1. Introduction
Total atmospheric carbon dioxide (CO
2) has increased from approximately 280 to 379 ppm over the past century, due to the burning of fossil fuels for expanding industrial activities [
1]. The annual increase in the CO
2 concentration has been as high as 1.9 ppm in the decade from 1995 to 2005, which is higher than the longer term increase of 1.4 ppm per year that has been directly measured for 1960 to 2005 [
1]. CO
2 absorbs infrared radiation emitted from the earth’s surface, so an increase in CO
2 concentration leads to a rise in atmospheric temperatures. Temperature changes can cause feedback loops that alter CO
2 concentrations by influencing the biosphere [
2]. CO
2 and other greenhouse gases also influence tropospheric ozone and water vapor, further increasing their importance to the Earth’s radiative budget. Tropical land ecosystems contributed most of the interannual changes in Earth’s carbon balance through the 1980s, whereas northern mid- and high-latitude terrestrial ecosystems dominated from 1990 to 1995 [
3]. Therefore, CO
2 and other greenhouse gases, such as methane (CH
4), nitrous oxide (N
2O), hydrofluorocarbons (HFCs), perfluorocarbons (PFCs) and sulfur hexafluoride (SF
6), are subject to emissions regulations under the Kyoto Protocol [
4]. Research on the greenhouse effect and carbon monitoring require high precision and the long-term measurement of the atmospheric CO
2 concentration. Space-based remote sensing of the CO
2 column-average dry air mole fractions (XCO
2) has the potential to provide observed global constraints on CO
2 fluxes across the surface-atmosphere boundary and to provide insight into the related biogeochemical cycles [
5]. As satellite remote sensing technology has developed, a series of satellites that are able to detect CO
2 has been launched. Satellite observations of CO
2 offer new insights into the magnitude of regional sources and sinks and can help overcome the large uncertainties associated with the upscaling and interpretation of data on CO
2 concentration from the Earth’s surface [
6].
Currently, several satellite instruments can retrieve CO
2 and other greenhouse gas data with significant sensitivity. These include the Scanning Imaging Absorption Spectrometer for Atmospheric Cartography (SCIAMACHY) [
7,
8] on board the Environmental Satellite (ENVISAT), which was launched in 2002, and the Thermal and Near-infrared Sensor for Carbon Observation (TANSO) [
9] on board the Greenhouse Gases Observing Satellite (GOSAT), which was launched in 2009. The Atmospheric Infrared Sounder (AIRS), the Advanced Microwave Sounding Unit (AMSU) and the Humidity Sounder for Brazil (HSB) form an integrated cross-track scanning temperature and humidity sounding system on the Aqua satellite of the Earth Observing System (EOS) [
10]. The second Orbiting Carbon Observatory (OCO-2) [
11,
12] is another satellite designed to observe atmospheric CO
2 in the same spectral region as SCIAMACHY and TANSO in the lower troposphere. The future generation of satellites, such as CarbonSat, which is to be launched in 2019 at the earliest [
13–
15], will also be able to constrain the parameterization of anthropogenic CO
2 emissions. To study CO
2 sources and sinks, China has launched the Chinese carbon dioxide observation satellite (TanSat) project [
16,
17]. The TanSat-Chinese will be launched in 2015 and will monitor the CO
2 in the Sun-synchronous orbit.
XCO
2 products retrieved from these satellites have been validated with reference to high-resolution ground-based Fourier Transform Spectrometers (g-b FTS) data and model data. Morino
et al. [
4] validated the GOSAT short wave infrared (SWIR) L2 V01.xx XCO
2 products with the g-b FTS data in nine TCCON sites, and their preliminary findings were that the difference between the GOSAT XCO
2 data and the g-b FTS data was −8.85 ± 4.75 ppm or −2.3 ± 1.2%. These biases and standard deviations are somewhat higher than those of other validations [
5,
6,
18]. Yoshida
et al. [
19] identified and corrected the Version 01.xx GOSAT XCO
2 products using a revised version of the retrieval algorithm (Version 02.xx). The improved retrieval algorithm had much smaller biases and standard deviations (−1.48 ppm and 2.10 ppm) for XCO
2 than did Version 01.xx. Inoue
et al. [
20] used two approaches to validate the GOSAT XCO
2 products (Version 02.00) with aircraft measurement data. Both methods indicated that the Version 02.00 of GOSAT XCO
2 products were improvements over the previous Version, and the bias was 1–2 ppm, with a standard deviation of 1–3 ppm. Schneising
et al. [
21,
22] compared SCIAMACHY XCO
2 data to g-b FTS measurements and model results (CarbonTracker XCO
2) for the period from 2003 to 2009. The relative accuracy was 1.14 ppm relative to TCCON and 1.20 ppm relative to CarbonTracker. Wang
et al. [
23] analyzed SCIAMACHY XCO
2 data levels in China and found that the largest peak-to-trough amplitude of SCIAMACHY was approximately 16 ppm during 2003–2005 and that peaks occurred in the spring, with the trough in winter or autumn. Bai
et al. [
24] validated the AIRS XCO
2 products from 2003 to 2008 using five ground-based stations located throughout the world. The correlation coefficients between AIRS and the other five ground stations were greater than 0.77, with a monthly mean difference of ∼0.62 ± 3.0 ppm. The average concentration of atmospheric CO
2 was higher in the Northern Hemisphere than in the Southern Hemisphere, with the approximately 2 ppm per year of annual growth in China.
These XCO2 products have been validated with g-b FTS data and model data, but there are some gaps in these comparisons. These XCO2 products have been validated individually, but we do not know the differences among the XCO2 values retrieved from the three sensors (SCIAMACHY, AIRS and GOSAT). Therefore, we have no gauge of which sensors are more precise under what circumstances; additionally, we do not know the differences among these satellite products for different regions. In this paper, the satellite products of GOSAT, SCIAMACHY and AIRS are compared with the reference calibrated data obtained using g-b FTS in the TCCON sites from 2003 to 2011. Through these comparisons, we try to explain why the validations of satellite products differ, to understand the different retrieval methods of the satellite products and to give an overall evaluation. Such a comparison is a prerequisite to evaluating the precision of each product and the suitability for their use in different conditions.
The three sets of satellite data are described in Section 2, where we present an overview of these projects and compare these satellite data sets. Reference data measured with g-b FTS and comparison methods are described in Section 3. The precision analysis of the satellite data products and the preliminary comparison to the reference data are presented in Section 4, where we also analyze the spatial distribution feature, linear trend and seasonal cycle using monthly mean data. The discussion and conclusions follow.
5. Discussions
Column average dry air mole fractions of CO2 from 2003 to 2011 have been compared using GOSAT (2009–2011), SCIAMACHY (2003–2009), AIRS (2003–2011) and g-b FTS measurements. The comparison is also performed for global zonal averages latitudinal from 60° S to 80° N in 10° steps. The comparison is performed by comparing monthly mean data in the entire analyzed time period and two subperiods, respectively. Both approaches yield similar results.
Among the three satellite products, the accuracy of SCIAMACHY data is relatively low, and the observation range is limited. The scatter of GOSAT retrievals is well below 1%, though this is a substantial improvement over earlier GOSAT validation efforts [
4,
28]. The XCO
2 data retrieved from SCIAMACHY perform better in inland areas. The values of SCIAMACHY are lower than g-b FTS, but the difference is never more than 2 ppm. The XCO
2 data retrieved from SCIAMACHY are inferior in offshore areas and the difference is larger. The XCO
2 data values retrieved from GOSAT are lower than g-b FTS and the difference amounts to 7 ppm. However, the GOSAT data do match well with g-b FTS on islands. This finding shows that the stability and correlation of GOSAT data have improved globally, especially in oceanic and offshore areas. The AIRS data products have the distinct advantage in terms of coverage range and measurement accuracy, which also provides more opportunity for comparisons with g-b FTS data. The absence of some high values in the AIRS data is consistent with the mid- and upper troposphere, being less sensitive to surface emissions [
51]. We also sampled both SCIAMACHY and AIRS data sets within ±2.5 degrees and, then, compared with the original data. The results are listed in
Table 8.
The differences of global offset and mean correlation are small. However, the different spatial resolution imperfect match has significantly contributed to the observed standard deviations [
50].
We have also estimated linear trends from monthly mean data for different periods. In general, the XCO2 seasonal cycle amplitudes derived from satellite data are somewhat larger than those from g-b FTS data. Because the time periods considered at certain TCCON sites are rather short, these trend estimates are only used to identify potential instrumental issues with the GOSAT and SCIAMACHY data. Although the XCO2 retrievals from AIRS are in the troposphere, the products are more consistent with the g-b FTS measurements.
The relative accuracy of AIRS data is 1.11 ppm (0.30%) and 1.08 ppm (0.28%) in spring and autumn, respectively. The relative accuracy of GOSAT data is 2.31 ppm (2.23%) in summer and SCIAMACHY data is 1.68 ppm (0.34%) in winter. Although there are different biases for XCO2, the satellite data retrievals and g-b FTS data show similar seasonal behaviors over the Northern Hemisphere: higher in spring and lower in autumn. The seasonal change in atmospheric CO2 concentration is mainly influenced by CO2 absorption and emission by terrestrial ecosystems. In summer and autumn, the strong photosynthesis of the lush vegetation leads to the decrease of the CO2 concentration and reaches to a low in October. In winter and spring, weak photosynthesis and winter heating lead to higher CO2 concentrations, which maintain a higher level and peak in April.
6. Conclusions
In this paper, we analyze the XCO2 products retrieved from Imaging Absorption Spectrometer for Atmospheric Cartography (SCIAMACHY), Greenhouse Gases Observing Satellite (GOSAT), Atmospheric Infrared Sounder (AIRS) and use high-resolution ground-based Fourier Transform Spectrometers (g-b FTS) with reference to calibration data obtained at ten Total Carbon Column Observing Network (TCCON) from 2003 to 2011. The validation and comparison reveal that the satellite data are biased by −6.53 ± 1.77 ppm (0.46%), −0.78 ± 4.67 ppm (1.22%) and 1.84 ± 2.76 ppm (0.72%) for GOSAT, SCIAMACHY and AIRS relative to the reference values, respectively. The relative accuracy of these satellite data are 1.50 ppm (0.38%), 3.35 ppm (0.87%) and 0.96 ppm (0.25%), respectively, and the mean correlation coefficients are 0.64, 0.43 and 0.56 compared to g-b FTS data, respectively. The mean annual increase in XCO2 of GOSAT, SCIAMACHY, AIRS and g-b FTS data are 1.78, 1.06, 2.07 and 0.81 ppm per year, respectively. The relative accuracy of AIRS data is 1.11 ppm (0.30%) and 1.08 ppm (0.28%) in spring and autumn, respectively. The relative accuracy of GOSAT data is 2.31 ppm (2.23%) in summer and SCIAMACHY data, 1.68 ppm (0.34%) in winter. Due to the product selection for validation, the spatial distributions in XCO2 between three sensor measurements are different. The SCIAMACHY data are confined to the land, because of lower surface reflectance; GOSAT XCO2 data are filtered for aerosol optical depth less than 0.5 and are removed over high mountain ranges. AIRS XCO2 product get larger global data coverage scale by losing accuracy in the product process.
GOSAT data offer certain advantages, but also have high systemic bias. The XCO
2 data retrieved from SCIAMACHY perform better in inland areas, but the difference is larger. Compared to the differences between the former two satellites, the system bias of AIRS is lowest for each site. Especially in mid-latitude regions, the AIRS XCO
2 values agree very well with g-b FTS. Overall, AIRS data show largely the same trend as the g-b FTS data. Therefore, the AIRS data product can reflect the distribution characteristics and change rules for global CO
2 atmospheric concentration very well. The uncertainties in sensor measurements are about the cloud, lower surface reflectance and systematic deviations, due to aerosols, thin cirrus clouds and even spectrum instrument depreciation of sensor. The accuracies of satellite data is also affected by the accuracies of retrieval algorithm. In the future, we plan to investigate interferences by aerosols and thin cirrus clouds using aerosol LIDaRs and/or sky-radiometers at selected FTS sites. Further improvements could be achieved by evaluating systematic errors with an empirical neural-network-type multivariate regression with physically meaningful regression coefficients in an approach similar to [
52] or by accounting for additional physical parameters in future models (e.g., cloud parameters, as in [
34,
53]).