Variational inverse modeling within the Community Inversion Framework v1.1 to assimilate δ13C(CH4) and CH4: a case study with model LMDz-SACS
- 1Laboratoire des Sciences du Climat et de l'Environnement, CEA-CNRS-UVSQ, IPSL, Gif-sur-Yvette, France
- 2INSTAAR, University of Colorado, Boulder, Boulder, CO, USA
Correspondence: Joël Thanwerdas (firstname.lastname@example.org)
Atmospheric CH4 mole fractions resumed their increase in 2007 after a plateau during the 1999–2006 period, indicating relative changes in the sources and sinks. Estimating sources by exploiting observations within an inverse modeling framework (top-down approaches) is a powerful approach. It is, nevertheless, challenging to efficiently differentiate co-located emission categories and sinks by using CH4 observations alone. As a result, top-down approaches are limited when it comes to fully understanding CH4 burden changes and attributing these changes to specific source variations. δ13C(CH4)source isotopic signatures of CH4 sources differ between emission categories (biogenic, thermogenic, and pyrogenic) and can therefore be used to address this limitation. Here, a new 3-D variational inverse modeling framework designed to assimilate δ13C(CH4) observations together with CH4 observations is presented. This system is capable of optimizing both the emissions and the associated source signatures of multiple emission categories at the pixel scale. To our knowledge, this represents the first attempt to carry out variational inversion assimilating δ13C(CH4) with a 3-D chemistry transport model (CTM) and to independently optimize isotopic source signatures of multiple emission categories. We present the technical implementation of joint CH4 and δ13C(CH4) constraints in a variational system and analyze how sensitive the system is to the setup controlling the optimization using the LMDz-SACS 3-D CTM. We find that assimilating δ13C(CH4) observations and allowing the system to adjust isotopic source signatures provide relatively large differences in global flux estimates for wetlands (−5.7 Tg CH4 yr−1), agriculture and waste (−6.4 Tg CH4 yr−1), fossil fuels (+8.6 Tg CH4 yr−1) and biofuels–biomass burning (+3.2 Tg CH4 yr−1) categories compared to the results inferred without assimilating δ13C(CH4) observations. More importantly, when assimilating both CH4 and δ13C(CH4) observations, but assuming that the source signatures are perfectly known, these differences increase by a factor of 3–4, strengthening the importance of having as accurate signature estimates as possible. Initial conditions, uncertainties in δ13C(CH4) observations, or the number of optimized categories have a much smaller impact (less than 2 Tg CH4 yr−1).
Methane (CH4) is a powerful greenhouse gas and is responsible for 23 % (Etminan et al., 2016) of the radiative forcing induced by the well-mixed greenhouse gases (CO2, CH4, N2O). Atmospheric CH4 mole fractions have increased quasi-continuously since the preindustrial era and by about 9 ppb yr−1 (parts per billion per year) from 1984 to 1998 (Dlugokencky, 2021). After a plateau between 1999 and 2006 that still generates attention and controversy (e.g., Fujita et al., 2020; Thompson et al., 2018; McNorton et al., 2018; Turner et al., 2017; Schaefer et al., 2016; Schwietzke et al., 2016; Rice et al., 2016), the mole fractions resumed their increase at a large rate, exceeding 10 ppb yr−1 in 2014 and 2015. Trends in atmospheric CH4 are caused by a small imbalance between large sources and sinks. Assessing their spatiotemporal characteristics is particularly challenging, considering the variety of CH4 emissions. Yet, identifying and quantifying the processes contributing to these changes is mandatory to formulate relevant CH4 mitigation policies that would contribute to meeting the target of the 2015 UN Paris Agreement on Climate Change and to limit climate warming to 2 ∘C.
Thanks to continuous efforts of surface monitoring networks, the spatial coverage and the accuracy of the atmospheric CH4 measurements provided to the scientific community have increased over the last decades. Consequently, top-down estimates using inversion methods emerged and became relevant, along with bottom-up estimates, for explaining and quantifying the recent sources and sinks variations. The first inverse modeling techniques were designed in the late 1980s and early 1990s for inferring greenhouse gas sources and sinks from atmospheric CO2 measurements (Enting and Newsam, 1990; Newsam and Enting, 1988). Without a regularization of the problem, e.g., providing prior information, the inverse problem is ill-conditioned (or ill-posed). It means that there is no unique solution to the problem but also that a small error in the assimilated data (here atmospheric observations) can result in large errors in the derived solution. Several inversion methods have been designed over the years, among which there are analytical (e.g., Bousquet et al., 2006; Gurney et al., 2002), ensemble (e.g., Zupanski et al., 2007; Peters et al., 2005), and variational methods (e.g., Chevallier et al., 2005). The variational formulation uses the adjoint equations of a specific model to compute the gradient of a cost function and then minimize it, for example, using a gradient descent method. Computational times and memory costs do not scale with the number of measurements and the number of variables to control, contrary to the analytical and ensemble methods, which can hardly accommodate very large observational datasets and control vectors at the same time. Thus, the variational formulation is preferred to the others when optimizing emissions and sinks at the pixel scale using large volumes of observational data, although its main limitation is the numerical cost for accessing posterior uncertainties when there is nonlinearity in the inversion problem (Berchet et al., 2021).
Inversion systems generally assimilate measurements from ground-based stations and/or satellites to constrain the global sources and sinks of CH4, starting from a prior knowledge of these. These systems are very effective for providing total emission estimates (e.g., Saunois et al., 2020; Bergamaschi et al., 2018, 2013; Saunois et al., 2017; Houweling et al., 2017, and references therein). However, differentiating the contributions of multiple co-located CH4 source categories is challenging as it only relies on different seasonality cycles and on applied spatial distributions and error correlations (e.g., Bergamaschi et al., 2013, 2010). The atmospheric isotopic signal contains additional information on CH4 emissions that can help to separate emission categories based on their source origin. The atmospheric isotopic signal δ13C(CH4) is defined as follows:
where R and Rstd denote the sample and standard 13CH4:12CH4 ratios. We use the Vienna Pee Dee Belemnite (V-PDB) scale with Rstd = 0.00112372 (Craig, 1957) throughout this paper. The isotopic source signatures of CH4, here denoted by δ13C(CH4)source, notably differ between emission categories ranging from 13C-depleted biogenic sources (−61.7 ± 6.2 ‰; 1 standard deviation) and thermogenic sources (−44.8 ± 10.7 ‰) to 13C-enriched thermogenic sources (−26.2 ± 4.8 ‰) (Sherwood et al., 2017; Schwietzke et al., 2016), although the distributions are very large and overlaps exist between the extreme values. Consequently, δ13C(CH4) depends on both CH4 emissions and their isotopic signatures. Saunois et al. (2017) pointed out that many emission scenarios inferred from atmospheric inversions are not consistent with δ13C(CH4) observations and that this constraint must be integrated into the inversion systems to avoid such inconsistencies. In addition, they highlighted the sensitivity of the atmospheric isotopic signal to the source partitioning and prescribed isotopic ratios. Since the 1990s, δ13C(CH4) has been monitored at multiple sites, providing opportunities to use this constraint within an inversion framework. In addition, these values have been shifting towards more negative values since 2006 (Nisbet et al., 2019) when CH4 trends resumed their increase, suggesting that this isotopic data can help to understand the processes that contributed to the renewed growth. However, implementing the assimilation of such measurements into an inversion system is not straightforward and introduces additional complexity.
Hereinafter, the assimilation of δ13C(CH4) observations to constrain the estimates of an inversion is referred to as the isotopic constraint. The implementation of such a constraint in an inversion system has already been attempted in previous studies focusing on CH4 (e.g., Thompson et al., 2018; McNorton et al., 2018; Rigby et al., 2017; Rice et al., 2016; Schaefer et al., 2016; Schwietzke et al., 2016; Rigby et al., 2012; Neef et al., 2010; Bousquet et al., 2006; Fletcher et al., 2004) but, to our knowledge, never in a variational system associated to a 3-D chemistry transport model (CTM). Adding this isotopic constraint to a variational inversion system is challenging as, in contrast to an analytic inversion in which the response functions of the model are precomputed, the isotopic constraints have to be considered both in the forward (simulated isotopic values) and the adjoint (sensitivity of isotopic observations to optimized variables) versions of the model.
This new system was implemented in the Community Inversion Framework (CIF), supported by the European Union H2020 project VERIFY (http://community-inversion.eu, last access: 3 June 2022) and required to implement new forward, tangent linear and adjoint operations. The forward operations were previously used to estimate the impact of the Cl sink on the modeling of CH4 and δ13C(CH4) in LMDz-SACS (Thanwerdas et al., 2019). The purpose of this study is to present the technical implementation of the isotopic constraint in a variational inversion system and to investigate the sensitivity of this new configuration to different parameters. Our aim is not to estimate trends in sectoral emissions over the last 2 decades: future studies will address the estimation of CH4 emissions over longer periods of time using this new system. The technical implementation and the various tested configurations are presented in Sect. 2. We analyze the results in Sect. 3. Section 4 presents our conclusions and recommendations on using such a multi-constraint variational system.
2.1 Theory of variational inversion
The notations introduced here follow the convention defined by Ide et al. (1997) and Rayner et al. (2019). The observation vector is called yo. It includes all available observations here, namely CH4 and δ13C(CH4) measurements retrieved by surface stations, over the full simulation time window (see Sect. 2.4.2). The associated errors are assumed to be unbiased and Gaussian and are described within the error covariance matrix R. This matrix accounts for all errors contributing to mismatches between simulated and observed values. x is the control vector and includes all the variables (here CH4 surface fluxes, initial CH4 mole fractions, source signatures δ13C(CH4)source, and initial δ13C(CH4) values) optimized by the inversion system. Hereinafter, these variables will be referred to as the control variables. Prior information about the control variables are provided by the vector xb. Its associated errors are also assumed to be unbiased and Gaussian and are described within the error covariance matrix B. ℋ is the observation operator that projects the control vector x into the observation space. This operator mainly consists of the 3-D CTM (here LMDz-SACS, as introduced in Sect. 2.2). Nevertheless, the CTM is followed by spatial and time operators, which interpolate the simulated fields to produce simulated equivalents of the assimilated observations at specific locations and times, making the simulations and observations comparable. An additional transformation operator, implemented in the new system, enables comparison between distinct simulated tracers, e.g., 12CH4 and 13CH4, and observations, e.g., δ13C(CH4) (see Sect. 2.3).
In a variational formulation of the inference problem that allows for ℋ nonlinearity, the cost function J is defined as follows:
The cost function is therefore a sum of the following two parts:
The first part is induced by the differences between the posterior and prior variables (Jb).
The second is induced by the differences between simulations and observations (Jo).
The minimum of J can be reached iteratively with a descent algorithm that requires several computations of the gradient of J with respect to the control vector x, as follows:
ℋ* denotes the adjoint operator of ℋ. As in analytical and ensemble methods, the variational formulation necessitates the inversion of both error matrices R and B. In most applications, R is considered diagonal as point observations are distant in time and space (i.e., uncorrelated observation errors), allowing for the inverse to be calculated easily, although that assumption should be revised with the increasing availability of satellite sources (Liu et al., 2020). B is rarely diagonal due to spatial and temporal correlations of errors in the fluxes. However, B is often decomposed as combinations of smaller matrices, e.g., using Kronecker products of sub-correlation matrices, which allows us to compute its inverse by blocks.
2.2 The chemistry transport model
The LMDz general circulation model (GCM) is the atmospheric component of the Institut Pierre-Simon Laplace Coupled Model (IPSL-CM) developed at the Laboratoire de Météorologie Dynamique (LMD) (Hourdin et al., 2006). The version of LMDz we use is an offline version dedicated to the inversion framework created by Chevallier et al. (2005). The precomputed air mass fluxes provided by the online version of LMDz are given as inputs to the transport model, significantly reducing the computational time. The model is set up at a horizontal resolution of 3.8∘ × 1.9∘ (96 grid cells in longitude and latitude) with 39 hybrid sigma pressure levels reaching an altitude up to about 75 km. About 20 levels are dedicated to the stratosphere and the mesosphere. The model time step is 30 min, and the output mole fractions are 3 h snapshots. The horizontal winds are nudged towards ECMWF meteorological analyses (ERA-Interim) in the online version of the model and then fed to the offline version. Vertical diffusion is parameterized by a local approach from Louis (1979), and deep convection processes are parameterized by the Tiedtke (1989) scheme.
The offline model LMDz is coupled with the Simplified Atmospheric Chemistry System (SACS; Pison et al., 2009). This chemistry system was previously used to simulate the oxidation chain of hydrocarbons, including CH4, formaldehyde (CH2O), carbon monoxide (CO), and molecular hydrogen (H2). For the purpose of this study, this system was converted into a chemistry parsing system. It follows the same principle as the one used by the regional model CHIMERE (Menut et al., 2013) and therefore allows for user-specific chemistry reactions. As a result, it generalizes the previous SACS module to any possible set of reactions. The adjoint code has also been implemented to allow variational inverse modeling. The different species are either prescribed (here OH, O(1D), and Cl) or simulated (here 12CH4 and 13CH4). The prescribed species are neither transported in LMDz, nor are their mole fractions updated through chemical production or destruction. Such species are only used to calculate reaction rates to update the simulated species at each model time step. In this study, the isotopologues 12CH4 and 13CH4 are simulated as separate tracers, and CH4 is defined as the sum of both isotopologues. Cl + CH4 oxidation was implemented to complete the chemical removal of CH4, which previously only accounted for OH + CH4 and O(1D) + CH4 in the SACS scheme.
In the atmosphere, radicals (OH, O(1D), or Cl) react faster with 12CH4 than with 13CH4. This effect is called the kinetic isotope effect (KIE) or the fractionation effect. Fractionation values are prescribed to the different sinks in SACS. Here, this value is defined by , where k12 is the rate constant of a reaction between a radical and 12CH4. k13 is the rate constant of the reaction between the same radical and 13CH4. Additional information and prescribed KIE values are provided in Sect. S2 in the Supplement.
The chemistry transport LMDz-SACS is used to test the new variational inverse modeling system that is described in the next section.
2.3 Technical implementation of the isotopic constraint
The isotopic multi-constraint system was implemented in the CIF. The CIF has been designed to allow comparison of different approaches, models, and inversion systems used in the inversion community (Berchet et al., 2021). Different atmospheric transport models, regional and global and Eulerian and Lagrangian, are implemented within the CIF. The system presented in this paper was originally designed to run and be tested with LMDz-SACS but can theoretically be coupled with all models implemented in the CIF framework. The system is able to do the following:
assimilate δ13C(CH4) and CH4 observations together,
independently optimize fluxes and isotopic signatures for multiple emission categories, and
optimize δ13C(CH4) and CH4 initial conditions.
Figure 1 shows the different steps of a minimization iteration of the cost function. Each iteration performed with the descent algorithm can be decomposed into the four main steps presented below. For clarity, here we only present the optimization of CH4 fluxes and associated source signatures, but CH4 and δ13C(CH4) initial conditions can also be optimized by the system following the same process.
, and are the CH4, 12CH4, and 13CH4 mass fluxes of a specific category i, respectively. MT, M12, and M13 are the CH4, 12CH4, and 13CH4 molar masses, respectively. is the isotopic signature of the category i. MT should preferably depend on M12 and M13 when converting the mass fluxes, as follows:
However, the complexity of the forward, tangent linear, and adjoint codes would be largely enhanced by such a relationship. The code structure would also be less generic, i.e., it could not be used for a joint assimilation of multiple isotopologues of CH4, such as both δ13C(CH4) and δD(CH4). We choose to implement MT as a constant that can be prescribed freely by the user, therefore without considering any influence of the M12 and M13 values, which are also prescribed by the user. As the observed isotopic source signatures roughly vary between −70 ‰ and −10 ‰, a maximum variation of 0.004 % in MT could be expected. It will very likely not affect the results of our study or that of any other inversion performed with our system.
The 12CH4 and 13CH4 total fluxes are then calculated by summing all categories and are used by the model LMDz-SACS to simulate the 12CH4 and 13CH4 atmospheric mole fractions over the time window considered. After the simulation, the simulated values are converted to the CH4- and δ13C(CH4)-simulated equivalent of the assimilated observations using Eqs. (9) and (10) below, as follows:
[CH4], [12CH4], and [13CH4] are CH4, 12CH4, and 13CH4 atmospheric mole fractions simulated by the model in moles per mole (hereafter mol mol−1), respectively.
These simulated values are then compared to the available observations in order to compute ℋ(x)−yo, which is further used to infer the cost function and generate CH4 and δ13C(CH4) adjoint forcings (indicated by the superscripted asterisk) that compose the vector δy* as follows:
Although this vector is normally used directly as input to the adjoint model (see Eq. 4), the CH4 and δ13C(CH4) adjoint forcings must first be converted into the 12CH4 and 13CH4 adjoint forcings in the new system.
and are adjoint forcings associated with CH4 observations. and are adjoint forcings associated with δ13C(CH4) observations. The adjoint code of the CTM is then run with these adjoint forcings as inputs.
Outputs of the adjoint run provide the sensitivities of the adjoint forcings to the 12CH4 and 13CH4 mass fluxes of a specific category i, denoted by and . Equations (15) and (16) convert them back to sensitivities to the initial control variables, denoted by and .
The minimization algorithm utilizes these sensitivities to compute the gradient of the cost function. It then finds an optimized control vector which reduces the cost function and is used for the next iteration.
In order to confirm that the several adjoint operations have been correctly implemented, we also provide the results of multiple adjoint tests in Sect. S4 in the Supplement.
2.4 Setup of the reference simulation
The reference configuration (REF) is a variational inversion that optimizes the CH4 emission fluxes and δ13C(CH4) isotopic source signatures of the following five different categories: biofuels–biomass burning (BB), agriculture and waste (AGW), fossil fuels (FFs), wetlands (WET), and other natural sources (NAT). CH4 and δ13C(CH4) initial conditions are also optimized. The assimilation time-window is the 2012–2017 period. The five categories originate from an aggregation of 10 subcategories (see Table 1) and are chosen to be as isotopically consistent as possible. Sinks are not optimized here.
2.4.1 Control vector x and B matrix
We adopt the CH4 emissions compiled for inversions performed as part of the global methane budget (Saunois et al., 2020). Anthropogenic (including biofuels) and biomass burning emissions are based on the EDGARv4.3.2 database (Janssens-Maenhout et al., 2017) and the GFED4s databases (van der Werf et al., 2017), respectively. Statistics from British Petroleum (BP) and the Food and Agriculture Organization of the United Nations (FAO) have been used to extend the EDGARv4.3.2 database, which ended 2012, until 2017. The natural source emissions are based on averaged literature values; see Poulter et al. (2017) for wetlands, Kirschke et al. (2013) for termites, Lambert and Schmidt (1993) for oceanic sources, and Etiope (2015) for geological (onshore) sources. Emissions from geological sources have been scaled down to 15 Tg CH4 yr−1 in the prior emissions adopted in Saunois et al. (2020). All prior fluxes are prescribed at a monthly resolution and at the spatial resolution of LMDz. Globally averaged emissions over the 2012–2017 period are listed in Table 1.
Prior estimates of isotopic source signatures are provided either at the pixel scale (for wetlands), at the regional scale based on Atmospheric Tracer Transport Model Intercomparison Project (TransCom) regions (Patra et al., 2011) or at the global scale. The wetlands signature map is taken from Ganesan et al. (2018). Livestock isotopic source signatures are taken from Chang et al. (2019) and aggregated into the 11-region map by selecting region-specific values. Livestock source signatures have been likely decreasing over time since the 1990s due to changes in the C3/C4 diet within the major livestock-producing countries, and therefore, annual values are prescribed. However, these estimates end in 2013, and we set the years 2014 to 2017 equal to the year 2013. Consequently, only the year 2012 has a different prescribed value from the other years. Coal and oil, gas, and industry (OGI) isotopic signature values are inferred from Sherwood et al. (2017) and Zazzeri et al. (2016) and aggregated into the same 11-region map. The EDGARv4.3.2 categories PRO_OIL and PRO_GAS (fugitive emissions during oil and gas exploitation) largely contribute (∼ 90 %) to the total of the oil, gas, and industry subcategory. Therefore, we chose to neglect the influence of other sub-subcategories (such as industry) on the isotopic signature of the category. As for the biofuels–biomass burning category, we use region-specific signatures over the 11 regions. A global signature value is prescribed for each of the other categories. Except for the livestock category, all prior signatures are set constant over time. To infer the δ13C(CH4)source map of a category based on the subcategories, the 12CH4 and 13CH4 fluxes for each emission subcategory within a category are derived based on Eqs. (5) and (6) and added up. The resulting fluxes are then converted back to a δ13C(CH4)source map representing the aggregated isotopic signature of the category. Additional information regarding the chosen isotopic signatures and their references is provided in Sect. S1 in the Supplement.
In total, three values per month (10 d, 10 d, and the rest) for fluxes and their associated isotopic signatures are included in the control variables. Although the time variations in isotopic signatures are poorly constrained in the literature, we choose to include the same number of variables for fluxes and isotopic signatures in order to illustrate the full capabilities of the system and have it ready when more isotopic constraints will appear.
The portion of the diagonal of B associated to prior CH4 emission fluxes is filled in with the variances set to 100 % of the square of the maximum of emissions over the cell and its eight neighbors during each month. Off-diagonal terms of B (covariances) are based on correlation e-folding lengths (500 km over land and 1000 km over sea). The same method is applied for isotopic source signatures, although a specific percentage of uncertainties deduced from the global values of Sherwood et al. (2017) is used to infer each category's diagonal term (see Table 1). No temporal correlations are considered here. Finally, prior uncertainties in initial conditions are set to 10 % for CH4 (∼ 180 ppb) and 3 % for δ13C(CH4) (∼ 1.4 ‰).
2.4.2 Observation vector y and R matrix
CH4 observations are taken from the data archived at the World Data Centre for Greenhouse Gases (WDCGG) of the World Meteorological Organization Global Atmospheric Watch (WMO-GAW) program. We selected 66 stations from 13 surface monitoring networks providing in situ measurements of CH4 mole fractions. The stations are displayed in Fig. 2.
δ13C(CH4) observations are taken from 18 surface stations from the Global Greenhouse Gas Reference Network (GGGRN), part of the NOAA Earth System Research Laboratory's (ESRL) Global Monitoring Laboratory (NOAA GML). Air samples were collected on an approximately weekly basis during the 2012–2017 period and analyzed by the Institute of Arctic and Alpine Research (INSTAAR) to provide δ13C(CH4) isotope ratio measurements. The analytical uncertainty of the isotopic measurements, based on a surveillance cylinder, is 0.06 ‰. In this study, we focused on estimating monthly and annual flux variations rather than investigating daily or weekly variations. Prescribing error correlations in the R matrix (introduced in Sect. 2.1) can be used to ensure that the inversion preferentially constrains the components we are interested in (i.e., long-term trend and seasonal cycle). In order to keep the R matrix diagonal and to focus on monthly and annual variations of the signal, we chose to use δ13C(CH4) observational data based on a curve fitting the original δ13C(CH4) observations. The fitting curve is a function including three polynomial parameters (quadratic) and eight harmonic parameters, as in Masarie and Tans (1995). After the fitting, the pseudo-observations were sampled at the same time as the original observations. We also hypothesized that the convergence would be slightly faster if a smooth curve fitting the real observations was used instead of the real observations, which appeared to be false (see Sect. 3.1). One sensitivity inversion aims at estimating the error introduced by this simplification (simulation S2 in Table 2).
The R matrix for both CH4 and δ13C(CH4) is defined as diagonal, assuming that observation errors are not correlated, neither in space nor in time. This diagonal matrix can be decomposed into two parts, i.e., measurement and model error variances. Measurement errors account for instrumental errors, whereas model errors encompass transport and representativity errors induced by the model as follows:
Here, we use the provided observation errors to fill the Rmeasurement diagonal matrix. GlobalView Methane (CH4; GLOBALVIEW-CH4, 2009) values are used to represent model errors and prescribe variances at each station for CH4 mixing ratio measurements in order to fill the Rmodel diagonal matrix. This simple approach has been used previously in atmospheric inversions (Locatelli et al., 2015, 2013; Yver et al., 2011; Bousquet et al., 2006; Rodenbeck et al., 2003). Errors in GlobalView CH4 are computed at each site as the root mean square error (RMSE) of the measurements on a smooth curve fitting them. As GlobalView CH4 does not provide errors for GlobalView CH4 measurements, the same method has been applied here. The RMSE of the measurements on a smooth curve, fitting them over the 2012–2017 period, is prescribed as the standard deviation for each site providing δ13C(CH4) measurements. These errors range between 3–19 ppb for CH4 observations and 0.11–0.20 ‰ for δ13C(CH4) observations. Mean prescribed errors for each station are provided in Tables S3 and S4 in the Supplement.
Before starting the inversion, the model has been spun-up over 30 years, using constant emissions and recycling meteorology from the year 2012 in order to consider the long timescales for isotopic changes (Tans, 1997). At the end of the spin-up, δ13C(CH4) values have been offset (+1.4 ‰) to fit the global mean δ13C(CH4) in January 2012, and CH4 mole fractions have been scaled to fit the global mean CH4 mole fraction in January 2012. Due to the nonlinearity of transport and mixing, offsetting δ13C(CH4) initial values in a forward run can generate errors. This impact is discussed later, using a configuration where δ13C(CH4) initial conditions have not been offset (S1).
2.4.4 Sensitivity tests
A set of nine different configurations, including REF, has been designed to assess the impact of assimilating δ13C(CH4) observations in addition to CH4 observations and also to evaluate the sensitivity of the inversion results to the system's setup.
Multiple parameters have been tested throughout the following configurations:
NOISO has no isotopic constraint. Therefore, this configuration only simulates CH4 and assimilates CH4 observations.
S1 uses δ13C(CH4) initial conditions that are not offset and are therefore directly taken from the spin-up.
S2 assimilates the real δ13C(CH4) observations instead of the fitting curve data.
In S3, the δ13C(CH4) model uncertainties are divided by a factor 2.
T1 uses 10 subcategories instead of 5 aggregated categories, increasing the degrees of freedom.
In theory, the system is capable of optimally adjusting two source signatures if the assimilated information is sufficient. For instance, the system can choose to shift one signature downward and another upward in a given pixel in order to improve the fitting in this specific pixel. The configuration T2 has been specifically designed to investigate whether the system would be able to retrieve a realistic distribution (similar to REF) starting from globally averaged signatures for each category.
In T3, the δ13C(CH4) source signature uncertainties are set to a very low value (1 %) in order to prevent the system from optimizing them. In other words, all changes are put on CH4 emissions.
Finally, T4 applies both changes from T2 and T3.
* Prior uncertainties in initial δ13C(CH4) conditions have been set to 10 %.
Table 2 summarizes the different configurations and the associated changes. The configurations have been grouped into two sets to facilitate the analysis of results. On the one hand, S-group configurations (REF + S1–S4) have setup variations that are not expected to largely influence the results compared to REF. On the other hand, T-group configurations (T1–T4) alter parameters that are very likely to impact the results.
3.1 Minimization of the cost function
The minimization process is performed using the M1QN3 algorithm (Gilbert and Lemaréchal, 1989). One full simulation (forward + adjoint) with the isotopic constraint necessitates about 170 central processing unit (CPU) hours to run for 6 years, i.e., 2.4 CPU hours per month simulated. The computational burden is increased by a factor of 2 in comparison to an inversion without the isotopic constraint due to the doubling of simulated tracers (12CH4 and 13CH4). One full simulation is generally enough to complete one iteration of the minimization process, but two or three simulations are sometimes required by M1QN3. Therefore, the number of simulations is slightly larger than the number of iterations. Figure 3 displays the minimization process of the cost function for all configurations.
Except for S1 and T1, the inversions were stopped when the gradient norm reduction exceeded 96 % for the third consecutive iteration. The number of iterations are compared to investigate the sensitivity of the computational cost to the setup. In total, 32 iterations (37 simulations) for NOISO, 43 iterations (47 simulations) for REF, and about 50 iterations for the others were necessary. Consequently, although assimilating δ13C(CH4) observations requires at least 11 additional iterations, the setup has little influence on the number of iterations if the same convergence criteria is used. Also, using curve-fitted data instead of real observations do not reduce the computational burden as we first speculated.
S1 and T1 inversions were extended until their cost function reached the same reduction as REF in order to estimate the additional computational burden required to reach similar results when initial conditions are not offset (S1) and the number of categories is increased (T1). There were 10 and 21 additional iterations necessary for T1 and S1, respectively. For T1, it shows that increasing the degrees of freedom also increases the computational burden. For S1, it highlights the benefits of offsetting δ13C(CH4) initial conditions.
As we assume no correlation of errors in R, Jo (see Eq. 3) can be divided into CH4 and δ13C(CH4) contributions. Figure 3 shows that all configurations lead to a fast reduction of the δ13C(CH4) contribution. During the first 10 iterations, it decreased from 50 %–90 % (depending on the configuration) to 10 %–20 %. Conversely, the CH4 contribution increased from 10 %–50 % to 80 %–90 %. By adjusting the isotopic source signatures (all configurations besides T3–T4), the system was able to efficiently and rapidly reduce the discrepancies between simulated and observed δ13C(CH4). As a result, the δ13C(CH4) RMSE decreased very rapidly during the first 10 iterations, while the CH4 RMSE decreased at a roughly constant rate. Consequently, the system is preferentially adjusting δ13C(CH4) over CH4 values to reduce the cost function, presumably because the ratio of RMSE to the prescribed observational error for δ13C(CH4) is, on average, about twice as large as for CH4. In other terms, it is simpler for the system to adjust δ13C(CH4) before attempting to modify CH4. The ratio of the number of δ13C(CH4) observations to the number of CH4 observations is not expected to play a significant role in the convergence process, although we did not study this influence rigorously. This ratio is only expected to affect the contribution of a component (δ13C(CH4) or CH4) to the total cost function.
The decrease rate associated with δ13C(CH4) RMSE can be increased by reducing the model uncertainties prescribed to the δ13C(CH4) observations. S3 is an example of such an adjustment, as the model uncertainties have been divided by two. With this configuration, the system requires five fewer iterations than REF to reach a similar δ13C(CH4) RMSE reduction but seven additional iterations to reach a similar CH4 RMSE reduction. T3 and T4 configurations constrain the isotopic signatures; thus, the reduction in the δ13C(CH4) contribution necessitates 25 more iterations than REF to reach similar RMSE reduction. To summarize, the decrease rate associated with δ13C(CH4) RMSE is highly dependent on the prescribed uncertainties in δ13C(CH4) observations and the ability of the system to adjust source signatures.
3.2 CH4 and δ13C(CH4) fitting
As expected, the assimilation process greatly improves the agreement between simulated and observed values for both CH4 and δ13C(CH4). Figure 4 shows the globally averaged time series of CH4 and δ13C(CH4).
CH4 RMSE using prior estimates is 19.4 ppb and drops to 14.3 ± 0.2 ppb (1σ) on average over all the configurations using posterior estimates. Prior estimates capture the observed CH4 well, and the improvement is therefore relatively small. In addition, all configuration results regarding CH4 are very similar. In particular, NOISO is not performing much differently than the other configurations, indicating that the additional isotopic constraint does not affect the fitting to CH4 observations.
Prior δ13C(CH4) prescribed in REF are continuously decreasing from −47.2 ‰ to −48.2 ‰ and thus agrees very poorly (RMSE is 0.47 ‰) with observed values. This can be due to an underestimation (values that are too negative) of some isotopic source signatures, an underestimation of the KIE values associated with the various sinks, an underestimation of the various sinks intensities (mostly Cl and OH), and/or a poor prior estimation of the source partitioning, i.e., an underestimation of 13C-enriched sources (FFs or BB) or an overestimation of 13C-depleted sources (WET or AGW). The data assimilation process reconciles simulated and observed δ13C(CH4) (RMSE is 0.086 ± 0.008 ‰) for all configurations, albeit that small differences, depending on the setup, emerge.
The S group provides a better match to δ13C(CH4) observations than the T group (0.081 ± 0.003 ‰ versus 0.091 ± 0.007 ‰). The fit is very similar within the S group. In contrast, the spread in the T group is larger, with δ13C(CH4) RMSE being equal to 0.093 ‰, 0.091 ‰, and 0.099 ‰, respectively, for T2, T3, and T4. These results suggest that giving more freedom to the system to adjust the isotopic signatures and providing region-specific estimates of prior source signatures instead of global values may be key elements for reaching a better agreement. Best results (i.e., smallest RMSE) are obtained with T1 (0.079 ‰). However, this configuration necessitates 10 additional iterations to reach better results than REF. Without these additional iterations, REF would have the best results (0.081 ‰).
Figure 5 shows the RMSE distribution at all measurement sites for each configuration. All sites exhibit a RMSE reduction (from prior to posterior) for both CH4 and δ13C(CH4), except for Bukit Kototabang, Indonesia (BKT), with T3 and T4 configurations. Furthermore, BKT, Moody, USA (WKT), Ulaan Uul, Mongolia (UUM), Anmyeon-do, Republic of Korea (AMY), and Pondicherry, India (PON), exhibit a posterior CH4 RMSE above 25 ppb, showing that CH4 measurements retrieved at these stations are not properly reproduced by the model, despite the optimization. Prescribed observation errors are likely not the main cause because mean values for these stations are large (10–15 ppb) but not the largest among all the assimilated stations. It can also be due to transport error or misrepresentation of sources close to the sites. Addressing this misfit is beyond the scope of this study, although the configuration influences the results. BKT and UUM fitting are notably deteriorated with T3 and T4 configurations. For example, BKT appears to be influenced by biomass burning sources in South East Asia, which are strongly dependent on the configuration (see Sect. 3.3). Moreover, T3 provides the poorest δ13C(CH4) fitting at AMY (0.24 ‰). Therefore, using global values for source signatures and preventing the system from optimizing them lead to poorer fitting. On the contrary, T1 improves the results, indicating that additional degrees of freedom can help to reconcile simulations with observations, especially in South East Asia and East Asia where these stations are located.
3.3 Global and regional emission increments
We are primarily interested in the additional information provided by the assimilation of δ13C(CH4) data. Rather than discussing the regional and global CH4 emissions and comparing these results to previous estimates, we investigate the differences between emissions inferred from configurations with and without the additional isotopic constraint. Long-term inversions will be run in the future with this system to provide more robust estimates of CH4 emissions and compare them to the existing literature.
The inversion time window is the 2012–2017 period. However, flux and source signature estimates in the 2012–2013 and 2016–2017 periods are not interpreted, as the system appears to require a 2-year spin-up (2012–2013) and a 2-year spin-down (2016–2017), over which the inversion problem is not sufficiently constrained, and isotopic signatures vary widely over time. Therefore, only the 2014–2015 estimates are analyzed in Sects. 3.3 and 3.4. Figure S2 in the Supplement shows the time series of isotopic signatures and illustrates this choice. These long effects are certainly caused by the relatively long relaxation timescales of isotopic ratios in the atmosphere (Tans, 1997) compared to that of total CH4. Fully understanding this would require a lot of time and running multiple inversions (or possibly only tangent linear simulations), starting from different initial conditions spanning the prescribed uncertainty envelope, to infer until when the initial atmospheric isotopic ratios and/or isotopic source signatures can influence the time series of atmospheric isotopic ratios. This was too much work for this study but will certainly be addressed in future studies.
Figure 6 shows global and regional increments from the NOISO and REF inversions relative to prior estimates. Hereinafter, these differences will be referred to as REF increment (REF – PRIOR) and NOISO increment (NOISO – PRIOR). The difference between both increments will be called an increment difference. Note that prior emissions are identical for all configurations. Posterior total emissions is 594.6 ± 1.2 Tg CH4 yr−1 over all configurations, indicating that the isotopic constraint and setup configurations do not significantly affect the posterior global emissions. A higher discrepancy between the budgets would have indicated a malfunction in the system, as the prescribed sinks are identical. The small associated standard deviation is likely caused by a slight difference in the fitting to the observations and/or by the spatial variability in the prescribed sink coupled with a small relocation of emissions, depending on the configuration. For instance, OH concentrations are larger in the tropics, and a relocation of emissions from the tropics to higher latitudes would be compensated for by larger global emissions. Between REF and NOISO, there is only a difference of 0.02 Tg CH4 yr−1. We can therefore conclude that the additional isotopic constraint either relocates the emissions or reallocates them between categories, as intended. All but one of the emission categories exhibit large changes between NOISO and REF, namely WET, FFs, AGW, and BB categories.
Overall, increments are large in regions with high emissions. Global increment differences (between REF and NOISO) in AGW (−6.4 Tg CH4 yr−1) and FF emissions (+8.6 Tg CH4 yr−1) are mainly due to regional increment differences in China and temperate Asia. AGW regional increment differences are equal to −2.1 Tg CH4 yr−1 in temperate Asia and in China. Similarly, FF regional increment differences are equal to +1.5 Tg CH4 yr−1 in temperate Asia and +5.0 Tg CH4 yr−1 in China. The WET global increment difference (−5.7 Tg CH4 yr−1) is mainly due to differences in Canada (−2.0 Tg CH4 yr−1) and South America (−2.3 Tg CH4 yr−1), but other regions such as Russia, temperate Asia, and South East Asia are involved. BB emissions are also modified when implementing the isotopic constraint. Their global increment difference is equal to +3.2 Tg CH4 yr−1, principally owing to regional increment differences in South East Asia (+1.7 Tg CH4 yr−1), Canada (+0.4 Tg CH4 yr−1), and Africa (+0.4 Tg CH4 yr−1). The NAT category exhibits very few changes (less than 1 Tg CH4 yr−1), even in relative values.
S group configurations infer posterior results that are consistent with REF, with only small variations, depending on the category and the region (see Table S5 in the Supplement). In particular, S1 provides roughly the same results as REF, but with more iterations, highlighting again that offsetting the initial conditions can help to reduce the computational burden without affecting the results. On the contrary, T-group configurations are affecting the increments, although T1 and T2 configurations are generally much closer to REF than T3 and T4. T1 (yellow dot; Fig. 6) and T2 (blue dot; Fig. 6) exhibit differences with the S group mainly in China, where WET and FF increments are modified (∼ −3 Tg CH4 yr−1). More importantly, almost freezing the isotopic signatures to their prior values (T3 and T4) results in increment differences 3 to 4 times larger than with REF, i.e., more than 10 Tg CH4 yr−1 at the global scale. It highlights the dependence of the inferred CH4 emissions on the prior source signatures estimates. In other words, the quality of isotopic source signatures (values and uncertainties) appears to be critical for the robustness of emissions estimates.
3.4 Global and regional source signature increments
Isotopic source signatures are also optimized by the system. Figure 7 provides the differences of flux-weighted source signatures between REF posterior and prior estimates for different regions and each emission category.
With configurations that allow the source signatures to be optimized, all source signatures are shifted upwards by the inversions in order to correct the excessively strong negative trend in δ13C(CH4). At the global scale, the flux-weighted source signatures of WET, FFs, AGW, BB, and NAT are increased by 1.7, 0.5, 0.9, 0.5, and 0.1 ‰, respectively. The global source signature is increased from −53.9 ‰ (prior) to −52.6 ± 0.2 ‰ (posterior, with a standard deviation over the configurations). More information is provided in Table S6 in the Supplement. The posterior global signature is strongly dependent on the KIE of atmospheric oxidation. This effect tends to deplete air in 13CH4, shifting the δ13C(CH4) to more positive values as the CH4 molecules emitted by the sources are removed from the atmosphere. The mean KIE in our simulations depends on (1) the prescribed OH, O(1D), and Cl concentrations and (2) the prescribed KIE values associated to the individual sinks. As the mean KIE is the same for all configurations, the posterior global source signatures are very close.
The WET global source signature, associated with REF posterior estimates, exhibits the larger upward shift compared to prior estimates, from a value of −60.8 ‰ to −59.1 ‰. Large upward WET source signature shifts are located in boreal regions (North America and Russia) but also in South America and temperate Asia. The AGW source signature is increased by 0.9 ‰, mainly due to changes in Asia. The FF source signature is increased by 0.5 ‰ due to a large increment in China (+1.2 ‰). Finally, the BB source signature is modified in South East Asia (+1.4 ‰) and Canada (+0.8 ‰).
These changes are consistent within the S group (see blue error bars in Fig. 7), although small variations are visible (e.g., ± 0.3 ‰ for WET in Canada). The source signature is therefore modified nearly to the same extent in all regions, no matter which configuration in the S group is analyzed. T1 (see the yellow dot in Fig. 7), with more optimized categories than the others, shows small differences at the global scale (less than 0.3 ‰ for all categories), although differences of more than 1 ‰ are found in China. Therefore, increasing the number of degrees of freedom leads to similar flux estimates but can affect the signatures at a regional scale. T2 estimates are shifted upward to reach a less negative global isotopic source signature without coming closer to the regional distribution of the S group. This is likely caused by the scarcity of δ13C(CH4) stations, and correcting this behavior seems challenging without additional observations. The problem might be circumvented by using the regional scale rather than the pixel scale to optimize isotopic signature values. Future inversions will test this assumption.
These results must be interpreted with caution because the input data suffer from high uncertainties. The artificial increase in the source signatures by our system can hardly be related to the literature and former investigations. Consequently, it is challenging to conclude whether an increase in the source signatures would be more realistic (i.e., supported by observational data) than, for instance, only increasing the emissions of 13C-enriched sources such as BB. This system is only based on a mathematical and physical framework connecting the several groups of uncertainties (observational, prior fluxes, prior source signatures, and prior sinks) and finding the most likely solution. Better estimates of these uncertainties must be prescribed before obtaining robust results. In particular, the uncertainties on KIE values and sink intensities have not been tested here and could largely influence the results. Also, the uncertainties on source signatures are relatively smooth in REF compared to recent country-specific estimates (Sherwood et al., 2017). Assessing these uncertainties should be a key aspect for future studies using this new inversion system to quantify the global CH4 budget.
3.5 Posterior uncertainties
Formally, posterior uncertainties are given by the Hessian of the cost function. This matrix can hardly be computed at an achievable cost, considering the size of the inverse problem. Other means must be implemented to obtain the posterior uncertainty, such as estimating a lower-rank approximation of the Hessian, using Monte Carlo ensembles of the variational inversion to represent the prior uncertainties, or computing multiple configurations covering a given range of possibilities. Here, using multiple configurations provides insight into the posterior uncertainty associated with the posterior fluxes. We calculated the full uncertainty range using the minimum and maximum values among all the configurations, as in Saunois et al. (2020). WET, AGW, FF, and BB flux estimates (Table 3) exhibit an uncertainty of 10 %, 7 %, 19 %, and 38 %, respectively. BB is the most uncertain estimate relative to its intensity, although FF shows the largest absolute uncertainty (23 Tg CH4 yr−1). These uncertainties are unlikely to be affected by the assimilation of additional δ13C(CH4) data because we expect the uncertainties on the isotopic source signatures to have a much larger influence. However, this remains to be tested in future work if posterior uncertainties can be calculated.
At present, M1QN3 is not the only optimization algorithm that can be utilized to perform variational inversions in the CIF. The CONGRAD algorithm (Fisher, 1998), which follows a conjugate gradient method combined with a Lanczos algorithm, is also implemented. In particular, it facilitates the computation of posterior uncertainties considerably. Any change in algorithm is very easy and accessible to any CTM embedded in the CIF. However, CONGRAD has not yet been tested with δ13C(CH4) data. As CONGRAD is only designed for linear problems, using this algorithm could radically change the results of the inversions performed with the isotopic constraints, and future work will focus on using CONGRAD to perform the inversions with isotopic constraints.
We present here a new variational inversion system designed to assimilate the observations of both a specific trace gas and its isotopic data. This system allows us to optimize both tracer emissions and associated isotopic signatures for multiple source categories. To test this system, we have assimilated CH4 and δ13C(CH4) data retrieved at different measurement sites over the globe.
Different configurations have been tested in order to assess the sensitivity of the system to the setup. We have shown that offsetting the δ13C(CH4) initial conditions before the inversion (S1), using δ13C(CH4) curve fitting data instead of the original observations (S2) and reducing the prescribed uncertainties in the δ13C(CH4) observations (S3), has very little effect on the inferred fluxes (less than 2 Tg CH4 yr−1 for each category at the global scale). However, offsetting δ13C(CH4) initial conditions before the inversion results in a reduced computational time (21 less iterations).
Other setup choices have more influence on the results. Increasing the number of source categories (T1) requires more computational time (10 more iterations) to reach a cost function (and RMSE) reduction similar to REF. Moreover, although the global posterior emissions with an increased number of categories are very close to those inferred with REF (less than 1 Tg CH4 yr−1), the posterior isotopic signatures can be modified in some regions (more than 1 ‰ in China). Also, starting from globally averaged values for the source signatures (T2) makes the system unable to retrieve the region-specific isotopic signatures from REF. Increasing the number of δ13C(CH4) observations could help us to cope with this issue. Finally, configurations constraining the source signatures (T3–T4) show differences in global flux estimates of more than 10 Tg CH4 yr−1, compared to REF. This emphasizes the need for good prior source signature estimates.
The major drawback of this inversion system is undoubtedly the large computational burden of a full minimization process. At least 40 iterations appear to be necessary to reach a satisfying convergence state at the regional scale. For the LMDz-SACS model, a maximum of eight CPUs can be run in parallel, resulting in an elapsed time of 5–6 weeks to run one of the inversions of this study. A new generation of transport models, such as DYNAMICO (Dubos et al., 2015), could help to address this problem in the future by allowing more processors to run in parallel. Also, further developments will implement some parallelization methods to enable computational burden reduction (e.g., Chevallier, 2013). In addition, variational inversions, as implemented in the CIF, do not provide a quantification (even approximated) of the posterior uncertainties. Dedicated efforts need to be made to address this issue in the future and at an achievable numerical cost. In particular, using the CONGRAD algorithm instead of M1QN3 could be a solution, as both algorithms can be easily selected in the CIF. However, additional work is needed to ensure that switching the optimization algorithm does not affect the results inferred with our new system.
This system is implemented within the CIF framework and can therefore be used for inversions with the various CTMs embedded in the CIF, provided the adjoint codes of the models exist. As the operations developed for the purpose of this study are performed outside the model structure, forward, tangent linear, and adjoint codes from other CTMs do not require any modifications as long as the model is capable of simulating both 12CH4 and 13CH4 simultaneously. The prior input must be adapted to the new model (spatial and time resolution), but the format of the observational data and of the prescribed errors can be preserved. Also, due to the variational method benefits, the efforts dedicated to the preparation of inputs do not scale with either the size of the observational datasets or the length of the simulation time window. Therefore, this system is very powerful and is particularly relevant to study, in a consistent way, the influence of multiple physical parameters on atmospheric isotopic ratios such as the transport, the isotopic signatures, the emission scenarios, the KIE values, etc. We did not try to assess the sensitivity of the system to these parameters here as only the technical aspects of the system were tested. This will be part of future analyses.
As mentioned in the introduction, future work will address the estimation of CH4 emissions over longer periods of time using this new system. For instance, the 2000–2006 CH4 stabilization period and the subsequent renewed growth are particularly interesting to study using the isotopic constraint as global δ13C(CH4) started to decrease after 2006. These periods of time have already attracted considerable critical attention from many inversion studies (with or without the isotopic constraint) and comparing the results derived from such a complete 3-D variational inversion system with other recent estimates should be highly relevant. The most important limitation of assimilating δ13C(CH4) lies in the fact that very limited δ13C(CH4) data are available, and therefore, evaluating the posterior simulated δ13C(CH4) is often challenging, if not impossible. However, satellite and balloon/AirCore data can easily be used to evaluate the posterior simulated CH4.
δ13C(CH4) is not the only kind of isotopic data that can be assimilated in such a system. Many δD(CH4) observations have also been retrieved during the 2004–2010 period at many different locations. These isotopic values can provide additional information that can further help to discriminate the co-emitted CH4 fluxes (Rigby et al., 2012). Moreover, ethane (C2H6) is co-emitted with CH4 by fossil fuel extraction and distribution (Kort et al., 2016; Smith et al., 2015), and observations have been available at a multitude of sites since the early 1980s. Therefore, assimilating these data can provide additional constraints. The system will therefore be improved in the future in order to assimilate δ13C(CH4), δD(CH4) and C2H6 observations together.
The code files of the CIF version used in the present paper are registered under the following link: https://doi.org/10.5281/zenodo.6304912 (Berchet et al., 2022). Prior anthropogenic fluxes (EDGARv4.3.2) can be downloaded from the EDGAR website (https://edgar.jrc.ec.europa.eu/dataset_ghg432, last access: 23 February 2022). Biomass burning fluxes can be downloaded from the GFED website (https://globalfiredata.org/pages/data/, last access: 23 February 2022). Prior natural fluxes and other data are available upon request (email@example.com). The CH4 data used in the present paper were provided by many stations and measurement networks around the world (a comprehensive list can be found in the Supplement and in the acknowledgements). Their data are freely available upon request to the station maintainers or via dedicated websites. The δ13C(CH4) observational data can be downloaded from the NOAA-GML website (https://gml.noaa.gov/dv/data/, last access: 23 February 2022).
The supplement related to this article is available online at: https://doi.org/10.5194/gmd-15-4831-2022-supplement.
JT implemented the variational inversion system within the CIF, with the precious help of AB. JT designed, ran, and analyzed the tested configurations. AB, MS, IP, and PB provided scientific and technical expertise. They also contributed to the analysis of this work. BHV and SEM provided the δ13C(CH4) data and scientific expertise regarding δ13C(CH4) observations. JT prepared the paper, with contributions from all co-authors.
The contact author has declared that neither they nor their co-authors have any competing interests.
Publisher's note: Copernicus Publications remains neutral with regard to jurisdictional claims in published maps and institutional affiliations.
This work has been supported by the CEA (Commissariat à l'Energie Atomique et aux Energies Alternatives). The study relies extensively on the meteorological data provided by the ECMWF. Calculations were performed using the computing resources of LSCE, maintained by François Marabelle and the LSCE IT team. The authors thank the reviewers (Peter Rayner and two anonymous referees) for their fruitful comments and suggestions on our work. We are also grateful to many station maintainers that provided the CH4 data. For the AGAGE network, we note that AGAGE is supported principally by NASA (USA) grants to MIT and SIO and also by BEIS (UK) and NOAA (USA) grants to Bristol University, CSIRO and BoM (Australia), FOEN grants to Empa (Switzerland), NILU (Norway), SNU (South Korea), CMA (China), NIES (Japan), and Urbino University (Italy). At the South African Weather Service Cape Point GAW station, we thank Casper Labuschagne, Thumeka Mkololo, and Warren Joubert. For the EC network, we thank Doug Worthy. For the MGO network, we thank Nina Paramonova and Victor Ivakhov. For the AMY network, we thank Haeyoung Lee and Sepyo Lee. The AMY data were funded by the Korea Meteorological Administration Research and Development Program (grant no. KMA2018-00522). For the ENEA network, we thank Alcide Disarra, Salvatore Piacentino, and Damiano Sferlazzo. For the EMPA network, we thank Martin Steinbacher and Brigitte Buchmann. The CH4 measurements at JFJ are run by EMPA in collaboration with FOEN and are also supported by ICOS-CH. For the BMKG-EMPA network, we thank Martin Steinbacher, Alberth Christian, and Sugeng Nugroho. The CH4 measurements at BKT are run by BMKG in collaboration with EMPA.
This research has been supported by the Commissariat à l'Energie Atomique et aux Energies Alternatives (grant no. CFR 2018).
This paper was edited by Richard Neale and reviewed by Peter Rayner and two anonymous referees.
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