The Impact of Investment Efficiency in the Digital Economy on Urban Waste Reduction: Evidence from China
Abstract
:1. Introduction
- Landfill disposal, a traditional waste management method, involves burying waste underground and relying on natural decomposition for disposal (Abdel-Shafy et al. [13]). While this method has relatively low processing costs, it is not without its issues. Landfill disposal requires significant land usage, and the leachate produced from waste decomposition can potentially contaminate groundwater, thus affecting the ecological environment (Parvin et al. [14]).
- Incineration offers higher waste reduction and harmlessness effects. Through high-temperature incineration, harmful organisms such as viruses and bacteria in the waste are eliminated, thereby reducing the risk of pandemic spread (Zu et al. [15]). Additionally, incineration can significantly reduce waste volume and alleviate pressure on land use (Makarichi et al. [16]).
2. Related Works
2.1. Digital Economy
2.2. Waste Treatment
2.3. Urban Development and Urban Waste
3. Model Setting
3.1. Sample Description
- An in-depth examination of the ‘total_treatment’ metric reveals a high average value coupled with a notable standard deviation, indicating a certain degree of variability and fluctuation in the overall treatment level. This observed variability can likely be attributed to factors such as disparities in economic development levels and varying degrees of policy implementation effectiveness across China’s diverse regions.
- Moreover, the minimum values of the ‘landfill’ and ‘burn’ indicators being zero highlights the existence of regions or time points where the amount of waste sent to landfills or incinerated is minimal, thus shedding light on regional disparities in waste management practices in China. This apparent imbalance can be tentatively linked to differences in urbanization levels, waste generation rates, and treatment capacities among various regions. Conversely, the relatively high maximum values recorded for these two indicators suggest that certain areas have achieved commendable levels of waste processing, which could be correlated with the level of economic activity and population concentration in those regions.
- Furthermore, the uniformly low values of the ‘dig_econ’ indicator underscore the considerable untapped potential for the growth and development of China’s digital economy. Given the increasingly prominent role that the digital economy plays in the global economic landscape, this represents an opportune and strategic direction for China’s future economic expansion.
- Lastly, the substantial standard deviations observed in the ‘consumption’ and ‘GDP’ indicators unveil noteworthy disparities in consumption levels and economic development across China’s vast regions. These disparities, while significant, can be rationalized by the considerable geographical differences and variations in natural environments, economic conditions, and policy landscapes that exist among regions.
3.2. Study Design
- Firstly, the digital economy is a complex system that involves multiple input and output factors. The DEA model is capable of handling situations with multiple inputs and outputs, thereby providing a comprehensive evaluation of the efficiency of digital economy infrastructure investment by considering these multiple factors. This capability makes the DEA model a suitable and comprehensive tool for assessing the digital economy.
- Secondly, as a non-parametric method, the DEA model does not require the pre-setting of production functions or the assumption of specific functional forms. This enhances the flexibility of the DEA model in practical applications and allows it to better adapt to the complexity and dynamics of the digital economy. Consequently, the DEA model accurately estimates investment efficiency.
- Thirdly, the DEA model can identify the efficiency frontier, also known as the best practice frontier, of decision-making units (DMUs) and the gaps between each DMU and the efficiency frontier. This capability enables decision-makers to gain a clear understanding of the efficiency level of digital economy infrastructure investment and identify the causes of inefficiency, as well as the direction for improvement. Moreover, by comparing the performance of different DMUs, the DEA model promotes cross-learning and benchmarking among industries, thereby fostering overall efficiency improvement.
4. Empirical Analysis
4.1. Baseline Results
4.2. Robustness Analysis
4.3. Heterogeneity Analysis
4.4. Endogeneity Analysis
4.5. Effect of Investment Efficiency in the Digital Economy
5. Conclusions and Perspective
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Acknowledgments
Conflicts of Interest
References
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Variable Name | Variable Description |
---|---|
(million tons) | Dependent variable representing the total amount of waste treated at unit i during time t. |
(million tons) | Dependent variable representing the amount of waste incinerated at unit i during time t. |
(million tons) | Dependent variable representing the amount of waste landfilled at unit i during time t. |
Index measuring the level of digital economic activity at unit i during time t. | |
Time dummy variable indicating the onset of the COVID-19 pandemic at time t. | |
Measure of economic activity, typically the Gross Domestic Product (GDP), at unit i during time t. | |
Total retail sales at unit i during time t. | |
Population density representing the number of individuals per unit area at unit i during time t. | |
Level of industrialization, measured as the industrial value-added as a percentage of GDP at unit i during time t. | |
Level of urbanization, representing the proportion of the population living in cities at unit i during time t. | |
Level of environmental regulation, measured as the ratio of investment in industrial pollution control to industrial value-added at unit i during time t. |
Count | Mean | Std | Min | 50% | Max | |
---|---|---|---|---|---|---|
Total_treatment | 330 | 6.440 | 5.197 | 0.576 | 4.918 | 33.457 |
Landfill | 330 | 3.410 | 2.570 | 0.000 | 2.997 | 17.394 |
Burn | 290 | 3.207 | 3.766 | 0.000 | 1.704 | 25.541 |
dig_econ | 330 | 0.119 | 0.108 | 0.009 | 0.084 | 0.647 |
Consumption | 330 | 10,541.159 | 8791.169 | 413.400 | 8120.750 | 44,187.700 |
GDP | 330 | 26,676.287 | 21,734.437 | 1670.440 | 20,094.000 | 124,370.000 |
Popu_density | 330 | 473.307 | 704.845 | 7.864 | 292.897 | 3925.870 |
Indu | 330 | 0.321 | 0.082 | 0.273 | 0.378 | 0.556 |
City | 330 | 0.596 | 0.121 | 0.511 | 0.656 | 0.896 |
Regu | 330 | 0.003 | 0.004 | 0.001 | 0.004 | 0.031 |
Total_Treatment | Burn | Landfill | |
---|---|---|---|
(1) | (2) | (3) | |
dig_econ | 0.410 *** | 0.314 *** | 0.312 *** |
(0.047) | (0.066) | (0.081) | |
dig_econ × T | −0.130 *** | 0.159 *** | −0.560 *** |
(0.039) | (0.054) | (0.103) | |
Constant | 0.065 ** | −0.180 *** | 0.187 ** |
(0.031) | (0.050) | (0.081) | |
Controls | Yes | Yes | Yes |
Province | Yes | Yes | Yes |
Observations | 330 | 290 | 330 |
R2 | 0.933 | 0.870 | 0.516 |
Adjusted R2 | 0.935 | 0.877 | 0.502 |
Total_Treatment | Burn | Landfill | ||||
---|---|---|---|---|---|---|
High | Low | High | Low | High | Low | |
dig_econ × T | 0.269 *** | −0.361 *** | 0.173 * | 0.212 * | 0.272 * | −1.02 *** |
(0.070) | (0.091) | (0.095) | (0.121) | (0.133) | (0.245) | |
Constant | −0.254 ** | 0.025 | 0.195 | −0.106 ** | 0.280 | 0.025 |
(0.157) | (0.031) | (0.213) | (0.049) | (0.296) | (0.083) | |
Controls | Yes | Yes | Yes | Yes | Yes | Yes |
Province | Yes | Yes | Yes | Yes | Yes | Yes |
R2 | 0.950 | 0.933 | 0.935 | 0.850 | 0.421 | 0.565 |
Adjusted R2 | 0.935 | 0.931 | 0.915 | 0.845 | 0.245 | 0.551 |
Total_Treatment | ||
---|---|---|
dig_econ × T | Total_Treatment | |
First Stage | Second Stage | |
dig_econ × T | −0.7016 *** | |
(0.230) | ||
Tele | 0.0885 ** | |
(0.031) | ||
Constant | 0.0161 | −0.1610 *** |
(0.038) | (0.024) | |
Controls | Yes | Yes |
Province | Yes | Yes |
R2 | 0.298 | 0.917 |
Adjusted R2 | 0.283 | 0.915 |
Total_Treatment | Burn | Landfill | |
---|---|---|---|
(1) | (2) | (3) | |
Rate | 0.0447 ** | −0.0945 ** | 0.1859 *** |
(0.021) | (0.032) | (0.099) | |
Constant | −1.0536 *** | −0.3583 *** | −0.0363 |
(0.024) | (0.040) | (0.062) | |
Controls | Yes | Yes | Yes |
Year | Yes | Yes | Yes |
Province | Yes | Yes | Yes |
Observations | 330 | 290 | 330 |
R2 | 0.916 | 0.840 | 0.374 |
Adjusted R2 | 0.914 | 0.836 | 0.360 |
Total_Treatment | ||
---|---|---|
Rate | Total_Treatment | |
First Stage | Second Stage | |
Rate | 0.8154 *** | |
(0.238) | ||
patent | 0. 1818 * | |
(0.103) | ||
Constant | 0.2689 *** | −0.3115 *** |
(0.099) | (0.049) | |
Controls | Yes | Yes |
Year | Yes | Yes |
Province | Yes | Yes |
R2 | 0.254 | 0.916 |
Adjusted R2 | 0.234 | 0.913 |
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Feng, H.; Li, Y.; Mu, R.; Wu, L. The Impact of Investment Efficiency in the Digital Economy on Urban Waste Reduction: Evidence from China. Sustainability 2023, 15, 16731. https://doi.org/10.3390/su152416731
Feng H, Li Y, Mu R, Wu L. The Impact of Investment Efficiency in the Digital Economy on Urban Waste Reduction: Evidence from China. Sustainability. 2023; 15(24):16731. https://doi.org/10.3390/su152416731
Chicago/Turabian StyleFeng, Hui, Yirong Li, Renyan Mu, and Lei Wu. 2023. "The Impact of Investment Efficiency in the Digital Economy on Urban Waste Reduction: Evidence from China" Sustainability 15, no. 24: 16731. https://doi.org/10.3390/su152416731