Investigation of monthly and seasonal changes of methane gas with respect to climate change using satellite data
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Climate change and global warming are the biggest challenges in the current century. Methane gas is one of the most important greenhouse gases which can contribute to creating warming weather (about 19%). In this research, satellite data from GOSAT and MODIS and also climatic data of precipitation, temperature and humidity are used to analyze monthly and seasonal methane changes in 2012 to 2018 in North America. The results show that the methane gas has increased during this period and it increases from 1789 to 1824 ppb. The gas has monthly fluctuation and in October and September has the maximum concentration and in March and April has the minimum value. The relationship between the methane gas and temperature and LST is positive, and the relationship between the methane gas and NDVI, precipitation and humidity is negative. This verifies that the increase in methane concentration has significant relationship with low vegetation cover and high temperature. Therefore, conservation of vegetation cover can help to reduce the methane concentration.
KeywordsMethane concentration Climate change Global warming Satellite data NDVI LST
List of abbreviations
Land surface temperature
Normalized difference vegetation index
Greenhouse Gases Observing Satellite
Moderate Resolution Imaging Spectroradiometer
Environmental Protection Agency
National Environmental Studies Association
Greenhouse gas observation sensor
Climate change, especially global warming, has attracted attention due to rising greenhouse gas emissions in the atmosphere. CO2 and other greenhouse gases, including CH4, N2O, HFCs, PFCs and SF6, are the ones that their release is under the control of the Kyoto Protocol (Iwata and Okada 2014). Methane gas alone accounts for more than 18% of the heat generated from greenhouse gas emissions. Changing the methane rate from 700 to 1808 ppb between 1850 and 2010 has shown an increase of 158% since the industrialization period (Heede 2014). The methane cycle has seasonal variations, which depend on the seasonality of the production resources (wetlands, rice fields and burning biomass) and the outflow from the atmospheric reaction of this gas (Saunois et al. 2016). Methane release sources are divided into three categories: thermogeneic, biogenetic and pyrogenic. Biogenic involves the production of microbial methane in anaerobic environments such as natural wetlands and rice fields, limited fresh oxygen reservoirs, including dams, digestive system of ruminant, termite and leachate sewage disposal sites and animal fertilizers (Wu et al. 2018). Thermogenic sources include explosions, fossil fuels from the ground and natural volcanoes, and pyrogenic sources include incomplete combustion of fossil fuels. There are various ways to measure greenhouse gases, including the use of ground bases in tall towers, ships, airplanes, airships and satellites (Schaefer et al. 2016). In the context of satellite monitoring of greenhouse gases, AIRS, SCIAMACHY, GOSAT and OCO-2’s sensors can be mentioned (Alexe et al. 2015). Currently, GOSAT is the only satellite that measures greenhouse gas mechanics and has a precision measurement of less than 1% (Kuze et al. 2016). Considering the new satellite monitoring of greenhouse gases, many studies have not been carried out in this area. Only a study in this area was conducted by Turner et al. 2015. They examined the use of MODIS satellite data to study the monthly and seasonal changes in greenhouse gas emissions of carbon dioxide. Given the widespread concern in the international community about climate change and according to reports by the Institute for International Natural Resources on the location of the leading greenhouse gas emissions in the Portal 2015, as well as the lack of ground bases, measurement of greenhouse gases in this area in the present study uses satellite data of GOSAT to investigate the monthly and seasonal changes in methane gas in this area (McKain et al. 2015). Considering the necessity of implementing the Environmental Council’s regulations on the design and deployment of a low-carbon economy system, the purpose of this study is to extract the satellite’s monitoring of methane gas and analyze its changes in this region in terms of time and the reasons that it can be understanding the potential sources of carbon emissions and releases, planning for macroeconomic policies and environmental measures to help assess the carbon cycle equilibrium of drought ecosystems.
Materials and methods
North America is bounded to the north via the Arctic Ocean, to the east through the Atlantic Ocean, to the west and south through the Pacific Ocean and to the southeast through South America and the Caribbean Sea (King 2015).
The area of North America is about 24,709,000 km2 (9,540,000 square miles). North America is the third biggest continent through area, after Asia and Africa, and the fourth through population following Asia, Africa and Europe. The population is assessed about 580 million people in 2018.
North America has different kinds of climate, from the dry, mild cold of the Arctic to the humid of the tropics. The central of Greenland always has subzero temperatures. The North American tundra, the enormous treeless plain of the far north, temperature can increase above freezing for just a short period each summer. In the far south, there are some regions which always have hot and rainy weather.
The residue of North America is cold in the winter and warm in the summer, with slight precipitation. Some regions have slight winters and long hot summers, and other districts have severe winters and slight summers. North America expands to within 10° of latitude of both the equator and the North Pole and embraces every climatic zone, from tropical rain forest and savanna on the lowlands of Central America to regions of enduring ice cap in central Greenland (Doubler et al. 2015).
North America includes the USA and Canada as two of the biggest global emitters of the greenhouse gases, especially methane and CO2, that can provide a warming climate. All ten of the “hotspot” classifications are found in this district, including alterations like polar warming in Alaska, coral reef bleaching in Florida, animal range shifts in California, glaciers melting in Montana and marsh loss in the Chesapeake Bay.
Environmental Protection Agency (EPA) inventory data represented that emissions from oil and gas and from livestock each estimated for about a third of the methane made by the North America, while landfill waste was calculated for 21–22% and coal was estimated for 10–13% of methane emissions (Sweeney et al. 2015).
North America methane emissions have enlarged through more than 30% in the past decade, making the area participate to the global rise in emissions. It seems the growth is largely due to supplies in the central area which is the only region in the nation to show statistically significant growths in methane production. Recent increases in oil and gas production as well as shale gas production can possibly estimate for this change; however, other supplies could be engaged as well.
Data used in this study
Satellite level 2 data of GOSAT for the extraction of methane
The satellite for estimating greenhouse was launched in 2009 on the island of Tangashima in Japan. GOSAT is a joint project of the Japan Space Exploration Agency, the Ministry of the Environment, the National Environmental Studies Association (NIES), with investment of 20 billion yen. The satellite is at a height of 166 km above the ground; each time it completes the rotation in about 100 min, with a rotational time of 12 min and 48 s. The primary objective of the GOSAT project is to accurately estimate the sources of emissions and greenhouse gas emissions in subcontinental scale to help environmental managers assess the carbon cycle equilibrium of terrestrial ecosystems. The satellite is the world’s first satellite designed for measurements of carbon dioxide and methane oxide emissions from the SWIR band and global coverage every 3 days. The satellite is also tracked with a deviation of 98 degrees and has a spatial resolution of two tenths, and its spatial resolution is a circle of ten and a half km. The satellite is equipped with TANSO-FTS and TANSO-CAI sensors to measure greenhouse gases. The carbon dioxide and methane molecules in the atmosphere absorb rays of particular wavelengths and measure how much carbon dioxide and methane are found in pillars from the ground up to the top. The columns are taken at 5-point latitude, at a radius of ten and a half km, with an approximate distance of 100 km between these columns. Due to the fact that the time of the return of the satellite is every 3 days, there are many observations that cover the entire world, but because of the limitations of the cloudless conditions, only 10% of the observations made by TANSO-FTS can be used to recover carbon dioxide and methane used. Satellite data of GOSAT have different levels, so that the data from the TANSO-FTS and TANSO-CAI sensors are level 1 data. These data are not validated and require validation. NIES is responsible for validating and developing algorithms for recovering average carbon dioxide and methane columns from level 1 data, and after validation by ground or airborne databases, surface-level data are generated. The accuracy of the evaluation of the frequency of retrieved columns for GOSAT is less than 1% in most cases.
MODIS satellite products for monitoring vegetation cover and surface temperature
MODIS sensor is an important tool installed on Terra and Aqua and is the most reliable data source on a continental scale. MODIS has 36 band spectra that collect data in a range of 14 to 14 km in range, and can view the whole surface of the earth for 1 to 2 days. One of the strengths of the MODIS is the global coverage of high-resolution separation and accurate calibration in visible near–infrared bands and infrared heat. More than 10 types of information can be extracted from MODIS. In the present study, MOD13Q1 and MOD11C3 products are used which represent the normalized plant differences (NDVI) and ground temperature (LST). After downloading the data from the site, due to the wide area of the study area and its location in different blocks, the data in the software ArcGIS 10.3 and using the mosaic method were put together, and in the end, the pixel size of the data was uniformly matched using the bilinear method.
The meteorological parameters used in this study were the average monthly temperature, the average monthly relative humidity and the average monthly precipitation received by the meteorological organization. It is worth noting that these data were obtained after averaging of daily data. In this study, synoptic stations are located at less than 50 km from methane columns. In the present study, while there were 290 synoptic stations, only 62 of the stations that escaped less than 50 km from methane metering columns were used.
Statistical analysis and correlation coefficient between methane columns, meteorological parameters (temperature, humidity and rainfall) and LST and NDVI indicators from MODIS satellite in SPSS software were investigated. In order to examine the difference between the methane gas content of the study area in 2009 and 2015, one-way ANOVA was used and Duncan’s test was used to determine the difference between the groups.
Descriptive statistics of the studied variables
Statistical analysis of variables
Average temperature (°C)
Average humidity (%)
Methane change trends from 2012 to 2018
Correlation between climatic parameters and methane in 2018
Correlation between NDVI and methane in different months in 2018
NDVI in winter
NDVI in autumn
NDVI in summer
NDVI in spring
Correlation between LST and methane in different months in 2018
LST in winter
LST in autumn
LST in summer
LST in spring
Monthly change in methane from 2012 to 2018
The relationship between methane and meteorological parameters and LST and NDVI
As shown in Fig. 3, the results of the correlation between methane gas and the average monthly temperature of 2018 are positive, so that the concentration of methane gas increased with temperature rise in 2018.
According to Fig. 4, methane gas has a negative correlation with the humidity variable, so that in 2018, the concentration of methane gas decreased with increasing monthly relative humidity. The reason for this correlation is related to free radicals of OH in dry air. As shown in Fig. 5, methane gas has a negative correlation with the rainfall variable in 2018, as the amount of methane concentration in the studied area decreases with increasing rainfall.
According to the results, methane gas has had a steady change from 2012 to 2018 so that the gas volume rises from 1789 to 1824 ppb, indicating an increase of 36 ppb in the gas in the region. In this regard, Luo et al. (2015) explored the annual changes in carbon dioxide and methane gas in China and Mongolia using satellite. They saw an increasing trend in the changes in these two gases in their study area. In another study, Kumar et al. (2016) used the satellite and ground base of NOAA to study the trend of carbon dioxide change in India from 2003 to 2011. In their study, they saw an increasing amount of carbon dioxide, but did not see significant growth in methane in the study area. Thompson et al. (2015) reviewed the annual methane change from 2009 to 2013 in East Asia. In their research, they observed an increase in this gas in the studied area at a rate of 6 over the 5-year period. Methane annual changes from 2007 to 2013 were also reviewed in a study by the Japan Meteorological Agency (Tsuboi et al. 2016). During this period, the average annual methane 6 was measured. The research results of the aforementioned studies confirm the increasing trend of methane in most parts of the world in recent years.
According to the results of this study, methane gas has seasonal fluctuations from 2009 to 2015, so that the maximum concentration of this gas was observed in October and September and at least in most of the years under review in March.
In similar studies, Dangal et al. (2017) reported a low concentration of methane in China and Mongolia in May and it peaked in September. They said that the rise in methane from May to September was due to rising temperatures during this period.
Akimoto et al. (2015) in the study of methane changes in East Asia witnessed seasonal changes in methane in their study area, which peaked in August and at least observed in February and March. Ganesan et al. (2017) measured India’s minimum methane concentration in winter and its peak concentration in August and July. Chandra et al. (2017) in a study in the eastern region of India said that the reason for the increase in methane in summer is due to increased microbial activity in these areas. They came to the conclusion that since June, the average atmospheric methane concentration has increased, reaching its peak in August and September. In another study, Tian et al. (2015) linked seasonal changes to methane with rice cultivation, wetlands and burning biomass. The results of methane gas fluctuations in this study are consistent with the results of this study.
The present study shows that in all seasons the relationship between methane gas and NDVI index is negative and the relationship between this gas and the LST index is positive. As the temperature increases and the NDVI decreases, in all seasons, the concentration of methane gas has increased. It is worth noting, however, that all the expressed relationships do not have a high correlation with the methane variable. This is seen in similar studies in other countries. Finstad et al. (2016) reported that the relationship between methane and NDVI is negative and the regression coefficient of this gas with NDVI is 0.5. Kim et al. (2015) explored the spatial distribution of methane in East Asia and expressed concern about environmental parameters associated with greenhouse gases and understood that NDVI has a negative and significant relationship with methane. So if NDVI increases, then CH4 will decrease in the study area. They reported that the regression coefficient of this variable with NDVI is 0.7. They expressed the most important cause of methane reduction by oxidation of methane by free radical hydroxyl. The most important source of methane in the troposphere is its oxidation by free radicals of hydroxyl so that more than 90% of the atmospheric methane is released by these free radicals from the atmosphere. In the atmosphere, ozone molecules decay energy from the rays of the sun into O2 molecules and O atom and the result of the reaction of O atom with steam is the production of free radicals of hydroxyl (OH). In areas where the temperature is high and the humidity is low, the atmosphere is reduced, and subsequently, the OH decreases. Sweeney et al. (2016) stated that methane emissions are sensitive to temperature so that a 10° increase in temperature at the temperature range doubles the methane concentration. Based on the results of this study, which shows the relationship between methane gas content and LST temperature variables, and the negative relationship of this gas with NDVI variables, rainfall and humidity, in areas with high humidity and rainfall and low vegetation and regions with high temperature and high temperatures, the maximum concentration of methane gas is observed. Therefore, preserving natural ecosystems, especially plant coverings in arid and semiarid regions, can play an important role in regulating methane gas. In the end, it is suggested that, in order to understand the potential sources and outcomes of methane gas, the distribution of this gas on a national scale using satellite data is proposed.
We thank Esfahan Regional Water Authority for funding this study to collect necessary data easily and help the authors to collect the necessary data without payment, Mohammad Abdollahi and Hamid Zakeri for their helpful contributions to collect the data and all other sources of funding for the research collected from authors. We thank ForoughJafary who provided professional services for checking the grammar of this paper.
SJ designed this research, wrote this paper, collected the necessary data and did analysis of the data. SE participated in drafting the manuscript, contributed to the collection of data and interpretation of data and edited the format of the paper under the manuscript style. KOAA participated in the data collection and data analysis.
We thank Esfahan Regional Agricultural Authority and Esfahan Regional Water Authority for funding this study to collect necessary data easily and help the authors to collect the necessary data without payment, Mohammad Abdollahi and Hamid Zakeri for their helpful contributions to collect the data and all other sources of funding for the research collected from authors.
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Conflicts of interest
All authors have declared that they have no conflicts of interest.
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