Analysis of Nitrogen Dioxide Concentration at Highway Toll Stations Based on fsQCA—Data Sourced from Sentinel-5P
Abstract
:1. Introduction
2. Data and Methods
2.1. Study Area
2.2. Data Sources
2.3. Measurement of Variables in fsQCA
2.3.1. Outcome Variable
2.3.2. Conditional Variables
Region Area
Number of COVID-19 Infections
Average Temperature During Holidays
Number of Holiday Days
The Number of Family Cars
2.3.3. Conditional Variable Data Processing
2.4. Data Calibration
3. Results and Discussion
3.1. Necessity Analysis
3.2. Results of the fsQCA
3.2.1. Combined Effects of COVID-19 Infections and Family Cars
3.2.2. Combined Effects of Region Area and COVID-19 Infections
3.2.3. Combined Effects of Region Area and Family Cars
3.3. Robustness Analysis
4. Conclusions and Implications
4.1. Conclusions
- The combined impact of the number of COVID-19 infections and family cars is analyzed, revealing that the implementation of lockdown policies during the COVID-19 pandemic had a significant effect on highway toll stations. Strict inspection measures led to a substantial increase in vehicle waiting times at toll booths. Simultaneously, the pandemic induced changes in public travel preferences, with family cars becoming the primary mode of transportation. This shift resulted in a sharp increase in the number of family cars at highway toll stations. The combined effect of these two factors caused a significant rise in NO2 concentration at highway toll stations.
- Under the combined effects of region area and number of COVID-19 infections, it was found that lockdown policies during the COVID-19 pandemic significantly restricted public travel, leading to a reduction in the number of family cars. In cities with larger land areas, due to their vast geographic scope and better air circulation conditions, air pollutants were found to disperse more easily. The synergy of these factors led to an overall reduction in NO2 concentration at highway toll stations.
- Through an in-depth analysis of the interaction between the region area and the number of family cars, it was discovered that cities with larger land areas often possess more complex transportation networks. Diverse modes of transportation and a trend towards economical transport vehicles were identified in these cities. Notably, the proportion of semi-trailers, heavy trucks, and other large vehicles increases significantly in larger cities. While these vehicles improve transportation efficiency, their larger engine sizes allow for greater fuel storage, primarily powered by diesel. However, NO2 emissions released during diesel combustion are significantly higher compared to family cars. Despite the reduction in the number of family cars during the pandemic, emissions from large vehicles were relatively greater. The combined effect led to an increase in NO2 concentration at highway toll stations.
4.2. Implications
- The promotion of ETC system adoption is critically important. Increasing the penetration of ETC devices and raising the proportion of ETC lanes can effectively reduce vehicle retention times at manual toll lanes, thereby lowering exhaust emissions. In addition, it is necessary to optimize the layout of public transportation networks and improve their service quality to enhance their appeal. This can encourage the public to prioritize green travel options. These measures will help further alleviate traffic congestion and mitigate environmental pollution issues.
- To further improve air quality, cities should focus on establishing an efficient air quality monitoring system, promoting the concept of a simple, moderate, green, and low-carbon lifestyle, and popularizing clean energy vehicles, thereby reducing the impact of tailpipe emissions on air quality.
- It is significant that the transportation structure be optimized to reduce reliance on large vehicles, transportation routes be refined, logistics efficiency be improved, and empty or inefficient vehicle trips be minimized. Furthermore, it is essential to enhance environmental standards for large vehicles. More stringent diesel vehicle emissions standards should be formulated and implemented, along with regular inspections of large vehicles to ensure compliance with environmental requirements.
4.3. Limitations and Future Work
Author Contributions
Funding
Institutional Review Board Statement
Informed Consent Statement
Data Availability Statement
Conflicts of Interest
References
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Area | Xiasha | Ningbo | Wenzhou | Jiaxing | Quzhou |
---|---|---|---|---|---|
Mean | 2.97 | 1.56 | 0.95 | 1.84 | 1.11 |
Standard deviation | 6.04 | 1.49 | 0.83 | 2.25 | 1.26 |
Minimum | 0.08 | 0.04 | 0.08 | 0.08 | 0 |
Maximum | 95.02 | 15.61 | 8.52 | 28.23 | 11.81 |
Holiday | Year | Date |
---|---|---|
New Year’s Day | 2019 | 1–3 January |
2020 | 1–3 January | |
2021 | 1–3 January | |
2022 | 1–3 January | |
2022–2023 | 30 December 2022–1 January 2023 | |
Spring Festival | 2019 | 5–11 February |
2020 | 25–31 January | |
2021 | 12–17 February | |
2022 | 1–7 February | |
2023 | 22–28 January | |
Qingming Festival | 2019 | 4–6 April |
2020 | 4–6 April | |
2021 | 4–6 April | |
2022 | 3–5 April | |
2023 | 4–6 April | |
Labor Day | 2019 | 1–5 May |
2020 | 1–5 May | |
2021 | 1–5 May | |
2022 | 30 April–4 May | |
2023 | 1–5 May | |
Dragon Boat Festival | 2019 | 6–8 June |
2020 | 12–14 June | |
2021 | 12–14 June | |
2022 | 3–5 June | |
2023 | 21–23 June | |
National Day | 2019 | 1–7 October |
2020 | 1–7 October | |
2021 | 1–7 October | |
2022 | 1–7 October | |
2023 | 1–7 October |
Variable Type | Variables | Data Volume | Unit |
---|---|---|---|
Condition variable | Region area | 5 | Square kilometers |
COVID-19 infections | 5 | Ten thousand people | |
Holiday days | 6 | Days | |
Average temperature | 6 | Celsius | |
Family cars | 9593 | Vehicles | |
Result variable | NO2 | 2399 | ppb |
Variable Abbreviation | Region Area | COVID-19 Infections | Holiday Days | Average Temperature | Family Cars |
---|---|---|---|---|---|
Mean | 10,182 | 3598 | 5 | 17 | 15,437 |
Standard deviation | 4122 | 4501 | 2 | 8 | 12,196 |
Minimum | 4237 | 0 | 3 | 6 | 1002 |
Maximum | 16,853 | 9929 | 7 | 26 | 71,307 |
Variables | Full Membership | Crossover Point | Full Non-Membership |
---|---|---|---|
Region area | 16,853 | 9365 | 4237 |
COVID-19 infections | 9929 | 13 | 0 |
Holiday days | 7 | 4 | 3 |
Average temperature | 26 | 20 | 6 |
Family cars | 33,618 | 11,305 | 2215 |
Variables | Consistency | Coverage |
---|---|---|
Region area | 0.71 | 0.60 |
~Region area | 0.63 | 0.59 |
COVID-19 infections | 0.70 | 0.56 |
~COVID-19 infections | 0.58 | 0.59 |
Holiday days | 0.52 | 0.51 |
~Holiday days | 0.64 | 0.53 |
Average temperature | 0.50 | 0.45 |
~Average temperature | 0.80 | 0.70 |
Family cars ~Family cars | 0.60 0.68 | 0.54 0.60 |
Conditions | C1 | C2 | C3 | C4 | C5 | C6 |
---|---|---|---|---|---|---|
Region area | ⊗ | ● | ⊗ | ● | ||
COVID-19 infections | ⊗ | ⊗ | ● | ● | ||
Holiday days | ⊗ | ⊗ | ⊗ | ⊗ | ⊗ | ⊗ |
Average temperature | ⊗ | ⊗ | ⊗ | ⊗ | ⊗ | ⊗ |
Family cars | ⊗ | ⊗ | ● | ● | ||
Raw Coverage | 0.274 | 0.246 | 0.303 | 0.294 | 0.323 | 0.321 |
Unique Coverage | 0.005 | 0.003 | 0.012 | 0.006 | 0.011 | 0.010 |
Overall Consistency | 0.841 | |||||
Overall Coverage | 0.485 |
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Xu, S.; Yang, X. Analysis of Nitrogen Dioxide Concentration at Highway Toll Stations Based on fsQCA—Data Sourced from Sentinel-5P. Atmosphere 2025, 16, 517. https://doi.org/10.3390/atmos16050517
Xu S, Yang X. Analysis of Nitrogen Dioxide Concentration at Highway Toll Stations Based on fsQCA—Data Sourced from Sentinel-5P. Atmosphere. 2025; 16(5):517. https://doi.org/10.3390/atmos16050517
Chicago/Turabian StyleXu, Shenghao, and Xinxiang Yang. 2025. "Analysis of Nitrogen Dioxide Concentration at Highway Toll Stations Based on fsQCA—Data Sourced from Sentinel-5P" Atmosphere 16, no. 5: 517. https://doi.org/10.3390/atmos16050517
APA StyleXu, S., & Yang, X. (2025). Analysis of Nitrogen Dioxide Concentration at Highway Toll Stations Based on fsQCA—Data Sourced from Sentinel-5P. Atmosphere, 16(5), 517. https://doi.org/10.3390/atmos16050517