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Article

Spatial Heterogeneity of the Recovery of Road Traffic Volume from the Impact of COVID-19: Evidence from China

School of Economics and Management, Wuhan University, Wuhan 430072, China
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Author to whom correspondence should be addressed.
Sustainability 2022, 14(21), 14297; https://doi.org/10.3390/su142114297
Submission received: 7 October 2022 / Revised: 24 October 2022 / Accepted: 31 October 2022 / Published: 1 November 2022

Abstract

:
The impact of COVID-19 on traffic volume makes it essential to study the spatial heterogeneity and impact mechanisms of the recovery of road traffic volume to promote the sustainability of related industries. As the research method, this study used a principal component analysis to evaluate the recovery of road traffic volume in China quantitatively, and further conducted an empirical study using a spatial autocorrelation index and a dynamic spatial panel model. The results show that income has a negative impact on the recovery of road traffic volume, while climate suitability has a positive impact. Economic development and COVID-19 can play moderating and mediating effects, respectively. From the aspect of spatial heterogeneity, the recovery of road traffic volume has a positive spatial spillover effect on the surrounding provinces, while the spread of COVID-19 has a negative short-term indirect spatial spillover effect. Corresponding practical insights are provided for the stakeholders based on the above findings. The results of this study will contribute to the development of effective policies to facilitate the recovery of road traffic volume from the impact of COVID-19 and the revitalization of the transportation industry.

1. Introduction

In early 2020, the COVID-19 pandemic spread rapidly, causing a widespread public health crisis [1]. Major countries and regions worldwide adopted non-pharmaceutical interventions as one of the main strategies to contain the pandemic [2]. These measures negatively affected the transport sector, with traffic in the United Kingdom down by over 60% and traffic in Europe falling by 70% [3]. The combined output of the passenger traffic sector in China dropped by 11.44% [4], while intercity traffic fell by 51.35% [5].
Several studies have reported a causal relationship between the lockdown measures imposed against COVID-19 and the decline in road traffic volume [6]. For example, Aloi et al. confirmed the negative impact of lockdown and quarantine measures on road traffic volume based on recorded data from traffic control cameras and environmental sensors [7]. A similar finding was verified in a series of empirical studies in regions such as China [8], Portugal [9], and Canada [10]. From another perspective, the impact of lockdown measures can also be found in the air [11] and railway [12] traffic volume and has negatively affected the revitalization of the transportation industry.
In addition to the lockdown measures, the negative impact of pandemics on traffic volume can be found in terms of tourist psychology [13] and the quality of road service [14]. Specifically, the perceived threat of COVID-19 can reduce people’s subjective willingness to travel across regions [15]. The impact of this mechanism may be influenced by individual attitudes toward the pandemic and previous experience with infection [16]. Furthermore, according to Luan et al., the COVID-19 pandemic could not only change people’s travel patterns, but also significantly affect their willingness to purchase traffic tools and may lead to a decrease in traffic volume [17].
Because of the strong relationship between traffic volume and economic development [18], the recovery of traffic volume from the impact of COVID-19 has an essential role in promoting economic recovery [19]. Therefore, a feasible way to recover traffic volume has been the focus of recent academic discussions. Several empirical studies have shed some light on the effects of COVID-19 on air [20] and urban public [21] transport volume and have further discussed practical measures to promote recovery. A basic consensus among the studies is that there is a significant change in traffic behavior, which can be manifested as decision preferences [22] or traffic modes [23], potentially leading to a decrease in the efficiency of traditional traffic management methods [24]. For example, Cruz et al. suggest that traffic companies should adjust their operational strategies promptly to cope with the negative impact of COVID-19 [25]. Similar findings have been identified in France [26] and Greece [27].
The above studies reflect the broad concern of scholars regarding the pandemic crisis. However, few studies have taken quantitative approaches to the spatial heterogeneity of the recovery of road traffic volume, which is of essential academic and practical significance in promoting the sustainability of related industries. Specifically, the research question in this paper is whether there are factors that can influence the recovery of road traffic volume from the impact of COVID-19. Further, if there are factors that can have an impact, whether this impact is influenced by mediating or moderating effects of other factors or whether it is spatially heterogeneous. To investigate these questions, based on provincial spatial panel data in mainland China, we test the spatial spillover effect of the recovery of road traffic volume from the impact of COVID-19 using a dynamic spatial panel model. Furthermore, we investigate the mechanisms and the robustness of the findings under different spatial weight matrices. Compared with existing studies, the contributions of this paper are as follows:
(1)
A quantitative evaluation method of the recovery of road traffic volume based on a principal component analysis is proposed.
(2)
The above quantitative evaluation methods and dynamic spatial panel models are applied to test the spatial heterogeneity of the recovery of road traffic volume in China.
(3)
The mechanism of the above spatial heterogeneity is discovered through the mediating effect test and the decomposition of the spatial–temporal effect.
The remaining sections of this paper are organized as follows. Section 2 reviews the relevant literature and presents the research hypotheses. Section 3 reports the methodology used for the study and the construction of variables. Section 4 reports the process and results of the empirical study. Section 5 discusses the findings of the empirical study, makes policy recommendations, and compares the results with existing studies. Section 6 summarizes the conclusions of this paper and presents further research perspectives.

2. Literature Review and Hypotheses

2.1. Income and Economic Development

As an essential part of the transport industry, road traffic has long been one of the major modes of transport [28]. It has better destination accessibility than other modes of transport, such as rail or air [29]. Since the 1980s, the analysis of factors influencing road traffic volume has gradually attracted more and more attention. For example, Gu et al. used the Bayesian combination model [30], the neural network model [31], and other algorithms to test the possible effect of factors such as economic development on road traffic volume. In general, areas with higher income and economic development have higher road traffic volume, a phenomenon supported by studies from the United States [32] and Greece [33].
The above studies illustrate the impact of income and economic development on road traffic volume. However, two issues remain for further empirical study. First, according to Valdes et al., the share of non-essential traffic demand, such as tourism, in overall traffic demand is higher in areas with higher income [34]. This non-essential traffic demand is more negatively affected by COVID-19 than the essential traffic demand, such as seasonal population movement, making it more difficult to recover to the same level as the pre-pandemic level [35]. Therefore, the recovery of road traffic volume in areas with higher income may be relatively low. Meanwhile, economic development can generally lead to a rise in income [36], potentially having a moderating effect in the latter’s mechanism on road traffic volume. Based on this, the following hypotheses are proposed:
Hypothesis 1a (H1a).
Income has a negative effect on the recovery of road traffic volume.
Hypothesis 1b (H1b).
Economic development has a moderating effect in the mechanism of income on the recovery of road traffic volume.

2.2. COVID-19 and Climate Suitability

Since the rapid spread of COVID-19, many scholars have studied the adverse impact of the pandemic on road traffic volume. According to a study by Macioszek et al. based on remote sensing video, the pandemic had a widespread negative impact on traffic volume and led to changes in the characteristics of the temporal distribution of road traffic volume [37]. Many studies point to the lockdown measures [11] and changes in tourist psychology [38] as the main reasons for the negative impact of the pandemic on traffic volume. Specifically, due to the concern of potential travelers about the infection, road traffic volume tended to decrease with the increase of confirmed COVID-19 cases [19]. Several studies have confirmed the existence of this adverse effect in regions such as China [8], the United States [39], and Korea [40].
Furthermore, climate suitability has also been widely considered to affect road traffic volume. Excessively cold weather can lead to a decrease in the travel intentions of potential travelers and, in turn, have a negative impact on road traffic volume, a phenomenon that has been observed in the United States [41] and Canada [42]. In addition to temperature, several studies have pointed out that rainfall [43], floods [44], and other weather events [45] may also have a significant impact on road traffic volume. In particular, according to Bi et al., the effect of climate suitability on road traffic volume varies with urban spatial layout and geographical conditions [46], which suggests the importance of further research using spatial panel models.
From another point of view, there is a strong link between climatic suitability and COVID-19, whereby climatic factors can determine the transmission characteristics of the pandemic. Several empirical studies based in Australia [47], the United States [48], and other regions have demonstrated the impact of climatic factors in the epidemiological process of COVID-19 and confirmed that COVID-19 is more transmissible in areas at higher latitudes with lower temperatures [49]. Climatic suitability can have both a direct effect on road traffic volume and an indirect influence on the ability of COVID-19 to spread. Therefore, COVID-19 may be an essential part of the mechanism of climate suitability on road traffic volume and may play a mediating effect. Based on this, the following hypotheses are proposed:
Hypothesis 2a (H2a).
Climate suitability has a positive effect on the recovery of road traffic volume.
Hypothesis 2b (H2b).
COVID-19 has a mediating effect in the mechanism of climate suitability on the recovery of road traffic volume.

2.3. Spatial Spillover Effect

According to Tobler’s first law of geography, there is a specific spatial correlation between any two subjects, and this correlation always strengthens as the distance between the subjects decreases [50]. Therefore, when considering econometric models, ignoring the spatial factor will lead to biased estimation results, a phenomenon known as the spatial effect [51]. Since the 1990s, the spatial effect has been increasingly used in traffic research. Many scholars support the existence of spatial effects when considering the factors influencing road traffic volume [52]. Specifically, this can be reflected in the spatial correlation of road traffic volume within cities [53] and the spatial spillover effect across cities and provinces [54]. The spatial effect may also be present in the processes of the recovery of road traffic volume from the impact of COVID-19.
In addition to the direct spatial spillover effect generated by road traffic volume, other factors may also spatially affect road traffic volume in the surrounding area. This mechanism is known as the indirect spatial spillover effect [55]. Zhang et al. showed that COVID-19 could significantly affect the economic development of the surrounding area through the indirect spatial spillover effect [56]. From the perspective of travelers’ psychology, when the spread of COVID-19 occurs in the surrounding area, potential travelers may cancel their travel plans to avoid the risk of contracting the disease [57]. Therefore, the indirect spatial spillover effect of COVID-19 may affect the recovery of road traffic volume in the surrounding province. Based on this, the following hypotheses are proposed:
Hypothesis 3a (H3a).
The recovery of road traffic volume has a positive direct spatial spillover effect on the surrounding province.
Hypothesis 3b (H3b).
COVID-19 has a negative indirect spatial spillover effect on the recovery of road traffic volume in the surrounding province.
Figure 1 shows the research hypotheses and model framework of this study. Among them, H1a represents the effect of income on the recovery of road traffic volume, and H1b represents the moderating effect of economic development on this mechanism, which together constitute the first part of the hypotheses of this study. Similarly, H2a represents the effect of climate suitability on the recovery of road traffic volume, and H2b represents the mediating effect of COVID-19, which together constitute the second part of the hypotheses. In the third part of the hypotheses, H3a represents the direct spatial spillover effect of local traffic volume on the surrounding region, and H3b represents the indirect spatial spillover effect of COVID-19. The hypotheses of each part are distinguished using dashed lines.

3. Methods and Data

The Data Flow Chart for this study is shown in Figure 2, where we describe all the methodological steps. In the remainder of this section, we detail each method’s specifics and the data’s processing.

3.1. Principal Component Analysis

Representative indicators such as road passenger turnover and transportation volume can be used to evaluate road traffic volume [58]. In line with Yang et al., to comprehensively reflect the actual situation of each relevant indicator, this paper adopts a principal component analysis (PCA) to reduce the dimensionality of the above indicators [59]. PCA aims to reflect the typical characteristics of the data with as little information as possible. It has the advantages of high information retention and can effectively avoid the problem of multicollinearity [60]. Suppose there are R samples and B indicators, represented by vectors as P = ( P 1 , P 2 , …, P B ), where P B = ( p 1 b , p 2 b , …, p R B ) t , p r b represents the observation of the rth sample (r = 1, 2, …, R) on the bth (b = 1, 2, …, B) index. At this point, the cth principal component can be expressed as follows:
Z c = b = 1 B a b c X b
In Equation (1), Z c is the value of the cth principal component and a b c is the loading of the bth index in the cth principal component.

3.2. Spatial Autocorrelation

To study the spatial heterogeneity of road traffic volume, we should first test whether there is significant spatial autocorrelation. In this paper, we adopt Moran’s I to evaluate the spatial autocorrelation [61], which can be expressed as follows:
I t = N S 0 × i = 1 N j = 1 N W i j   ( M i t     M t ¯ ) ( M j t     M t ¯ ) i = 1 N ( M i t     M t ¯ ) 2
In Equation (2), I t is Moran’s I in period t; N is the number of study areas. M i t and M j t are the study data of areas i and j in period t. M t ¯ is the mean of the study data in period t. S 0 is the sum of all elements in the spatial weight matrix. W i j is the spatial weight matrix. The range of Moran’s I is [−1, 1]. When Moran’s I is significantly not equal to 0, it can be considered that there is spatial autocorrelation; when it is greater than 0, there is positive spatial autocorrelation, and when the opposite is the case, there is negative spatial autocorrelation. We mainly consider the distance weight matrix W i j D [62] and the economic distance weight matrix W i j E [63], which are calculated as follows.
W i j D = { 1 D i j 2 ,   when   i     j   0 ,   when   i = j  
W i j E = { 1 | G D P i     GDP j | × D i j ,   when   i     j   0 ,   when   i = j  
In Equations (3) and (4), D ij is the Euclidean distance between area i and area j. GDP i and GDP j are the regional GDP per capita in area i and area j.

3.3. Spatial Panel Model

The spatial panel model can be used to identify and deal with the interaction effect between spatial data. The main principle is to incorporate the spatial distribution characteristics of the panel data into the econometric model and to achieve an unbiased estimation of the spatial heterogeneity of the data and its influencing factors [64]. The general nested spatial model can be represented as follows.
{ Y t = ρ WY t + β X t + θ WX t + μ + u t u t = λ Wu t + ε t  
In Equation (5), Y t is a vector of the explained variable of order N × 1 in period t (t = 1, 2, 3,…, T), where N is the number of spatial areas in the sample; W is a spatial weight matrix; ρ and θ are spatial autoregressive coefficients of explained variable and explanatory variables; WY t is the direct spatial spillover effect of the explained variables; X t is the explanatory variables matrix of order N × K, where K is the number of explanatory variables; β is a vector of the coefficient to be estimated of order K × 1, indicating the degree of impact of the explanatory variables on the explained variable; WX t is the indirect spatial spillover effect of the explanatory variables; μ is the fixed effect; u t is a vector of interference of order N × 1; λ is the autoregressive coefficient of the spatial error; Wu t is the spatial spillover effect of the interference; and ε t is the regression error.
When θ = 0 and λ = 0, the model is called the spatial lag model (SLM); when θ = 0 and ρ = 0, the model is called the spatial error model (SEM); and when λ = 0, the model is called the spatial Durbin model (SDM). Each of the above models is based on different assumptions and has a different scope of application and study significance [65]. Therefore, the models will be further tested and selected according to the data characteristics. Based on the above GNS model and referring to the studies of Akter et al. in the field of road traffic volume using spatial panel models [45], the econometric model constructed in this study is shown as follows:
Y it = ρ j = 1 N W ij Y jt + β X it + θ j = 1 N W ij X jt + μ it + ε it
Y it = ρ j = 1 N W ij Y jt + γ j = 1 N W ij Y jt 1 + β X it + θ j = 1 N W ij X jt + μ it + ε it
In Equation (6), i and j are different areas; t is different times; W is the spatial weight matrix; Y is the explained variable; X is the explanatory and control variables; ρ and θ are the spatial autoregressive coefficients; μ is the fixed effect; and ε is the regression error. In line with the study of Yang et al. [66], the dynamic spatial panel model is shown in Equation (7) by adding the time lag term.

3.4. Variables and Data Source

3.4.1. Explained Variable

The process of constructing the explained variable in this study is as follows:
PRR it = PN it PP it
TRR it = TN it TP it
In Equations (8) and (9), PN it and TN it are road passenger transportation volume and road passenger turnover volume in month t of the year 2021 in province i, respectively; PP it and TP it are average values of road passenger transportation volume and road passenger turnover volume in month t of the five years before the COVID-19 outbreak (2015 to 2019) in province i, respectively; PRR it and TRR it are the recovery rate of road passenger transportation volume and road passenger turnover volume in month t of 2021 in province i, respectively. To avoid the influence of multicollinearity, PCA is applied to PRR it and TRR it dimensionality reduction by province [67].
According to Alemzero et al., Bartlett’s test can be used to test the correlation between variables and to determine whether the variables are independent of each other. Bartlett’s test should be performed first before performing PCA. If the results reject the null hypothesis significantly, then the results of PCA are acceptable [68]. The critical values of Bartlett’s test are given by χ2 distribution approximation. Therefore, we performed Bartlett’s test and PCA using Stata 17, and the results are shown in Table 1.
As the Bartlett test results have strong significance and the variance proportion is higher than 85% in most provinces, the PCA results have solid statistical significance and empirical value. As a result, we can obtain the recovery index Recovery it of road traffic volume in period t and province i as follows:
Recovery it = PRR it   ×   a 1 i + TRR it   ×   a 2 i
In Equation (10), a 1 i and a 2 i are the PCA loadings of PRR it and TRR it in the ith province. Recovery it is the explained variable in the spatial panel model. Figure 3 shows the recovery index of road traffic volume for March, June, September, and December of 2021 to demonstrate the four quarters. Among them, we label the province serial numbers consistent with Table 1. It can be visualized that the provinces with higher recovery indices and those with lower indices tend to be adjacent, so we perform further analysis to investigate its spatial heterogeneity.

3.4.2. Explanatory and Control Variables

We take the per capita disposable income, per capita gross domestic product, temperature and humidity index (THI), and the number of confirmed COVID-19 cases as the explanatory variables. All of the above variables are widely considered suitable explanatory variables for studying income and economic development [69], climate suitability [70], and the spread of COVID-19 [71]. The Chow-Lin frequency transformation method is applied to convert some quarterly data into monthly data. This method has a good conversion effect and is widely used in social science research [72].
Some studies have also pointed out that air quality [73] and season [74] may impact road traffic volume. Therefore, these two factors are added to the model as control variables to avoid endogeneity problems caused by omitted variables. The air quality indicator is the air quality index (AQI). According to the existing air pollution classification standards in China, the monthly average value of AQI in most provinces falls in the same interval, which cannot reflect the control effect. Therefore, Jenks natural breaks is adopted to categorize AQI [75]. As a result, AQI = 1 represents the best air quality, and AQI = 5 represents the worst. For the seasonal index, in line with Liu et al., the season is assigned a value of 1 for the period from June to August and 0 for the rest of the year [76]. The above variables constitute the balanced panel data used for the empirical study. The time series length is 12, representing January to December of 2021, and the cross-section is 31, representing all 31 provinces in mainland China. Table 2 shows the description and statistics of the variables.

4. Results

4.1. Spatial Autocorrelation Index

Table 3 shows the results of Moran’s I and the corresponding two-tailed test for recovery from January to December 2021. On the whole, Moran’s I has values in the range of −0.112 to 0.544 and is significant at the 1% confidence level in most periods. It is positive except for January, indicating that the recovery of road traffic volume in mainland China shows a significant positive spatial autocorrelation. Provinces with better and worse recovery tend to be spatially adjacent.
The results of Moran’s I suggest a spatial autocorrelation in the recovery of road traffic volume during the pandemic, indicating that it is scientific and necessary to consider the spatial effect in further empirical studies.

4.2. Tests of Spatial Panel Models

To further test the spatial heterogeneity of the recovery of road traffic volume and its mechanism, we use spatial panel models for the empirical analysis. Each continuous-type variable is log-transformed to clarify the economic significance of the results. Furthermore, based on the distance weight matrix and economic distance weight matrix, the Lagrange multiplier (LM) test, Wald test, likelihood ratio (LR) test, and Hausman test are adopted to screen the spatial panel model [77]. Table 4 shows the results.
As Table 4 shows, the study data passed the LM test and robust LM test with high significance, indicating that the ordinary least squares estimate for the study data is biased and that the spatial lag effect and spatial error effect exist simultaneously [78]. The results of the Wald test and LR test are generally consistent, both of which can significantly reject the possibility of degenerating SDM into SEM but cannot reject the possibility of degenerating SDM into SLM. Therefore, we combine the log-likelihood, the Akaike information criterion (AIC), and the Bayesian information criterion (BIC) to make a comprehensive judgment on the validity of SLM and SDM [79]. Meanwhile, the Hausman test for both SLM and SDM can reject the null hypothesis at the 1% significance level. Therefore, the fixed-effect model is chosen for further research [80]. The results tested based on the economic-distance weight matrix are generally consistent with the distance weight matrix, thereby verifying the robustness of the above results.

4.3. Dynamic Spatial Panel Model

Table 5 shows the results of the empirical analysis of static and dynamic spatial panel models based on the distance weight matrix. Among them, Model 1 to Model 4 use the static models set in Equation (6); Model 5 to Model 8 use the dynamic models set in Equation (7). Specifically, Model 1 and Model 2 use the static SLM, Model 3 and Model 4 use the static SDM, Model 5 and Model 6 use the dynamic SLM, and Model 7 and Model 8 use the dynamic SDM.
The explained variable in each model is the recovery index of road traffic volume, while the explanatory variables are not exactly the same. To test the moderating effect, the variable Economic representing economic development and the interaction term Income × Economic are added to Model 2, Model 4, Model 6, and Model 8, and the other models represent the results without considering the moderating effect. In addition, AQI has five categorical intervals, so we represent it with four dummy variables to avoid multicollinearity. We add AQI = 2, AQI = 3, AQI = 4, AQI = 5, and Season as control variables to the model to control the effects of air quality and season on road traffic volume. We report the interaction terms of the spatial weight matrix and the explanatory variables, which can respond to the spatial spillover effects of the explanatory variables.
Comparing the performance of SLM and SDM on log-likelihood, AIC, BIC, and other indicators, it can be seen that the fitting effect of SLM is better than that of SDM. Therefore, further analysis will be mainly based on the results of SLM. In Model 1, the coefficient of income is significantly negative, indicating that it has a significant negative impact on the recovery of road traffic volume, and hypothesis H1a is supported.
In Model 2, the coefficients of Income and Economic are found to be negative. The coefficient of the interaction term is significantly positive, indicating that economic development and income have a significant negative impact on the recovery of road traffic volume, and economic development can play a positive moderating effect, and hypothesis H1b is supported. Additionally, in Model 3 and Model 4, which are based on SDM, the coefficients of the main explanatory variables are generally consistent with other models, indicating that the above results are robust.
The empirical results of each explanatory variable in Model 5 to Model 8 are generally consistent with those of the static spatial panel, proving that the spatial panel models are less affected by endogeneity. W × Recoveryit, representing spatial effect, is significantly positive in Model 1 to Model 8, indicating that the recovery of road traffic volume will be affected by the positive spatial spillover effect of the current situation in the surrounding provinces. Therefore, hypothesis H3a is supported.

4.4. Robustness Tests

The distance weight matrix is replaced with the economic distance weight matrix for robustness testing. Table 6 shows the results.
Comparative analysis of Table 5 and Table 6 shows that the empirical results of the models constructed with different spatial weight matrices do not differ significantly, indicating that the effect of explanatory variables on the recovery is robust. In Model 10 and Model 12, the coefficient of the interaction term is significantly positive, consistent with the results before replacing the spatial weight matrix, thereby verifying the robustness of the moderating effect.

4.5. Mediating Effect and Spatial Effect Decomposition

In line with Jin et al. [81], a stepwise method is used to test the mediating effect based on the dynamic SLM to test hypotheses H2a and H2b. Table 7 shows the results. Model 17 and Model 18 test the direct effect of COVID-19 Cases and THI on recovery, and the results show that they have significant negative and positive effects, respectively. Model 19 tests the indirect effect of THI on COVID-19 cases, and the results are significantly negative, indicating that COVID-19 has more potent propagation in wet and cold weather. Model 8 tests the total effect of COVID-19 cases and THI on recovery, and the results show that the regression coefficients are significant. The above models constitute a complete test path for the mediating effect, indicating that the spread of COVID-19 can have a significant mediating effect in the mechanism of THI acting on recovery. Therefore, hypotheses H2a and H2b are supported.
In Model 16 and Model 20 to Model 22, we replace the distance weight matrix with the economic distance weight matrix and repeat the above mediating effect test. The results are generally consistent, which illustrates the robustness of the above results.
The spatial–temporal effect decomposition of the dynamic SLM is adopted. Table 8 shows the results. Among them, Model 5 and Model 6 represent the decomposition results of the spatial–temporal effect before and after considering the moderating effect. In the short term, COVID-19 cases had a significant direct, indirect, and total effect on the surrounding provinces; the regression coefficients are all less than 0. The above results indicate that COVID-19 not only has a significant negative impact on recovery in the local province but also has a particular negative spatial spillover effect on the surrounding provinces. Therefore, hypothesis H3b is supported.

5. Discussion

5.1. Discussion of the Empirical Results

From a temporal perspective, Moran’s I fluctuates between −0.112 and 0.326 from January to May, with an insignificant trend and small absolute value, indicating that the spatial autocorrelation of recovery is relatively weak. Moran’s I reaches a peak of 0.544 in August and maintains a high level of 0.331 to 0.443 after August, indicating that the spatial autocorrelation of road traffic volume in summer is the strongest, and the spatial autocorrelation is stronger overall in the second half of the year than in the first half.
As Model 5 to Model 8 show, compared with the traditional static spatial panel model, the dynamic spatial panel model can effectively test and avoid the endogeneity problem of the model [82]. Income and economic development have a significant adverse effect on the recovery of road traffic volume, and the level of economic development has a significant positive moderating effect on the mechanism of income. The above results confirm the mutual impact between the surrounding province in the recovery of road traffic volume, indicating that the provinces should actively collaborate to jointly promote the recovery of road traffic volume and the recovery of related industries.
In Models 13 to 16, we construct a dynamic spatial panel model based on the economic distances weight matrix. Its main empirical results are generally consistent with the static spatial panel model. In addition, W × Recoveryit is significantly positive in Model 9 to Model 16, indicating a significant spatial spillover effect of recovery in both the distance weight matrix and economic distance weight matrix. The above results further validate the robustness of the above empirical findings and avoid the interference of endogeneity [83].
The result of the mediating effect test indicates that the spread of COVID-19 is more potent in provinces with lower temperature and humidity indices, factors that can negatively impact the recovery of road traffic volume. In line with Jankelova et al., the Sobel test is used to further test the mediating effect [84]. The Z-value statistic is 2.28, corresponding to a p-value of 0.023, which verifies the significance of the above mediating effect. Furthermore, by replacing the distance weight matrix with the economic distance weight matrix, the robustness of the above empirical results is supported in this paper.
In the long term, the indirect effect of COVID-19 cases is not significant, indicating that the spatial spillover effect of COVID-19 on recovery in the surrounding provinces will gradually disappear in the long term. This is because China’s non-pharmaceutical interventions for COVID-19 will be dynamically adjusted as the outbreak progresses, whereby its negative impact on the recovery of road traffic volume in the surrounding provinces will gradually diminish after the pandemic. Model 13 and Model 14 reflect the decomposition results of the spatial effect after replacing the distance weight matrix with the economic distance weight matrix, and it can be found that coefficients of explanatory variables are generally unaffected, verifying the robustness of the above empirical results.

5.2. Policy Recommendations

Considering that factors such as the spread of COVID-19, income, and climate suitability all significantly affect the recovery of road traffic volume, the government should formulate policy measures that meet real needs according to the time and place. For example, when the temperature and humidity indices are low, consideration can be given to increasing policy support for traffic and other related industries to promote the recovery of road traffic volume [85]. At the same time, because the recovery of road traffic volume has a positive spatial spillover effect, the government should minimize traffic closures in the surrounding province to achieve the overall recovery of the traffic volume.
The recovery of road traffic volume is poor in most provinces and fluctuates with the spread of COVID-19. Therefore, traffic companies and other related companies should adjust their risk response strategies and be prepared to face the pressure of the pandemic in the long term [86] and consider the changes in travelers’ behavior [87]. Additionally, traffic companies should focus on further market development in provinces with relatively low income and economic development levels. This is because such provinces have better recovery of road traffic volume.
Due to the negative impact and indirect spatial spillover effect of COVID-19 on traffic volume, communities, residents, and other stakeholders should take measures to avoid the spread of COVID-19, such as maintaining social distance [88]. If the spread of a new pandemic begins, the recovery gains already achieved may be lost, and the development of the surrounding provinces may also be adversely affected.

5.3. Comparison with Existing Studies

As we mentioned above, studying road traffic volume from the impact of COVID-19 is one of the current hot topics of scientific research. Existing studies have mainly discussed the mechanisms of COVID-19 effects on road traffic volume. For example, the number of COVID-19 cases [37] and lockdown measures [7] lead to a decrease in road traffic volume, which is consistent with the above findings. Therefore, the results of this study fit well with the existing literature, and the research hypotheses are supported.
Furthermore, there are some unique findings in this study. According to a series of existing studies, high-income provinces have higher road traffic volume [89]. However, when we study the recovery index of road traffic volume, the opposite is found, with higher-income provinces having a lower recovery index. This is because the current lockdown measures are mainly for non-essential traffic [90], while it occupies a higher proportion of the total traffic in high-income provinces [34]. As a result, it is more difficult for high-income provinces to recover road traffic volume to pre-pandemic levels. This makes it necessary for the government to consider different policies in different provinces to facilitate the recovery of road traffic volume.
From another perspective, by constructing dynamic spatial panel models, we also found the short-term indirect spatial spillover effect of COVID-19. In other words, local COVID-19 cases lead to a short-term decrease in the recovery of road traffic volume in surrounding provinces. This result has not been reported in the existing literature and has important implications for the transportation industry with the impact of COVID-19. According to the above results, there is a need for solidarity and collaboration among surrounding provinces to take measures to overcome the threat of the pandemic together; otherwise, they will be negatively affected by each other.

6. Conclusions

Based on the spatial panel data of all 31 provinces in mainland China in 2021, this paper uses PCA to evaluate the recovery of road traffic volume under the impact of the pandemic. It investigates the spatial heterogeneity of the recovery of road traffic volume and its mechanism by using the spatial autocorrelation index and dynamic spatial panel model, with the following main findings.
The recovery of road traffic volume in China shows a strong positive spatial autocorrelation in general [91]. It is relatively weak between January and May and strong between June and December, indicating that the spatial autocorrelation of the recovery of road traffic volume shows a trend from weak to strong. Road traffic volume in provinces with better income and economic development is slower to recover to pre-pandemic levels. This is because non-essential traffic demand accounts for a higher proportion of total traffic demand [34], and this non-essential traffic demand is more negatively affected by the pandemic than essential traffic demand [35]. From the other point of view, climate suitability can affect the recovery of road traffic volume both indirectly through COVID-19 and directly. This indicates that a warm and humid climate is not conducive to the spread of COVID-19 compared to a cold climate [49] and to the recovery of road traffic volume [92].
Furthermore, in terms of spatial heterogeneity, the recovery of road traffic volume has a positive spatial spillover effect, which can be manifested as a mutual impact between surrounding provinces. At the same time, COVID-19 can have a negative indirect spatial spillover effect in the short term. For example, the spread of the pandemic in one province may have a short-term negative impact on the recovery of road traffic volume in the surrounding provinces [93]. Therefore, the government and other stakeholders should take measures to reduce the spread of COVID-19 to facilitate the recovery of road traffic volume in the local and surrounding provinces.
There are some limitations to our research. First, as COVID-19 continues to spread globally, there is an opportunity to make new findings if further empirical analysis is conducted based on the latest situation of the pandemic and the recovery of traffic volume. Second, we mainly use the distance weight matrix and the economic distance weight matrix, in addition to a variety of spatial weight matrices with different economic significance, for further selection and study [94]. Considering the negative impact of COVID-19, further research on the recovery of traffic would provide vital assistance to stakeholders.

Author Contributions

Conceptualization, J.Z.; methodology, J.Z. and S.Z.; software, J.Z. and S.Z.; validation, J.Z. and C.P.; writing, S.Z. and X.G. All authors have read and agreed to the published version of the manuscript.

Funding

This research received no external funding.

Institutional Review Board Statement

Not applicable.

Informed Consent Statement

Not applicable.

Data Availability Statement

Not applicable.

Acknowledgments

The authors would like to thank the reviewers for their revisions.

Conflicts of Interest

The authors declare no conflict of interest.

Nomenclature

AcronymsDefinition
PCAPrincipal Component Analysis
SLMSpatial Lag Model
SEMSpatial Error Model
SDMSpatial Durbin Model
THITemperature and Humidity Index
AQIAir Quality Index
LMLagrange Multiplier
LRLikelihood Ratio
AICAkaike Information Criterion
BICBayesian Information Criterion

References

  1. Zhou, F.; Yu, T.; Du, R.; Fan, G.; Liu, Y.; Liu, Z.; Xiang, J.; Wang, Y.; Song, B.; Gu, X.; et al. Clinical course and risk factors for mortality of adult inpatients with COVID-19 in Wuhan, China: A retrospective cohort study. Lancet 2020, 395, 1054–1062. [Google Scholar] [CrossRef]
  2. Gössling, S.; Scott, D.; Hall, C.M. Pandemics, tourism and global change: A rapid assessment of COVID-19. J. Sustain. Tour. 2020, 29, 1–20. [Google Scholar] [CrossRef]
  3. Liu, A.; Kim, Y.R.; O’Connell, J.F. COVID-19 and the aviation industry: The interrelationship between the spread of the COVID-19 pandemic and the frequency of flights on the EU market. Ann. Tourism. Res. 2021, 91, 103298. [Google Scholar] [CrossRef]
  4. Cui, Q.; He, L.; Liu, Y.; Zheng, Y.; Wei, W.; Yang, B.; Zhou, M. The impacts of COVID-19 pandemic on China’s transport sectors based on the CGE model coupled with a decomposition analysis approach. Transp. Policy 2021, 103, 103–115. [Google Scholar] [CrossRef]
  5. Li, T.; Wang, J.; Huang, J.; Yang, W.; Chen, Z. Exploring the dynamic impacts of COVID-19 on intercity travel in China. J Transp. Geogr. 2021, 95, 103153. [Google Scholar] [CrossRef]
  6. Olayode, I.O.; Severino, A.G.; Campisi, T.; Tartibu, L.K. Comprehensive Literature Review on the Impacts of COVID-19 Pandemic on Public Road Transportation System: Challenges and Solutions. Sustainability 2022, 14, 9586. [Google Scholar] [CrossRef]
  7. Aloi, A.; Alonso, B.; Benavente, J.; Cordera, R.; Echaniz, E.; Gonzalez, F.; Ladisa, C.; Lezama-Romanelli, R.; Lopez-Parra, A.; Mazzei, V.; et al. Effects of the COVID-19 Lockdown on Urban Mobility: Empirical Evidence from the City of Santander (Spain). Sustainability 2020, 12, 3870. [Google Scholar] [CrossRef]
  8. Guo, W.; Feng, Y.; Luo, W.; Ren, Y.; Tan, J.; Jiang, X.; Xue, Q. The Impacts of COVID-19 and Policies on Spatial and Temporal Distribution Characteristics of Traffic: Two Examples in Beijing. Sustainability 2022, 14, 1733. [Google Scholar] [CrossRef]
  9. Aparicio, J.T.; Arsenio, E.; Henriques, R. Understanding the Impacts of the COVID-19 Pandemic on Public Transportation Travel Patterns in the City of Lisbon. Sustainability 2021, 13, 8342. [Google Scholar] [CrossRef]
  10. Tian, X.; An, C.; Chen, Z.; Tian, Z. Assessing the impact of COVID-19 pandemic on urban transportation and air quality in Canada. Sci. Total Environ. 2021, 765, 144270. [Google Scholar] [CrossRef]
  11. Lau, H.; Khosrawipour, V.; Kocbach, P.; Mikolajczyk, A.; Ichii, H.; Zacharski, M.; Bania, J.; Khosrawipour, T. The association between international and domestic air traffic and the coronavirus (COVID-19) outbreak. J. Microbiol. Immunol. 2020, 53, 467–472. [Google Scholar] [CrossRef] [PubMed]
  12. Wang, F.; Niu, F. Understanding the Spread of COVID-19 in China: Spatial-Temporal Characteristics, Risk Analysis and the Impact of the Quarantine of Hubei Province on the Railway Transportation Network. Sustainability 2021, 13, 5163. [Google Scholar] [CrossRef]
  13. Monterde-i-Bort, H.; Sucha, M.; Risser, R.; Kochetova, T. Mobility Patterns and Mode Choice Preferences during the COVID-19 Situation. Sustainability 2022, 14, 768. [Google Scholar] [CrossRef]
  14. Ma, Y.; Xu, J.; Gao, C.; Gu, C.; Tong, X. The Limited Responses of Provincial Expressway Network Operation Quality to the Impact of COVID-19: Taking Shaanxi Province as an Example. Sustainability 2022, 14, 10859. [Google Scholar] [CrossRef]
  15. Baig, F.; Kirytopoulos, K.; Lee, J.; Tsamilis, E.; Mao, R.; Ntzeremes, P. Changes in People’s Mobility Behavior in Greece after the COVID-19 Outbreak. Sustainability 2022, 14, 3567. [Google Scholar] [CrossRef]
  16. Ghodsi, M.; Ardestani, A.; Rasaizadi, A.; Ghadamgahi, S.; Yang, H. How COVID-19 Pandemic Affected Urban Trips? Structural Interpretive Model of Online Shopping and Passengers Trips during the Pandemic. Sustainability 2021, 13, 11995. [Google Scholar] [CrossRef]
  17. Luan, S.L.; Yang, Q.F.; Jiang, Z.T.; Wang, W. Exploring the impact of COVID-19 on individual’s travel mode choice in China. Transp. Policy 2021, 106, 271–280. [Google Scholar] [CrossRef]
  18. Maparu, T.S.; Mazumder, T.N. Transport infrastructure, economic development and urbanization in India (1990–2011): Is there any causal relationship? Transp. Res. Part A Policy Pract. 2017, 100, 319–336. [Google Scholar] [CrossRef]
  19. Li, Y.; Yang, Y.; Luo, G.; Huang, J.; Wu, T. The Economic Recovery from Traffic Restriction Policies during the COVID-19 through the Perspective of Regional Differences and Sustainable Development: Based on Human Mobility Data in China. Sustainability 2022, 14, 6453. [Google Scholar] [CrossRef]
  20. Andribet, P.; Baumgartner, M.; Garot, J.M.; Air, S.A. Reinventing European air traffic control based on the covid-19 pandemic experience. Util. Policy 2022, 75, 101343. [Google Scholar] [CrossRef]
  21. Jiao, F.; Huang, L.; Song, R.J.; Huang, H.F. An Improved STL-LSTM Model for Daily Bus Passenger Flow Prediction during the COVID-19 Pandemic. Sensors 2021, 21, 5950. [Google Scholar] [CrossRef] [PubMed]
  22. Zhang, C.; Tian, Y. Forecast daily tourist volumes during the epidemic period using COVID-19 data, search engine data and weather data. Expert Syst. Appl. 2022, 210, 118505. [Google Scholar] [CrossRef] [PubMed]
  23. Ku, D.; Um, J.; Byon, Y.; Kim, J.; Lee, S. Changes in Passengers’ Travel Behavior Due to COVID-19. Sustainability 2021, 13, 7974. [Google Scholar] [CrossRef]
  24. Simovic, S.; Ivanisevic, T.; Bradic, B.; Cicevic, S.; Trifunovic, A. What Causes Changes in Passenger Behavior in South-East Europe during the COVID-19 Pandemic? Sustainability 2021, 13, 9398. [Google Scholar] [CrossRef]
  25. Cruz, C.O.; Sarmento, J.M. The Impact of COVID-19 on Highway Traffic and Management: The Case Study of an Operator Perspective. Sustainability 2021, 13, 5320. [Google Scholar] [CrossRef]
  26. Li, X.; de Groot, M.; Bäck, T. Using forecasting to evaluate the impact of COVID-19 on passenger air transport demand. Decis. Sci. 2021. [Google Scholar] [CrossRef]
  27. Kitsou, S.P.; Koutsoukis, N.S.; Chountalas, P.; Rachaniotis, N.P. International Passenger Traffic at the Hellenic Airports: Impact of the COVID-19 Pandemic and Mid-Term Forecasting. Aerospace 2022, 9, 143. [Google Scholar] [CrossRef]
  28. Dutschke, E.; Engel, L.; Theis, A.; Hanss, D. Car driving, air travel or more sustainable transport? Socio-psychological factors in everyday mobility and long-distance leisure travel. Travel Behav. Soc. 2022, 28, 115–127. [Google Scholar] [CrossRef]
  29. Chen, K.D.; Lin, H.L.; Liao, L.Y.; Lu, Y.C.; Chen, Y.O.; Lin, Z.H.; Teng, L.X.; Weng, A.F.; Fu, T.Q. Nonlinear Rail Accessibility and Road Spatial Pattern Effects on House Prices. Sustainability 2022, 14, 4700. [Google Scholar] [CrossRef]
  30. Gu, Y.L.; Lu, W.Q.; Xu, X.Y.; Qin, L.Q.; Shao, Z.Z.; Zhang, H.Y. An Improved Bayesian Combination Model for Short-Term Traffic Prediction with Deep Learning. IEEE Trans. Intell. Transp. Syst. 2020, 21, 1332–1342. [Google Scholar] [CrossRef]
  31. Xiang, Y.; Chen, J.; Yu, W.; Wu, R.; Liu, B.; Wang, B.; Li, Z. A Two-Phase Approach for Predicting Highway Passenger Volume. Appl. Sci. 2021, 11, 6248. [Google Scholar] [CrossRef]
  32. Das, S. Traffic volume prediction on low-volume roadways: A Cubist approach. Transp. Plan. Technol. 2021, 44, 93–110. [Google Scholar] [CrossRef]
  33. Nikolaou, K.; Basbas, S. Urban Traffic and Air Quality Evolution Under Economic Recession Conditions. Glob. Nest J. 2014, 16, 866–872. [Google Scholar]
  34. Valdes, V. Determinants of air travel demand in Middle Income Countries. J. Air Transp. Manag. 2015, 42, 75–84. [Google Scholar] [CrossRef]
  35. Nunkoo, R.; Daronkola, H.K.; Gholipour, H.F. Does domestic tourism influence COVID-19 cases and deaths? Curr. Issues Tour. 2022, 25, 338–351. [Google Scholar] [CrossRef]
  36. Nolan, B.; Roser, M.; Thewissen, S. GDP Per Capita Versus Median Household Income: What Gives Rise to the Divergence Over Time and how does this Vary Across OECD Countries? Rev. Income Wealth 2019, 65, 465–494. [Google Scholar] [CrossRef]
  37. Macioszek, E.; Kurek, A. Extracting Road Traffic Volume in the City before and during covid-19 through Video Remote Sensing. Remote Sens. 2021, 13, 2329. [Google Scholar] [CrossRef]
  38. Angel, A.; Cohen, A.; Dalyot, S.; Plaut, P. Impact of COVID-19 policies on pedestrian traffic and walking patterns. Environ. Plan. B Urban Anal. City Sci. 2022, 23998083221113332. [Google Scholar] [CrossRef]
  39. Goenaga, B.; Matini, N.; Karanam, D.; Underwood, B.S. Disruption and Recovery: Initial Assessment of COVID-19 Traffic Impacts in North Carolina and Virginia. J. Transp. Eng. Part A Syst. 2021, 147, 06021001. [Google Scholar] [CrossRef]
  40. Lee, H.; Noh, E.; Jeon, H.; Nam, E.W. Association between traffic inflow and COVID-19 prevalence at the provincial level in South Korea. Int. J. Infect. Dis. 2021, 108, 435–442. [Google Scholar] [CrossRef]
  41. Sathiaraj, D.; Punkasem, T.O.; Wang, F.H.; Seedah, D. Data-driven analysis on the effects of extreme weather elements on traffic volume in Atlanta, GA, USA. Comput. Environ. Urban 2018, 72, 212–220. [Google Scholar] [CrossRef]
  42. Roh, H.J. Development and Performance Assessment of Winter Climate Hazard Models on Traffic Volume with Four Model Structure Types. Nat. Hazards Rev. 2020, 21, 04020023. [Google Scholar] [CrossRef]
  43. Dunne, S.; Ghosh, B. Weather Adaptive Traffic Prediction Using Neurowavelet Models. IEEE Trans. Intell. Transp. Syst. 2013, 14, 370–379. [Google Scholar] [CrossRef]
  44. Praharaj, S.; Chen, T.D.; Zahura, F.T.; Behl, M.; Goodall, J.L. Estimating impacts of recurring flooding on roadway networks: A Norfolk, Virginia case study. Nat. Hazards 2021, 107, 2363–2387. [Google Scholar] [CrossRef]
  45. Akter, T.; Mitra, S.K.; Hernandez, S.; Corro-Diaz, K. A spatial panel regression model to measure the effect of weather events on freight truck traffic. Transp. A Transp. Sci. 2020, 16, 910–929. [Google Scholar] [CrossRef]
  46. Bi, H.; Ye, Z.; Zhu, H. Data-driven analysis of weather impacts on urban traffic conditions at the city level. Urban Clim. 2022, 41, 101065. [Google Scholar] [CrossRef]
  47. Ward, M.P.; Xiao, S.; Zhang, Z.J. The role of climate during the COVID-19 epidemic in New South Wales, Australia. Transbound. Emerg. Dis. 2020, 67, 2313–2317. [Google Scholar] [CrossRef]
  48. Bashir, M.F.; Ma, B.J.; Bilal; Komal, B.; Bashir, M.A.; Tan, D.J.; Bashir, M. Correlation between climate indicators and COVID-19 pandemic in New York, USA. Sci. Total Environ. 2020, 728, 138835. [Google Scholar] [CrossRef]
  49. Chen, S.; Prettner, K.; Kuhn, M.; Geldsetzer, P.; Wang, C.; Bärnighausen, T.; Bloom, D.E. Climate and the spread of COVID-19. Sci. Rep. 2021, 11, 9042. [Google Scholar] [CrossRef]
  50. Anselin, L. Space and Applied Econometrics-Introduction. Reg. Sci. Urban Econ. 1992, 22, 307–316. [Google Scholar] [CrossRef]
  51. Zhu, Y.M.; Zhou, X.Y.; Li, J.J.; Wang, F. Technological Innovation, Fiscal Decentralization, Green Development Efficiency: Based on Spatial Effect and Moderating Effect. Sustainability 2022, 14, 4316. [Google Scholar] [CrossRef]
  52. Liang, X.; Li, P.G. Empirical Study of the Spatial Spillover Effect of Transportation Infrastructure on Green Total Factor Productivity. Sustainability 2021, 13, 326. [Google Scholar] [CrossRef]
  53. Chen, T.; Fang, J.; Xu, M.Y.; Tong, Y.F.; Chen, W.T. Prediction of Public Bus Passenger Flow Using Spatial-Temporal Hybrid Model of Deep Learning. J. Transp. Eng. Part A Syst. 2022, 148, 04022007. [Google Scholar] [CrossRef]
  54. Yue-di, Y.; Liu, J.; Ma, M.S.; Chen, X.C. Impact of Air Service on High-Speed Railway Passenger Flow. Int. J. Transp. Econ. 2019, 46, 137–158. [Google Scholar]
  55. Li, F.; Li, G.D. Agglomeration and Spatial Spillover Effects of Regional Economic Growth in China. Sustainability 2018, 10, 4695. [Google Scholar] [CrossRef] [Green Version]
  56. Zhang, S.R.; Wang, S.; Yuan, L.R.; Liu, X.G.; Gong, B.L. The impact of epidemics on agricultural production and forecast of COVID-19. China Agric. Econ. Rev. 2020, 12, 409–425. [Google Scholar] [CrossRef]
  57. Donaire, J.A.; Gali, N.; Camprubi, R. Empty Summer: International Tourist Behavior in Spain during COVID-19. Sustainability 2021, 13, 4356. [Google Scholar] [CrossRef]
  58. Han, J.; Hayashi, Y. A system dynamics model of CO2 mitigation in China’s inter-city passenger transport. Transp. Res. Part D Transp. Environ. 2008, 13, 298–305. [Google Scholar] [CrossRef]
  59. Yang, Y.; Li, T.Z.; Zhang, T.; Yu, Q. Time dimension analysis: Comparison of Nanjing local driving cycles in 2009 and 2017. Sustain. Cities Soc. 2020, 53, 101949. [Google Scholar] [CrossRef]
  60. Mikulić, J.; Krešić, D.; Kožić, I. Critical Factors of the Maritime Yachting Tourism Experience: An Impact-Asymmetry Analysis of Principal Components. J. Travel Tour. Mark 2015, 32, S30–S41. [Google Scholar] [CrossRef]
  61. Tian, X.B.; Zhang, M.R. Research on Spatial Correlations and Influencing Factors of Logistics Industry Development Level. Sustainability 2019, 11, 1356. [Google Scholar] [CrossRef] [Green Version]
  62. Harris, R.; Moffat, J.; Kravtsova, V. In Search of ‘W’. Spat. Econ. Anal. 2011, 6, 249–270. [Google Scholar] [CrossRef]
  63. Parent, O.; LeSage, J.P. Using the variance structure of the conditional autoregressive spatial specification to model knowledge spillovers. J. Appl. Econ. 2008, 23, 235–256. [Google Scholar] [CrossRef]
  64. Bivand, R.; Piras, G. Comparing Implementations of Estimation Methods for Spatial Econometrics. J. Stat. Softw. 2015, 63, 1–36. [Google Scholar] [CrossRef] [Green Version]
  65. Lv, K.; Yu, S.R.; Fu, D.A.; Wang, J.W.; Wang, C.C.; Pan, J.B. The Impact of Financial Development and Green Finance on Regional Energy Intensity: New Evidence from 30 Chinese Provinces. Sustainability 2022, 14, 9207. [Google Scholar] [CrossRef]
  66. Yang, K.; Lee, L.F. Identification and estimation of spatial dynamic panel simultaneous equations models. Reg. Sci. Urban Econ. 2019, 76, 32–46. [Google Scholar] [CrossRef]
  67. Choi, S.W.; Kim, B. Applying PCA to Deep Learning Forecasting Models for Predicting PM2.5. Sustainability 2021, 13, 3726. [Google Scholar] [CrossRef]
  68. Alemzero, D.A.; Sun, H.; Mohsin, M.; Iqbal, N.; Nadeem, M.; Vo, X.V. Assessing energy security in Africa based on multi-dimensional approach of principal composite analysis. Environ. Sci. Pollut. Res. 2021, 28, 2158–2171. [Google Scholar] [CrossRef]
  69. Xu, B.J.; Zhong, R.Y.; Liu, Y.F. Comparison of CO2 emissions reduction efficiency of household fuel consumption in China. Sustainability 2019, 11, 979. [Google Scholar] [CrossRef] [Green Version]
  70. Ichim, P.; Sfica, L. The Influence of Urban Climate on Bioclimatic Conditions in the City of Iasi, Romania. Sustainability 2020, 12, 9652. [Google Scholar] [CrossRef]
  71. Zhu, Z.Y.; Xie, H.M. What Do We Know and What Do We Need to Know about COVID-19’s Implications on Business Economics? From Bibliometric Analysis to a Conceptual Framework. Sustainability 2022, 14, 6396. [Google Scholar] [CrossRef]
  72. Aditian, A.; Kubota, T.; Shinohara, Y. Comparison of GIS-based landslide susceptibility models using frequency ratio, logistic regression, and artificial neural network in a tertiary region of Ambon, Indonesia. Geomorphology 2018, 318, 101–111. [Google Scholar] [CrossRef]
  73. Moon, J.; Hong, J.G.; Park, T.W. A Novel Method for Traffic Estimation and Air Quality Assessment in California. Sustainability 2022, 14, 9169. [Google Scholar] [CrossRef]
  74. Qu, L.C.; Li, W.; Li, W.J.; Ma, D.F.; Wang, Y.H. Daily long-term traffic flow forecasting based on a deep neural network. Expert Syst. Appl. 2019, 121, 304–312. [Google Scholar] [CrossRef]
  75. Jiang, B. Head/Tail Breaks: A New Classification Scheme for Data with a Heavy-Tailed Distribution. Prof. Geogr. 2013, 65, 482–494. [Google Scholar] [CrossRef]
  76. Liu, X.C.; Li, L.S.; Liu, X.H.; Zhang, T.; Rong, X.Y.; Yang, L.; Xiong, D.Z. Field investigation on characteristics of passenger flow in a Chinese hub airport terminal. Build. Environ. 2018, 133, 51–61. [Google Scholar] [CrossRef]
  77. Debarsy, N.; Ertur, C. Testing for spatial autocorrelation in a fixed effects panel data model. Reg. Sci. Urban Econ. 2010, 40, 453–470. [Google Scholar] [CrossRef] [Green Version]
  78. Ouchen, A.; Montargot, N. Non-spatial and spatial econometric analysis of tourism demand in a panel of countries around the world. Spat. Econ. Anal. 2021, 17, 262–283. [Google Scholar] [CrossRef]
  79. Burnham, K.P.; Anderson, D.R. Multimodel Inference. Sociol. Method Res. 2004, 33, 261–304. [Google Scholar] [CrossRef]
  80. Baltagi, B.H.; Liu, L. Random Effects, Fixed Effects and Hausman’s Test for the Generalized Mixed Regressive Spatial Autoregressive Panel Data Model. Econ. Rev. 2016, 35, 638–658. [Google Scholar] [CrossRef]
  81. Jin, X.T.; Zhao, Y.R.; Song, W.; Zhao, T.Y. Save for Safe: Effect of COVID-19 Pandemic on Consumers’ Saving and Spending Behavior in China. Front. Psychol. 2021, 12, 636859. [Google Scholar] [CrossRef] [PubMed]
  82. Wang, J.B.; Yamamoto, T.; Liu, K. Spatial dependence and spillover effects in customized bus demand: Empirical evidence using spatial dynamic panel models. Transp. Policy 2021, 105, 166–180. [Google Scholar] [CrossRef]
  83. Wu, H.T.; Xu, L.N.; Ren, S.Y.; Hao, Y.; Yan, G.Y. How do energy consumption and environmental regulation affect carbon emissions in China? New evidence from a dynamic threshold panel model. Resour. Policy 2020, 67, 101678. [Google Scholar] [CrossRef]
  84. Jankelova, N.; Skorkova, Z.; Joniakova, Z.; Nemethova, I. A Diverse Organizational Culture and Its Impact on Innovative Work Behavior of Municipal Employees. Sustainability 2021, 13, 3419. [Google Scholar] [CrossRef]
  85. Wu, L.; Achyldurdyyeva, J.; Jou, W.; Foung, W.; Jaw, B. Relief, Recovery, and Revitalization Measures for Tourism and Hospitality Industry During Covid-19 Pandemic: Case Study from Taiwan. SAGE Open 2021, 11, 1999480888. [Google Scholar] [CrossRef]
  86. Lin, A.J.; Chang, H.Y.; Hung, B. Identifying Key Financial, Environmental, Social, Governance (ESG), Bond, and COVID-19 Factors Affecting Global Shipping Companies-A Hybrid Multiple-Criteria Decision-Making Method. Sustainability 2022, 14, 5148. [Google Scholar] [CrossRef]
  87. Pacurar, C.M.; Albu, R.G.; Pacurar, V.D. Tourist Route Optimization in the Context of Covid-19 Pandemic. Sustainability 2021, 13, 5492. [Google Scholar] [CrossRef]
  88. Zhang, H.Y.; Song, H.Y.; Wen, L.; Liu, C. Forecasting tourism recovery amid COVID-19. Ann. Tour. Res. 2021, 87, 103149. [Google Scholar] [CrossRef]
  89. Graham, D.J.; Glaister, S. Decomposing the determinants of road traffic demand. Appl. Econ. 2005, 37, 19–28. [Google Scholar] [CrossRef]
  90. Hamidi, S.; Zandiatashbar, A. Compact development and adherence to stay-at-home order during the COVID-19 pandemic: A longitudinal investigation in the United States. Landsc. Urban Plan. 2021, 205, 103952. [Google Scholar] [CrossRef]
  91. Fu, W.J.; Jiang, P.K.; Zhou, G.M.; Zhao, K.L. Using Moran’s I and GIS to study the spatial pattern of forest litter carbon density in a subtropical region of southeastern China. Biogeosciences 2014, 11, 2401–2409. [Google Scholar] [CrossRef] [Green Version]
  92. Fitchett, J.M.; Robinson, D.; Hoogendoorn, G. Climate suitability for tourism in South Africa. J. Sustain. Tour. 2017, 25, 851–867. [Google Scholar] [CrossRef]
  93. Deng, T.T.; Li, X.; Ma, M.L. Evaluating impact of air pollution on China’s inbound tourism industry: A spatial econometric approach. Asia Pac. J. Tour. Res. 2017, 22, 771–780. [Google Scholar] [CrossRef]
  94. Zhang, X.; Yu, J. Spatial weights matrix selection and model averaging for spatial autoregressive models. J. Econ. 2018, 203, 1–18. [Google Scholar] [CrossRef]
Figure 1. Research hypotheses and model framework.
Figure 1. Research hypotheses and model framework.
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Figure 2. Data Flow Chart.
Figure 2. Data Flow Chart.
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Figure 3. Recovery index of road traffic volume in 31 provinces of mainland China.
Figure 3. Recovery index of road traffic volume in 31 provinces of mainland China.
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Table 1. Results of Bartlett’s test and PCA.
Table 1. Results of Bartlett’s test and PCA.
Serial NumberProvinceBartlett’s TestVariance ProportionLoading 1 ( a 1 i ) Loading 2 ( a 2 i )
1Beijing22.091 ***0.9760.6390.769
2Tianjin26.698 ***0.9850.6420.766
3Hebei16.029 ***0.9710.4130.911
4Shanxi (1)21.867 ***0.9810.4810.877
5Neimenggu23.930 ***0.9810.6070.794
6Liaoning16.339 ***0.9540.6480.761
7Jilin30.306 ***0.9920.5040.864
8Heilongjiang10.447 ***0.9100.6460.764
9Shanghai0.231 ***0.9920.6780.735
10Jiangsu20.740 ***0.9760.5330.846
11Zhejiang5.421 **0.8440.5600.829
12Anhui12.547 ***0.9280.6900.724
13Fujian20.639 ***0.9810.4500.893
14Jiangxi4.483 **0.8280.5250.851
15Shandong18.344 ***0.9650.6000.800
16Henan19.752 ***0.9680.6930.720
17Hubei14.287 ***0.9560.4770.879
18Hunan22.824 ***0.9770.6570.754
19Guangdong17.447 ***0.9590.6630.748
20Guangxi7.612 ***0.9020.4600.888
21Hainan28.674 ***0.9910.4680.884
22Chongqing10.260 ***0.9080.6530.757
23Sichuan24.980 ***0.9880.4520.892
24Guizhou18.830 ***0.9790.4050.914
25Yunnan17.805 ***0.9760.4190.908
26Xizang12.497 ***0.9710.3110.950
27Shanxi (2)17.249 ***0.9860.2920.956
28Gansu22.188 ***0.9760.6620.750
29Qinghai10.139 ***0.9710.2560.967
30Ningxia10.833 ***0.9240.5460.838
31Xinjiang17.166 ***0.9590.6370.771
** and *** denote significance at the 5%, and 1% levels.
Table 2. Description and statistics of variables.
Table 2. Description and statistics of variables.
CategoryVariableDescriptionSourceExpected EffectMeanMedianMinMaxSD
Explained
Variable
RecoveryRecovery index of road traffic volumeMinistry of Transport of
the People’s Republic of China and authors computation
/54.03150.39215.288129.05619.277
Explanatory
Variables
THITHI indexNational Meteorological Administration of the People’s Republic of China+57.94659.22011.36381.53215.362
IncomeDisposable income per capitaNational Bureau of Statistics of the People’s Republic of China2914.4892557.0161447.3347182.9541175.549
EconomicGDP per capitaNational Bureau of Statistics of the People’s Republic of China6636.5355666.0432830.19016,542.8622956.007
COVID-19 CasesNumber of confirmed cases of COVID-19National Health Commission of the People’s Republic of China40.987601514121.636
Control
Variables
AQILevel of air pollutionNational Meteorological Administration of
the People’s Republic of China and authors computation
/2.5432151.104
SeasonSeasonal indexAuthors computation/0.2500010.434
Table 3. Spatial autocorrelation index.
Table 3. Spatial autocorrelation index.
MonthMoran’s IZ-Valuep-ValueSpatial Pattern
January−0.112−0.5800.562Random
February0.3262.6780.007Positive
March0.1261.2160.224Random
April0.2251.9920.046Positive
May0.1191.1290.259Random
June0.2702.2410.025Positive
July0.3001.5110.012Positive
August0.5444.6220.000Positive
September0.4433.7400.000Positive
October0.3332.7240.006Positive
November0.4063.3330.001Positive
December0.3312.7520.006Positive
Table 4. Tests of spatial panel models.
Table 4. Tests of spatial panel models.
TestsDistance Weight MatrixEconomic-Distance Weight Matrix
LM spatial lag49.752 ***18.782 ***
Robust LM spatial lag36.218 ***44.302 ***
LM spatial error28.911 ***8.136 ***
Robust LM spatial error15.377 ***33.656 ***
Wald spatial lag11.83715.448
Wald spatial error17.145 *18.487 **
LR spatial lag11.73115.198
LR spatial error17.327 *18.096 *
Hausman for SLM151.71 ***46.95 ***
Hausman for SDM76.53 ***108.49 ***
*, **, and *** denote significance at the 10%, 5%, and 1% levels.
Table 5. Empirical results of spatial panel models.
Table 5. Empirical results of spatial panel models.
VariablesSLMSDMDynamic SLMDynamic SDM
Model 1Model 2Model 3Model 4Model 5Model 6Model 7Model 8
COVID-19 Cases–0.018 **
(–2.289)
–0.016 **
(–2.010)
–0.018 **
(–2.207)
–0.015 *
(–1.867)
–0.019 **
(–2.383)
–0.018 **
(–2.144)
–0.018 **
(–2.222)
–0.016 *
(–1.941)
THI0.128 **
(2.561)
0.119 **
(2.322)
0.179 **
(2.564)
0.159 **
(2.255)
0.138 ***
(2.722)
0.127 **
(2.455)
0.185 ***
(2.647)
0.162 **
(2.303)
Income–0.396 ***
(–4.955)
–5.000 **
(–2.375)
–0.322 ***
(–3.621)
–5.110 **
(–2.373)
–0.377 ***
(–4.659)
–4.970 **
(–2.361)
–0.314 ***
(–3.522)
–5.076 **
(–2.357)
Economicn.a.–4.170 **
(–2.181)
n.a.–4.285 **
(–2.203)
n.a.–4.145 **
(–2.168)
n.a.–4.248 **
(–2.183)
Income × Economicn.a.0.536 **
(2.188)
n.a.0.561 **
(2.244)
n.a.0.535 **
(2.183)
n.a.0.557 **
(2.227)
AQI = 20.072 **
(2.145)
0.070 **
(2.082)
0.087 **
(2.470)
0.088 **
(2.514)
0.072 **
(2.137)
0.070 **
(2.091)
0.089 **
(2.511)
0.090 **
(2.550)
AQI = 30.132 ***
(3.043)
0.130 ***
(2.964)
0.141 ***
(2.878)
0.140 ***
(2.839)
0.126 ***
(2.887)
0.125 ***
(2.841)
0.140 ***
(2.874)
0.141 ***
(2.865)
AQI = 40.168 ***
(3.115)
0.166 ***
(3.045)
0.163 ***
(2.623)
0.159 **
(2.557)
0.152 ***
(2.781)
0.151 ***
(2.747)
0.160 ***
(2.581)
0.159 **
(2.560)
AQI = 50.249 ***
(3.667)
0.241 ***
(3.516)
0.244 ***
(3.043)
0.231 ***
(2.878)
0.221 ***
(3.148)
0.215 ***
(3.044)
0.239 ***
(2.987)
0.231 ***
(2.875)
Season–0.039
(–1.459)
–0.036
(–1.358)
–0.073
(–1.507)
–0.071
(–1.469)
–0.056 *
(–1.920)
–0.053 *
(–1.824)
–0.077
(–1.593)
–0.073
(–1.507)
W × COVID-19 casesn.a.n.a.–0.029
(–1.118)
–0.018
(–0.584)
n.a.n.a.–0.037
(–1.366)
–0.027
(–0.835)
W × THIn.a.n.a.–0.276
(–1.639)
–0.299 *
(–1.715)
n.a.n.a.–0.287 *
(–1.704)
–0.307 *
(–1.759)
W × Incomen.a.n.a.–0.548*
(–1.946)
–11.215
(–1.476)
n.a.n.a.–0.495 *
(–1.746)
–9.604
(–1.224)
W × Economicn.a.n.a.n.a.–9.701
(–1.430)
n.a.n.a.n.a.–8.255
(–1.178)
W × Income × Economicn.a.n.a.n.a.1.192
(1.396)
n.a.n.a.n.a.1.017
(1.156)
W × AQI2n.a.n.a.–0.377 *
(–1.661)
–0.460 **
(–2.029)
n.a.n.a.–0.369
(–1.627)
–0.447 **
(–1.968)
W × AQI3n.a.n.a.–0.324
(–1.282)
–0.454 *
(–1.776)
n.a.n.a.–0.354
(–1.396)
–0.459 *
(–1.799)
W×AQI4n.a.n.a.–0.338
(–1.312)
–0.459 *
(–1.768)
n.a.n.a.–0.388
(–1.491)
–0.478 *
(–1.834)
W × AQI5n.a.n.a.–0.366
(–1.332)
–0.499 *
(–1.793)
n.a.n.a.–0.441
(–1.576)
–0.531 *
(–1.890)
W × Seasonn.a.n.a.0.082
(0.831)
0.071
(0.726)
n.a.n.a.0.062
(0.625)
0.060
(0.608)
W × Recoveryit0.771 ***
(11.027)
0.777 ***
(11.256)
0.749 ***
(9.563)
0.751 ***
(9.620)
0.765 ***
(10.711)
0.771 ***
(10.913)
0.753 ***
(9.579)
0.752 ***
(9.604)
W × Recovery it–1n.a.n.a.n.a.n.a.0.148
(1.468)
0.149
(1.484)
0.149
(1.310)
0.099
(0.814)
R 2 0.2400.2450.2490.2700.2350.2390.2490.268
Log-likelihood114.086116.465118.267122.330114.590116.973118.604122.397
AIC–208.171–208.929–200.533–200.660–207.179–207.946–199.207–198.794
BIC–168.982–161.903–129.993–114.444–164.072–157.001–124.748–108.660
*, **, and *** denote significance at the 10%, 5%, and 1% levels.
Table 6. Robustness and endogeneity tests.
Table 6. Robustness and endogeneity tests.
VariablesSLMSDMDynamic SLMDynamic SDM
Model 9Model 10Model 11Model 12Model 13Model 14Model 15Model 16
COVID-19 Cases–0.021 **
(–2.412)
–0.021 **
(–2.318)
–0.020 **
(–2.334)
–0.022 **
(–2.407)
–0.021 **
(–2.451)
–0.022 **
(–2.401)
−0.020 **
(−2.341)
−0.022 **
(−2.440)
THI0.197 ***
(3.602)
0.184 ***
(3.265)
0.213 ***
(3.695)
0.190 ***
(3.183)
0.205 ***
(3.724)
0.190 ***
(3.368)
0.212 ***
(3.678)
0.188 ***
(3.142)
Income–0.498 ***
(–5.609)
–4.545 *
(–1.927)
–0.426 ***
(–4.643)
–4.373 *
(–1.860)
–0.490 ***
(–5.514)
–4.606 *
(–1.956)
−0.426 ***
(−4.642)
−4.397 *
(−1.870)
Economicn.a.–3.611 *
(–1.686)
n.a.–3.505
(–1.642)
n.a.–3.658 *
(–1.710)
n.a.−3.522 *
(−1.650)
Income × Economicn.a.0.471 *
(1.715)
n.a.0.457 *
(1.672)
n.a.0.479 *
(1.746)
n.a.0.459 *
(1.681)
AQI = 20.074 **
(1.976)
0.075 **
(1.978)
0.074 *
(1.957)
0.073 *
(1.928)
0.073 *
(1.955)
0.074 **
(1.972)
0.074 *
(1.957)
0.073 *
(1.927)
AQI = 30.156 ***
(3.205)
0.158 ***
(3.217)
0.146 ***
(2.972)
0.145 ***
(2.935)
0.149 ***
(3.054)
0.152 ***
(3.089)
0.146 ***
(2.978)
0.146 ***
(2.937)
AQI = 40.219 ***
(3.647)
0.222 ***
(3.662)
0.192 ***
(3.050)
0.192 ***
(3.033)
0.206 ***
(3.380)
0.209 ***
(3.415)
0.192 ***
(3.056)
0.192 ***
(3.035)
AQI = 50.338 ***
(4.484)
0.338 ***
(4.432)
0.294 ***
(3.797)
0.289 ***
(3.677)
0.317 ***
(4.124)
0.317 ***
(4.093)
0.295 ***
(3.802)
0.289 ***
(3.679)
Season−0.054 *
(−1.830)
−0.050 *
(−1.680)
−0.049
(−1.422)
−0.042
(−1.205)
−0.063 **
(−2.067)
−0.059 *
(−1.927)
−0.049
(−1.418)
−0.042
(−1.204)
W × COVID-19 Casesn.a.n.a.–0.079
(–1.106)
–0.081
(–1.092)
n.a.n.a.−0.088
(−1.115)
−0.101
(−1.204)
W × THIn.a.n.a.–0.272
(–0.585)
–0.176
(–0.377)
n.a.n.a.−0.263
(−0.564)
−0.156
(−0.333)
W × Incomen.a.n.a.–3.094 **
(–2.310)
50.928
(0.861)
n.a.n.a.−3.017 **
(−2.205)
52.267
(0.883)
W × Economicn.a.n.a.n.a.49.643
(0.909)
n.a.n.a.n.a.50.794
(0.930)
W × Income × Economicn.a.n.a.n.a.–6.266
(–0.911)
n.a.n.a.n.a.−6.400
(−0.930)
W × AQI2n.a.n.a.−1.662
(−1.167)
−1.174
(−0.772)
n.a.n.a.−1.665
(−1.169)
−1.183
(−0.775)
W × AQI3n.a.n.a.−1.519
(−1.049)
−1.059
(−0.682)
n.a.n.a.−1.512
(−1.044)
−1.064
(−0.684)
W × AQI4n.a.n.a.−0.876
(−0.608)
−0.391
(−0.248)
n.a.n.a.−0.846
(−0.582)
−0.387
(−0.246)
W × AQI5n.a.n.a.−0.775
(−0.514)
−0.221
(−0.134)
n.a.n.a.−0.708
(−0.454)
−0.200
(−0.119)
W × Seasonn.a.n.a.−0.222
(−0.913)
−0.246
(−1.011)
n.a.n.a.−0.212
(−0.833)
−0.242
(−0.950)
W × Recoveryit0.815 ***
(3.287)
0.824 ***
(3.341)
0.602 **
(2.146)
0.627 **
(2.244)
0.810 ***
(3.229)
0.820 ***
(3.284)
0.609 **
(2.168)
0.642 **
(2.297)
W × Recoveryit–1n.a.n.a.n.a.n.a.0.415
(1.340)
0.451
(1.456)
0.116
(0.267)
0.224
(0.506)
R 2 0.2260.2320.2470.2540.2270.2330.2460.252
*, **, and *** denote significance at the 10%, 5%, and 1% levels.
Table 7. Results of the mediating effect tests.
Table 7. Results of the mediating effect tests.
VariablesDistance Weight MatrixEconomic-Distance Weight Matrix
Model 17Model 18Model 19Model 8Model 20Model 21Model 22Model 16
COVID-19 Casesn.a.–0.023 ***
(–2.953)
n.a.–0.018 **
(–2.144)
n.a.–0.031 ***
(–3.526)
n.a.–0.022 **
(–2.401)
THI0.158 ***
(3.185)
n.a.–1.672 ***
(–5.063)
0.127 **
(2.455)
0.230 ***
(4.254)
n.a.–1.926 ***
(–6.307)
0.190 ***
(3.368)
Income–5.361 **
(–2.544)
–5.399 **
(–2.560)
20.853
(1.579)
–4.970 **
(–2.361)
–5.067 **
(–2.142)
–5.217 **
(–2.190)
21.656
(1.620)
–4.606 *
(–1.956)
Economic–4.567 **
(–2.390)
–4.418 **
(–2.303)
22.136 *
(1.847)
–4.145 **
(–2.168)
–4.159 *
(–1.939)
–4.028 *
(–1.859)
23.439 *
(1.933)
–3.658 *
(–1.710)
Income × Economic0.580 **
(2.366)
0.576 **
(2.345)
–2.431
(–1.582)
0.535 **
(2.183)
0.533 *
(1.935)
0.536 *
(1.933)
–2.536
(–1.630)
0.479 *
(1.746)
AQI = 20.068 **
(2.011)
0.065 *
(1.917)
0.137
(0.648)
0.070 **
(2.091)
0.071 *
(1.881)
0.066 *
(1.727)
0.136
(0.640)
0.074 **
(1.972)
AQI = 30.124 ***
(2.794)
0.111 **
(2.526)
0.149
(0.540)
0.125 ***
(2.841)
0.150 ***
(3.030)
0.131 ***
(2.638)
0.127
(0.456)
0.152 ***
(3.089)
AQI = 40.159 ***
(2.887)
0.121 **
(2.244)
−0.305
(−0.896)
0.151 ***
(2.747)
0.219 ***
(3.557)
0.163 ***
(2.688)
−0.318
(−0.922)
0.209 ***
(3.415)
AQI = 50.221 ***
(3.121)
0.161 **
(2.386)
−0.146
(−0.340)
0.215 ***
(3.044)
0.324 ***
(4.148)
0.233 ***
(3.133)
−0.134
(−0.309)
0.317 ***
(4.093)
Season−0.060 **
(−2.079)
−0.013
(−0.537)
0.499 ***
(2.975)
−0.053 *
(−1.824)
−0.070 **
(−2.324)
−0.001
(−0.035)
0.586 ***
(3.520)
−0.059 *
(−1.927)
W × Recoveryit0.778 ***
(11.152)
0.791 ***
(11.677)
n.a.0.771 ***
(10.913)
0.820 ***
(3.279)
0.845 ***
(3.408)
n.a.0.820 ***
(3.284)
W × Recoveryit–10.126
(1.255)
0.123
(1.222)
n.a.0.149
(1.484)
0.405
(1.298)
0.367
(1.172)
n.a.0.451
(1.456)
W × COVID-19 Casesitn.a.n.a.0.270 **
(2.328)
n.a.n.a.n.a.0.139
(0.502)
n.a.
W × COVID-19 Casesit–1n.a.n.a.0.038
(0.251)
n.a.n.a.n.a.–0.538
(–1.434)
n.a.
R 2 0.2240.2360.2020.2390.2200.2100.1870.233
*, **, and *** denote significance at the 10%, 5%, and 1% levels.
Table 8. Results of spatial–temporal effect decomposition.
Table 8. Results of spatial–temporal effect decomposition.
EffectsVariablesDistance Weight MatrixEconomic-Distance Weight Matrix
Model 5Model 6Model 13Model 14
Short TermLong Term Short TermLong Term Short TermLong Term Short TermLong Term
Direct
effect
COVID-9 Cases–0.021 **
(–2.518)
–0.023 *
(–1.922)
–0.020 **
(–2.252)
–0.022 *
(–1.898)
–0.022 ***
(–2.583)
–0.023 **
(–2.518)
–0.023 **
(–2.520)
–0.024 **
(–2.376)
THI0.155 ***
(2.984)
0.172 **
(2.401)
0.143 ***
(2.696)
0.160 **
(2.068)
0.213 ***
(3.996)
0.221 ***
(3.658)
0.198 ***
(3.634)
0.206 ***
(3.457)
Income –0.407 ***
(–4.655)
–0.461 ***
(–2.722)
–5.422 **
(–2.379)
–6.123 *
(–1.781)
–0.495 ***
(–5.502)
–0.514 ***
(–4.603)
–4.676 **
(–1.982)
–4.882 *
(–1.909)
Economicn.a.n.a.–4.524 **
(–2.187)
–5.112 *
(–1.674)
n.a.n.a.–3.714 *
(–1.735)
–3.879 *
(–1.685)
Income × Economicn.a.n.a.0.584 **
(2.202)
0.660 *
(1.686)
n.a.n.a.0.486 *
(1.772)
0.508 *
(1.717)
Indirect
effect
COVID-19 Cases–0.016 **
(–2.081)
–0.035
(–0.624)
–0.016 *
(–1.729)
–0.033
(–0.737)
–0.002 *
(–1.674)
–0.003
(–0.965)
–0.002
(–1.562)
–0.004
(–0.748)
THI0.119 **
(2.424)
0.245
(0.722)
0.115 **
(2.184)
0.235
(0.639)
0.018 *
(1.939)
0.035
(0.894)
0.017 **
(2.078)
0.034
(1.106)
Income–0.317 ***
(–2.876)
–0.696
(–0.725)
–4.420 *
(–1.812)
–9.380
(–0.591)
–0.040 **
(–2.149)
–0.080
(–0.873)
–0.403
(–1.476)
–0.828
(–0.835)
Economicn.a.n.a.–3.693 *
(–1.711)
–7.857
(–0.574)
n.a.n.a.–0.320
(–1.357)
–0.660
(–0.808)
Income × Economicn.a.n.a.0.477 *
(1.717)
1.014
(0.578)
n.a.n.a.0.042
(1.374)
0.086
(0.804)
Total
effect
COVID-19 Cases–0.036 **
(–2.413)
–0.058
(–0.880)
–0.036 **
(–2.079)
–0.055
(–1.011)
–0.024 **
(–2.570)
–0.026 **
(–2.284)
–0.025 **
(–2.488)
–0.027 **
(–1.999)
THI0.273 ***
(2.882)
0.417
(1.052)
0.258 ***
(2.588)
0.395
(0.915)
0.231 ***
(3.926)
0.256 ***
(2.866)
0.215 ***
(3.613)
0.240 ***
(2.952)
Income–0.724 ***
(–3.984)
–1.157
(–1.039)
–9.842 **
(–2.182)
–15.502
(–0.823)
–0.535 ***
(–5.395)
–0.594 ***
(–3.190)
–5.079 **
(–1.974)
–5.711 *
(–1.736)
Economicn.a.n.a.–8.217 **
(–2.024)
–12.969
(–0.795)
n.a.n.a.–4.034 *
(–1.730)
–4.538
(–1.560)
Income × Economicn.a.n.a.1.061 **
(2.035)
1.674
(0.801)
n.a.n.a.0.528 *
(1.766)
0.594
(1.583)
*, **, and *** denote significance at the 10%, 5%, and 1% levels.
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Zhang, J.; Zhao, S.; Peng, C.; Gong, X. Spatial Heterogeneity of the Recovery of Road Traffic Volume from the Impact of COVID-19: Evidence from China. Sustainability 2022, 14, 14297. https://doi.org/10.3390/su142114297

AMA Style

Zhang J, Zhao S, Peng C, Gong X. Spatial Heterogeneity of the Recovery of Road Traffic Volume from the Impact of COVID-19: Evidence from China. Sustainability. 2022; 14(21):14297. https://doi.org/10.3390/su142114297

Chicago/Turabian Style

Zhang, Jun, Shenghao Zhao, Chaonan Peng, and Xianming Gong. 2022. "Spatial Heterogeneity of the Recovery of Road Traffic Volume from the Impact of COVID-19: Evidence from China" Sustainability 14, no. 21: 14297. https://doi.org/10.3390/su142114297

APA Style

Zhang, J., Zhao, S., Peng, C., & Gong, X. (2022). Spatial Heterogeneity of the Recovery of Road Traffic Volume from the Impact of COVID-19: Evidence from China. Sustainability, 14(21), 14297. https://doi.org/10.3390/su142114297

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