Atmospheric Carbon Dioxide (CO2), a significant greenhouse gas, drives climate change, influencing temperature, rainfall, and the hydrologic cycle. This alters precipitation patterns, intensifies storms, and changes drought frequency and timing of floods, impacting ecosystems, agriculture, water resources, and societies globally. Understanding how global CO2 fluctuations impact regional atmospheric CO2 levels can inform mitigation strategies and Facilitate water resources management. The study investigates how global CO2 fluctuations affect atmospheric CO2 concentrations (XCO2) in Iran from 2015 to 2020, aiming to inform mitigation strategies against climate change. XCO2 data OCO-2 satellite and CO2 surface flux data from the Copernicus Atmosphere Monitoring Service (CAMS) were analyzed. Over the 6 years, XCO2 in Iran increased steadily by 12.66 ppm, mirroring global rises. However, Iran's CO2 surface flux decreased, with slight increases in anthropogenic emissions but decreased natural and total fluxes. Monthly patterns of XCO2 and surface flux exhibited variations, with XCO2 reaching its zenith in spring and dipping to its lowest point during summer, while surface flux peaked during the summer months. The results reveal a significant discrepancy between Iran's surface CO2 flux and atmospheric XCO2 trends. While Iran's anthropogenic emissions increased barely from 2015–2020, its natural and total CO2 fluxes decreased. However, XCO2 increased steadily over this period, indicating the dominant impact of global rather than local factors on Iran's XCO2. Curbing worldwide greenhouse gas output is imperative to disrupt the current trajectory of climate change. Reporting CO2 levels can inform climate mitigation plans, reducing emissions to combat global warming and minimize global impacts on the hydrologic cycle.

  • Global CO2 changes significantly impacted atmospheric CO2 levels in Iran from 2015–2020.

  • Atmospheric CO2 in Iran increased 12.66 ppm despite decreases in natural CO2 fluxes.

  • The discrepancy between surface flux and atmospheric CO2 trends indicates global dominance.

  • Emphasizes the critical role of global CO2 changes over local emissions.

Climate change, driven by increasing greenhouse gas (GHG) emissions, demands attention (Hatami et al. 2024). Projected sea level rise under various scenarios underscores the urgency of mitigation efforts. Connecting CO2 emissions to global warming, strategic actions can mitigate climate change impacts on critical water resources like groundwater, surface water, rainfall patterns, and floods (Safaeian et al. 2023; Mousavi et al. 2022a; Moshir Panahi et al. 2020; Fu et al. 2019) and led to global concerns in the international community (Bonneuil et al. 2021; Borhani et al. 2022); hence, environmentalists have been concerned about GHG emissions (Darvishi et al. 2024; Hatami et al. 2024; Khordehbin et al. 2020). In light of the Industrial Revolution's commencement, the surging demand for energy, primarily stemming from the combustion of fossil fuels, has precipitated a marked escalation in GHG emissions (Jenn et al. 2019; Fu et al. 2020; Mousavi et al. 2020). Atmospheric carbon dioxide (XCO2) is a significant GHG arising from a combination of human activities and natural phenomena (Mehmood et al. 2020; Borhani et al. 2024). Thus, the average concentration of XCO2 from 280 ppm in 1750 reached 417 ppm in 2021 (Tocco et al. 2021). The persistent emission of greenhouse gases into the atmosphere presents substantial challenges to the ecosystems of our planet, as well as to weather patterns and the broader sustainability of our environment (Cheraghi & Borhani 2016; Borhani et al. 2023a, 2023b). The Earth can be viewed as a dynamic system with various sources contributing to the input and output of carbon. Input sources release carbon dioxide (CO2) into the atmosphere, while output sources are reservoirs that store carbon (Rahman et al. 2017). Carbon input sources encompass a range of factors, including the consumption of fossil fuels, soil processes, plant respiration, and alterations in land use. Conversely, carbon output sources involve phenomena such as plant photosynthesis and the absorption of carbon by marine ecosystems (Mac Dowell et al. 2017; Ghayoumi et al. 2022, 2023). The equilibrium between carbon input and output from natural sources was historically maintained.

Nevertheless, in recent decades, the equilibrium has been disrupted due to the escalation of anthropogenic activities and the resulting increase in CO2 emissions. This disruption has precipitated climate change and global warming as consequential outcomes (Change 2007; Peiro et al. 2022; Sun et al. 2022). Comprehending the intricacies of the carbon cycle and the carbon budget is paramount when investigating the origins and reservoirs of XCO2. Consequently, quantifying and categorizing sources contributing to emissions and absorption affecting XCO2 concentration serve as valuable tools for environmental assessment and carbon management strategies.

Atmospheric carbon dioxide can be quantified using diverse techniques, including ground-based stations, tall towers, atmospheric measurements conducted via balloons, and data collected from ships and aircraft (O'Dell et al. 2018; Chiba et al. 2019; Shah et al. 2019; Bluestein et al. 2022; Pellegrini et al. 2022). Although these techniques produce accurate measurements, their major weakness is spatial restriction, as there is no ground station in many parts of the world, like Iran and the Middle East (Mousavi et al. 2023). Remote sensing science solves this issue by continuously tracking GHG levels across the planet and taking measurements everywhere (Pan et al. 2021). The XCO2 is measured by a variety of satellites, including the ‘National Aeronautics and Space Administration (NASA)’ ‘Orbiting Carbon Observatory-2 (OCO-2)’ and OCO-3 satellites, the ‘Greenhouse Gas Observing Satellite (GOSAT),’ and GOSAT-2 satellite, and the ‘Scanning Imaging Absorption Spectrometer for Atmospheric CHartography (SCIAMACHY)’ satellite from the ‘European Space Agency’ (Butz et al. 2011; Kavitha & Nair 2016; Wunch et al. 2017; Shim et al. 2019; Suto et al. 2021).

The OCO-2 satellite, launched in 2014 and has been continually measuring to date, is one of the most accurate CO2 monitoring satellites. According to validation research, this satellite has an uncertainty of less than 1% (Reuter et al. 2019; Kiel et al. 2021). Satellites for detecting GHG, such as the OCO-2, exclusively monitor the CO2 concentration in the atmosphere. The CO2 molecules are counted from the Earth's surface to the top of the atmosphere using these measurements (Liang et al. 2017; He et al. 2020). These observations only offer the XCO2 data.

Several studies have assessed the GHG emissions, trend variations, and their modeling in Iran, examining the issue from various perspectives. Notable among these are the works of Mousavi et al. (2017) who assessed the relationship between XCO2 and meteorological parameters; Falahatkar et al. (2017) who investigated the spatial distribution of XCO2 in Iran in different seasons; Mousavi & Falahatkar (2020) who assessed the relationship between CH4 concentration and environmental variables, Mousavi et al. (2022b) who analyzed the spatiotemporal patterns of XCO2, Siabi et al. (2019) who assessed the spatial distribution of XCO2 in growing seasons by using eight environmental variables, Golkar & Shirvani (2020) who investigated the spatial and temporal distribution of XCO2, Mousavi et al. (2018) who determined the relationship between XCO2 and CH4 concentration and environmental variables, and Golkar & Mousavi (2022) who studied the role of anthropogenic CO2 emission on XCO2 in the middle east.

So far, no research has been conducted to explore the influence of net CO2 absorption and emission on XCO2 levels in Iran. Therefore, the central question in the present research is to gain insights into how global fluctuations in XCO2 levels impact the XCO2 in Iran. Comparing CO2 surface flux data obtained from the Copernicus Atmosphere Monitoring Service (CAMS), which reveals net CO2 absorption and emission, with atmospheric CO2 concentration data from OCO-2 allows us to examine the role of global fluctuations in XCO2 levels and their impact on XCO2 concentrations. This study aimed to examine and compare the quantity of net CO2 emitting and absorption of Iran with its atmospheric concentration to determine the potential consequences of global CO2 changes on its concentration in Iran. Reporting CO2 levels aids policymakers and environmental planners in emission reduction and implementing mitigation strategies, which is crucial for managing water resources amidst climate change impacts. In this study, first, by using monthly XCO2 data from the OCO-2 satellite, the monthly and yearly amplitude of XCO2 from 2015 to 2020 were examined. Then, to examine the exact amount of CO2 emission and absorption, the CAMS data were used for this period.

Study area

Iran is a country in West Asia and the center of the Middle East, which lies between 25°–40° N latitudes and 44°–64° E longitude (Figure 1). Iran has an approximate area of 165 million hectares, including 90 million hectares of rangeland (54.6%), 34 million hectares of deserts (20.6%), 12.4 million hectares of forest (7.5%), 18.5 million hectares of cropland (11.2%), and 1.10 million hectares of residential areas, infrastructure, and water bodies (6.4%). Precipitation in Iran, with a mean annual of 250 mm, varies widely across regions, influenced by factors such as geography and monsoons, while evapotranspiration is high due to arid conditions, posing challenges for water management (Fathian et al. 2020; Ghalami et al. 2021). Also, Iran has a variety of climates, such as the temperate and humid southern coastlines of the Caspian Sea, the cold climate of the western mountains, the hot and dry climate of the central plateau, and the warm and humid climate of the southern coasts (Food and Agriculture Organization 2021, February 14). Iran's average annual precipitation, temperature, and mean elevation are 245 mm, 18.2 °C, and 1,200 m above sea level, respectively. Its highest point is Damavand Mountain, at a height of 5,610 m, and its lowest point is a location in the Lut desert at 56 m below the sea level (Kousari et al. 2011; Food and Agriculture Organization 2021, February 14). With a share of 18.2% of global gas reserves and 9.3% of global oil reserves, respectively, Iran is the largest holder of gas and the fourth holder of oil resources in the world (British Petroleum 2021, March 16). According to the Ministry of Energy statistics, the amounts of GHG emissions of CO2 reported in Table 1 are caused by the usage of various fuels in agriculture; industry; transportation; domestic, commercial, and public use; refineries; and power plants (Crippa et al. 2020). In December 2014, Iran ratified the Kyoto Protocol and announced cooperation regarding reducing GHGs in various energy, oil, gas, agriculture, natural resources, and forestry sectors.
Table 1

Anthropogenic carbon dioxide (CO2) emission from various sectors in Iran from 2000 to 2019

SectorCO2 emission (ton)CO2 emission (%)
Agriculture 12.5 million 2.14 
Industry 94 million 16.10 
Transportation 148.44 million 25.43 
Domestic, commercial, public 139.51 million 23.90 
Refineries 15.05 million 2.57 
Power plants 174.01 million 29.99 
SectorCO2 emission (ton)CO2 emission (%)
Agriculture 12.5 million 2.14 
Industry 94 million 16.10 
Transportation 148.44 million 25.43 
Domestic, commercial, public 139.51 million 23.90 
Refineries 15.05 million 2.57 
Power plants 174.01 million 29.99 
Figure 1

Location of the study area and anthropogenic CO2 emissions in different places.

Figure 1

Location of the study area and anthropogenic CO2 emissions in different places.

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Datasets

  • 1.

    Atmospheric carbon dioxide concentration CO2 dataset of OCO-2 satellite

NASA's first satellite mission to observe atmospheric column CO2 concentration, the Orbiting Carbon Observatory-2 (OCO-2), was launched in 2014 (Frankenberg et al. 2014; Wunch et al. 2017). The OCO-2 satellite flies in a sun-synchronous, near-polar orbit that completes its rotation in 98.8 min each time, and the ascending node crosses the equator at 13:36 mean local time (GMT) (Crisp et al. 2004; National Aeronautics and Space Administration 2018, January 23). Passing in the early afternoon maximizes the available reflectance signals and minimizes measurements of daily CO2 skewness associated with photosynthesis (Parkinson et al. 2006). The flight height of this satellite is 705 km, and its primary purpose is to measure CO2 gas concentration on a continental and regional scale with a spatial resolution of approximately 3 km2 (Eldering et al. 2017). The OCO-2 satellite carries a sensor that includes three network spectrometers with high magnification that measure the intensity of three bands in the spectral regions of the near-infrared and short-wave infrared in ranges of 0.76 μm (A band for O2), 1.6 μm (weak CO2 band), and 2 μm (strong CO2 band), each specific to one of the three spectrometers (Yang et al. 2020). This satellite can track alterations on the surface by simultaneously measuring gases in the exact location over time (Frankenberg et al. 2014). Twenty-four spectra are recorded by each spectrometer per second (Osterman et al. 2016). Although about one million datasets are collected daily, only about 10% of these data will be suitable for calculating the amount of carbon CO2 due to the limitation of cloud cover (Osterman et al. 2016; Richardson et al. 2017). This satellite's simultaneous collection of O2 and CO2 values with high spatial magnification reduces the random error and minimizes the influence of cloudiness, aerosols, and other disturbing sources on recording the CO2 values (Parkinson et al. 2006). The OCO-2 satellite retrieves the XCO2 in three observation modes: nadir, glint spot, and target.

In contrast to the nadir and glint modes regarded as scientific, the target mode is intended to test the OCO-2 XCO2 products' accuracy by focusing on validation sites. This satellite performs its measurements in the SWIR regions, and its measurement accuracy is 0.3% (Crisp et al. 2004; Miller et al. 2005; Pillai et al. 2010; Cortesi et al. 2014). Daily CO2 gas data from level 2 of the OCO-2 satellite from 2015 to 2020 were used in this investigation. It should be emphasized that level 2 data, verified using ground-based sources, only provides 10% of all the data that are reliable for public use.

  • 2.

    Carbon dioxide surface flux data

In 2020, the CAMS, managed by the European Centre for Medium-Range Weather Forecasts (ECMWF), provided a series of global surface flux data products for CO2, CH4, and nitrous oxide (N2O) at 3-h intervals at a spatial resolution of 1.875° × 3.75°. Mousavi et al. (2024) validated these data with ground stations and stated that the CO2 flux data have high reliability with less than 1 ppm error. For this investigation, according to the purpose of the research, the latest version (v20r3) was used from January 2015 to January 2020, whose data include (a) natural CO2 emission and absorption, (b) anthropogenic CO2 emission, and (c) total CO2 emission caused by natural and human activities.

This study comprises five primary sections, as delineated in Figure 2 through an illustrative flowchart: (a) Acquiring essential data involves retrieving XCO2 and CO2 surface flux data spanning the years 2015–2020. (b) During this phase, a series of preprocessing procedures, such as screening, is conducted. Monthly data are then extracted and delineated for the study area, and prepared for diverse analyses. (c) In this stage, computations are performed using the prepared dataset from 2015 to 2020 to determine monthly and annual averages, along with their variations. In addition, spatial distribution maps for XCO2 and carbon flux are generated. (d) The final stage involves a comparative analysis of monthly, seasonal, and annual fluctuations in these two categories of CO2 data. The objective is to ascertain the global influence of atmospheric carbon dioxide on its local counterpart.
Figure 2

The logical flowchart of this study.

Figure 2

The logical flowchart of this study.

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In this study, the researchers categorized the seasons based on the respective months of the year: winter (JFM), spring (AMJ), summer (JAS), and autumn (OND) as outlined (Luo et al. 2013).

  • 1.

    Monthly and annual changes in atmospheric CO2 concentration:

The annual changes in XCO2 obtained from the OCO-2 satellite are shown in Figure 3; this gas increased from 399.77 ppm in 2015 to 412.43 ppm in 2020, indicating an increase of 12.66 ppm. Furthermore, it is noteworthy that XCO2 exhibited annual increments each year within this timeframe, with an average annual increase of 2.53 ppm. The increase in XCO2 levels in Iran correlates with the global rise in atmospheric carbon dioxide (Tans & Keeling 2023).
Figure 3

Changes in atmospheric column CO2 concentration (XCO2) over Iran from 2015 to 2021.

Figure 3

Changes in atmospheric column CO2 concentration (XCO2) over Iran from 2015 to 2021.

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In addition to the annual changes, monthly fluctuations in XCO2 were investigated using the OCO-2 satellite. Figure 4 demonstrates the monthly values of this gas from 2015 to 2021, and Figure 5 depicts the average changes in XCO2 during this period.
Figure 4

Monthly concentrations of atmospheric carbon dioxide from 2015 to 2021.

Figure 4

Monthly concentrations of atmospheric carbon dioxide from 2015 to 2021.

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Figure 5

Average monthly changes of atmospheric carbon dioxide from 2015 to 2021.

Figure 5

Average monthly changes of atmospheric carbon dioxide from 2015 to 2021.

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In the case of monthly and seasonal amplitude, XCO2 had intra-annual fluctuations. It demonstrated a notable cyclic pattern, reaching its peak during late winter in March and extending into early spring in April and May (Figure 4). These fluctuations were such that the XCO2 increased from January and reached its highest value in spring and May. The atmospheric concentration of this gas decreased from May onward and reached its minimum value in summer and September. Another increase from September onward followed it, and this was repeated during different years. The details of these changes are shown in Figure 5. Overall, these findings align with prior research studies conducted by Mousavi et al. (2022b), Falahatkar et al. (2017), Sheng et al. (2023), Gupta et al. (2019), and Chhabra & Gohel (2019).

In addition, we observed a notable surge in XCO2 levels during the transition from summer to autumn, with an approximately 4 ppm increase. However, as we transitioned from autumn to winter, the growth rate of XCO2 declined, suggesting a marginal increase or a stable XCO2 level. Monthly and seasonal variations in XCO2 are influenced by factors such as CO2 emissions, terrestrial ecosystems, temperature, rainfall, and other contributors (Cao et al. 2019; Lv et al. 2020).

  • 2.

    Annual and monthly changes in CO2 surface flux in Iran

In this research, apart from examining XCO2, as discussed in the preceding section, we also analyzed the monthly and annual variations in CO2 surface flux in Iran to discern the possible ramifications of global CO2 fluctuations on its concentration within Iran. These values are given in three forms: surface flux of natural CO2, anthropogenic CO2, and the total natural and anthropogenic CO2 (Figure 6).
Figure 6

The trend of annual changes in CO2 surface flux (natural, anthropogenic, and total natural and fossil) from 2015 to 2020 in Iran.

Figure 6

The trend of annual changes in CO2 surface flux (natural, anthropogenic, and total natural and fossil) from 2015 to 2020 in Iran.

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In the study of the annual changes in the CO2 surface flux in Iran, it was realized that anthropogenic emissions have increased slightly during the period from 2015 to 2020 in Iran. Meanwhile, Iran's total anthropogenic and natural emissions and natural emissions and absorption not only did not increase but also did not decrease, whose details are displayed in Figure 6. Furthermore, this trend increased only in 2017 compared to the previous year, but its amount decreased in the next 2 years. Also, in 2019, the most significant decrease was observed compared to the previous year, in both natural and total emissions. In 2018 and 2019, Iran experienced heavy rainfall, especially in 2019, which marked the highest precipitation in the past 50 years (Sadeghi et al. 2021). These episodes of intense rainfall had far-reaching impacts on various aspects of the environment. They triggered significant changes in vegetation dynamics, leading to flourishing plant growth across various landscapes. This surge in vegetation had significant implications for the ecosystem's ability to capture and store CO2. As vegetation expanded and thrived in the wake of ample rainfall, it acted as a potent carbon sink, absorbing greater amounts of CO2 from the atmosphere. This carbon sequestration process was vital in mitigating greenhouse gas emissions and regulating atmospheric CO2 levels. Thus, the pronounced increase in vegetation cover following the heavy rainfall events in 2018 and 2019 exemplifies the intricate interplay between climate patterns, vegetation dynamics, and the global carbon cycle, underscoring the importance of understanding and managing these relationships in the context of climate change mitigation and ecosystem resilience. In addition to the annual changes in the CO2 surface flux, its monthly changes also included the surface flux of natural CO2, anthropogenic CO2, and total natural and anthropogenic CO2 examined, which are shown in Figures 79.
Figure 7

Monthly CO2 surface flux from anthropogenic emissions from 2015 to 2020.

Figure 7

Monthly CO2 surface flux from anthropogenic emissions from 2015 to 2020.

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Figure 8

Monthly CO2 surface flux from natural emissions and adsorption from 2015 to 2020.

Figure 8

Monthly CO2 surface flux from natural emissions and adsorption from 2015 to 2020.

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Figure 9

Monthly CO2 surface flux emission from the total natural and anthropogenic from 2015 to 2020.

Figure 9

Monthly CO2 surface flux emission from the total natural and anthropogenic from 2015 to 2020.

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In addition to Figures 79, which demonstrates the monthly values of the CO2 surface flux, the average values of the surface flux during these 5 years for natural, anthropogenic, and total natural and anthropogenic emissions are shown separately in Figure 10. Figure 7 shows that the maximum quantity of CO2 surface flux induced by human activities occurred in January. However, its emission rate declined from January forward, reaching its lowest level in July. After that, its value rose again, and this cycle was repeated yearly. Due to the lowest air temperatures, which primarily manifest during the winter, especially in January, there is a noticeable increase in the consumption of fossil fuels for heating purposes. This rise in fossil fuel usage during winter leads to the highest levels of human-generated emissions. In the Northern Hemisphere, particularly during January, winter's peak heating demands drive a substantial surge in the consumption of fossil fuels, including natural gas, oil, and coal, in densely populated regions of North America, Europe, and Asia (Zhang et al. 2013).
Figure 10

Average monthly changes of CO2 surface fluxes due to anthropogenic emissions, natural, and total anthropogenic and natural from 2015 to 2020.

Figure 10

Average monthly changes of CO2 surface fluxes due to anthropogenic emissions, natural, and total anthropogenic and natural from 2015 to 2020.

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Based on the results presented in Figure 8, the net CO2 emissions and absorption resulting from natural processes were in the negative range throughout the months of March, April, and May. This indicates that natural activities' absorption of atmospheric carbon dioxide outweighs its emission in these specific months. During the spring season, spanning from March through May, the peak in vegetation cover results in a notable surge in photosynthesis relative to respiration. Consequently, this season induces an increased uptake of atmospheric carbon dioxide by the prevailing vegetation (Yuan et al. 2018). The seasonal cycle of atmospheric CO2 is notably enhanced in northern mid-high latitudes, driven by the extended growing season resulting in increased photosynthesis and CO2 drawdown (Forkel et al. 2016). This amount was positive in other months of the year, indicating that CO2 emissions through natural activities (respiration) exceed CO2 absorption (photosynthesis). In cold seasons, reduced photosynthesis in plants, combined with continuous respiration by living organisms, results in more CO2 being released into the atmosphere than absorbed, contributing to the cyclic variation in atmospheric CO2 levels (Nogia et al. 2016; Gayathri et al. 2021). This phenomenon is affected by global temperatures, cellular respiration, and temperature responses to photosynthesis and respiration in plants (Aspinwall et al. 2016; Crous et al. 2022).

In this research, it is observed that in Iran, the monthly variations in CO2 surface flux depict discrepancies in comparison to XCO2 values. The difference in the dataset demonstrates the substantial impact of extra-regional and global factors on the regulation of atmospheric CO2 concentrations within Iran, thereby bearing significant implications for comprehending and mitigating environmental challenges in this realm. Substantive further examination and rigorous analysis are imperative to determine the root causes of these fluctuations. Carbon dioxide is a well-mixed gas renowned for its swift and uniform dispersion throughout the atmosphere (Roberts et al. 2017). Its existence is not limited to localized sources but rather arises from a multifaceted spectrum of global emissions, demonstrating its pervasive ubiquity and consequential impact on the Earth's climate (Crippa et al. 2022).

Weir et al. (2021) and Zeng et al. (2021) investigated global atmospheric carbon dioxide concentrations, revealing that during the COVID-19 pandemic, XCO2 levels experienced a notable reduction in all regions worldwide, even in areas with minimal emissions. This finding indicates that greenhouse gases emitted from any location have a far-reaching impact on people worldwide. Furthermore, the increase in atmospheric carbon dioxide concentration is a consequence of its widespread global influence, leading to a rise in its concentration throughout all regions of the world (Morgan 2000; Tyfield & Urry 2009).

Natural emissions in Iran began decreasing in January. By March, April, and May, they had reached negative levels, revealing not only a lack of emissions but also a phase of absorption during these months. Subsequently, initially in May, nature resumed CO2 emissions, reaching their peak in July and August. After that, there was a gradual reduction in the volume of natural CO2 emissions, with this recurring cycle happening annually. Figures 9 and 10 display a comprehensive compilation of CO2 surface flux emissions in Iran, including both natural and anthropogenic sources. In July, when anthropogenic and natural emissions reached their zenith, a noticeable pattern emerged, demonstrating the prevalence of natural emissions over anthropogenic counterparts during this specific seasonal period. The combined sum of natural and anthropogenic emissions initiated a decline in January, eventually reaching its lowest level during the spring, particularly in May. Due to rising temperatures, resulting in reduced vegetation and heightened soil and plant respiration in the aftermath of this period, a significant increase in emissions occurred. This recurring cycle persisted over multiple years (LeMay & Kurz 2017).

During the study period, Iran experienced an increasing trend in the annual change of XCO2. Meanwhile, the annual changes in the CO2 surface flux caused by natural and anthropogenic activities not only do not show growth but also show a decrease in this period. These consequences serve as compelling evidence of the global impact of CO2 on atmospheric concentrations of this gas within Iran. As previously mentioned, the monthly patterns of the CO2 surface flux in Iran exhibit notable distinctions from XCO2, demonstrating the global impacts of XCO2 on the concentration of this gas in Iran. Mousavi et al. (2017) and Falahatkar et al. (2017) investigated the changes in XCO2 without considering the amount of surface flux in Iran; however, in the current study, besides considering XCO2, the CO2 surface flux in Iran was examined, which includes anthropogenic emissions, natural emissions, and absorption, as well as the total of natural and anthropogenic emissions.

  • 3.

    Spatial distribution of CO2 surface flux and XCO2 in Iran

In the present research, another examination was conducted to compare the spatial distribution of atmospheric carbon dioxide and CO2 surface flux (including natural, anthropogenic, and the combined total of natural and fossil sources) across various seasons in Iran from 2015 to 2020. The investigation aimed to provide a comprehensive analysis of these parameters, as illustrated in Figures 11 and 12, facilitating a more nuanced understanding of their dynamics and interactions within the studied timeframe.
Figure 11

The spatial distributions of atmospheric carbon dioxide during various seasons from 2015 to 2020, as determined by analyzing data from the OCO-2 satellite.

Figure 11

The spatial distributions of atmospheric carbon dioxide during various seasons from 2015 to 2020, as determined by analyzing data from the OCO-2 satellite.

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Figure 12

Spatial distribution of CO2 surface flux (natural, anthropogenic, and total natural and fossil) from 2015 to 2020 in Iran according to the CAMS surface flux data.

Figure 12

Spatial distribution of CO2 surface flux (natural, anthropogenic, and total natural and fossil) from 2015 to 2020 in Iran according to the CAMS surface flux data.

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The spatial distribution map of atmospheric carbon dioxide reveals notable variations in concentration levels across different seasons in Iran. The highest concentrations are observed during the spring season, predominantly in the central and southern regions of the country. Conversely, the lowest atmospheric carbon dioxide levels are evident during the summer, particularly in the northern regions of Iran (Figure 11). These findings highlight seasonal disparities in carbon dioxide distribution, shedding light on regional dynamics and contributing factors.

Meanwhile, the analysis of total carbon emissions and net absorption depicts the highest values during the summer season, particularly concentrated in Iran's northern and western regions. Conversely, the lowest values are observed in the spring season, primarily in the northern and northwestern areas of the country (Figure 12). This observation underscores seasonal emissions and absorption pattern variations, providing valuable insights into the regional dynamics of carbon balance within Iran. As can be seen, the spatial distribution of atmospheric carbon dioxide and the net amount of emission and absorption of Iran are different, so these spatial differences between the seasonal XCO2 and f CO2 surface fluxes in Iran demonstrate the effect of CO2 global change on the atmospheric concentration of CO2 in the study area. The seasonal changes of XCO2 in Iran are in line with global changes (Tans & Keeling 2023).

The findings unequivocally demonstrate that the global impact of CO2 fluctuations significantly influenced the annual and monthly variations in Iran's XCO2. Golkar & Shirvani (2020) depicted that the principal factor contributing to the rise in XCO2 in Iran was identified as the increasing emissions from fossil fuel sources. In contrast, the results of this research revealed that certain factors extending beyond the confines of local changes in Iran exerted influence on the variations in XCO2. These findings indicate that the effects of global CO2 fluctuations predominantly contributed to these variations. The research studies of Mousavi et al. (2018), Siabi et al. (2019) also exclusively relied on atmospheric GHG concentrations, even though it was suggested that surface flux data be applied in future modeling investigations.

In studies by Zeng et al. (2020) and Dacre et al. (2021), which investigated the impact of carbon dioxide emission reduction during the COVID-19 lockdown, it was observed that, during this period, when carbon dioxide emissions decreased, atmospheric carbon dioxide levels also diminished, even in regions with no emissions. This underscores the global influence of atmospheric carbon dioxide fluctuations on local environments, confirming our results regarding the role of global fluctuations of XCO2 on local XCO2.

This research utilized atmospheric CO2 concentration and CO2 surface flux data obtained from OCO-2 and CAMS, respectively, to investigate the influence of global CO2 changes on annual and monthly local variations in XCO2 levels across Iran.

  • In Iran, the XCO2 levels displayed a consistent upward trend over six years, surging by 12.66 ppm, from 399.77 ppm in 2015 to 412.43 ppm in 2020. This equates to an average annual increase of approximately 2.11 ppm. This steady ascent closely parallels the ongoing global surge in atmospheric CO2 concentrations.

  • The total surface flux of CO2 emissions, comprising anthropogenic and natural sources, peaked in July, while its nadir was observed in May. Meanwhile, data from the OCO-2 satellite revealed the highest atmospheric CO2 concentration in May and the lowest in September.

  • The observed disparities in monthly and annual variations between XCO2 and surface flux in Iran underscore the significant influence of external and global factors on the country's atmospheric CO2 levels. This underscores the need for policymakers and environmental planners to consider local emissions and global CO2 fluctuations when developing strategies to manage water resources amidst climate change impacts.

  • The findings underscore the urgent requirement for a coordinated global initiative to enact science-based policies that reduce escalating CO2 emissions, essential for addressing global warming and minimizing its adverse impacts on water resources. It is imperative to curb greenhouse gas emissions worldwide to alter the current course of climate change, which profoundly affects the hydrologic cycle, including precipitation patterns, storm intensities, drought frequency, and flood timing.

  • Quantitative analysis of CO2 concentrations and surface fluxes offers valuable insights into the carbon cycle, aiding in predicting and mitigating climate change's impact on water resources. Such data can inform the development of adaptation strategies, including water conservation, flood control infrastructure, and drought preparedness plans.

  • Qualitatively, the research highlights the interconnectedness of global climate change, greenhouse gas emissions, and local water resource management, emphasizing the importance of international cooperation, knowledge sharing, and collaborative efforts to address these interconnected challenges effectively.

This research highlights the significant influence of global CO2 fluctuations on local XCO2, underscoring the necessity for international collaboration in addressing escalating emissions and their detrimental effects, such as climate changeapos;s effect on water resources. To enhance analytical accuracy and conduct further investigation, it is advisable to incorporate the latest atmospheric CO2 data sources, such as GOSAT-2 and OCO-3. Additionally, the utilization of GRACE satellite data is proposed to examine changes in water resources, facilitating a more accurate understanding of the connection between the water and carbon cycles.

This work is based upon research funded by Iran National Science Foundation (INSF) under project No. 4014326. The authors gratefully acknowledge the National Aeronautics and Space Administration (NASA), the OCO-2 team for making the XCO2 dataset available, and the Copernicus Atmosphere Monitoring Service (CAMS) for GHG fluxes data provision.

All relevant data are included in the paper or its Supplementary Information.

The authors declare there is no conflict.

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