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Article

The United States Energy Consumption and Carbon Dioxide Emissions: A Comprehensive Forecast Using a Regression Model

by
Krishnamurthy Baskar Keerthana
1,
Shih-Wei Wu
2,*,
Mu-En Wu
1 and
Thangavelu Kokulnathan
3
1
Department of Information and Financial Management, College of Management, National Taipei University of Technology, Taipei 10608, Taiwan
2
Department of Business Management, College of Management, National Taipei University of Technology, Taipei 10608, Taiwan
3
Department of Electro-Optical Engineering, National Taipei University of Technology, Taipei 10608, Taiwan
*
Author to whom correspondence should be addressed.
Sustainability 2023, 15(10), 7932; https://doi.org/10.3390/su15107932
Submission received: 7 April 2023 / Revised: 7 May 2023 / Accepted: 11 May 2023 / Published: 12 May 2023
(This article belongs to the Section Energy Sustainability)

Abstract

:
The Earth’s climate change, colloquially known as global warming, is detrimental to life across the globe. The most significant contributor to the greenhouse gas (GHG) effect is carbon dioxide (CO2) emission. In the United States (US) economy, the major benefactor of CO2 emissions is the energy sector, with the top contribution coming from fossil fuels. The estimated 2020 CO2 emission was 5981 million metric tons, despite a dramatic reduction in the trendline compared to the year 2019. An ultimatum for energy consumption rises from fiscal development, growing population, and technological advancements. Energy use and GHG emissions are inclined upward, provoking an unwholesome nation. This paper studies (i) the principal sources of energy use and CO2 emission, (ii) the inclination of such sources, (iii) trends and drivers of GHG emissions, (iv) low carbon development and carbon footprint, and (v) the diverse US projects for reducing GHG emissions and the challenges in deploying them. We have forecasted the emissions from fossil fuels from 2025 to 2050 and compared the results using MAPE to calculate the mean percentage error. The forecasted results of 2050 show high accuracy, suggesting probable approaches to reduce further CO2 emissions, measures to reduce emissions through carbon capture and sequestration, and help in the development of improved GHG mitigations for the nation.

1. Introduction

Climate change has become a severe problem of the era. According to data from NASA and the National Oceanic and Atmospheric Administration (NOAA), each successive decade since the 1980s has been warmer than the one before it, and the 2010s were no exception [1]. In 2019, the average global temperature was about 18 °F higher than the average temperature from the late 1800s, in which more than 80% of the energy produced is from fossil fuels-related greenhouse gas (GHG) emissions [2]. The Intergovernmental Panel on Climate Change (IPCC) shows a trend line that likely eases heat to 35.6 °F quite likely by 2100, with over 39.2 °F warming feasible. Rising temperatures can disrupt the ecosystem, upend long-standing climate norms, and peril all life [3,4]. Eradicating such actions that result in catastrophic damage has been the work of habitats for a long while. Due to heat holding ability, carbon footprint has become a revolutionary cause of global warming and a threat to the environment [5]. Substantially, if a country urges to have a consistent produce avoiding the traumatic effects of climate change, sharper and deeper cuts in GHG emissions are a demand for all energy-related sectors [6].
The primary gases contributing to such devastations include carbon dioxide (CO2), methane (CH4), nitrous oxide (N2O), and sulfur hexafluoride (SF6) produced by man-made activities, such as burning fossil fuels to generate electricity, power buildings, and deforestation [7,8]. Precisely, midst the other gases, CO2 reports >80% emissions, thus always manifested [9,10,11]. Globally, fossil fuel-related CO2 emissions (FFCO2) had a fall to 36 Gt in 2020, which is approximately 5.1% below that of 2019 emissions. With the 50-year global data comparison from 1970 to 2020, the huge reduction in FFCO2 was from the transport sector with almost 12%, and the per capita FFCO2 returned to 2005 levels of about 4.6 t CO2/capita [12]. Especially in the US, FFCO2 declined by 1.1% in 2017 but amplified by 3.1% in 2018 and again dropped to 2.4% in 2019, subsequently diminishing to 9.9% in 2020. On average, total FFCO2 accounted for 4.5 Gt with almost 94% shares from the combustion sources. The 2020 fall owes to falls in oil with 12.6% and coal with 19.1%; the population increase was over 12% compared to 2005 peaks. This warning in the FFCO2 emissions has roots in the reduction in coal consumption [13].
Considering all the emissions scenarios, the global temperature is said to continue uptrend for at least until mid-century [14]. According to IPCC-2021, unless deep reductions in CO2 and other GHG happen, the 2 °C global warming is expected to overdo during the 21st century [15]. Subsequently, since the early 19th century, the main cause of the climate crisis has been energy systems. Of these, total CO2 emissions have accounted for almost 90% of all the other gases, while total GHG is reported for about 75% [16]. Coal’s share of the global electric power output is the highest at 36.37%, making it the most used fossil fuel for power generation, followed by natural gas (23.32%) and oil (3.05%). Fossil fuels together account for 62.75% of the total electricity generated worldwide, as shown in Figure 1A,B [9]. The contribution of CO2 in the energy sector of the US for 2001–2021 is depicted in Figure 1.
The United Nations has projected 151 countries’ commitment towards the net zero CO2 pledge in 2050 [17]. Almost 90% of the global GDP and emissions are covered by the CO2 neutrality vows and net zero pledges [18]. The top contributors, namely China, the US, the European Union, and Japan, accounted for approximately 56% of GHG emissions with a pertinent increase in GHG per capita and carbon intensity per GDP [19]. Considering this, several international agreements and initiatives, such as the familiar Paris Agreement, Kyoto Protocol, and the Conference of the Parties (COP), are slated worldwide [20]. Amongst which the latest and outspoken are the COP26 and COP27 of the United Nations Framework Convention on Climate Change (UNFCCC). Since the first COP in 1992, the climate change and severity of global warming have had no adverse change. Hence, the COP26 held in 2021 agreed to the “Glasgow Pact”, which is a set of commitments by developed countries to increase the level of their emissions reduction targets and to provide financial and technical assistance to developing countries [21]. Another important outcome of the conference was the launch of the “Race to Zero” campaign, which aims to mobilize a global coalition of businesses, governments, investors, and cities to take ambitious action to reach net-zero greenhouse gas emissions by 2050 at the latest [22,23].
Şahin et al. have utilized the fractional nonlinear grey model to forecast CO2 emissions in the US until 2025 [24]. Namboori et al. used ARIMA, SVM, SVM-PSO, and Prophet models to forecast emissions until 2022 [25]. Silva et al. predicted emissions for 12 months using SSA, ARIMA, Holt-Winters, and EIA-SSA [26]. Steinhauser et al. use the MSFE (Mean Square Forecast Error) to forecast CO2 emissions until 2030 [27]. Bennedsen et al. have proposed forecasts comparing 2018 and 2021 using the RMSE, MAP, and SADFM (structural augmented dynamic factor model) [28]. Jena et al. created a model using Multilayer Artificial Neural Network, MAP, MAPE, and RMSE and forecasted for the years 2017 to 2019 [29]. Subsequently, to the best of our knowledge, there have been no studies that used regression models to develop models for the forecast of CO2 emissions. There have not been any studies detailing the top 10 CO2-emitting states, especially of fossil fuels in the US.
Hence, the objective of this paper is threefold. First, we understand, analyze and compare the total FFCO2 emissions, total population, and GDP per capita using a regression model. Secondly, we forecast the emissions until 2050 in consequent 5 years intervals. Thirdly, we use MAPE to find the average error comparing the actual values.

2. Energy Sector in the US

The energy sector in the US is an imperative constituent of the country’s economy with a significant quota for the country’s GDP and employment. It is a multifaceted web for most of the CO2 emissions to process steady energy supplies. Approximately 80% of the country’s energy consumption relies heavily on fossil fuels, including coal, oil, and natural gas.

2.1. GHG Emissions

GHG emissions in the US have been a significant issue for many years, as the country is one of the largest emitters in the world. The United States emitted 6558 million metric tons of carbon dioxide equivalent (MMTCO2e) in 2019, representing about 13% of the world’s total emissions. The largest source of GHG emissions in the United States is the burning of fossil fuels for energy, which includes transportation, electricity generation, and industrial processes. In 2019, the transportation sector was responsible for the largest share of emissions (29%), followed by electricity generation (25%) and industrial processes (23%), as in Figure 2. Other significant sources of GHG emissions in the United States include agriculture, forestry, and other land use, which accounted for 10% of emissions in 2019 [24]. Although the US is globally the second largest emitter of greenhouse gases, considering the individual fossil fuels, it mostly ranks number one. As per the latest data for 2022 ranking the most polluted countries in the world, China ranks first with 9.9 billion CO2e while US orders second with 4.4 CO2e [30]. Of which emissions are more prominent from the usage and burning of fossil fuels. Independently the territorial emissions show a hike of approximately 6.5% for the decade of 2010 to 2021. Of which coal’s share is about 14.3%, oil with 9.3%, but gas shows a reduction of about −0.7%. The highest emissions come from the usage of oil and gas, with 2644 MTCO2 and 1188 MTCO2 and next for coal, with 2190 MTCO2 [23,31,32,33]. In 2020, the topmost contribution is from oil with 2049 MTCO2, and gas and coal with 1654 MTCO2 and 879 MTCO2, respectively. Least emissions from gas flaring and cement with 68 MTCO2 and 41 MTCO2. Whereas in 2021, the oil’s share is seen to be the highest with 2234 MTCO2, with gas taking the next place with 1637 MTCO2, and coal with 1002 MTCO2. The least emissions are from gas flaring and cement, with 68 MTCO2 and 41 MTCO2 [34]. From 2019 to 2020, the decline in FFCO2 emissions was 5.6%, but eventually recoiled to comparable levels of 2019 in 2021 [32].
As an important participant in COP, the US has recently re-joined the Paris Agreement, which had been withdrawn by the previous administration, and has announced an ambitious target of reducing its greenhouse gas emissions by 50–52% below 2005 levels by 2030 and set a goal of reaching net-zero emissions no later than 2050 [35]. Emissions from the energy sector sum up to almost three-quarters of total GHG emissions, accounting for about 75% of the country’s total emissions, which is 4554 MtCO2eq exclusively in 2021 [36]. The sector wise emissions for the top 10 polluted states are shown as in Figure 2A. This includes emissions from electricity generation for both commercial and residential use, transportation, and industrial processes. The overall U.S. CO2 emissions in 2021 grew by 7% when compared to 2020, but they were still 5%, less than in 2019. The CO2 emissions of the transport sector increased by 11%, due to the increase in travel, the commercial sector had an increase of 7% owing to the change in the electricity fuel mix and other commercial activities, the residential sector’s emissions hiked by 4%, which was mostly from the fuel mix, and the industrial sector increased by 4% due to the high industrial emission [37].

2.2. Energy-Related Emissions

The fundamental bases of GHG emissions include energy-related emissions, emissions from transportation, electricity generation, industrial process, agriculture, and land use, which ultimately roots in the energy sector [38]. The estimations of state-level energy-related CO2 emissions include direct fossil fuel use across all sectors, involving industrial, residential, commercial, and transportation, as well as fossil fuels consumed for electricity generation [39]. Energy-related emissions and electricity generation are the largest sources of FFCO2 emissions which include the combustion of fossil fuels for electricity and heat production, transportation, industrial processes, and power plants that burn coal, natural gas, and other fossil fuels. Transportation is the next highest source involving emissions from cars, trucks, planes, ships, and other vehicles. Releases from the production of cement, steel, and other materials and chemical manufacturing comprise the industrial processes. Additionally, agriculture and land use rank next highest, emitting in the sector with emissions from livestock, soil management, and other agricultural practices, as well as from deforestation and other land use changes. According to EIA, in 2019, energy-related emissions accounted for about 5514 MMT CO2e, electricity generation for 1745 MMT CO2e, transportation for 1876 MMT CO2e, industrial processes for 465 MMT CO2e, and agriculture and land use for 663 MMT CO2e. It is worth noting that these figures may have changed since 2019, and the EPA typically updates its GHG inventory on an annual basis [40].

2.3. GDP and Emissions

In comparison to 2020, energy use per dollar of GDP was 1% lower in 2021. Although the growth of energy consumption and GDP are meticulously correlative, it is partly at equilibrium when energy-efficient changes in the economy end in less energy use per unit of economic output. Factors contributing to less energy consumption per capita also involve less energy consumption per dollar of GDP [41]. At low-income levels, CO2 levels have risen in correlation with GDP per capita, and at higher-income levels, the concentrations have fallen, causing an inverted U shape connection between the income evolution and pollution concentrations [8]. Emissions per GDP had a dip for 2010–2021 with −3.1%, but a rise of 0.8% for 2021. Whilst considering the emissions per capita for 2010–2021, there has been a downfall of about −1.9%, yet a highly increased rate of 6.1% for 2020–2021. Thus, the world is not on track to reach the Paris Agreement goals so the temperatures can reach 2.8 °C by the end of the century. Hence, cutting down emissions by 45 percent to avoid a global catastrophe becomes urgent [42].
The energy infrastructure is broadly eminent as three segments, namely electricity, oil, and natural gas. The electricity segment contains 1075 gigawatts of installed generation with more than 6413 power plants. It uses 48% of coal combustion, 22% of natural gas combustion, and 20% of nuclear power plants to produce electricity, as shown in Figure 2B. The reason for the connection between transport and energy is the hefty dependence on pipelines to distribute products across the nation. Hence, the remaining generation is contributed by hydroelectric plants at 6%, oil at 1%, and renewable resources at 3% [43]. In 2015, the direct and indirect subsidies for oil, gas, and coal reached nearly $649 billion, which is ten times and $50 billion more than the educational and defense spending [44].

3. Fossil Fuel-Related Emissions

The FFCO2 includes coal, crude oil, petroleum, and natural gas. The principles of such fuels, their trends, drivers, and Carbon Capture and Storage (CCS) are discussed below.

3.1. CO2 Emissions from Fossil Fuel

CO2 emissions from fossil fuels are more prominent in the US. The emissions are about 4.57 billion metric tons of CO2 from energy consumption in 2019, with the vast majority coming from the combustion of fossil fuels. The following are some key fossil fuels that contribute to FFCO2 emissions. Figure 3 depicts the fossil fuels and sector nexus of CO2 emissions for 2021.

3.1.1. Coal

Coal combustion is one significant source that owes to FFCO2 emissions. Coal-fired power plants accounted for approximately 34% of 2019, and 20% of 2020 of the country’s total emissions [45]. Although more than 300 coal-fired power plants retired or were slated for retirement in 2020, the emissions in 2021 were about 10.54 Btu, which is relatively high compared to 2020 emissions of 9.18 Btu [46]. Such plants are replaced with renewables, such as wind, solar, and natural gas. Despite the shift towards renewable energy, coal remains imperative in the energy mix and is sustained for electricity generation, industrial activities, and other purposes [47]. The burning of coal is prone to several health and environmental impacts. Nearly 52,000 premature deaths and $345 billion of damage to the economy were the results of coal-fired power plants, precisely in 2011 [48]. To further reduce the emissions of SF6, NO2, and CO2 during the generation of electricity, the US has managed to transit from coal to natural gas [49]. Production of coal emits CO2 over 60% from the electricity sector and 13% from the industrial sector. It is visible that there has been a declining trend in recent years. The production trend is depicted in Figure 4A. In comparison to 2005, coal combustion is seen to be reduced from 50% to 34% in 2019. Figure 4B shows the total coal consumption in the US. This is due to the shift from coal-fired power plants to renewable energy resources, the CCS is a technology that captures carbon emissions and stores them underground. Although it is not widely established in the US, it can lessen coal’s legacy of CO2 emissions.

3.1.2. Crude Oil and Petroleum

Crude oil and petroleum are widely used in the US as primary energy sources for various industrial, transportation, and household purposes. In 2019, almost 2.24 billion metric tons of CO2 was emitted from petroleum and other liquid fuels, about 49% of the country’s energy-related CO2 emissions [50]. The transportation sector is the largest consumer responsible for approximately 68% of emissions from these fuels merely in 2020 [48]. Although there are many improvements in vehicle emission standards and fuel quality, transport-related air pollution always remains a hazard. It has adverse effects on respiratory and cardiovascular diseases [51]. The production of crude oil and petroleum is exhibited in Figure 5A. In 2019, the US accounted for almost 21% of petroleum consumption and 14% of CO2 emissions from petroleum consumption as in Figure 5B [52]. Studies estimate that around $140 billion in annual health damages are caused by such fuels, of which premature death has the highest portion [53]. The Shale revolution and the global oil demand are the two most featured concerns in the oil industry. The boom in shale oil and gas production made possible by hydraulic fracturing (fracking) and horizontal drilling technologies eases a demand for crude oil and petroleum consumption estimated to increase by 1.4 million barrels per day in 2022 driven by economic growth and recovery from the COVID-19 pandemic [54,55,56,57]. Some states have already implemented one type of Zero Emission Vehicle (ZEV), which is a Battery Electric Vehicle (BEV) that uses electric energy [58]. Switching to renewable energy is a remedy to put off the FFCO2 emissions from crude oil and petroleum and the US has implemented various policies, such as fuel efficiency standards, incentives for electric vehicles and renewable energy, and carbon pricing initiatives.

3.1.3. Natural Gas

The next significant contributor of CO2 emissions is natural gas. Approximately 1580 million metric tons of CO2 were found to be emitted, which is about 31% of the country’s energy-related emissions in 2020. This represents a decrease of 2.3% from 2019, owing to a combination of factors [59]. Although natural gas is touted cleaner fossil fuel than coal, crude oil, and petroleum, its carbon footprint is remarkable. Yet, during the pandemic, the production and consumption of natural gas decreased, eventually reducing CO2 emissions [60]. Methane is the primary component and is a potent GHG, and over a 20-year time frame, it has a much greater warming potential than CO2 [61]. Another trend that paved the way for CO2 emission from natural gas is the shift away from coal-fired power generation. The replacement of natural gas-fired plants has increased the share of natural gas in electricity generation. While natural gas-fired power plants emit less CO2 than coal-fired plants, they still contribute to GHG emissions [62]. Using natural gas for transportation has also been a driver of CO2 emissions in the US. While natural gas vehicles emit less CO2 than gasoline and diesel vehicles, they still emit CO2 and other pollutants [63]. The production and consumption trend line of natural gas is shown in Figure 6A,B. The hike in such emissions is dedicated to the growth of hydraulic fracturing; hence leaks during the production, processing, and distribution of natural gas eventually increase the carbon footprint [64]. To reduce the CO2 emissions from natural gas, the US has implemented strategies to improve its energy efficiency, increase the use of renewable natural gas produced from organic waste materials and offset traditional natural gas use, and develop CCS technology [65].

4. Modelling and Forecasting Techniques

Data and Methodology

As aforementioned, this study typically involves the data of the topmost CO2-emitting states in the US. With Texas being the first-highest emitter and Michigan being the tenth-highest emitter, the data were collated from the information available on the United States Environmental Protection Agency webpage. In this regard, we have provided more prominence to the fossil fuels emissions from the Energy sector. Such chosen emitters include the burning of fossil fuel emissions from and using power plants, petroleum and natural gas, refineries, manufacturing industries, minerals, and metals. These emissions are due to the large facilities in the US for the year 2021. All the collected data are reported in million metric tons of CO2e for all fuel combustions, which includes coal, natural gas, petroleum products, process emissions, and use of sorbent and carbonates.
The first ten highest CO2 (fossil fuel related) emitting states of the US are as follows: Texas (TX), California (CA), Florida (FL), Louisiana (LS), Pennsylvania (PA), Ohio (OH), Illinois (IL), Indiana (IN), New York (NY), and Michigan (MI). The states’ total fossil fuel-related CO2 emissions, population per state, Gross Domestic Product Per Capita, and Human Development Index are listed. This data are for 2021, exclusively on the filtered fossil fuel combustions as in Table 1.
The selected variables are the Total emissions from fossil fuel (EFF), Total population (TP), and Gross Domestic Product Per Capita (GDPPC) for each state and are collected from the data freely available on the US official websites [66,67]. First, the main reason for choosing these variables is that their data and time series are exclusively available on the country’s official web pages. Second, they strongly correlate with the consumption and demand of energy resources. Thirdly, as the population rises, the demand and usage of fossil fuels tend to increase gradually, owing to the amplified human activities. Moreover, due to an upsurge in GDP per capita, fossil fuel emission increases intensifying associated energy demands [68]. The descriptive statistics of the variables were derived using the SPSS tool.
The descriptive statistics of the chosen variables are depicted in Table 2. The results show that each country’s mean is reasonably high compared to the standard deviations. For EFF the means of CA and TX are 428.9 and 830.95, while their standard deviations (SD) are 40.60 and 37.38, respectively. TP, TX, and FL show means of 25.60 and 19.21 with SD of 2.93 and 1.85, respectively. For GDPPC, CA, and TX’s means are 2166.95 and 1386.58 with SD of 352.47 and 269.50. The difference is comparatively high, exhibiting most related variation defined by CV and a good scatter plot. It is also understood that TX and CA have high relativity in terms of EFF, TP, and GDPPC. For almost every data set, we see that the mean is relatively higher than the standard deviation. This shows that the data are homogenous and consistent. The points when plotted, will be tightly clustered around the mean and will not exhibit much variability.
The general idea value for kurtosis and skewness to have a normal distribution for an observed series should be zero. Yet, some researchers have argued that it can be considered a normal distribution if both values are between ±1.5 [69,70,71]. Thus, the skewness and kurtosis values show a normal distribution. Specifically, EFF and TP show negative skewness which means that the values are skewed towards the left, indicating a longer tail on the left side of the distribution, whereas GDPPC indicates positive skewness demonstrating a fatter tail on the right side of the distribution. Additionally, from kurtosis, we see all values less than the normal value (≤3), which suggests the kurtosis curve is platykurtic. Except for CA, FL, and LS in EFF, which advises the kurtosis curve to be leptokurtic as the values are >3.
Furthermore, Table 3 outlines the findings of the correlation analysis. The data of all the independent values show a high degree of correlation over 0.80 compared to the dependent variable. It is observed that EFF, GDPPC, and TP have statistically significant correlations with the selected 10 states of the US. The data of all variables are between 2000 and 2021. The training and testing period uses the same range of data. The multiple regression tool from the SPSS statistical program application predicted the models. The suitable linear regression method was the backward multiple linear regression analysis methods, which consequently removes the values with the lowest partial F-value after including all variables for calculation. A model is created whenever the statistical contribution of the discarded variable is high. After the models are estimated, the goodness-to-fit is determined using various statistical methods. An adjusted coefficient of determination (adj. R2) was used to verify how well the model fits the data. F-test was carried out to test the presence of significance between the independent and dependent variables. Additionally, testing the influence of each coefficient of the model, the t-test opted. The actual and predicted data plots were used to study the linearity further. Finally, to check the accuracy of the forecasted values, mean absolute percentage error (MAPE) was adopted. The mathematical expression of MAPE is as defined:
MAPE = 1 n i = 1 n A i F i A i
A i is the actual value; F i is the forecast value; n is the total number of measurements.

5. Results

The developed regression models used to forecast the EFF are shown in Table 4. The contribution of each variable is also studied to evaluate the effectiveness of the developed models. Hence, the contribution rates are computed as shown in Table 5. We see the highest contribution of about 22.23% of EFF from TX, 20.98% of GDPPC from LS, and 166.17% of TP from MI. It is seen that GDPPC and TP show high contributions among the variables, on average LS and MI show higher levels of contributions when compared state-wise. The results of the data testing using the F-test, t-test, and adj. R2 are shown in Table 6. The tabulated F value is smaller than the calculated F value, indicating that all equations are significant at 95% confidence levels. The tabulated t values are higher than the calculated t values, which signify the coefficients used. The R2 values are almost 0.98 and 0.99, which indicates high relativity.
The forecasted EFF, as shown in Table 7, indicates that the emissions have eventually decreased and increased for every consecutive year. It is seen that the forecasted emissions for CA have reduced from 2025 to 2050. The average reduction is from 367.4 MMT to 248.3 MMT, which is a 119.1 MMT variance. More drastic change is seen in the states of OH and IN, where the difference is found to be 153.2 MMT and 141.02 MMT, respectively. An increase is found in TX with 2.5 MMT of emissions. However, other states show good decrease in the emissions of fossil fuels with an average of 60–70%. This indicates a positive measurement of the forecasted values and future emissions reduction in the US. As the major states’ emissions decrease, reaching net zero by 2050 is not a challenge. The MAPE model results shown in Table 8 suggest that the forecasted EFF is either highly or mostly accurate, as shown in Figure 7. TX, IL, LS, and CA show high accuracy, while PA and OH show good accuracy. This is an excellent fit model to suggest accuracy.

6. Current and Future Mitigations

Overall, the US is taking a multi-faceted approach to mitigating CO2 emissions, with a focus on transitioning to a more sustainable, low-carbon economy. There have been several measures to mitigate CO2 emissions and combat climate change in the country.
  • Increased Deployment of Renewable Energy Sources—The deployment of renewable energy sources, such as wind and solar power, has been an initiative to reduce emissions. According to a study conducted by the National Renewable Energy Laboratory, renewable energy has the potential to meet more than 80% of the country’s electricity demand by 2050 [72]. Such a strategy is effective in other countries, such as Germany, which has rapidly increased its renewable energy capacity in recent years [73]. Policy measures, such as tax incentives and renewable energy mandates, can help to encourage the adoption of renewable energy technologies.
  • Stricter Emissions Standards for Vehicles and Industries—The US has implemented more stringent emissions standards for vehicles and industries. In particular, the Environmental Protection Agency (EPA) has set targets for reducing emissions from power plants. According to a study by the American Lung Association, these regulations have resulted in significant reductions in air pollution and associated health benefits [66]. Corporate Average Fuel Economy (CAFE) standards for vehicles are another approach to reducing emissions. These standards require automakers to meet minimum fuel economy targets for their fleets, which has led to the development of more fuel-efficient vehicles that emit less CO2 [74]. A study by the International Council on Clean Transportation found that the CAFE standards have led to a reduction of about 6% in CO2 emissions from light-duty vehicles [75].
  • Carbon Capture and Sequestration Technologies—The US is investing in CCS, which allows for capturing and storing CO2 emissions from industrial processes. The Global CCS Institute studied that there are currently 28 large-scale carbon capture and storage projects operating or under construction worldwide, with the majority located in the US [76]. Among the 28 large-scale CCS projects, the United States has a renowned project named “The Petra Nova Carbon Capture Project”. Having begun operating in 2017, it has shown some notable results. Firstly, it has successfully captured approximately 90% of CO2 emissions from the flue gas of the coal-fired power plant unit at the W.A. Parish Generating Station [77]. Secondly, it has shown that post-combustion carbon capture technology can be integrated into existing coal-fired power plants without significantly reducing their efficiency. Thirdly, the captured CO2 from the Petra Nova project is being used for enhanced oil recovery (EOR) at an oil field located approximately 82 miles away from the W.A. Parish Generating Station. This process has been shown to increase the recovery of oil from depleted oil reservoirs, which can have economic benefits. Finally, it has provided valuable information about the costs and technical feasibility of post-combustion carbon capture technology [78]. Another potential strategy is implementing carbon capture and storage (CCS) technologies in fossil fuel power plants. This involves capturing CO2 emissions from power plants and storing them underground or in other long-term storage facilities. CCS is effective in reducing CO2 emissions in pilot projects around the world [79].
  • Shift Towards Sustainable Transportation Options—The US is shifting towards more sustainable transportation options, such as electric vehicles and public transit systems. According to a study by the International Council on Clean Transportation, adopting electric vehicles (EVs) can significantly reduce CO2 emissions from the transportation sector [80]. The International Energy Agency in 2020 reported that EVs accounted for around 2.4% of all passenger cars on the road in the US. The sales of EVs have been increasing in recent years, with 2020 seeing a slight uptick in sales despite the challenges posed by the COVID-19 pandemic, and there are predictions from industry analysts that the sales will continue to grow in the coming years [81]. Studies suggest that EVs emit 50–70% less GHG than conventional gasoline vehicles. This emission reduction is even more remarkable when the electricity used to power the EVs comes from renewable resources [82]. E-bike sharing programs, electric vehicle charging stations, and a public transit system that runs on renewable energy are a few steps towards a greener society by the Seattle government [83].
  • Public Awareness and Education—The US also focuses on public awareness and education on the importance of reducing CO2 emissions and combating climate change. According to a study by the Yale Program on Climate Change Communication, there has been a significant increase in public awareness and concern about climate change in recent years [84]. Finally, there is also a need to promote energy efficiency and conservation measures in industries and households. This could include policies, such as building codes that require energy-efficient buildings, incentives for using energy-efficient appliances, and education programs to promote energy-saving behaviors [85].
The Clean Air Act, the Clean Power Plan, and the Paris Agreement are a few other initiatives of the government. However, the country’s GHG emissions have been relatively stable since 2005, with a slight decrease in recent years. To achieve significant reductions in GHG emissions, further action will be necessary, including transitioning to cleaner energy sources, increasing energy efficiency, and reducing emissions from transportation and industry. The conferences of the parties (COP) are held by the UNFCCC annually to discuss and negotiate global action on climate change. The 26th COP (COP26) was scheduled in Glasgow, UK, in November 2020 but was postponed due to the COVID-19 pandemic. The latest COP meeting was held in Sharm El-Sheikh, Africa, in 2022 under the central themes of “together for implementation” and “net zero”. The takeaways of the summit include the funds established to support “loss and damage” for countries suffering severe climate changes, the planned implementations discussed at COP26 were not achieved, and the chances of achieving them in 2050 are less fortunate, as there is a need to reform the broader public financial system, revisit and strengthen their 2030 targets, to accelerate renewable energy deployment, global stocktake, and nature-based solutions [86,87]. Overall, the COP conferences are important forums for global action on climate change, and COP26 and COP27 are crucial conferences for advancing progress toward the Paris Agreement goals.

7. Discussion and Future Direction

The results of the study indicate that the carbon emissions from fossil fuels gradually decrease over time. As far as we know, there has been no detailed study on fossil fuel CO2 emissions in the US. As per the IPCC forecasts, we understand that the temperature will hike until 2030 if it continues in the same trend and after severe mitigations, the emissions might fall, taking a downward drift [88]. Other studies have forecasted emissions for either 12 to 36 months or until 2030. Yet, from our study, we conclude that the emissions from fossil fuels can be reduced to a larger extent by switching to renewable energy or energy mix. This can be taken as a series of mitigation which will reduce carbon emissions, which is a serious threat to the environment. Despite what the other literature says on the forecast, our results indicate that the US CO2 emissions from fossil fuels will eventually decrease with the increase in the use of renewable energy. We see that the emissions rate is gradually declining, which is a good sign that the country is working towards the net-zero policy. Adapting to green energy is a strong mitigation to see a drastic change in CO2 emissions. While comparing our results with the literature, there are similar and more diverse results found.
Previous studies by Jacobson et al. discuss the potentiality of the US to transition to 100% renewable energy WWS (Wind, Water, and Sunlight) by 2050 and the implications for reducing CO2 emissions [89]. Similarly, Ding et al. studied CO2 emissions of the US as one of the countries using the Choquet fuzzy integral and grey multivariate delay model. Forecast results show that the emissions in the US will be reduced by 5.08% in 2025 using the Green Economic Development Strategy [90]. Wang et al. projected the emissions for 2020 and 2021, which showed a rise. The proposal of the study is if the Zero Carbon Action Plan adopted by the country in 2020 works well, the US emissions and the results of the global carbon reduction will be lower and better [91]. Şahin et al. use ROFANGBM to predict emissions in the US and show an increase in 2025 compared to 2020 [24]. Bennedsen et al. used a structural augmented dynamic factor model to compare 2018 and 2019 CO2 emissions in the US and projected a reduction of about 2.6% per capita CO2 emissions compared to 2018 [28]. Our study uses the regression model to analyze and create forecast models. In the future, other methodologies can be used or even changing the independent variables might result in different results. Different countries or other states of the US can be forecasted as our study details only the top 10 emitting states. Such forecasts might help the country to be cautious about the forthcoming.

8. Conclusions

The issue of CO2 emissions in the United States is complex and multifaceted. While there have been some efforts to reduce emissions, such as the introduction of renewable energy sources and energy-efficient technologies, the US still heavily relies on fossil fuels for energy production, transportation, and manufacturing. Additionally, the US has a high consumption and waste level, contributing to carbon emissions. One of the main reasons for the US’s high level of carbon emissions is its economic and political structure [92,93,94,95]. The country has historically prioritized economic growth and development over environmental concerns, with many industries and politicians resistant to change. Additionally, the US has not always been willing to participate in international agreements to reduce greenhouse gas emissions, such as the Kyoto Protocol [96,97]. However, there has been some progress in recent years. Several states and cities in the US have set ambitious goals to reduce carbon emissions, and there has been an increase in renewable energy production.
The current study has discussed the emissions of fossil fuels in the US, especially for the top emitting states. We have forecasted and verified the error percentage to confirm the data further. Despite many studies on the forecasting techniques of CO2 emissions, there has been no study on fossil fuel emissions in the US energy sector. Although this study discusses EFF in the US, the major limitation is that it does not commit with all states and all sectors in the United States. In the future, concentrating on a broader angle to forecast and compare is a good option. Even though the emissions have increased in all sectors, they have never surpassed the 2019 emission rate. Thus, it is notable that the United States has a hard time meeting anticipated national energy efficiency, utilizing renewable energy sources, reducing carbon emissions, and achieving a decarbonized economy. Overall, the issue of carbon emissions in the US is a complex and ongoing challenge that requires sustained effort and collaboration from all sectors of society. Our study is a notable entity as it forecasts EFF and shows the ways to reduce the carbon footprint to set a goal of achieving a 100% clean energy economy by 2050.

Author Contributions

K.B.K.—Conceptualization, methodology, validation, data curation, writing—original draft, review and editing; S.-W.W.—Visualization, resources, supervision; M.-E.W.—Supervision; T.K.—Formal analysis. 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

The datasets used and analyzed during the current study are available from the corresponding author on reasonable request.

Acknowledgments

Authors thank the National Taipei University of Technology, Taipei, Taiwan for their support.

Conflicts of Interest

The authors declare no conflict of interest.

References

  1. Farahmand, A.; Ray, S.; Thrastarson, H.; Licata, S.; Granger, S.; Fuchs, B. A Workshop on Using NASA Airs Data to Monitor Drought for the U.S. Drought Monitor. Bull. Am. Meteorol. Soc. 2023, 104, E22–E30. [Google Scholar] [CrossRef]
  2. U.S. Energy Information Administration—EIA—Independent Statistics and Analysis. U.S. Energy-Related Carbon Dioxide Emissions. 2021. Available online: https://www.eia.gov/environment/emissions/carbon/index.php (accessed on 8 February 2023).
  3. Sengupta, S. Climate change, International Justice and global order. Int. Aff. 2023, 99, 121–140. [Google Scholar] [CrossRef]
  4. UNEP. UNEP Copenhagen Climate Centre (UNEP-CCC). Emiss. Gap Rep. 2020, 2020, 1–128. Available online: https://www.unep.org/emissions-gap-report-2020 (accessed on 8 February 2023).
  5. Udemba, E.N. A sustainable study of economic growth and development amidst ecological footprint: New insight from Nigerian perspective. Sci. Total Environ. 2020, 732, 139270. [Google Scholar] [CrossRef] [PubMed]
  6. Masson-Delmotte, V.; Zhai, P.; Pörtner, H.O.; Roberts, D.; Skea, J.; Shukla, P.R.; Pirani, A.; Moufouma-Okia, W.; Péan, C.; Pidcock, R.; et al. Waterfield. Global Warming of 1.5 °C. In An IPCC Special Report on the Impacts of Global Warming of 1.5 °C above Pre-Industrial Levels and Related Global Greenhouse Gas Emission Pathways, in the Context of Strengthening the Global Response to the Threat of Climate Change, Sustainable Development, and Efforts to Eradicate Poverty; Cambridge University Press: Cambridge, UK; New York, NY, USA, 2022. [Google Scholar]
  7. Kumar, A.; Singh, P.; Raizada, P.; Hussain, C.M. Impact of COVID-19 on Greenhouse Gases Emissions: A critical review. Sci. Total Environ. 2022, 806, 150349. [Google Scholar] [CrossRef]
  8. Saqib, N. Green Energy, non-renewable energy, financial development and economic growth with carbon footprint: Heterogeneous panel evidence from cross-country. Econ. Res. Ekon. Istraz. 2022, 35, 6945–6964. [Google Scholar] [CrossRef]
  9. Aghahosseini, A.; Solomon, A.A.; Breyer, C.; Pregger, T.; Simon, S.; Strachan, P.; Jäger-Waldau, A. Energy system transition pathways to meet the global electricity demand for ambitious climate targets and cost competitiveness. Appl. Energy 2023, 331, 120401. [Google Scholar] [CrossRef]
  10. Kanas, A.; Molyneux, P.; Zervopoulos, P.D. Systemic Risk and CO2 Emissions in the U.S. J. Fin. Stab. 2023, 64, 101088. [Google Scholar] [CrossRef]
  11. Park, J.H.; Yang, J.; Kim, D.; Gim, H.; Choi, W.Y.; Lee, J.W. Review of recent technologies for transforming carbon dioxide to carbon materials. Chem. Eng. J. 2022, 427, 130980. [Google Scholar] [CrossRef]
  12. Crippa, M.; Guizzardi, D.; Solazzo, E.; Muntean, M.; Schaaf, E.; Monforti-Ferrario, F.; Banja, M.; Olivier, J.; Grassi, G.; Rossi, S.; et al. GHG Emissions of All World Countries; EUR 30831 EN; Publications Office of the European Union: Luxembourg, 2021. [Google Scholar]
  13. Ya-wen, L.I.U. BP Statistical Review of World Energy-2021 Edition Published: The Energy Market Suffered a Huge Shock, 70th ed.; BP: London, UK, 2021; pp. 1–72. [Google Scholar]
  14. Connors, S.; Dionne, M.; Hanak, G.; Musulin, R.; Aellen, N.; Amjad, M.; Bowen, S.; Carrascal, D.R.; Coppola, E.; Moro, E.D.; et al. Climate Science: A Summary for Actuaries-What the IPCC Climate Change Report-2021 Means for the Actuarial Profession; International Actuarial Association: Ottawa, ON, Canada, 2022. [Google Scholar]
  15. Cohen, R.; Eames, P.C.; Hammond, G.P.; Newborough, M.; Norton, B. Briefing: The 2021 Glasgow Climate Pact: Steps on the transition pathway towards a low carbon world. Proc. Inst. Civ. Eng. Energy. 2022, 175, 97–102. [Google Scholar] [CrossRef]
  16. United Nations. Causes and Effects of Climate Change, United Nations. Available online: https://www.un.org/en/climatechange/science/causes-effects-climate-change (accessed on 10 February 2023).
  17. United Nations Framework Convention on Climate Change. Climate Initiatives Platform. Available online: https://climateaction.unfccc.int/Initiatives?id=95 (accessed on 12 February 2023).
  18. COP26. COP26 World Leaders’ Summit Presidency Summary. Available online: https://ukcop26.org/cop26-world-leaders-summit-presidency-summary/ (accessed on 18 February 2023).
  19. World Resources Institute. Climate Watch—Greenhouse Gas Emissions. Available online: https://www.climatewatchdata.org/ghg-emissions?end_year=2018&start_year=1990 (accessed on 28 February 2023).
  20. Tauseef Hassan, S.; Wang, P.; Khan, I.; Zhu, B. The Impact of Economic Complexity, Technology Advancements, and Nuclear Energy Consumption on the Ecological Footprint of the USA: Towards Circular Economy Initiatives. Gondwana Res. 2023, 113, 237–246. [Google Scholar] [CrossRef]
  21. Pandey, D.K.; Kumar, R.; Kumari, V. Glasgow Climate Pact and the global clean energy index constituent stocks. Int. J. Emerg. Mark. 2023. [Google Scholar] [CrossRef]
  22. Gautam, A.; Mondal, M.K. Review of recent trends and various techniques for CO2 capture: Special emphasis on biphasic amine solvents. Fuel 2023, 334, 126616. [Google Scholar] [CrossRef]
  23. United Nations Framework Convention on Climate Change. Report of the Conference of the Parties Serving as the Meeting of the Parties to the Paris Agreement on Its Third Session, Held in Glasgow from 31 October to 13 November 2021. In Proceedings of the Addendum, Part Two: Action Taken by the Conference of the Parties Serving as the Meeting of the Parties to the Paris Agreement at Its Third Session, Glasgow, UK, 31 October–13 November 2021; Available online: https://unfccc.int/documents/460952 (accessed on 1 March 2023).
  24. Şahin, U. Forecasting share of renewables in primary energy consumption and CO2 emissions of China and the United States under covid-19 pandemic using a novel Fractional Nonlinear Grey Model. Expert Syst. Appl. 2022, 209, 118429. [Google Scholar] [CrossRef]
  25. Namboori, S. Forecasting Carbon Dioxide Emissions in the United States Using Machine Learning. Ph.D. Thesis, National College of Ireland, Dublin, Ireland, 2020. [Google Scholar]
  26. Silva, E.S. A combination forecast for energy-related CO2 emissions in the United States. Int. J. Energy Stat. 2013, 1, 269–279. [Google Scholar] [CrossRef]
  27. Steinhauser, R.; Auffhammer, M. Forecasting US CO2 Emissions Using State-Level Data; University of California Berkeley: Berkeley, CA, USA, 2005. [Google Scholar]
  28. Bennedsen, M.; Hillebrand, E.; Koopman, S.J. Modeling, forecasting, and nowcasting US CO2 emissions using many macroeconomic predictors. Energy Econ. 2021, 96, 105118. [Google Scholar] [CrossRef]
  29. Jena, P.R.; Managi, S.; Majhi, B. Forecasting the CO2 emissions at the global level: A multilayer artificial neural network modelling. Energies 2021, 14, 6336. [Google Scholar] [CrossRef]
  30. United States Environmental Protection Agency. Global Greenhouse Gas Emissions Data. Available online: https://www.epa.gov/ghgemissions/global-greenhouse-gas-emissions-data (accessed on 20 March 2023).
  31. Crippa, M.; Guizzardi, D.; Muntean, M.; Schaaf, E.; Solazzo, E.; Monforti-Ferrario, F.; Olivier, J.G.J.; Vignati, E. Fossil CO2 Emissions of All World Countries—2020 Report; EUR 30358 EN; Publications Office of the European Union: Luxembourg, 2020. [Google Scholar]
  32. Perera, F.; Nadeau, K. Climate change, fossil-fuel pollution, and children’s health. N. Engl. J. Med. 2022, 386, 2303–2314. [Google Scholar] [CrossRef]
  33. Yegorov, Y. Risks from Transition to Low-Carbon Energies and Global Warming for FSU Countries. In World-Systems Evolution and Global Futures; Springer International Publishing: Cham, Switzerland, 2023; pp. 17–30. [Google Scholar]
  34. International Energy Agency. Greenhouse Gas Emissions from Energy Data Explorer. Available online: https://www.iea.org/data-and-statistics/data-tools/greenhouse-gas-emissions-from-energy-data-explorer (accessed on 20 March 2023).
  35. BP Statistical Review of World Energy-2022—71st Edition. Available online: https://www.bp.com/content/dam/bp/business-sites/en/global/corporate/pdfs/energy-economics/statistical-review/bp-stats-review-2022-full-report.pdf (accessed on 20 March 2023).
  36. United Nations Environment Programme. Emissions Gap Report. 2022. Available online: https://www.unep.org/resources/emissions-gap-report-2022 (accessed on 20 March 2023).
  37. United Nations Environment Programme. Home Page. Available online: https://www.unep.org (accessed on 20 March 2023).
  38. Bouckaert, S.; Pales, A.F.; McGlade, C.; Remme, U.; Wanner, B.; Varro, L.; D’Ambrosio, D.; Spencer, T. Net Zero by 2050: A Roadmap for the Global Energy Sector; Internation Energy Agency: Paris, France, 2021. [Google Scholar]
  39. Andrew, R.; Peters, G. The Global Carbon Project’s Fossil CO2 Emissions Dataset (2022v27); Zenodo: Geneva, Switzerland, 2021. [Google Scholar] [CrossRef]
  40. U.S. Simple-Cycle Natural Gas Turbines Operated at Record Highs in Summer. 2022. Available online: https://www.eia.gov/todayinenergy/detail.php?id=55680# (accessed on 20 March 2023).
  41. Dąbrowski, M. The Contemporary Russian Economy: A Comprehensive Analysis; Palgrave Macmillan: Cham, Switzerland, 2023. [Google Scholar]
  42. Annual Energy Outlook 2022—U.S. Energy Information Administration (EIA). Available online: https://www.eia.gov/outlooks/aeo/narrative/electricity/sub-topic-01.php (accessed on 20 March 2023).
  43. International Energy Agency. Emissions Factors-Database Documentation. In Annual GHG Emission Factors for World Countries from Electricity and Heat Generation, 2022th ed; International Energy Agency: Paris, France, 2022. [Google Scholar]
  44. U.S. Energy Information Administration—EIA—Independent Statistics and Analysis. Available online: https://www.eia.gov/energyexplained/use-of-energy/ (accessed on 20 March 2023).
  45. Kumar, P.; Bartzis, J.G.; Di Sabatino, S.; Ketzel, M.; Pirjola, L.; Kukkonen, J.; Ratti, C.; Johansson, C.; De Gennaro, G.; Wierzbicka, A.; et al. Measures and Policies for Reducing PM Exceedances through the Use of Air Quality Modeling: The Case of Thessaloniki, Greece. ACS Earth Space Chem. 2019, 3, 2008–2017. [Google Scholar]
  46. Energy Sector-Specific Plan—2015: CISA. Available online: https://www.cisa.gov/resources-tools/resources/energy-sector-specific-plan-2015 (accessed on 20 March 2023).
  47. Shahzad, U.; Fareed, Z.; Shahzad, F.; Shahzad, K. Investigating the Nexus between Economic Complexity, Energy Consumption and Ecological Footprint for the United States: New Insights from Quantile Methods. J. Clean. Prod. 2021, 279, 123806. [Google Scholar] [CrossRef]
  48. United States Energy Information Administration—Energy Information Administration—Independent Statistics and Analysis. Available online: https://www.eia.gov/energyexplained/electricity/electricity-in-the-us.php (accessed on 20 March 2023).
  49. United States—United States Energy Information Administration. Available online: https://www.eia.gov/beta/states/data/dashboard/coal (accessed on 20 March 2023).
  50. Coal Explained—United States Energy Information Administration. Available online: https://www.eia.gov/energyexplained/coal (accessed on 20 March 2023).
  51. Zhang, Q.; Jiang, X.; Tong, D.; Davis, S.J.; Zhao, H.; Geng, G.; Feng, T.; Zheng, B.; Lu, Z.; Streets, D.G.; et al. Transboundary Health Impacts of Transported Global Air Pollution and International Trade. Nature 2017, 543, 705–709. [Google Scholar] [CrossRef] [PubMed]
  52. Siler-Evans, K.; Azevedo, I.L.; Morgan, M.G. Marginal Emissions Factors for the U.S. Electricity System. Environ. Sci. Technol. 2012, 46, 4742–4748. [Google Scholar] [CrossRef] [PubMed]
  53. Use of Energy for Transportation—United States Energy Information Administration (EIA). Available online: https://www.eia.gov/energyexplained/use-of-energy/transportation.php (accessed on 20 March 2023).
  54. Use of Oil—United States Energy Information Administration (EIA). Available online: https://www.eia.gov/energyexplained/oil-and-petroleum-products/use-of-oil.php (accessed on 20 March 2023).
  55. Mao, X.; Tal, A.; Heo, J.; Zhang, Y.; Zhang, Q. Trends and drivers of transportation-related air pollution in the United States from 1990 to 2010. Atmos. Chem. Phys. 2016, 16, 12667–12680. [Google Scholar]
  56. United States—United States Energy Information Administration (EIA). Available online: https://www.eia.gov/beta/states/data/dashboard/crude-oil-petroleum (accessed on 21 March 2023).
  57. Tessum, C.W.; Apte, J.S.; Goodkind, A.L.; Muller, N.Z.; Mullins, K.A.; Paolella, D.A.; Polasky, S.; Springer, N.P.; Thakrar, S.K.; Marshall, J.D.; et al. Inequity in Consumption of Goods and Services Adds to Racial-Ethnic Disparities in Air Pollution Exposure. Proc. Natl. Acad. Sci. USA 2019, 116, 6001–6006. [Google Scholar] [CrossRef] [PubMed]
  58. The United States is Projected to be a Net Exporter of Crude Oil in Two AEO2020 Side Cases. Available online: https://www.eia.gov/todayinenergy/detail.php?id=42795 (accessed on 21 March 2023).
  59. United States Energy Information Administration—EIA—Independent Statistics and Analysis. Available online: https://www.eia.gov/outlooks/steo/ (accessed on 21 March 2023).
  60. Krupnick, A.; Munnings, C. Differentiation of Natural Gas Markets by Climate Performance. Resources for the Future. Available online: https://www.rff.org/publications/reports/differentiation-natural-gas-markets-climate-performance/ (accessed on 21 March 2023).
  61. Wang, X.; Liu, H.; Zhang, J.; Wang, X.; Cheng, J.; Wang, J. Shale Oil Development and Utilization and Its Role in Energy Industry. Energy Fuels 2017, 31, 2635–2647. [Google Scholar]
  62. Wicki, M.; Brückmann, G.; Quoss, F.; Bernauer, T. What Do We Really Know about the Acceptance of Battery Electric Vehicles?—Turns out, Not Much. Transp. Rev. 2023, 43, 62–87. [Google Scholar] [CrossRef]
  63. Total Energy Monthly Data-March 2023—United States Energy Information Administration (EIA). Available online: https://www.eia.gov/totalenergy/data/monthly/ (accessed on 21 March 2023).
  64. U.S. Energy Information Administration. How Much Carbon Dioxide is Produced When Different Fuels are Burned? Available online: https://www.eia.gov/tools/faqs/faq.php?id=73&t=11 (accessed on 21 March 2023).
  65. Brandt, A.R.; Heath, G.A.; Kort, E.A.; O’Sullivan, F.; Pétron, G.; Jordaan, S.M.; Tans, P.; Wilcox, J.; Gopstein, A.M.; Arent, D.; et al. Fossil Fuel Industry Methane Emissions in the United States: A Review of the Current State of Knowledge and Opportunities for Reductions. Environ. Sci. Technol. 2014, 48, 8349–8359. [Google Scholar]
  66. Jordaan, S.M.; Ruttinger, A.W.; Surana, K.; Nock, D.; Miller, S.M.; Ravikumar, A.P. Global Mitigation Opportunities for the Life Cycle of Natural Gas-Fired Power. Nat. Clim. Chang. 2022, 12, 1059–1067. [Google Scholar] [CrossRef]
  67. United States Energy Information Administration. How Much Carbon Dioxide is Produced from Burning Natural Gas? Available online: https://www.eia.gov/tools/faqs/faq.php?id=73&t=11 (accessed on 21 March 2023).
  68. Harrabin, R. Methane Emissions in U.S. Exceed Estimates, Erasing Climate Benefits of Natural Gas. Inside Climate News. 2019. Available online: https://insideclimatenews.org/news/16042019/methane-leaks-exceed-estimates-natural-gas-climate-change-global-warming (accessed on 21 March 2023).
  69. Erbay, Ş.; Beydoğan, H.Ö. Eğitimcilerin Eğitim Araştirmalarina yönelik tutumlari, Ahi Evran Üniversitesi Kırşehir Eğitim Fakültesi Dergisi. Kirsehir Ahi Evran University. 2017. Available online: https://dergipark.org.tr/en/pub/kefad/issue/59420/853376 (accessed on 21 March 2023).
  70. George, D.; Mallery, P. IBM SPSS Statistics 27 Step by Step; Routledge: New York, NY, USA, 2021. [Google Scholar] [CrossRef]
  71. Urbano, R.C. Using Secondary Datasets to Understand Persons with Developmental Disabilities and Their Families. In International Review of Research in Developmental Disabilities; Elsevier: Amsterdam, The Netherlands, 2013. [Google Scholar] [CrossRef]
  72. Renewable Natural Gas Coalition. Renewable Natural Gas (RNG) Basics. Available online: https://www.rngcoalition.com/rng-basics (accessed on 21 March 2023).
  73. Brown, M.A.; Patel, D.; Frew, B.A.; Wiser, R. Renewable Energy Has the Potential to Meet More Than 80% of US Electricity Demand. IEEE J. Photovolt. 2018, 8, 793–798. [Google Scholar]
  74. Dincer, I.; Aziz, M.A.; Naterer, G.F. The Green Hydrogen as a Renewable Energy Source and Storage in the Transportation Sector of Germany. Int. J. Hydrogen Energy 2021, 46, 2289–2296. [Google Scholar]
  75. Karakurt, I.; Aydin, G. Development of Regression Models to Forecast the CO2 Emissions from Fossil Fuels in the BRICS and MINT Countries. Energy 2023, 263, 125650. [Google Scholar] [CrossRef]
  76. Novacheck, J.E.; Brinkman, G.L.; Porro, G.S. Operational Analysis of the Eastern Interconnection at Very High Renewable Penetrations; Office of Scientific and Technical Information (OSTI): Oak Ridge, TN, USA, 2018.
  77. Armpriester, A.; Smith, R.; Scheriffius, J.; Smyth, R.; Istre, M.W.A. Parish Post-Combustion CO2 Capture and Sequestration Project Phase 1 Definition; Petra Nova Power Holdings LLC.: Thompsons, TX, USA, 2014. [Google Scholar] [CrossRef]
  78. Kennedy, G. WA Parish Post-Combustion CO2 Capture and Sequestration Demonstration Project; Final Technical Report; No. DOE-PNPH-03311; Petra Nova Power Holdings LLC.: Thompsons, TX, USA, 2020. [Google Scholar]
  79. Breyer, C.; Bogdanov, D.; Gulagi, A.; Aghahosseini, A.; Barbosa, L.S.N.S.; Koskinen, O.; Barasa, M.; Caldera, U.; Afanasyeva, S.; Child, M.; et al. On the Role of Solar Photovoltaics in Global Energy Transition Scenarios. Prog. Photovolt. 2017, 25, 727–745. [Google Scholar] [CrossRef]
  80. U.S. Environmental Protection Agency. Petroleum Refinery Sector: Revised New Source Performance Standards. Available online: https://www.epa.gov/stationary-sources-air-pollution/petroleum-refinery-sector-revised-new-source-performance-standards (accessed on 22 March 2023).
  81. Becker, T.A.; Sidhu, I.; Tenderich, B. Electric Vehicles in the United States: A New Model with Forecasts to 2030; Center for Entrepreneurship and Technology, University of California: Berkeley, CA, USA, 2009; Volume 24. [Google Scholar]
  82. International Energy Agency Fuel Economy—Fuels & Technologies. Available online: https://www.iea.org/fuels-and-technologies/fuel-economy (accessed on 22 March 2023).
  83. International Council on Clean Transportation. The Effectiveness of the U.S. Corporate Average Fuel Economy Standards. 2019. Available online: https://www.theicct.org/publications/effectiveness-us-corporate-average-fuel-economy-standards (accessed on 22 March 2023).
  84. Kearns, D.; Liu, H.; Consoli, C. Technology readiness and costs of CCS. Glob. CCS Inst. 2021, 3. [Google Scholar]
  85. Intergovernmental Panel on Climate Change (IPCC). 2018. Available online: https://www.ipcc.ch/2018 (accessed on 24 March 2023).
  86. Race to zero: How Manufacturers are Positioned for Zero-Emission Commercial Trucks and Buses in North America. International Council on Clean Transportation. Available online: https://theicct.org/publication/race-to-zero-how-manufacturers-are-positioned-for-zero-emission-commercial-trucks-and-buses-in-north-america (accessed on 24 March 2023).
  87. Petrauskienė, K.; Galinis, A.; Kliaugaitė, D.; Dvarionienė, J. Comparative Environmental Life Cycle and Cost Assessment of Electric, Hybrid, and Conventional Vehicles in Lithuania. Sustainability 2021, 13, 957. [Google Scholar] [CrossRef]
  88. Pörtner, H.O.; Roberts, D.C.; Adams, H.; Adler, C.; Aldunce, P.; Ali, E.; Begum, R.A.; Betts, R.; Kerr, R.B.; Biesbroek, R.; et al. Climate Change 2022: Impacts, Adaptation and Vulnerability; IPCC: Geneva, Switzerland, 2022; p. 3056. [Google Scholar]
  89. Jacobson, M.Z.; Delucchi, M.A.; Bauer, Z.A.F.; Goodman, S.C.; Chapman, W.E.; Cameron, M.A.; Bozonnat, C.; Chobadi, L.; Clonts, H.A.; Enevoldsen, P.; et al. 100% Clean and Renewable Wind, Water, and Sunlight All-Sector Energy Roadmaps for 139 Countries of the World. Joule 2017, 1, 108–121. [Google Scholar] [CrossRef]
  90. Ding, Q.; Xiao, X.; Kong, D. Estimating energy-related CO2 emissions using a novel multivariable fuzzy grey model with time-delay and interaction effect characteristics. Energy 2023, 263, 126005. [Google Scholar] [CrossRef]
  91. Wang, Y.; Yang, P.; Song, Z.; Chevallier, J.; Xiao, Q. Intelligent Prediction of Annual CO2 Emissions Under Data Decomposition Mode. Comput. Econ. 2023. [Google Scholar] [CrossRef]
  92. Seattle Department of Transportation. Available online: https://www.seattle.gov/transportation (accessed on 24 March 2023).
  93. Maibach, E.; Frumkin, H.; Roser-Renouf, C. Climate Silence on the Web Sites of US Health Departments. Am. J. Public Health 2020, 110, 1121–1122. [Google Scholar] [CrossRef]
  94. IEA (International Energy Agency). Energy Efficiency 2020. 2020. Available online: https://www.iea.org/reports/energy-efficiency-2020 (accessed on 24 March 2023).
  95. Peters, G.P.; Minx, J.C.; Weber, C.L.; Edenhofer, O. Growth in emission transfers via International Trade from 1990 to 2008. Proc. Natl. Acad. Sci. USA 2011, 108, 8903–8908. [Google Scholar] [CrossRef]
  96. Ma, S.; Lei, T.; Meng, J.; Liang, X.; Guan, D. Global Oil Refining’s contribution to greenhouse gas emissions from 2000 to 2021. Innovation 2023, 4, 100361. [Google Scholar] [CrossRef]
  97. Thorve, S.; Baek, Y.Y.; Swarup, S.; Mortveit, H.; Marathe, A.; Vullikanti, A.; Marathe, M. High resolution synthetic residential energy use profiles for the United States. Sci. Data 2023, 10, 76. [Google Scholar] [CrossRef] [PubMed]
Figure 1. (A) CO2 contribution from the four major energy sectors. (B) CO2 contribution from fossil fuels.
Figure 1. (A) CO2 contribution from the four major energy sectors. (B) CO2 contribution from fossil fuels.
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Figure 2. (A) Sector-wise CO2 emissions for the top 10 polluted states (Texas (TX), California (CA), Florida (FL), Louisiana (LS), Pennsylvania (PA), Ohio (OH), Illinois (IL), Indiana (IN), New York (NY) and Michigan (MI)). (B) Facility level contribution of CO2 emissions from the top 10 polluted states.
Figure 2. (A) Sector-wise CO2 emissions for the top 10 polluted states (Texas (TX), California (CA), Florida (FL), Louisiana (LS), Pennsylvania (PA), Ohio (OH), Illinois (IL), Indiana (IN), New York (NY) and Michigan (MI)). (B) Facility level contribution of CO2 emissions from the top 10 polluted states.
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Figure 3. Fossil fuels and sector nexus of CO2 emissions.
Figure 3. Fossil fuels and sector nexus of CO2 emissions.
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Figure 4. (A) Total coal production in the US. (B) Total coal consumption in the US.
Figure 4. (A) Total coal production in the US. (B) Total coal consumption in the US.
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Figure 5. (A) Total crude oil and petroleum production in the US. (B) Total crude oil and petroleum consumption in the US.
Figure 5. (A) Total crude oil and petroleum production in the US. (B) Total crude oil and petroleum consumption in the US.
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Figure 6. (A) Total natural gas production in the US. (B) Total natural gas consumption in the US.
Figure 6. (A) Total natural gas production in the US. (B) Total natural gas consumption in the US.
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Figure 7. Forecasted vs. action EFF.
Figure 7. Forecasted vs. action EFF.
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Table 1. National characteristics and emissions of the US states.
Table 1. National characteristics and emissions of the US states.
RankStateTotal Emissions (MMT CO2e)Population (Million)GDP Per Capita (Thousand $)HDI *HDI Rank
1TX83125.618310.91732
2CA42937.3828710.93615
3FL26919.2110090.91633
4LS23445.612280.89345
5PA29812.667140.92826
6OH27911.566150.91930
7IL27012.77750.93422
8IN2436.483530.91236
9NY21319.4214920.94410
10MI2069.974730.91831
* HDI ≥ 0.8 → very high; HDI = 0.7 → high; HDI = 0.55~ 0.69 → medium; HDI ≤ 0.54 → low.
Table 2. Descriptive statistics.
Table 2. Descriptive statistics.
VariablesStatisticsTXCAFLLSPAOHILINNYMI
** EFFMean830.95428.91269.45234.32298.23278.64269.77242.64212.82206.18
Range165.00188.00157.00168.0080.00100.0092.0098.0073.0063.00
Maximum888.00472.00297.00381.00328.00322.00294.00273.00246.00232.00
Minimum723.00284.00140.00213.00248.00222.00202.00175.00173.00169.00
Standard Deviation37.3840.6031.2834.3524.5434.5025.2729.2220.5816.68
Variance1397.191648.18978.551179.66602.181190.43638.37853.96423.58278.16
Skewness−1.29−2.24−3.594.03−0.39−0.12−1.55−0.910.15−0.09
Kurtosis2.407.2915.2517.66−1.07−1.622.000.00−1.08−0.54
** TPMean25.6037.3819.2145.6112.6611.5612.706.4819.429.97
Range9.395.526.203.790.730.430.460.741.100.19
Maximum30.2939.5022.2446.8113.0111.7912.896.8320.1010.06
Minimum20.9033.9816.0443.0212.2811.3612.436.0919.009.87
Standard Deviation2.931.801.851.020.220.120.140.230.290.06
Variance8.573.233.411.040.050.020.020.050.080.00
Skewness−0.08−0.41−0.03−0.92−0.310.26−0.35−0.210.44−0.18
Kurtosis−1.31−1.21−1.040.39−0.89−0.80−0.97−1.06−0.35−1.20
** GDPPCMean1386.582166.95819.45230.57634.73553.49713.15302.871281.48439.26
Range835.701179.10365.9842.05177.38112.45136.9393.15402.5590.19
Maximum1831.362871.421008.69247.77716.17615.42777.65352.621494.74473.33
Minimum995.661692.32642.71205.72538.79502.97640.72259.471092.19383.14
Standard Deviation269.50352.4797.3810.9955.5334.3942.8125.13132.9121.68
Variance72,630.76124,233.019482.55120.773083.311182.451832.83631.6217,663.9469.85
Skewness0.140.520.12−0.75−0.190.32−0.210.070.12−0.76
Kurtosis−1.28−0.74−0.380.56−1.12−1.06−0.91−0.52−1.320.81
** EFF—Emissions from fossil fuel (MMT CO2e); TP—Total Population (millions); GDPPC—Gross Domestic Product Per Capita (Current USD ($)).
Table 3. Results of the correlation analysis.
Table 3. Results of the correlation analysis.
StateTXCA
VariablesEFFGDPPCTPEFFGDPPCTP
EFF10.820.9810.630.69
GDPPC0.8210.990.6310.93
TP0.980.9910.690.931
StateFLLS
VariablesEFFGDPPCTPEFFGDPPCTP
EFF10.670.7910.890.77
GDPPC0.6710.920.8910.98
TP0.790.9210.770.981
StatePAOH
VariablesEFFGDPPCTPEFFGDPPCTP
EFF1−0.87−0.861−0.83−0.93
GDPPC−0.8710.94−0.8310.91
TP−0.860.941−0.930.911
StateILIN
VariablesEFFGDPPCTPEFFGDPPCTP
EFF1−0.660.881−0.81−0.87
GDPPC−0.6610.64−0.8110.94
TP0.880.641−0.870.941
StateNYMI
VariablesEFFGDPPCTPEFFGDPPCTP
EFF1−0.89−0.8910.990.98
GDPPC−0.891.000.860.9910.99
TP−0.890.8610.980.991
Table 4. Model development.
Table 4. Model development.
StateModels
TXTP = (14.613) − (0.004) · EFF + (0.010) · GDPPC
CATP = (25.757) + (0.002) · EFF + (0.005) · GDPPC
FLTP = (7.361) − (0.005) · EFF + (0.016) · GDPPC
LSTP = (126.161) – (0.175) · EFF − (0.192) · GDPPC
PATP = (1539.156) − (98.143) · GDPPC
OHTP = (11.219) − (0.002) · EFF + (0.002) · GDPPC
ILTP = (11.236) + (0.002) · GDPPC
INTP = (5.258) − (0.002) · EFF + (0.006) · GDPPC
NYTP = (20.828) − (0.01) ·EFF + (0.001) · GDPPC
MITP = (8.923) +(0.001) · EFF + (0.002) · GDPPC
Table 5. Contribution percentages of variables to the developed models.
Table 5. Contribution percentages of variables to the developed models.
VariablesEFF (%)GDPPC (%)TP (%)
TX22.235.159.04
CA10.576.1520.72
FL8.608.4110.84
LS6.8220.9843.84
PA11.4357.47
OH8.0616.0996.26
IL16.790.8
IN812.0529.39
NY89.6466.92
MI1020.26166.17
Table 6. Verification of the statistical results.
Table 6. Verification of the statistical results.
StateIndependent
Variables
StandardtcalculatedttableFcalculatedFtableR2
Error of Estimation
TXConstant0.40738 2.093489.4343.520.98
EFF 99.592
GDPPC 23.937
Constant0.72275 2.09355.7713.520.85
CAEFF 43.928
GDPPC 28.474
Constant0.70982 2.09355.3853.520.85
FLEFF 36.581
GDPPC 39.205
Constant12.04626 2.09318.213.520.98
LSEFF 25.710
GDPPC 79.265
Constant12.73524 2.08657.9713.520.99
PAEFF 54.175
GDPPC 52.739
Constant0.03269 2.093129.2393.520.92
OHEFF 36.192
GDPPC 74.156
Constant0.10978 2.08613.6493.520.99
ILEFF 47.664
GDPPC 76.899
Constant0.06591 2.093108.2453.520.92
INEFF 37.659
GDPPC 55.778
Constant0.12201 2.09348.8463.520.84
NYEFF 43.525
GDPPC 44.623
Constant0.04222 2.09311.2563.520.99
MIEFF 55.236
GDPPC 93.064
Table 7. Forecasted CO2 emission.
Table 7. Forecasted CO2 emission.
Projected PeriodForecasted EFF (MMT CO2)
StateTXCAFLLSPAOHILINNYMI
2025812.0367.4255.4198.3236.5198.6215.00177.04161.67160.60
2030819.4339.4238.9193.2207.8162.8186.00144.79138.05141.12
2035822.8319.4231.3183.2183.3134.0159.20114.16120.91124.41
2040809.8292.1221.8175.6160.5106.7134.6690.07100.56105.40
2045814.7274.1213.8165.7138.776.3118.6366.8182.9591.28
2050814.5248.3202.1158.3112.545.489.4736.0262.3572.26
Table 8. Performance methods for the proposed models.
Table 8. Performance methods for the proposed models.
StateMAPE (%)Forecast Accuracy for the MAPE
MAPE ≤ 10 ⇒Highly accurate;
11 ≤ MAPE ≤ 50 ⇒Mostly Accurate;
21 ≤ MAPE ≤ 51 ⇒Reasonable;
MAPE > 51 ⇒Inaccurate [65]
TX3.99Highly accurateMAPE ≤ 10
CA6.52
FL17.67
LS5.94
PA12.17Mostly accurate11 ≤ MAPE ≤ 50
OH14.04
IL4.13Highly accurateMAPE ≤ 10
IN8.81
NY9.61
MI11.48
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Keerthana, K.B.; Wu, S.-W.; Wu, M.-E.; Kokulnathan, T. The United States Energy Consumption and Carbon Dioxide Emissions: A Comprehensive Forecast Using a Regression Model. Sustainability 2023, 15, 7932. https://doi.org/10.3390/su15107932

AMA Style

Keerthana KB, Wu S-W, Wu M-E, Kokulnathan T. The United States Energy Consumption and Carbon Dioxide Emissions: A Comprehensive Forecast Using a Regression Model. Sustainability. 2023; 15(10):7932. https://doi.org/10.3390/su15107932

Chicago/Turabian Style

Keerthana, Krishnamurthy Baskar, Shih-Wei Wu, Mu-En Wu, and Thangavelu Kokulnathan. 2023. "The United States Energy Consumption and Carbon Dioxide Emissions: A Comprehensive Forecast Using a Regression Model" Sustainability 15, no. 10: 7932. https://doi.org/10.3390/su15107932

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