital and labor elements, constitutes the basic elements of modern urban production. Moreover, the theoretical logic of urban economic development can be best explained by the Cobb–Douglas production function.
The contribution of the land element to urban economic development may be overestimated in existing studies, and the spatial and temporal differences are characterized here. In terms of the degree of contribution of the three major elements to urban economic development, the output elasticity coefficients of capital, labor, and land are 0.4823, 0.3243, and 0.3059, respectively. The respective contribution rates are 52.3891%, 16.7153%, and 6.8353%. Moreover, the contribution rate of land in the eastern region shows a trend of first increasing and then decreasing. In the central region, it increases gradually and this has occurred more rapidly in recent years. The contribution rate of land in the western region shows a slowly increasing trend, but the total contribution rate is small. Therefore, studies of land financing and urban sprawl may, to a certain extent, obscure the objective role of the land element in urban economic development.
There are different convergence effects of land-element contribution rates in China, including the eastern, central, and western regions, and the national and provincial regions have developed toward their respective steady-state levels. First, there is a σ convergence trend in the land-element contribution rate in the eastern region, but not nationally or in the central and western regions. There is an absolute β convergence effect nationally and in the eastern and central regions, but not in the west. Finally, there is a significant conditional β convergence effect in the land-element contribution rate nationally and in the three regions, and the rate will converge toward a steady-state level.

5.2. Discussion

As a result of a new series of scientific and industrial revolutions, our world has changed dramatically in recent years. Given the complicated and volatile international political and economic environment, China was committed to developing a development pattern by 2020 in which the bulk of the components are recycled locally. Undoubtedly, stringent policies or plans are required to manage land resources; yet, land use should also be tailored to local conditions. We engaged in considerable discussion about condemning the practice of obtaining large quantities of money quickly via land-transfer fees, but the next step is to reconsider how we use urban space. In the current context of slowing economic growth, rethinking the role of land deserves serious consideration, and we cannot overlook the fact that central and western areas take a long time to promote economic growth patterns. In this scenario, the government should think about how to support continuous energy for regional development, and it is time to reassess land’s function in urban development as a foundation for leveraging many aspects of city administration.
Our findings have policy implications. First, the central government should adopt varied land-supply policies based on regional development levels, with a focus on promoting economic growth by building land in the central and western regions. Second, the government must design a more scientific and visionary land-supply strategy to avoid inefficient use of urban construction land. Third, it will boost the economy of cities by sensibly distributing construction land for industrial development and public services. Land types such as industrial land, commercial land, residential land, and public administrative land have the potential to have a short-term driving effect. Fourth, to bring out the vibrancy of all parts of city management, a complete monitoring mechanism with a robust land-supply benefit evaluation system is required for this active land-supply strategy.
There are certain limitations to our research. On the one hand, China has 283 cities with significant regional and spatial variation in terms of natural resources and social development. This research seeks to reveal the urban growth mechanism on a macroscopic size; if we focus on a municipal scale, the production function model will reveal more specifics. On the other side, this article used urban construction land as a variable from a statistics yearbook; nevertheless, using remote sensing image data in the analysis will yield a more accurate result.

Author Contributions

Conceptualization, G.X. and X.Y.; methodology, G.X.; software, X.Y.; validation, G.W.; formal analysis, X.Y.; investigation, G.X.; resources, G.W.; data curation, N.G.; writing—original draft preparation, G.X. and X.Y.; writing—review and editing, G.X. and X.Y.; visualization, N.G.; supervision, G.W. and G.X.; project administration, G.W.; funding acquisition, G.X. and G.W. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the National Natural Science Foundation of China, grant number 42161047, 41701196. China Postdoctoral Science Foundation, grant number 2018M642583.

Data Availability Statement

The data of employees in secondary and tertiary industries, gross fixed assets, gross national product, and urban land area are from the China Statistical Yearbook; data link is http://www.stats.gov.cn/tjsj/ndsj/ (accessed on 1 May 2021).

Acknowledgments

The authors are particularly grateful to the editors and reviewers for their suggestions and comments on improving this study.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Zielke, P.; Waibel, M. Comparative urban governance of developing creative spaces in China. Habitat Int. 2014, 41, 99–107. [Google Scholar] [CrossRef]
  2. Hong, Y.; Zhou, C. Reform of urban management and urban government. Manag. World 2003, 8, 57–62. [Google Scholar]
  3. Zhu, J. Misunderstanding and system reconstruction of evaluation for urban master plan implementation under the logic of city management. Mod. Urban Res. 2019, 10, 49–55. [Google Scholar]
  4. Huang, N.Q.; Ning, G.J.; Rong, Z. Destination homeownership and labour force participation: Evidence from rural-to-urban migrants in China. J. Hous. Econ. 2022, 55, 101827. [Google Scholar] [CrossRef]
  5. Lu, M.; Jiang, S.Q. Labor market reform, income inequality and economic growth in China. China World Econ. 2008, 6, 63–80. [Google Scholar] [CrossRef]
  6. Shi, S.; Wong, S.K.; Zheng, C. Network capital and urban development: An inter-urban capital flow network analysis. Reg. Stud. 2022, 56, 406–419. [Google Scholar] [CrossRef]
  7. Mikesell, J.L.; Wang, J.Q.; Zhao, Z.J.; He, Y.; Information, R. Impact of Transportation Investment on Economic Growth in China. Transp. Res. Rec. 2015, 2531, 9–16. [Google Scholar] [CrossRef]
  8. Tian, L.; Ma, W. Government intervention in city development of China: A tool of land supply. Land Use Policy 2009, 26, 599–609. [Google Scholar] [CrossRef]
  9. Fan, J.S.; Zhou, L. Three-dimensional intergovernmental competition and urban sprawl: Evidence from Chinese prefectural-level cities. Land Use Policy 2019, 87, 104035. [Google Scholar] [CrossRef]
  10. Yue, W.Z.; Liu, X.; Zhou, Y.Y.; Liu, Y. Impacts of urban configuration on urban heat island: An empirical study in China mega-cities. Sci. Total Environ. 2019, 671, 1036–1046. [Google Scholar] [CrossRef]
  11. Wang, Y.; Yang, G. Intervention for economic growth: An analysis of local governments’ land concession strategies. Manag. World 2016, 05, 18–31. [Google Scholar]
  12. Liu, S.Y.; Wang, Z.; Zhang, W.; Xiong, X. The exhaustion of China’s “land-driven development” mode: An analysis based on threshold regression. Manag. World 2020, 36, 80–92. [Google Scholar]
  13. Hou, S.; Song, L.; Wang, J.; Ali, S. How land finance affects green economic growth in Chinese cities. Land 2021, 10, 819. [Google Scholar] [CrossRef]
  14. Lee, Y. The Rule of Law, Anti-corruption and Land Expropriation: Evidence from China. China-Int. J. 2020, 18, 85–101. [Google Scholar]
  15. Dias, V.M.; Soares, P.P.D.A.; Brondizio, E.S.; Cruz, S.H.R. Grassroots mobilization in Brazil’s urban Amazon: Global investments, persistent floods, and local resistance across political and legal arenas. World Dev. 2021, 146, 105572. [Google Scholar] [CrossRef]
  16. Long, H.L.; Liu, Y.Q.; Hou, X.G.; Li, T.T.; Li, Y.R. Effects of land use transitions due to rapid urbanization on ecosystem services: Implications for urban planning in the new developing area of China. Habitat Int. 2014, 44, 536–544. [Google Scholar] [CrossRef]
  17. Clement, M.T.; York, R. The asymmetric environmental consequences of population change: An exploratory county-level study of land development in the USA, 2001–2011. Popul. Environ. 2017, 39, 47–68. [Google Scholar] [CrossRef]
  18. Hu, J.J.; Huang, Y.; Du, J. The impact of urban development intensity on ecological carrying capacity: A case study of ecologically fragile areas. Int. J. Environ. Res. Public Health 2021, 18, 7094. [Google Scholar] [CrossRef]
  19. Liu, C.; Xu, Y.Q.; Lu, X.H.; Han, J. Trade-offs and driving forces of land use functions in ecologically fragile areas of northern Hebei Province: Spatiotemporal analysis. Land Use Policy 2021, 104, 105387. [Google Scholar] [CrossRef]
  20. Scandurra, G.; Romano, A.A.; Ronghi, M.; Carfora, A. On the vulnerability of small island developing states: A dynamic analysis. Ecol. Indic. 2018, 84, 382–392. [Google Scholar] [CrossRef]
  21. Dong, G.L.; Ge, Y.B.; Jia, H.W.; Sun, C.Z.; Pan, S.Y. Land Use Multi-Suitability, Land resource scarcity and diversity of human needs: A new framework for land use conflict identification. Land 2021, 10, 1003. [Google Scholar] [CrossRef]
  22. Ji, Y.Y.; Guo, X.X.; Zhong, S.H.; Wu, L.N. Land financialization, Uncoordinated development of population urbanization and land urbanization, and economic growth: Evidence from China. Land 2020, 9, 481. [Google Scholar] [CrossRef]
  23. Yang, R.H.; Yang, Q.Y. Restructuring the state: Policy transition of construction land supply in urban and rural China. Land 2021, 10, 15. [Google Scholar] [CrossRef]
  24. Zaborowski, T. It’s all about details. Why the polish land policy framework fails to manage designation of developable land. Land 2021, 10, 890. [Google Scholar] [CrossRef]
  25. Lu, X.H.; Wang, M.C.; Tang, Y.F. The spatial changes of transportation infrastructure and its threshold effects on urban land use efficiency: Evidence from China. Land 2021, 10, 346. [Google Scholar] [CrossRef]
  26. Zhang, Y.W.; Xie, H.L. Interactive relationship among urban expansion, Economic development, and population growth since the Reform and Opening up in China: An analysis based on a vector error correction model. Land 2019, 8, 153. [Google Scholar] [CrossRef] [Green Version]
  27. Dominguez, A.; Sierra, H.E.; Ballesteros, N.C. Regional spatial structure and land use evidence from Bogota and 17 Municipalities. Land 2021, 10, 908. [Google Scholar] [CrossRef]
  28. Tang, Y.K.; Wang, K.; Ji, X.M.; Xu, H.; Xiao, Y.Q. Assessment and spatial-temporal evolution analysis of urban land use efficiency under green development orientation: Case of the Yangtze River delta urban agglomerations. Land 2021, 10, 715. [Google Scholar] [CrossRef]
  29. He, C.F.; Huang, Z.J.; Wang, R. Land use change and economic growth in urban China: A structural equation analysis. Urban Stud. 2014, 51, 2880–2898. [Google Scholar] [CrossRef]
  30. Koomen, E.; Koekoek, A.; Dijk, E. Simulating land-use change in a regional planning context. Appl. Spat. Anal. Policy 2011, 4, 223–247. [Google Scholar] [CrossRef] [Green Version]
  31. Peng, Y.F.; Yang, F.L.; Zhu, L.W.; Li, R.R.; Wu, C.; Chen, D. Comparative analysis of the factors influencing land-use change for emerging industry and traditional industry: A case study of Shenzhen city, China. Land 2021, 10, 575. [Google Scholar] [CrossRef]
  32. Wang, J.; Lin, Y.F.; Glendinning, A.; Xu, Y.Q. Land-use changes and land policies evolution in China’s urbanization processes. Land Use Policy 2018, 75, 375–387. [Google Scholar] [CrossRef]
  33. Yin, J.; Yin, Z.E.; Zhong, H.D.; Xu, S.Y.; Hu, X.M.; Wang, J.; Wu, J.P. Monitoring urban expansion and land use/land cover changes of Shanghai metropolitan area during the transitional economy (1979–2009) in China. Environ. Monit. Assess. 2011, 177, 609–621. [Google Scholar] [CrossRef]
  34. Liu, Y.L.; Luo, T.; Liu, Z.Q.; Kong, X.S.; Li, J.W.; Tan, R.H. A comparative analysis of urban and rural construction land use change and driving forces: Implications for urban-rural coordination development in Wuhan, Central China. Habitat Int. 2015, 47, 113–125. [Google Scholar] [CrossRef]
  35. Li, H.; Chen, K.; Yan, L.; Zhu, Y.; Liao, L.; Chen, Y. Urban land-use transitions and the economic spatial spillovers of central cities in China’s urban agglomerations. Land 2021, 10, 644. [Google Scholar] [CrossRef]
  36. Salvati, L. Monitoring high-quality soil consumption driven by urban pressure in a growing city (Rome, Italy). Cities 2013, 31, 349–356. [Google Scholar] [CrossRef]
  37. Salverda, T.; Nkonde, C. When land becomes a burden: An analysis of an underperforming zambian land deal. Afr. Stud. Rev. 2021, 64, 653–674. [Google Scholar] [CrossRef]
  38. Gao, J.L.; Wei, Y.D.; Chen, W.; Chen, J.L. Economic transition and urban land expansion in Provincial China. Habitat Int. 2014, 44, 461–473. [Google Scholar] [CrossRef]
  39. Gao, J.L.; Chen, W.; Yuan, F. Spatial restructuring and the logic of industrial land redevelopment in urban China: I. Theoretical considerations. Land Use Policy 2017, 68, 604–613. [Google Scholar] [CrossRef]
  40. Lichtenberg, E.; Ding, C.R. Local officials as land developers: Urban spatial expansion in China. J. Urban Econ. 2009, 66, 57–64. [Google Scholar] [CrossRef] [Green Version]
  41. Wang, L.; Li, C.C.; Ying, Q.; Cheng, X.; Wang, X.Y.; Li, X.Y.; Hu, L.Y.; Liang, L.; Yu, L.; Huang, H.B.; et al. China’s urban expansion from 1990 to 2010 determined with satellite remote sensing. Chin. Sci. Bull. 2012, 57, 2802–2812. [Google Scholar] [CrossRef] [Green Version]
  42. Halleux, J.M.; Marcinczak, S.; van der Krabben, E. The adaptive efficiency of land use planning measured by the control of urban sprawl. The cases of the Netherlands, Belgium and Poland. Land Use Policy 2012, 29, 887–898. [Google Scholar] [CrossRef]
  43. Gluszak, M.; Zygrnunt, R. Development density, administrative decisions, and land values: An empirical investigation. Land Use Policy 2018, 70, 153–161. [Google Scholar] [CrossRef]
  44. Wu, Q.; Li, Y.; Yan, S. The incentives of China’s urban land finance. Land Use Policy 2015, 42, 432–442. [Google Scholar]
  45. Yan, Y.; Liu, H.; Wang, N.C.; Yao, S.J. How does Low-Density urbanization reduce the financial sustainability of Chinese cities? A debt perspective. Land 2021, 10, 981. [Google Scholar] [CrossRef]
  46. Buttimer, R.J.; Clark, S.P.; Ott, S.H. Land development: Risk, return and risk management. J. Real Estate Financ. Econ. 2008, 36, 81–102. [Google Scholar] [CrossRef]
  47. Hersperger, A.M.; Oliveira, E.; Pagliarin, S.; Palka, G.; Verburg, P.; Bolliger, J.; Gradinaru, S. Urban land-use change: The role of strategic spatial planning. Glob. Environ. Change-Hum. Policy Dimens. 2018, 51, 32–42. [Google Scholar] [CrossRef]
  48. Padeiro, M. Conformance in land-use planning: The determinants of decision, conversion and transgression. Land Use Policy 2016, 55, 285–299. [Google Scholar] [CrossRef]
  49. Ferreira, J.G.; Hawkins, A.J.S.; Bricker, S.B. Management of productivity, environmental effects and profitability of shellfish aquaculture—The Farm Aquaculture Resource Management (FARM) model. Aquaculture 2007, 264, 160–174. [Google Scholar] [CrossRef]
  50. Jones, C.I. The shape of production functions and the direction of technical change. Q. J. Econ. 2005, 120, 517–549. [Google Scholar]
  51. Sarkar, S.; Arcaute, E.; Hatna, E.; Alizadeh, T.; Searle, G.; Batty, M. Evidence for localization and urbanization economies in urban scaling. R. Soc. Open Sci. 2020, 7, 191638. [Google Scholar] [CrossRef] [PubMed] [Green Version]
  52. Stewart, K.G. How important are land values in house price growth? Evidence from Canadian cities. Can. J. Econ. /Rev. Can. D’économique 2022, 55, 249–271. [Google Scholar] [CrossRef]
  53. Liu, Y.S.; Zhang, Z.W.; Zhou, Y. Efficiency of construction land allocation in China: An econometric analysis of panel data. Land Use Policy 2018, 74, 261–272. [Google Scholar] [CrossRef]
  54. Montalbano, P.; Nenci, S. Does Global value chain participation and positioning in the agriculture and food sectors affect economic performance? A global assessment. Food Policy 2022, 108, 102235. [Google Scholar] [CrossRef]
  55. Hajkova, D.; Hurnik, J. Cobb-Douglas production function: The case of a converging economy. Financ. A Uver-Czech J. Econ. Financ. 2007, 57, 465–476. [Google Scholar]
  56. Yuan, C.Q.; Liu, S.F.; Wu, J.L. Research on energy-saving effect of technological progress based on Cobb-Douglas production function. Energy Policy 2010, 38, 2611. [Google Scholar] [CrossRef]
  57. Kannebley, S.R.; Borges, D.A.; de Prince, D. Scientific production and its collective determinants: An econometric analysis for the Brazilian research labs. Sci. Public Policy 2018, 45, 661–672. [Google Scholar] [CrossRef]
  58. Wang, W.; Zhang, X.L.; Wu, Y.Z.; Zhou, L.; Skitmore, M. Development priority zoning in China and its impact on urban growth management strategy. Cities 2017, 62, 1–9. [Google Scholar] [CrossRef] [Green Version]
  59. Pasquali, D.; Marucci, A. The effects of urban and economic development on coastal zone management. Sustainability 2021, 13, 6071. [Google Scholar] [CrossRef]
  60. Zhang, J.; Zhang, Y. Re-estimation of China’s capital stock K. Econ. Res. 2003, 07, 35–42. [Google Scholar]
  61. Shih, M. Land and people: Governing social conflicts in China’s state-led urbanisation. Int. Dev. Plan. Rev. 2019, 41, 293–310. [Google Scholar] [CrossRef]
  62. Shu, C.; Xie, H.L.; Jiang, J.F.; Chen, Q.R. Is urban land development driven by economic development or fiscal revenue stimuli in China? Land Use Policy 2018, 77, 107–115. [Google Scholar] [CrossRef]
  63. Ma, J.W. Land financing and economic growth: Evidence from Chinese counties. China Econ. Rev. 2018, 50, 218–239. [Google Scholar]
  64. Alexashin, Y.; Blenkinsopp, J. Changes in Russian managerial values: A test of the convergence hypothesis? Int. J. Hum. Resour. Manag. 2005, 16, 427–444. [Google Scholar] [CrossRef]
  65. Rivas, M.D.G.; Villarroya, I.S. Testing the convergence hypothesis for OECD countries: A reappraisal. Economics 2017, 11, 1864–6042. [Google Scholar] [CrossRef] [Green Version]
  66. Sofi, A.A.; Sasidharan, S.; Bhat, M.Y. Economic growth and club convergence: Is there a neighbour’s effect? Int. J. Financ. Econ. 2021, 05, 1076–9307. [Google Scholar] [CrossRef]
  67. Xue, J.; Zhang, A. Analysis of biased technological progress and convergence test of total element productivity index for urban land use in the Yellow River Basin. Hubei Soc. Sci. 2021, 06, 73–80. [Google Scholar]

Note

1
Data are from the 2021 China Statistical Yearbook.
Table 1. Descriptive statistics.
Table 1. Descriptive statistics.
Variable TypeVariablesVariable ExplanationAverageMax.Min.Std. Dev.
Explained variablesEconomic growth(Y)GDP (RMB 108)16,11211,06011717,758
Explanatory variablesCapital element (K)Total value of fixed assets (RMB 108)31,462220,5175038,357
Labor force element(L)Number of people employed in secondary and tertiary industries (104 people)240121414187
Land element (S)Construction land area (km2)13695896761016
Table 2. Tests for smoothness of variables.
Table 2. Tests for smoothness of variables.
VariableslnYitlnKitlnLitlnSit
LLC Inspection−11.525−12.213−11.014−9.145
(0.0001)(0.0002)(0.0001)(0.0003)
IPS Inspection−6.008−4.686−11.428−8.188
(0.0002)(0.0000)(0.0002)(0.0001)
Fisher–ADF Inspection135.661227.472223.796175.865
(0.0002)(0.0002)(0.0000)(0.0004)
Table 3. Table of element output elasticity coefficients.
Table 3. Table of element output elasticity coefficients.
VariablesNationalEastMiddleWest
K0.482 ***
(46.314)
0.608 ***
(40.779)
0.456 ***
(33.875)
0.436 ***
(22.864)
L0.324 ***
(12.148)
0.217 ***
(13.574)
0.315 ***
(15.909)
0.428 ***
(18.965)
S0.306 ***
(9.548)
0.176 ***
(5.583)
0.229 ***
(6.029)
0.155 ***
(5.179)
R20.9580.9420.9240.935
Note: *** represent the significance of the parameters at 1% confidence levels.
Table 4. Comparison of element contribution rates.
Table 4. Comparison of element contribution rates.
CategoryVariablesNationalEastMiddleWest
Contribution rate of each elementK52.38954.03961.35358.642
L16.71515.4378.15710.483
S6.8354.4319.1356.337
A24.06026.09221.35624.539
Table 5. Land element’s contribution to economic growth.
Table 5. Land element’s contribution to economic growth.
RegionFifteen11th Five-Year Plan12th Five-Year Plan13th Five-Year Plan
Beijing6.7937.9245.4353.214
Tianjin4.3445.5424.1723.582
Hebei3.9134.6713.3853.031
Shanxi4.8916.9217.5428.394
Inner Mongolia2.9434.3144.8615.342
Liaoning3.7015.7923.9833.751
Jilin4.3537.2107.8528.654
Heilongjiang4.5625.1828.2749.044
Shanghai5.8626.6344.9813.062
Jiangsu5.0216.9214.6353.965
Zhejiang4.9936.7355.4823.811
Anhui4.3617.8428.4369.045
Fujian6.0227.4655.8923.552
Jiangxi4.1615.3727.4548.946
Shandong4.4635.0635.8323.977
Henan4.8246.0337.8358.582
Hubei4.9435.9318.5919.651
Hunan4.5236.7447.6338.945
Guangdong5.4346.7234.5353.662
Guangxi2.9434.3144.8625.346
Hainan4.9915.7354.6863.812
Chongqing3.0404.0364.4925.036
Sichuan3.9414.4974.9846.341
Guizhou3.5934.8235.8316.815
Yunnan2.8924.1954.8555.932
Shaanxi4.3445.3116.3025.926
Gansu4.5925.1955.9846.272
Qinghai3.9834.9325.5325.381
Ningxia3.4824.0164.4946.315
Xinjiang2.8443.6744.5714.942
Table 6. Results of σ convergence test for the whole country and different regions.
Table 6. Results of σ convergence test for the whole country and different regions.
Test StatisticNationalEastMiddleWest
Lichtenberg values0.9357.2630.4500.126
Threshold value
(1% significance level)
2.4312.9436.1534.453
Table 7. National and regional absolute β convergence estimation results.
Table 7. National and regional absolute β convergence estimation results.
CoefficientNationalEastMiddleWest
β−0.048 **−0.043 **−0.035 **−0.068
(−5.13)(−1.06)(−8.71)(−2.21)
α0.0020.0030.0020.003
−3.970−1.320−2.680−1.760
R20.4960.5350.9150.137
N3011118
Note: The numbers in parentheses below the parameter estimates indicate t-test values. ** represents parameter estimates significant at the 5% confidence level.
Table 8. Conditional β convergence test for land-element contribution.
Table 8. Conditional β convergence test for land-element contribution.
NationalEastMiddleWest
α0.0810.1840.0530.036
(1.065)(1.263)(0.548)(0.298)
β + 1−1.278 ***−1.239 ***−1.201 ***−1.149 ***
(−13.956)(−12.067)(−18.274)(−11.063)
Adjusted R20.7020.7330.7150.674
Note: *** represents the significance of parameters at the 1% confidence levels. T-test values are in parentheses.
Publisher’s Note: MDPI stays neutral with regard to jurisdictional claims in published maps and institutional affiliations.

Share and Cite

MDPI and ACS Style

Xu, G.; Yin, X.; Wu, G.; Gao, N. Rethinking the Contribution of Land Element to Urban Economic Growth: Evidence from 30 Provinces in China. Land 2022, 11, 801. https://doi.org/10.3390/land11060801

AMA Style

Xu G, Yin X, Wu G, Gao N. Rethinking the Contribution of Land Element to Urban Economic Growth: Evidence from 30 Provinces in China. Land. 2022; 11(6):801. https://doi.org/10.3390/land11060801

Chicago/Turabian Style

Xu, Guoliang, Xiaonan Yin, Guangdong Wu, and Ning Gao. 2022. "Rethinking the Contribution of Land Element to Urban Economic Growth: Evidence from 30 Provinces in China" Land 11, no. 6: 801. https://doi.org/10.3390/land11060801

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

Article Metrics

Back to TopTop