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Anthropogenic methane output on rise again after falling Coupled with natural changes net CH4 may again rise soon

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Posted 28 September 2006 - 08:56 PM

Editor's Summary
Methane: masked intruder

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Changes in atmospheric methane levels over the past twenty years are well documented, but the causes of these changes remain uncertain. Bousquet et al. use inverse (top-down) modelling to quantify variations in methane emissions from different sources between 1983 and 2004. They find that a decrease in the growth rate of atmospheric methane during the 1990s was caused by a decrease in anthropogenic emissions, but that anthropogenic emissions have increased again since 1999. To date, this trend has been masked by a coincident decrease in wetland emissions, but it is possible that it will cause total methane levels to rise again in the near future.


Letter

Nature 443, 439-443(28 September 2006) | doi:10.1038/nature05132; Received 10 April 2006; Accepted 3 August 2006
Contribution of anthropogenic and natural sources to atmospheric methane variability
P. Bousquet1,2, P. Ciais1, J. B. Miller3,4, E. J. Dlugokencky3, D. A. Hauglustaine1, C. Prigent5, G. R. Van der Werf6, P. Peylin7, E.-G. Brunke8, C. Carouge1, R. L. Langenfelds9, J. Lathière1, F. Papa5,10, M. Ramonet1, M. Schmidt1, L. P. Steele9, S. C. Tyler11 and J. White12

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Methane is an important greenhouse gas, and its atmospheric concentration has nearly tripled since pre-industrial times1. The growth rate of atmospheric methane is determined by the balance between surface emissions and photochemical destruction by the hydroxyl radical, the major atmospheric oxidant. Remarkably, this growth rate has decreased2 markedly since the early 1990s, and the level of methane has remained relatively constant since 1999, leading to a downward revision of its projected influence on global temperatures. Large fluctuations in the growth rate of atmospheric methane are also observed from one year to the next2, but their causes remain uncertain2, 3, 4, 5, 6, 7, 8, 9, 10, 11, 12, 13. Here we quantify the processes that controlled variations in methane emissions between 1984 and 2003 using an inversion model of atmospheric transport and chemistry. Our results indicate that wetland emissions dominated the inter-annual variability of methane sources, whereas fire emissions played a smaller role, except during the 1997–1998 El Niño event. These top-down estimates of changes in wetland and fire emissions are in good agreement with independent estimates based on remote sensing information and biogeochemical models. On longer timescales, our results show that the decrease in atmospheric methane growth during the 1990s was caused by a decline in anthropogenic emissions. Since 1999, however, they indicate that anthropogenic emissions of methane have risen again. The effect of this increase on the growth rate of atmospheric methane has been masked by a coincident decrease in wetland emissions, but atmospheric methane levels may increase in the near future if wetland emissions return to their mean 1990s levels.


News and Views

Nature 443, 405-406(28 September 2006) | doi:10.1038/443405a; Published online 27 September 2006
Climate change: A nasty surprise in the greenhouse
Jos Lelieveld1

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Abstract
The Kyoto Protocol aims to reduce emissions of greenhouse gases such as methane. But it seems that the fall in human-induced methane emissions in the 1990s was only transitory, and atmospheric methane might rise again.

Methane is a potent greenhouse gas — per molecule, more than 20 times as powerful as carbon dioxide1. Moreover, when methane emissions rise, so too does the concentration of the pollutant ozone in the troposphere, the lowest layer of Earth's atmosphere2. Methane also consumes hydroxyl radicals, whose oxidative effects are essential to atmospheric cleansing. On page 439 of this issue3, Bousquet et al. recount the results of an international effort to measure atmospheric methane concentrations and combine these data with a computer model of atmospheric chemistry and transport. The bad news is that the slowdown in global methane emissions in the past few decades was only temporary: reports of the emissions' control have been exaggerated.

At present, about two-thirds of global methane comes from anthropogenic sources, and most emissions occur in the Northern Hemisphere (Fig. 1, below). Of naturally produced methane, the largest proportion stems from bacteria in wetlands that produce the gas when decomposing organic material. The growth rate of atmospheric methane was more than 10% per decade before 1980, but by the 1990s it had dropped to nearly zero (Fig. 2, below)4. Bousquet and colleagues3 compute the global methane source distribution, especially its variability over recent decades. This is a rather controversial issue, as it is difficult to determine whether this variability should be attributed to fluctuations in the sources or in the sinks; the sink mechanisms are dominated by the good offices of the atmospheric hydroxyl radicals5.

The authors used a so-called inversion modelling technique, which starts from observed concentrations at Earth's surface and back-calculates using models of transport and loss processes to optimize source estimates. The measurements stem from a global network of monitoring stations, and include isotope data (in particular, the relative proportion of carbon-13) that provide an additional clue as to what methane came from where. Methane from biomass burning, fossil-fuel-related sources and bacterial processes have distinct isotopic signatures; methane emissions from wetlands, for example, are substantially depleted in carbon-13.

The approach is novel because the model computations optimized both methane emissions and methane loss through hydroxyl oxidation. The crux of the findings is that fluctuations of natural emissions, in particular by wetlands in the tropics, are a dominant factor in the variability of methane from year to year. These emissions are in turn sensitive to meteorological parameters: during dry periods, methane flux from wetlands is depressed.

Thus, during the most recent part of the analysis period — from 1999 onward — extended droughts have reduced natural methane emissions. This has concealed the fact that anthropogenic emissions have resumed their increase, an increase perhaps associated with the accelerating use of fossil fuels by booming Asian economies. Continued monitoring of atmospheric methane, and especially its relation to wetland inundation and drying, will be needed to substantiate this prediction.

Bousquet and colleagues' study3 is not incompatible with the recent suggestion that terrestrial vegetation is a strong methane source6. It sounds paradoxical that adding a large new source such as this, which contributes 30% of the global methane flux to the model, and decreasing the others proportionately can be done without fundamentally changing the inversion calculations. But the combination of the relatively strong meridional methane gradient (Fig. 2) and too few measurement stations in the tropics makes constraining the size of single-source categories such as forests and wetlands tricky.

Further confirmation of a large vegetation source comes from satellite measurements showing that methane concentrations are enhanced over the tropical rainforests7. It is remarkable not only that this large new methane source has just been discovered, but also that mechanisms for producing methane deviate from the known anaerobic formation by microbes. The role of oxygen in methanogenesis, including its application in renewable energy production, should receive much more attention in the coming years.

Atmospheric methane is a factor in the amplification of climate change, because the amount of methane released by wetlands and vegetation responds sensitively to temperature and moisture conditions. This establishes a positive-feedback mechanism that has contributed to rapid climate shifts during the last glacial cycle8. But Bousquet and colleagues' analysis3 also allows for a negative-feedback mechanism, put in place by atmospheric chemistry. In dry periods of reduced methane emissions, methane removal by hydroxyl radicals also decreases. The dryness aggravates vegetation fires, which release large amounts of carbon monoxide, and this pollutant gas also consumes hydroxyl. With less hydroxyl around, less methane is broken down, and the decrease in methane concentration is not as large as might be expected.

This phenomenon is not natural, however: most fires are ignited by humans. Furthermore, vast amounts of methane are deposited as hydrates in permafrost regions and in marine sediments. It is as yet unclear to what extent the melting of permafrost and increasing ocean temperature will affect these methane reservoirs, destabilize the hydrates and exacerbate greenhouse warming. These processes influence both atmospheric methane and hydroxyl, and are potentially important feedback mechanisms that require further research.

It will be both essential and difficult to control greenhouse-gas emissions and verify nationally reported inventories. Human-induced emissions scale with fossil-fuel consumption, and the global yearning for energy, especially in nations that do not recognize the Kyoto Protocol on climate change, gives rise to concern about climate change. The uncertainty range associated with climate projections1 implies that large changes will be as likely as modest ones. Such large and possibly disruptive climate changes ask for short-term solutions.

Unfortunately, the response times of most greenhouse gases in the atmosphere and their climatic effects are slow — decades to centuries. Measures to control methane emissions should be placed high on the agenda because they, in contrast, become effective within a few years. In a situation where climate change is accelerating, there is no time to lose: we need effective solutions, and we must act fast.

References

1. Ramaswamy, V. et al. in Climate Change 2001: The Third Assessment Report of the Intergovernmental Panel on Climate Change (eds Houghton, J. T. et al.) 349–416 (Cambridge Univ. Press, 2001).
2. Lelieveld, J. , Crutzen, P. J. & Dentener, F. J. Tellus 50B, 128–150 (1998).
3. Bousquet, P. et al. Nature 443, 439–443 (2006). | Article |
4. Dlugokencky, E. J. et al. Geophys. Res. Lett. 30, 1992 (2003). | Article | ChemPort |
5. Houweling, S. et al. J. Geophys. Res. 104, 26137–26160 (1999). | Article | ChemPort |
6. Keppler, F. et al. Nature 439, 187–191 (2006). | Article | PubMed | ISI | ChemPort |
7. Frankenberg, C. et al. Science 308, 1010–1014 (2005). | Article | PubMed | ISI | ChemPort |
8. Brook, E. J. et al. Glob. Biogeochem. Cycles 14, 559–572 (2000). | Article | ChemPort |


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