Submitted:
20 October 2023
Posted:
24 October 2023
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Abstract
Keywords:
1. Introduction
1.1. Greenhouse Gas Emissions in Oman
- Energy Production: The energy sector is a significant contributor to greenhouse gas emissions in Oman. The country heavily relies on oil and natural gas to generate electricity and fuel its industry, which results in the combustion of fossil fuels in power plants and industrial processes, releasing significant amounts of carbon dioxide (CO2) into the atmosphere.
- Transportation: Oman's growing economy and population have led to an increase in the number of vehicles on the road, resulting in gasoline- and diesel-powered vehicles being the major sources of CO2 emissions. The lack of a well-developed public transportation system also contributes to the reliance on private vehicles.
- Industrial Processes: Industrial activities, such as petrochemical production, cement manufacturing, and metal smelting, release greenhouse gases as byproducts of their operation. These emissions include CO2 and other gases like methane (CH4) and nitrous oxide (N2O).
- Waste management plays a crucial role in reducing methane emissions. The improper disposal of solid waste in landfills can result in anaerobic decomposition of organic materials, leading to the generation of methane. Conversely, adopting appropriate waste management and recycling practices can help to minimize these emissions.
- Agriculture is a significant contributor to greenhouse gas emissions in Oman, particularly from methane emissions resulting from enteric fermentation in livestock and rice cultivation. Nitrous oxide emissions can also arise from the application of synthetic fertilizers in agriculture.
- Land use changes, such as deforestation and urbanization, can lead to a decline in carbon sinks and the release of stored carbon into vegetation and soils. This reduction in carbon sinks can have a significant impact on the environment and climate.
- Wastewater management systems can contribute to greenhouse gas emissions if not properly managed. Improved wastewater management systems can help to reduce methane emissions and improve overall environmental health.
- Natural factors, such as wildfires, dust storms, and geological emissions, can also release greenhouse gases into the atmosphere. However, these events are exacerbated by climate change

1.2. Causes of Air Pollution in Oman
- Industrial Emissions: Industrial activities, including oil and gas extraction, petrochemical manufacturing, and other heavy industries, release various pollutants into the air. These emissions can include sulfur dioxide (SO2), nitrogen oxides (NOx), particulate matter, and volatile organic compounds (VOCs).
- Vehicle Emissions: The increasing number of vehicles on the road contributes to air pollution. Diesel and gasoline vehicles emit pollutants such as carbon monoxide (CO2), NOx, VOCs, and particulate matter.
- Construction and Infrastructure Development: Rapid urbanization and construction projects can lead to dust and particulate matter in the air. These particles can cause respiratory problems and reduce air quality.
- Natural Sources: Dust storms, especially in the arid climate of Oman, can contribute significantly to air pollution. Dust and sand particles are lifted into the air and can affect air quality when they settle.
- Maritime Transport: Oman's strategic location near the Arabian Sea and the Gulf of Oman means it has a significant shipping industry. Ship emissions can include sulfur dioxide, NOx, and particulate matter, affecting coastal air quality.
- Waste Management: Inefficient waste disposal and open burning of trash can release pollutants into the air. This is especially a concern in some less-developed areas.
- Oil and Gas Operations: Oman is a major oil and gas producer, and the extraction and processing of these resources can release pollutants and greenhouse gases into the atmosphere.
- Refineries and Petrochemical Plants: The processing of oil and natural gas in refineries and petrochemical plants can release various pollutants into the air.
- Agricultural Activities: The use of fertilizers and pesticides in agriculture can release ammonia (NH3) and other chemicals into the atmosphere.
- Power Generation: The combustion of fossil fuels for electricity generation can release pollutants into the air. Oman is working to diversify its energy sources, including through renewable energy projects, to reduce this source of pollution.
2. Related Literature
2.1. Economic Growth and Air Pollution
2.2. Urbanization and Air Pollution
2.3. Energy consumption and Air Pollution
3. Model Specification and Data
| Variable | Definition | Codes of Variable | Source |
| Dependent Variable | Real GDP at constant 2011 national prices (in mil. 2011US$) | RGDPc | PWT 10.0* |
| Independent Variables | CO2 emissions (metric tons per capita) Nitrous oxide emissions (thousand metric tons of CO2 equivalent) | CO2N2O | WDI, 2022WDI, 2022 |
| Control Variables | Urban population (% of the total population) | URBN | WDI, 2022 |
| Energy use (kg of oil equivalent per capita | ENGU | WDI, 2022 |
4. Results and Discussion
4.1. Descriptive Statistics
4.2. DOLS estimates
4.3. Unit Root Test
4.4. Cointegration test results
4.4.1. Results of Johansen Cointegration test
4.4.2. Results of Granger-Causality Tests
5. Conclusions and policy implications
Acknowledgments
Conflicts of Interest
References
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| Variables | Mean | Median | Maximum | Minimum | Std. Dev. | CV* |
| Ln RGDPC | 18747.86 | 19189.55 | 21458.39 | 14792.32 | 1740.012 | 9.281123286 |
| Ln CO2 | 12.5148 | 13.0604 | 17.30974 | 6.566793 | 3.623088 | 28.95042669 |
| Ln N2O | 703.4375 | 655 | 1090 | 340 | 265.1671 | 37.69590049 |
| Ln URP | 75.26406 | 72.6835 | 87.044 | 66.102 | 5.698879 | 7.571846377 |
| Ln ENGU | 126.1235 | 122.4913 | 181.8656 | 76.75578 | 39.29334 | 31.15465397 |
| Variables | RGDPC | CO2 | N2O | URBN | ENGU |
| Ln RGDPC | 1 | ||||
| Ln CO2 | 0.241857 | 1 | |||
| Ln N2O | -0.096951 | 0.915519 | 1 | ||
| Ln URP | -0.316633 | 0.762638 | 0.94191 | 1 | |
| Ln ENGU | 0.056571 | 0.893628 | 0.89911 | 0.747322 | 1 |
| Dependent Variable: RGDPC | ||||
| Sample: 1990 2021 | ||||
| Included observations: 32 | ||||
| Variable | Coefficient | Std. Error | t-Statistic | Prob. |
| Ln CO2 | 1164.263 | 145.1280 | 8.022319 | 0.0000 |
| Ln N2O | -21.55100 | 1.961402 | -10.98754 | 0.0000 |
| Ln URP | 236.2125 | 11.94890 | 19.76856 | 0.0000 |
| Ln ENGU | 12.30533 | 12.52318 | 0.982604 | 0.3342 |
| R-squared | 0.632001 | Mean dependent var | 18747.86 | |
| Adjusted R-squared | 0.592572 | S.D. dependent var | 1740.012 | |
| S.E. of regression | 1110.651 | Akaike info criterion | 16.97975 | |
| Sum squared resid | 34539276 | Schwarz criterion | 17.16297 | |
| Log likelihood | -267.6760 | Hannan-Quinn criter. | 17.04048 | |
| Durbin-Watson stat | 0.868178 | |||
| Dependent Variable: N2O | ||||
| Sample: 1990 2021 | ||||
| Included observations: 32 | ||||
| Variable | Coefficient | Std. Error | t-Statistic | Prob. |
| Ln RGDPC | 0.149294 | 0.020395 | 7.320290 | 0.0000 |
| Ln RGDPC2 | -3.81E-06 | 6.92E-07 | -5.511561 | 0.0000 |
| Ln CO2 | 27.15082 | 5.716932 | 4.749195 | 0.0001 |
| Ln URP | 21.56324 | 2.447204 | 8.811379 | 0.0000 |
| Ln ENGU | 1.490693 | 0.361947 | 4.118538 | 0.0003 |
| R-squared | 0.986968 | Mean dependent var | 703.4375 | |
| S.E. of regression | 32.43592 | Akaike info criterion | 9.939011 | |
| Sum squared resid | 28406.40 | Schwarz criterion | 10.16803 | |
| Log-likelihood | -154.0242 | Hannan-Quinn criter. | 10.01492 | |
| Durbin-Watson stat | 0.875121 | |||
| Variables | LevelCritical Values | First DifferenceCritical Values | ||||||||
| 1% | 5% | 10% | t-values | p-values | 1% | 5% | 10% | t-values | p-values | |
| Ln CO2 | -3.662 | -2.96 | -2.612 | -2.6192 | 0.4791 | -3.670 | -2.964 | -2.621 | -4.88688 | 0.0004* |
| Ln N2O | -3.6617 | -2.960 | -2.6192 | 0.013780 | 0.9529 | -3.6702 | -2.9640 | -2.612 | -4.445660 | 0.0014* |
| Ln RGDPc | -3.6702 | -2.9640 | -2.621 | -0.902244 | 0.7735 | -3.6892 | -2.9719 | -2.6251 | -6.875273 | 0.0000** |
| Ln URP | -3.6892 | -2.9719 | -2.6251 | 2.556510 | 1.0000 | -3.6892 | -2.972 | -2.6251 | -3.048164 | 0.0421** |
| Ln ENRU | -3.6892 | -2.9719 | -2.6251 | -0.822161 | 0.7972 | -3.679 | -2.9678 | -2.6229 | -5.727279 | 0.0001* |
| Lag | LogL | LR | FPE | AIC | SC | HQ |
| 0 | 23.02299 | NA | 6.60e-05 | -1.112388 | -0.980428 | -1.066331 |
| 1 | 124.4002 | 180.2262 | 3.91e-07 | -6.244458 | -5.716618* | -6.060227 |
| 2 | 128.8578 | 7.181681 | 5.09e-07 | -5.992102 | -5.068382 | -5.669699 |
| 3 | 145.3521 | 23.82506* | 3.46e-07* | -6.408450* | -5.088851 | -5.947875* |
| Hypothesized | Trace | 0.05 | ||
| No. of CE(s) | Eigenvalue | Statistic | Critical Value | Prob.** |
| None * | 0.657911 | 84.88720 | 69.81889 | 0.0020 |
| At most 1 * | 0.512398 | 52.70670 | 47.85613 | 0.0163 |
| At most 2 * | 0.409125 | 31.15902 | 29.79707 | 0.0346 |
| At most 3 | 0.255103 | 15.37452 | 15.49471 | 0.0521 |
| At most 4 * | 0.195855 | 6.539257 | 3.841466 | 0.0105 |
| Trace test indicates 3 cointegrating eqn(s) at the 0.05 level | ||||
| * Denotes rejection of the hypothesis at the 0.05 level | ||||
| **MacKinnon-Haug-Michelis (1999) p-values | ||||
| Error Correction: | D(N2O) | D(CO2) | D(RGDPC) | D(RGDPC2) | D(URP) | D(ENGU) |
| CointEq1 | -0.149294 | -0.008377 | -5.620052 | -215635.7 | 0.001124 | 0.096518 |
| (0.020395) | (0.00216) | (2.11362) | (82262.9) | (0.00092) | (0.06386) | |
| [-7.320290] | [-3.88557] | [-2.65897] | [-2.62130] | [ 1.21631] | [ 1.51144] |
| Variables | F-Stat. | p-value | Causality |
| RGDPc → N2 O | 4.647 | 0.0192 | Yes |
| N2O → RGDPc | 3.099 | 0.0628 | No |
| ENGU → CO2 | 16.149 | 0.000 | Yes |
| CO2 → ENGU | 11.583 | 0.0003 | Yes |
| URP → RGDPc | 4.281 | 0.0252 | Yes |
| RGDPc → URP | 4.363 | 0.0237 | Yes |
| URP → CO2 | 0.82434 | 0.4501 | No |
| CO2 → URP | 5.92209 | 0.0078 | Yes |
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