globalchange  > 气候变化事实与影响
DOI: doi:10.1038/nclimate2313
论文题名:
Recent trends in African fires driven by cropland expansion and El Niño to La Niña transition
作者: Niels Andela
刊名: Nature Climate Change
ISSN: 1758-1206X
EISSN: 1758-7326
出版年: 2014-08-10
卷: Volume:4, 页码:Pages:791;795 (2014)
语种: 英语
英文关键词: Fire ecology ; Developing world ; Atmospheric science
英文摘要:

Landscape fires are key in African ecosystems1, 2, 3 and the continent is responsible for 70% of global burned area and 50% of fire-related carbon emissions4, 5. Fires are mostly human ignited, but precipitation patterns govern when and where fires can occur6. The relative role of humans and precipitation in driving the spatio-temporal variability in burned area is not fully disentangled but is required to predict future burned area7, 8. Over 2001–2012, observations indicate strong but opposing trends in the African hemispheres4. Here we use satellite data and statistical modelling and show that changes in precipitation, driven by the El Niño/Southern Oscillation (ENSO), which changed from El Niño to La Niña dominance over our study period, contributed substantially (51%) to the upward trend over southern Africa. This also contributed to the downward trend over northern Africa (24%), but here rapid demographic and socio-economic changes were almost as important (20%), mainly due to conversion of savannah into cropland, muting burned area. Given the economic perspective of Africa and the oscillative nature of ENSO, future African savannah burned area will probably decline. Combined with increasing global forest fire activity due to climate change9, 10, 11, our results indicate a potential shift in global pyrogeography from being savannah dominated to being forest dominated.

Landscape fires form an integral part of the African savannah ecosystem1. Savannas, which evolved around 8 million years ago, mostly consist of grasslands interspersed with fire-tolerant trees12. In the (sub)tropics, fire occurrence in xeric savannas is limited by a lack of fuel as a consequence of reduced productivity, whereas in more mesic regions the main limitation is the short dry seasons13. In Africa, dry-season length gradually increases when moving away from the Equator14. The highest annual burned area has been observed in savannas with intermediate levels of precipitation and productivity, and distinct wet and dry seasons13 (Fig. 1a). Most of the fire emissions originate from these savannah ecosystems on the continent5. Although not net contributors, African savannah fires are a source of inter-annual variability of atmospheric CO2 concentrations and in addition emit substantial amounts of other greenhouse gases including CH4 and N2O (ref. 5).

Figure 1: Annual burned area: mean, recent trends and drivers, for areas with precipitation rates between 400 and 1,500 mm yr−1 based on 2001–2012 data.
Annual burned area: mean, recent trends and drivers, for areas with precipitation rates between 400 and 1,500 mm yr-1 based on 2001-2012 data.

a, Observed mean annual burned area. b, Observed trend in annual burned area. c, Observed trend in cropland extent. d, Observed trend in precipitation. e, Modelled trend in burned area driven by trends in cropland extent. f, Modelled trend in annual burned area driven by precipitation.

Monthly burned area (BA) data22 (MCD64A1; 08-2000 onwards) and annual land cover information24 (MCD12C1.51; 2001 onwards) were scaled to the 0.25° resolution of the monthly precipitation data23 (TRMM 3B43 version 7; 1998 onwards). Our study domain included all African grid cells with annual precipitation rates between 400 and 1,500 mm yr−1 precipitation to focus on savannah regions. We developed a statistical model that aimed to explain variability in annual BA using antecedent precipitation (API) and changes in cropland extent (dCROP) for each grid cell. As input for the statistical model, we removed the mean seasonal cycle from the BA and precipitation data (Supplementary Information). We calculated the annual BA anomaly for each grid cell not on the basis of calendar years but as the sum of the BA anomaly from 5 months before the month of peak burning until 6 months after, to circumvent issues in northern Africa where the peak fire season is in December and January. We used data from August 2000 until June 2013, resulting in 12 annual cycles for all grid cells.

Building on earlier work25, a multiple linear regression model was used to explain the BA anomaly for each grid cell (x, y) and year (t):

where β, b0 and b1 are optimally fitted parameters to minimize the sum of ordinary least squares of the errors (ε). Positive dCROP values indicate conversion of natural vegetation into cropland. The impact of dCROP on annual BA was found to vary mostly with actual cropland extent and mean annual precipitation. To prevent overfitting we clustered grid cells into cropland extent–mean annual precipitation bins, and determined the slope βi for each bin (i) separately (Fig. 2b). The BA–precipitation response was more variable and the slope b0x, y was therefore optimized for each grid cell individually. We included an intercept that varied between grid cells (b1) as done in ref. 25, representing the initial annual BA. Both explanatory variables are discussed below and in more detail in the Supplementary Information.

Antecedent precipitation is often thought to be the single most important driver of inter-annual variability of BA in savannas13, 25. For each grid cell, the effect of precipitation on annual BA was explored by calculating Pearson’s r between antecedent precipitation and annual BA using averaging periods from 1 up to 24 months. In general, for a given grid cell short averaging periods will be negatively correlated with BA as precipitation shortly before the burning season increases fuel moisture; whereas longer averaging periods will be positively correlated with BA through the process of fuel build-up25. It is therefore possible that precipitation has both a positive and a negative effect on annual burned area for each grid cell. However, we found that both effects are rarely important at the same time (3% of the grid cells when p < 0.1; see Supplementary Information). Therefore, we include only one precipitation–BA response variable per grid cell in the model, based on the strongest absolute response (positive or negative). API may therefore be estimated for each grid cell (x, y) and year (t) using:

where T is the averaging period (ranging from 1 to 24 months) for API that led to the highest absolute correlation (Pearson’s r) between the running mean of the monthly precipitation anomaly p and the annual BA anomaly and m is the month of maximum burning (Supplementary Fig. 1 and Section 2). As the effect of API may be positive or negative and is based on different T for each grid cell, we decided to optimally fit b0 for each grid cell. Although we used a statistical model and did not investigate underlying processes in more detail, confidence in our model may be derived from the strong correlation between API and the annual BA anomaly and from the clear spatial patterns in optimal T (Supplementary Fig. 1).

Including dCROP in the model is a logical step because the distribution of croplands has a considerable impact on current BA distribution in northern Africa (Fig. 2a), and because strong trends were observed over our relatively short study period. Owing to the limited confidence in inter-annual variation of the land cover product, we used the linear trend derived from the whole 2001 to 2012 study period.

As explained above, the short study period (2001–2012) constrains the number and ways that explanatory variables can be included in the multiple linear regression model, which is further discussed in the Supplementary Information. Trend maps (Fig. 1) are shown for all significance levels, because in general the less significant trends were part of spatial systems of significant and larger trends. Outliers may have affected some of the trends computed, especially trends observed in regions of high inter-annual climate variability, but this effect is thought to be marginal (for further details see Supplementary Information).

To investigate the role of ENSO as a driver of inter-annual variation in BA, we calculated for each pixel Pearson’s r between the annual BA anomaly (as defined above) and the mean MEI index over the same period (from 5 month before the peak burning until 6 months after; Fig. 3). We then computed mean inter-annual variation separately for positively and negatively correlated areas of northern and southern Africa (Supplementary Fig. 3).

  1. Scholes, R. J. & Archer, S. R. Tree-grass interactions in savannas. Annu. Rev. Ecol. Syst. 28, 517544 (1997).
  2. Bond, W. J., Woodward, F. I. & Midgley, G. F. The global distribution of ecosystems in a world without fire. New Phytol. 165, 525537 (2005).
  3. Bowman, D. M. J. S. et al. Fire in the Earth system. Science 324, 481484 (2009).
  4. Giglio, L., Randerson, J. T. & van der Werf, G. R. Analysis of daily, monthly, and annual burned area using the fourth-generation global fire emissions database (GFED4). J. Geophys. Res. 118, 317328 (2013).
  5. Van der Werf, G. R. et al. Global fire emissions and the contribution of deforestation, savanna, forest, agricultural, and peat fires (1997–2009). Atmos. Chem. Phys. 10, 1170711735 (2010).
  6. Archibald, S., Roy, D. P., van Wilgen, B. W. & Scholes, R. J. What limits fire? An examination of drivers of burnt area in Southern Africa. Glob. Change Biol. 15, 613630 (2009).
  7. Pechony, O. & Shindell, D. T. Driving forces of global wildfires over the past millennium and the forthcoming century. Proc. Natl Acad. Sci. USA 107, 1916719170 (2010).
  8. Kloster, S., Mahowald, N. M., Randerson, J. T. & Lawrence, P. J. The impacts of climate, land use, and demography on fires during the 21st century simulated by CLM-CN. Biogeosciences 9, 509525 (2012). URL:
http://www.nature.com/nclimate/journal/v4/n9/full/nclimate2313.html
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资源类型: 期刊论文
标识符: http://119.78.100.158/handle/2HF3EXSE/5031
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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Niels Andela. Recent trends in African fires driven by cropland expansion and El Niño to La Niña transition[J]. Nature Climate Change,2014-08-10,Volume:4:Pages:791;795 (2014).
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