globalchange  > 气候变化事实与影响
DOI: doi:10.1038/nclimate2446
论文题名:
Permafrost collapse after shrub removal shifts tundra ecosystem to a methane source
作者: Ake L. Nauta
刊名: Nature Climate Change
ISSN: 1758-1106X
EISSN: 1758-7226
出版年: 2014-11-24
卷: Volume:5, 页码:Pages:67;70 (2015)
语种: 英语
英文关键词: Ecosystem ecology ; Cryospheric science ; Climate-change ecology
英文摘要:

Arctic tundra ecosystems are warming almost twice as fast as the global average1. Permafrost thaw and the resulting release of greenhouse gases from decomposing soil organic carbon have the potential to accelerate climate warming2, 3. In recent decades, Arctic tundra ecosystems have changed rapidly4, including expansion of woody vegetation5, 6, in response to changing climate conditions. How such vegetation changes contribute to stabilization or destabilization of the permafrost is unknown. Here we present six years of field observations in a shrub removal experiment at a Siberian tundra site. Removing the shrub part of the vegetation initiated thawing of ice-rich permafrost, resulting in collapse of the originally elevated shrub patches into waterlogged depressions within five years. This thaw pond development shifted the plots from a methane sink into a methane source. The results of our field experiment demonstrate the importance of the vegetation cover for protection of the massive carbon reservoirs stored in the permafrost and illustrate the strong vulnerability of these tundra ecosystems to perturbations. If permafrost thawing can more frequently trigger such local permafrost collapse, methane-emitting wet depressions could become more abundant in the lowland tundra landscape, at the cost of permafrost-stabilizing low shrub vegetation.

Arctic tundra ecosystems are characterized by permanently frozen ground (permafrost) covered by a soil layer, named the active layer, which thaws and refreezes every year. Permafrost thaw and the resulting release of carbon dioxide and methane by microbial decomposition of previously frozen organic carbon is considered one of the most significant potential feedbacks from terrestrial ecosystems to the climate system1, 2. Warming and thawing of permafrost have been observed in many locations in recent decades7. Although thawing depth is controlled to a large extent by the regional climate, non-climatic factors, such as changes in vegetation and hydrology, can strongly modify the response of permafrost to global warming8, 9.

For a better understanding of the response of permafrost to climate change, it is important to determine how observed vegetation changes, for example, deciduous shrub expansion5, 6, contribute to stabilization or destabilization of the permafrost. We set up a shrub removal experiment at a Northeast-Siberian tundra site in 200710. The study site represents poorly drained lowland tundra underlain by thick continuous permafrost in the Low Arctic climate zone. We clipped off all aboveground biomass of the dominant deciduous shrub species Betula nana (dwarf birch) in five 10-m-diameter plots, leaving a few other shrubs, graminoids (grasses and sedges), mosses and lichens. The five control plots consisted of undisturbed B. nana-dominated vegetation. B. nana is a common tundra shrub species and is expected to benefit from climate warming11. The control and B. nana-removal plots were very similar at the start of the experiment (Supplementary Table 1). Here, we report on our field observations over six years during which the removal plots have undergone major changes.

Shrub removal increased the thawing depth (active layer thickness) within one year (Fig. 1). This was consistent with larger ground heat fluxes in the removal plots10. In the following years the difference in active layer thickness between control and removal plots increased further, from a difference of 5 cm on average in 2008 to 15 cm in 2012 (Fig. 1; 2012: control = 25.8 ± 0.8 cm (mean ± s.e.m., n = 5 plots), removal = 40.8 ± 1.8 cm; F1,8 = 30.1, P = 0.001). In the control plots, active layer thickness was largest in 2011 (Fig. 1), which experienced an exceptionally wet and warm summer (Supplementary Table 2).

Figure 1: Late-July active layer thickness in control and B. nana removal plots from 2007 to 2012.
Late-July active layer thickness in control and B. nana removal plots from 2007 to 2012.

Data are mean values ± s.e.m., n = 5 plots. xx indicate years of B. nana removal. , and indicate significant differences between the two treatments (p < 0.05, p < 0.01, p < 0.001, respectively).

Study site.

The study was conducted at the Chokurdakh Scientific Tundra Station (70° 49′ N, 147° 29′ E, 10 m above sea level) located in the Kytalyk (Siberian crane) Wildlife Reserve in the Indigirka lowlands in north-eastern Yakutia, Russian Federation. Chokurdakh mean annual air temperature is −13.4 °C (1981–2010), with −34.0 °C mean January temperature and 10.3 °C mean July temperature. Mean annual precipitation is 196 mm (1981–2010), of which 76 mm (39%) falls in the summer months (June to August). The study area is underlain by thick continuous permafrost with a high ice content (>20% by volume)20, which reaches more than 300 m depth. The field experiment was set up in a drained lake basin, which consists mostly of elevated shrub patches dominated by Betula nana L. (dwarf birch) shrubs surrounded by a diffuse drainage network of wet depressions dominated by the graminoid species Eriophorum angustifolium Honck. See Supplementary Methods for a more extensive site description.

Experimental design.

We established ten circular plots of 10 m diameter in the elevated B. nana patches within the drained thaw lake basin in summer 200710. Plots were selected pairwise, on the basis of proximity and similarity in vegetation composition and shrub density. Subsequently, the two treatments were randomly assigned to the plots within each pair: a control treatment (no shrub removal) and a removal treatment. Aboveground biomass of B. nana was removed by clipping stems at the moss surface to minimize disturbance. To maintain the B. nana removal treatment, regrowth of B. nana was removed in summer 2010. It was not necessary to remove the regrowth every year. One year after removal there was very limited regrowth, but by the third year regrowth was substantial in all removal plots and therefore removed. Regrowth could occur as the stems were clipped off at the moss surface, so new shoots could develop from remaining belowground resources in coarse roots. Only permanently wet conditions seemed to prevent recolonization.

Measurements.

At the start of the experiment before manipulation, plant species abundance measurements and aboveground biomass harvests have been made for all ten plots. In addition, soil thawing depth, soil moisture and soil temperatures were measured during experiment establishment in mid-July 2007. Active layer thickness, using a bluntly tipped metal probe, and plant species abundances, using the point-intercept method, have been measured every summer since the start of the experiment. Relative surface elevation and water table depth were measured in summer 2011 and 2012. Methane fluxes were measured in summer 2012 using a closed chamber of 29 cm diameter connected to an INNOVA 1312 photo-acoustic field gas monitor. See Supplementary Methods for details of the measurements.

Data analysis.

The effect of the B. nana removal treatment on active layer thickness, relative surface elevation, water level, snow depth and vegetation cover was assessed using a repeated measures analysis of variance (RM-ANOVA) with treatment (control, removal) as between-subject factor and year as within-subject factor. Subsequently, differences between control and removal treatment in specific years were analysed using one-way ANOVA. As plot pair generally had no effect on the measured variables, it was not included in the ANOVA. All data were tested for a normal distribution and equality of variance. These statistical analyses were performed using SPSS 19. See Supplementary Methods for methane flux calculations and data analysis.

  1. IPCC Climate Change 2013: The Physical Science Basis (eds Stocker, T. F. et al.) (Cambridge Univ. Press, 2013).
  2. Tarnocai, C. et al. Soil organic carbon pools in the northern circumpolar permafrost region. Glob. Biogeochem. Cycles 23, GB2023 (2009).
  3. Schuur, E. A. G. et al. The effect of permafrost thaw on old carbon release and net carbon exchange from tundra. Nature 459, 556559 (2009).
  4. Hinzman, L. D. et al. Trajectory of the Arctic as an integrated system. Ecol. Appl. 23, 18371868 (2013).
  5. Tape, K., Sturm, M. & Racine, C. The evidence for shrub expansion in Northern Alaska and the Pan-Arctic. Glob. Change Biol. 12, 686702 (2006).
  6. Elmendorf, S. C. et al. Plot-scale evidence of tundra vegetation change and links to recent summer warming. Nature Clim. Change 2, 453457 (2012).
  7. Romanovsky, V. E., Smith, S. L. & Christiansen, H. H. Permafrost thermal state in the polar Northern Hemisphere during the International Polar Year 2007–2009: A Synthesis. Permaf. Periglac. Process. 21, 106116 (2010).
  8. Walker, D. A. et al. Vegetation-soil-thaw-depth relationships along a Low-Arctic bioclimate gradient, Alaska: Synthesis of information from the ATLAS studies. Permaf. Periglac. Process. 14, 103123 (2003).
  9. Jorgenson, M. T. et al. Resilience and vulnerability of permafrost to climate change. Can. J. For. Res. 40, 12191236 (2010).
  10. Blok, D. et al. Shrub expansion may reduce summer permafrost thaw in Siberian tundra. Glob. Change Biol. 16, 12961305 (2010).
  11. Bret-Harte, M. S. et al. Developmental plasticity allows Betula nana to dominate tundra subjected to an altered environment. Ecology 82, 1832 (2001).
  12. Van Huissteden, J., Maximov, T. C. & Dolman, A. J. High methane flux from an Arctic floodplain (Indigirka lowlands, eastern Siberia). J. Geophys. Res. 110, G02002 (2005).
  13. Elberling, B. et al. Linking soil O2, CO2, and CH4 concentrations in a wetland soil: Implications for CO2 and CH4 fluxes. Environ. Sci. Technol. 45, 33933399 (2011).
URL: http://www.nature.com/nclimate/journal/v5/n1/full/nclimate2446.html
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资源类型: 期刊论文
标识符: http://119.78.100.158/handle/2HF3EXSE/4934
Appears in Collections:气候变化事实与影响
科学计划与规划
气候变化与战略

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Ake L. Nauta. Permafrost collapse after shrub removal shifts tundra ecosystem to a methane source[J]. Nature Climate Change,2014-11-24,Volume:5:Pages:67;70 (2015).
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