The role of methane in future climate strategies: mitigation potentials and climate impacts
This study examines model-specific assumptions and projections of methane (CH4) emissions in deep mitigation scenarios generated by integrated assessment models (IAMs). For this, scenarios of nine models are compared in terms of sectoral and regional CH4 emission reduction strategies, as well as resulting climate impacts. The models’ projected reduction potentials are compared to sector and technology-specific reduction potentials found in literature. Significant cost-effective and non-climate policy related reductions are projected in the reference case (10–36% compared to a “frozen emission factor” scenario in 2100). Still, compared to 2010, CH4 emissions are expected to rise steadily by 9–72% (up to 412 to 654 Mt CH4/year). Ambitious CO2 reduction measures could by themselves lead to a reduction of CH4 emissions due to a reduction of fossil fuels (22–48% compared to the reference case in 2100). However, direct CH4 mitigation is crucial and more effective in bringing down CH4 (50–74% compared to the reference case). Given the limited reduction potential, agriculture CH4 emissions are projected to constitute an increasingly larger share of total anthropogenic CH4 emissions in mitigation scenarios. Enteric fermentation in ruminants is in that respect by far the largest mitigation bottleneck later in the century with a projected 40–78% of total remaining CH4 emissions in 2100 in a strong (2 °C) climate policy case.
Studies have shown that anthropogenic non-CO2 greenhouse gas (GHG) emissions, predominantly methane (CH4) and nitrous oxide (N2O) from agriculture, are expected to represent an increasingly larger share of total GHG emissions in stringent mitigation (Clarke et al., 2014; Gernaat et al., 2015) This makes non-CO2 GHGs a possible obstacle in achieving the 2° to 1.5 °C climate target as agreed upon in the 2015 Paris Accords (UNFCCC, 2015). However, there is a large range in non-CO2 GHG projections, arising from uncertainty about emission levels when unabated and the availability and cost of technologies to mitigate emissions from specific sources. Understanding this uncertainty is crucial when determining optimal mitigation strategies.
As part of the Energy Modeling Forum (EMF)-30 Study on Short-Lived Climate Forcers and Air Quality (EMF, 2019), which examines the potential contribution of short-lived climate forcers (SLCFs) to climate policy, this study contributes a detailed analysis of CH4 emissions and emission reductions. With a shorter lifetime than CO2, CH4 emission reductions can more effectively contribute to climate mitigation in a short timeframe, but also long-term CH4 forcing is substantially more dependent on future emission levels rather than present-day emissions. The specific focus on CH4 is motivated by the expectation that it will continue to be the most influential GHG after CO2 (Gernaat et al., 2015; Saunois et al., 2016), which demands for a more in-depth assessment.
Assessing cost-effective and non-climate policy related improvements in CH4 emission intensity (i.e., the use of fugitive CH4 emissions as an energy source, air quality measures and net zero, or negative cost measures). This provides a better understanding of the baseline case without climate policy and starting point for further CH4 reductions.
Exploring the potential range in CH4 emission projections and resulting climate effects, from no climate policy to a stringent climate policy case.
Disentangling direct CH4 mitigation and indirect mitigation as a result of CO2 mitigation policy (the latter through a decrease in fossil fuel production, leading to less fugitive CH4 emissions).
In order to further understand what will be main bottlenecks and opportunities in limiting future CH4 emissions, the projected sectoral emission reductions are compared to maximum emission reductions found in literature. Differences in reduction potentials are, where possible, traced back to model-specific assumptions and insights from literature. As such, this analysis provides potential real-world implications for future climate policy and insights in required technological changes.
2.1 Scenario analysis
Nine models have taken part in a multi-integrated assessment model (IAM) scenario comparison,1 with a consistent experimental setup across the models: AIM/CGE, DNE21+, ENV-Linkages, GCAM, IMAGE, MESSAGE-GLOBIOM, POLES, REMIND, and WITCH-GLOBIOM (see section S1 in the Supplement). The IAMs have been widely used in climate policy research (e.g., Kriegler et al., 2014; Riahi et al., 2017; Tavoni et al., 2014; Van Vuuren et al., 2011) and include comprehensive global representations of the human economic system, its interaction with the natural system and associated emissions. Assumptions on the representation of mitigation options, technological, sectoral and regional detail, and the level of foresight for finding optimal policy strategies vary widely across the models. As such, the models cover a broad section of the solution space for reaching climate targets. All models represent the main CH4 sources: fossil energy production, agriculture, and waste, either as aggregated sector emissions or on a sub-sectoral level. These sources represented 89% of total anthropogenic CH4 emissions in 2012 (Saunois et al., 2016). Other sources (industrial processes, energy demand/fuel burning, deforestation, and international shipping and aviation) are occasionally missing in some of the models, in which case these models are not used in the analysis of the source concerned.
“Reference,” a no climate policy scenario with default model improvements in CH4 emission factors and default long-term air-pollutant emission controls. Cost-effective (i.e., leading to net zero or negative system costs) and non-climate policy related mitigation options are allowed; i.e., increased use of fugitive CH4 emissions for cost-effective energy production, reducing CH4 emissions as a safety risk, or as part of future air quality policy). The scenario is based on SSP2, a widely used model setup with middle-of-the-road development assumptions (Riahi et al., 2017).
“Fzn-CH4,” a diagnostic scenario analogous to Reference, but with constant (“frozen”) CH4 emission factors from 2010 onward, assuming no emissions control advancements beyond 2010. The scenario is used to diagnose the amount of emission control in the reference scenario.
“ClimPolicy,” a cost-optimal (i.e., minimized policy costs) 2 °C climate policy scenario, with a global cumulative energy and industry CO2 emissions constraint of 1000 GtCO2 from 2011 to 2100. This budget corresponds to the upper end of emission budgets of scenarios in the 430–480 ppm CO2 category of likely 2 °C scenarios. All GHGs are targeted together in a “multi-gas” approach with the same model-specific CO2 price and 100-year global warming potential metric to acquire non-CO2 emission prices (see Table S1.1 in the Supplement).
“ClimPolicy-CH4 only,”2 a diagnostic scenario to isolate the effect of direct (“end-of-pipe”) CH4 mitigation. The CH4 price from ClimPolicy is applied to CH4 reduction measures only, with no price applied to CO2 or any other GHG (note that under a CH4 price, some structural changes can occur that do affect other GHGs, e.g., a higher natural gas price can reduce natural gas production, which lowers CO2 emissions).
“ClimPolicy-CO2 only,” a diagnostic scenario to isolate the indirect CH4 mitigating effect of CO2 mitigation policy. It has the same CO2 budget as ClimPolicy, but no price is applied to any other GHGs.
Emission and climate effect of autonomous, cost-effective and non-climate policy related improvements in CH4 emission intensity (i.e., air quality measures and net zero or negative cost measures).
Sector and region-specific as well as total CH4 emissions with and without climate policy. Total range in CH4 RF.
Emission and climate effect of (1) direct CH4 mitigation, (2) indirect mitigation resulting from CO2 measures, (3) the combined effect of both
2.2 Model diagnostics and literature review
The model diagnostics and literature review of the study is aimed at (1) understanding how differences in CH4 emission projections are influenced by underlying model assumptions, (2) how the model projections compare to estimates from literature, and how any differences can be explained. In a diagnostic exercise, the models have introduced the same high carbon price (leading up to 1250 USD2015/tCO2 in 2100). The resulting total CH4 reduction in the models can (effectively) be considered the maximum reduction potential in a multi-gas strategy (comparable to ClimPolicy). This analysis has been done as part of a much broader assessment in the ADVANCE project (Luderer et al., 2016) and is made available for this study. All models, except ENV-Linkages, have taken part in both projects. The projected sectoral emission reductions are compared to maximum emission reductions found in literature. Based on this comparison, potential opportunities and barriers for each of the emission sources are identified.
3.1 Scenario analysis
Despite the improvements in emission factors, CH4 emissions in the Reference case are projected to rise steadily by 24–47% compared to 2010 in 2050 and by 10–72% in 2100, in line with projections used for the IPCC 5th Assessment Report (Clarke et al., 2014). Although the projection for 2100 is obviously more uncertain, the general trend is that emissions in the 2050–2100 period stabilize, driven mostly by a stabilizing global population and a decreasing importance of fossil fuels.
In the 2 °C climate policy case (ClimPolicy), the emissions are projected to be reduced, relative to Reference emissions, by 58% (43–70%) and 68% (58–84%) in 2050 and 2100, respectively, indicating that most of the reductions are realized in the short term and that smaller additional reductions are expected in the second half of the century. Emission levels in 2100 are projected to reach 159 Mt CH4/year on average (range, 78–229 Mt), less than half the emissions in 2010.
All models show a larger mitigation effect resulting from measures that directly target CH4 emissions (in ClimPolicy-CH4 only) than indirectly from structural changes resulting from CO2 mitigation policy (in ClimPolicy-CO2 only); hence, the former can be considered more effective in bringing down CH4 emissions. This is in line with earlier work (Gambhir et al., 2017). In 2100, direct mitigation alone is projected to lead to a reduction of 50% to 74% compared to the reference case, compared with 22% to 48% reduction indirectly resulting from CO2 policy.
3.1.2 Regional breakdown
3.1.3 Global sectoral breakdown
Fig. 3 shows the projected development of sectoral CH4 emissions in the Reference and ClimPolicy cases. In 2010, agriculture emissions (from livestock, rice, and other crops) are found to be the largest anthropogenic source (43–49% of total emissions), followed by energy supply and demand (32–39%), and waste (16–22%). Without climate policy, emissions from all three main aggregated sectors will continue to increase, with similar growth rates (i.e., their relative contribution to total emissions are not expected to change much in time, see Supplement S3). In ClimPolicy scenario, energy emissions are expected to decrease dramatically, due to a combination of direct mitigation and a reduction of fossil fuel. Waste emissions in 2100 are expected to decrease by half compared to 2010, while agriculture emissions are projected to only slightly decrease or even remain stable. This difference in sectoral mitigation potential makes agriculture CH4 emissions by far the largest source of remaining emissions under the climate policy scenario: 60–80% in of total emissions 2050 and 55–88% in 2100.
3.2 Diagnostic analysis and literature comparison
There is a relatively good agreement in projected CH4 emission reductions relative to baseline (between 64% and 82%, with most models between 64% and 72%) despite large differences in sectoral reduction potentials (see next section). The highest reduction is seen in POLES, leading up to 82% in 2100. Mainly, this is the result of very optimistic assumptions on reductions in agriculture (up to 74%).3 AIM/CGE also stands out with a relatively high MRP (up to 79% in 2100), mainly resulting from extrapolation of the underlying MAC data (Lucas et al., 2007), leading to relatively high sectoral reduction potentials.
Consistently across models, there is an increasing MRP as carbon prices increase to very high values. This is driven by three effects that vary in influence in the models: (1) increased potential in the MAC curves at high prices, (2) indirect mitigation from CO2 policy, and (3) economic feedbacks from high methane prices (i.e., lower demand for methane-intensive products). Regarding the first effect (1), POLES, AIM/CGE, DNE21+, ENV-Linkages, and MESSAGE-GLOBIOM make use of marginal abatement cost (MAC) curves that are (sometimes partly) based on extrapolation of underlying datasets, which allows for slowly increasing reduction levels under increasingly high carbon prices. The other models have assumed sectoral MRPs or marginal abatement cost curves that do not allow further reductions at a specific price (see Supplement S5 for model-specific MAC data and additional assumptions/modifications). The indirect mitigation effect from CO2 mitigation (2) is strongest in GCAM and IMAGE, followed by WITCH2016, DNE21+, and AIM (see Supplement S2). Economic feedbacks from methane prices on the demand of heavily methane-producing activities (3) (e.g., fossil fuel and livestock production) have been modeled in AIM/CGE, ENV-Linkages, GCAM, MESSAGE, and REMIND.
The maximum MRP values (i.e., the highest found among the models) are higher (so more ambitious) than any of the reduction potentials found in recent literature, and for several sources, the average MRPs can be considered on the high end of what is found in literature (see right panel). The higher MRPs in the models can partly be explained by the optimistic estimates (for coal, natural gas, and wetland rice) from Lucas et al. (2007) (used by AIM/CGE, IMAGE, and REMIND) as well as extrapolations of reduction potentials at higher carbon prices (e.g., for enteric fermentation). Note, however, that models do not always reach their MRP due to too low carbon prices or inertia in the speed of emission reduction (e.g., in IMAGE and POLES). In addition, Höglund-Isaksson et al., (2012, 2015) used as a comparison here is based on the technical potential of currently known technologies and can be considered relatively conservative. However, when considering the maximum MRPs, it can be concluded that some models assume that technology improvements and global implementations go beyond what is found in recent literature.
All models agree that enteric fermentation in ruminants can by far be considered the largest remaining mitigation bottleneck in a strong climate policy case. In ClimPolicy in 2100, emissions are projected to be an average 90 Mt/year (range, 31–137 Mt) or 58% (40–87%) of total emissions. These reductions are to a large extent realized by end-of-pipe measures and not by any human dietary changes, since this is not incorporated in the models’ MAC curves (note that most models do include price feedbacks, where ruminant meat and dairy demand is lowered somewhat as a result of higher CH4 prices). The average reduction in 2100 (55%) is comparable with the MRP estimated in Harmsen et al. (2019): 52%. This could be realized if all existing technologies (e.g., breeding through genetic selection, food supplements) would further develop and be optimally introduced worldwide. Höglund-Isaksson (2012) estimates the technical reduction potential at 50%, but only if there would be a large diet shift away from ruminant meat consumption. Due to physiological limitations, it seems very unlikely that much higher reductions (> 60%) are feasible without a global change in diets and/or a large-scale introduction of cultivated meat products.
For the remaining emission sources, the average model projections are generally in line with existing literature, although options for improvements exist and ranges in model outcomes are large, indicating substantial uncertainty (see Table S5.2 in the Supplement). Sewage and wastewater emissions are projected to be the second largest remaining emission source (with very large uncertainty). If all countries would reach the same per capita emissions as in OECD Europe, emission reductions would be 90% (Harmsen et al., 2019; US-EPA, 2013). This would require a large-scale implementation of centralized aerobic wastewater treatment systems, improvement of the CH4 recovery rate of existing plants, and additional abatement options for anaerobic treatment. With a reduction of 8% to 94% in ClimPolicy 2100 (average: 52%), some of the model projections can be considered conservative.
Projected emission reductions for rice also differ considerably across the models (in ClimPolicy, 29–87% in 2100) as do estimates from literature: In 2100, 31% according to Höglund-Isaksson (2012) and 77% according to Harmsen et al. (2019). The latter study assumes implementation of extra measures (see Supplement S6), maximized implementation potential, and technological improvements. Even in such a case, residual global emissions around 10 Mt/year may be unavoidable.
The models project an emission reduction of 20–74% of CH4 emissions from manure in ClimPolicy in 2100. Anaerobic digesters, centralized or farm scale, combined with efficient and enclosed manure collection and processing could bring down emissions by 75% or more if further developed (Graus et al., 2004). However, it is unlikely that this will ever be viable and implemented in the least developed regions, in particular for non-confined ruminant livestock. With very high carbon prices enforced worldwide, and maximized free trade, emission reductions could still be considerable, by reallocation of livestock production towards more efficient and less GHG intensive systems (Havlík et al., 2014).
For landfills and solid waste CH4 mitigation, a whole range of options exist that can bring down emissions, varying from waste diversion (recycling and reuse), to CH4 utilization and flaring, and all studies agree that high MRPs (80–90%) are feasible. The models project reductions of 37–99% (average 79%) in ClimPolicy in 2100, resulting in 7.5 Mt CH4/year residual emissions on average.
3.3 Climate impacts
The upper left panel also shows that the direct CH4 forcing in ClimPolicy_CH4 only is very close to the direct forcing in ClimPolicy (much closer than the CH4 emissions in the two scenarios; see Fig. 1). This is the result of a shorter CH4 lifetime in ClimPolicy_CH4 only, since the lifetime of CH4 is indirectly dependent on NOx, CO, and VOC concentrations, through its relation with tropospheric OH (Meinshausen et al., 2011).
Note in the upper right panel that in both Reference and ClimPolicy, the relative contribution of direct CH4 to total forcing decreases in time, as it is short-lived and does not accumulate in the atmosphere as much as CO2 and N2O (see Supplement S7 for forcer specific RF). Despite this decrease, CH4 is still projected as the most influential GHG second to CO2. This is clearly the case if no direct CH4 regulation would be enforced (in ClimPolicy-CO2 only in 2100, direct CH4 forcing constitutes 19% of total forcing on average), but also with maximum mitigation in a 2-degree scenario (on average, 13% of total forcing comes from CH4 in ClimPolicy in 2100), especially when considering the additional indirect contribution of CH4 to total forcing.
The lower panel shows the temperature differences between the five scenarios in 2050 and 2100, thus indicating the relevance of CH4 reducing measures. In 2100, cost-effective and non-climate policy-related CH4 reductions in the Reference case would reduce GMT 0.15 °C on average compared to Fzn-CH4, while strong CH4 mitigation policy (in ClimPolicy_CH4 only) can further bring down GMT by 0.46 °C (or 12% of total GMT change), in line with a similar assessment by Rogelj et al. (2015). The temperature difference between ClimPolicy-CO2 only and ClimPolicy represents the effect of including non-CO2 emissions in a 2 °C climate strategy, which amounts to 0.33 °C (or 16.5% of total GMT change) in 2100 on average. Although the exact value cannot be determined based on this assessment, more than half this difference can likely be attributed to CH4 mitigation (consistent with the estimate by Rogelj et al. 2015; 0.25 °C). Roughly half of the forcing difference between the two scenarios (47% on average in 2100) results from differences in direct CH4 forcing, and the total temperature increase from CH4 is estimated at 140% of the temperature increase from direct forcing alone (Smith et al., 2012). Note also that, particularly in the long term, some models have substantial indirect CO2 forcing reductions in ClimPolicy_CH4 only, due to increased fossil fuel prices resulting in CO2 concentration decreases (see discussion elsewhere in this special issue (Smith, 2018)).
Note that the results might be influenced by recent studies that could change the understanding of the climatic role of CH4. According to Etminan et al. (2016), the present-day RF of CH4 has been historically underestimated and should be increased by 25%. Additionally, Modak et al. (2018) suggest that efficacy (effective impact of RF on GMT) for CH4 should be reduced (17% lower than earlier assumed). In terms of impact on GMT, these factors may partially compensate each other.
4 Discussion and conclusions
Although this study has a comprehensive coverage of anthropogenic CH4 sources, there are several factors that could influence the conclusions.
The possible range in structural economic shifts (changes in diet patterns, relocation of agricultural production, increased waste incineration) is only partly included in the scenarios, in the sense that these are based on the moderate socioeconomic developments of SSP2 combined with a 2 °C target. However, note that in the complete set of stringent mitigation scenarios in the SSPs (including those more green-growth oriented (SSP1) or unsustainable (SSP3) socioeconomic assumptions, and 1.5 °C targets), there are only a few exceptions that fall outside the global CH4 emission projections in this study (GCAM, with up to 92 Mt CH4 higher emissions in the 2 °C case and AIM/CGE, with up to 31 Mt CH4 lower emissions in the 1.5 °C case) (Riahi et al., 2017).
While CH4 from wetlands is a natural source and therefore not included in this study, human-induced reduction and management of wetlands can have a large effect on emissions, positively or negatively, as total wetland emissions are very high (155–235 Mt CH4/year (Saunois et al., 2016)). This anthropogenic effect is highly uncertain and therefore poorly represented in most models.
The incorporated CH4 MAC curves are to a large extent based on existing or envisioned technologies. Although the models take unforeseen technological improvements into account by assuming deeper reductions at higher costs and in the longer term, than what is found in literature, this is also highly uncertain and represented quite differently across the models (indicated by a large spread in sectoral reduction potentials). The models could improve by updating the underlying MAC data, which, in many cases, is more than 10 years old. However, note that, to a large extent, the uncertain association with technological change also applies to the estimates derived from literature. Harmsen et al. (2019) provide single value estimates of reduction potentials per sector, which rely on a range of uncertain assumptions (See Supplement S6), which, if varied, would also lead to an uncertainty of range in sectoral reduction potentials. By including multiple models in our study, much of this intrinsic uncertainty is captured, giving more confidence in the robust results across models (i.e., this study’s main conclusions).
CH4 emissions from all three main aggregated sectors, fossil energy supply, agriculture, and waste, are projected to continue to increase steadily without climate policy, up to 150% of current (2010) emissions in 2100. Significant cost-effective and non-climate policy-related reductions (7–28% less in 2050 and 10–36% less in 2100, largely due to the use of fugitive CH4 emissions as an energy source) are expected to reduce emissions somewhat, but will not affect the general trend. While there are strong co-benefits with CO2 mitigation, direct CH4 mitigation is crucial and most effective in bringing down total CH4 emissions.
In a stringent (2 °C) climate policy scenario, energy CH4 emissions are expected to decrease dramatically due to a combination of direct CH4 abatement and a concurrent reduction in fossil fuel use. Waste emissions are decreased by half, while agriculture emissions are projected to only slightly decrease or even remain stable. Asia has the largest contribution to total CH4 emissions, although in relative terms that contribution declines in time. Per capita emissions in Latin America are projected to be the highest in 2100, due to a relatively high concentration of livestock.
Enteric fermentation in ruminants is by far the largest bottleneck by the end of the century. In a 2 °C case in 2100, emissions are estimated at 87 Mt/year (range, 31–137 Mt) or 57% (20–91%) of total emissions. It seems unlikely that these residual emissions can be avoided without a global change in human diets towards monogastric meat or an increasingly plant-based diet.
In terms of the maximum global CH4 reduction, there is a relatively large consensus (with most models projecting a maximum reduction between 64% and 72% compared to no climate policy), despite much larger differences in sector and source-specific reduction. In 2100, the maximum reduction potentials (MRPs) for the fossil fuel sectors and for landfills/solid waste are generally higher than 90%. There is large uncertainty about the MRP of wastewater and of the three main agriculture sources: enteric fermentation, rice, and manure, which are generally also much lower in all models (between 25% and 60% in 2100). The models’ MRPs can be considered on the high end of what is found in literature.
In all scenarios, the relative contribution of direct CH4 forcing to total forcing will decline; however, CH4 will remain the second most important GHG after CO2, with 13% (11–14%) of total radiative forcing in the 2 °C case. This is also reflected in the temperature reducing potential of CH4 mitigation measures (around 10% of the total temperature change in 2100); thus, optimizing mitigation is crucial in reaching low climate targets.
The scenario analysis has been performed as part of the 30th Energy Modelling Forum (EMF30), an international collaboration project with the goal of understanding the potential role of short-lived climate forcer (SLCF) mitigation in climate policy EMF (2017) EMF 30: short lived climate forcers/air quality.
This scenario is slightly different from the EMF30 scenario “CH4-only” which assumes a constant CH4 price between 2030 and 2100. In all models, that scenario leads to higher emissions (5–76%, average = 32%) in 2100. For better comparison with ClimPolicy and to assess the deepest CH4 reductions, ClimPolicy-CH4 only is used in this study.
Figure refers to world aggregate. Reductions in agriculture result from country-specific marginal abatement cost curves derived from multiple runs of the GLOBIOM model, with a linear extrapolation for high carbon prices. In more recent model configurations, without extrapolation, the resulting world MRP is 63% in 2100.
The research leading to these results has received funding from CWF (IIA/17/1303). We would like to thank them and our colleagues who have directly or indirectly supported the work within the EMF30 consortium. We would like to thank them and our colleagues who have directly or indirectly supported the work within the EMF30 consortium.
The research leading to these results has received funding from CWF (IIA/17/1303).
- Clarke L, et al. (2014) Assessing transformation pathways. In: Climate Change 2014: Mitigation of Climate Change. Contribution of Working Group III to the Fifth Assessment Report of the Intergovernmental Panel on Climate ChangeGoogle Scholar
- EMF (2019) Energy Modeling Forum (EMF)-30 Study on Short-Lived Climate Forcers (SLCF) and Air Quality. https://emf.stanford.edu/projects/emf-30-short-lived-climate-forcers-air-quality
- Etminan M et al (2016) Radiative forcing of carbon dioxide, methane, and nitrous oxide: a significant revision of the methane radiative forcing. Geophys Res Lett 43Google Scholar
- GECS (2002) Greenhouse gas emission control strategies - research project N° EVK2-CT-1999-00010. Thematic Programme : Environment and Sustainable Development of the DG Research Fifth Framework ProgrammeGoogle Scholar
- Graus WJ, et al. (2004) Marginal GHG-Abatement curves for agriculture. Ecofys report, EEP030339, April 2004Google Scholar
- Harmsen M et al. (2019) Long‐term emission reduction potential of non‐CO2 greenhouse gases. Environmental Science & Policy (in press)Google Scholar
- Höglund-Isaksson L (2017) Bottom-up simulations of methane and ethane emissions from global oil and gas systems 1980 to 2012. Environ Res Lett 12Google Scholar
- Höglund-Isaksson L et al (2015) AMAP chapter 5 CH4: AMAP assessment 2015: methane as an Arctic climate forcer: chapter 5: anthropogenic methane sources, emissions and future projections. Arctic Monitoring and Assessment Programme 2015:JRC99758Google Scholar
- IPCC (2013) Annex II: climate system scenario tables. In: Prather M, Flato G, Friedlingstein P, Jones C, Lamarque J-F, Liao H, Rasch P (eds) Climate change 2013: The Physical Science Basis. Contribution of Working Group I to the Fifth Assessment Report of the Intergovernmental Panel on Climate Change. Cambridge University Press, CambridgeGoogle Scholar
- Kriegler E et al (2014) Making or breaking climate targets: the AMPERE study on staged accession scenarios for climate policy. Technol Forecast Soc ChangGoogle Scholar
- Luderer G, et al. (2016) Deep decarbonisation towards 1.5 °C – 2 °C stabilisation. Policy findings from the ADVANCE project,〈hal-01579189〉 HALGoogle Scholar
- Modak A et al. (2018) Does shortwave absorption by methane influence its effectiveness?. Climate Dynamics 51(9-10):3653–3672Google Scholar
- Riahi K et al (2017) The shared socioeconomic pathways and their energy, land use, and greenhouse gas emissions implications: an overview. Glob Environ ChangGoogle Scholar
- Rogelj J et al (2015) Impact of short-lived non-CO2 mitigation on carbon budgets for stabilizing global warming. Environ Res Lett 10Google Scholar
- Smith S (2018) Forcing and temperature changes from methane and black carbon reduction scenarios, EMF30 special issue climatic change, forthcomingGoogle Scholar
- UNFCCC (2015) Paris agreement. Decision 1/CP.17. http://unfccc.int/resource/docs/2015/cop21/eng/l09r01.pdf, UNFCCC document FCCC/CP/2015/L.9/Rev.1
- US-EPA (2013) United States Environmental Protection Agency (USEPA), Global mitigation of non-CO2 greenhouse gases: 2010–2030Google Scholar
Open Access This article is distributed under the terms of the Creative Commons Attribution 4.0 International License (http://creativecommons.org/licenses/by/4.0/), which permits unrestricted use, distribution, and reproduction in any medium, provided you give appropriate credit to the original author(s) and the source, provide a link to the Creative Commons license, and indicate if changes were made.