globalchange  > 气候变化事实与影响
DOI: doi:10.1038/nclimate2272
论文题名:
Occurrence and persistence of future atmospheric stagnation events
作者: Daniel E. Horton
刊名: Nature Climate Change
ISSN: 1758-1269X
EISSN: 1758-7389
出版年: 2014-06-22
卷: Volume:4, 页码:Pages:698;703 (2014)
语种: 英语
英文关键词: Environmental health ; Atmospheric dynamics
英文摘要:

Poor air quality causes an estimated 2.6–4.4 million premature deaths per year1, 2, 3. Hazardous conditions form when meteorological components allow the accumulation of pollutants in the near-surface atmosphere4, 5, 6, 7, 8. Global-warming-driven changes to atmospheric circulation and the hydrological cycle9, 10, 11, 12, 13 are expected to alter the meteorological components that control pollutant build-up and dispersal5, 6, 7, 8, 14, but the magnitude, direction, geographic footprint and public health impact of this alteration remain unclear7, 8. We used an air stagnation index and an ensemble of bias-corrected climate model simulations to quantify the response of stagnation occurrence and persistence to global warming. Our analysis projects increases in stagnation occurrence that cover 55% of the current global population, with areas of increase affecting ten times more people than areas of decrease. By the late twenty-first century, robust increases of up to 40 days per year are projected throughout the majority of the tropics and subtropics, as well as within isolated mid-latitude regions. Potential impacts over India, Mexico and the western US are particularly acute owing to the intersection of large populations and increases in the persistence of stagnation events, including those of extreme duration. These results indicate that anthropogenic climate change is likely to alter the level of pollutant management required to meet future air quality targets.

Strategies to improve air quality typically focus on the reduction of emitted pollutants such as particulate matter (PM) and the precursors of tropospheric ozone (O3). However, changing climate dynamics are also likely to play a role in determining future air quality, although the magnitude and direction of this role is uncertain7, 8. A recent assessment8 of meteorological influences found more frequent air stagnation to be the only meteorological condition that consistently resulted in higher near-surface concentrations of both PM and O3. Given strong negative correlation between cyclone frequency and observed stagnation and pollution events5, 6, investigations of the response of air stagnation to enhanced radiative forcing have primarily focused on changes in cyclone frequency over regional (particularly US) domains (for example, refs 5, 6, 15, 16). However, understanding of the response of future air stagnation events to elevated global warming has been found deficient as a result of inaccuracies in the simulation of meteorological variables relevant to air quality (‘model bias)14, 17, uncertainties in the spatial pattern of projected changes in those variables due to internal climate variability and/or model formulation8, 13, 14, 15, 18, and lack of investigation of changes in stagnation event duration14, 18.

We examine air stagnation directly by applying a modified version of the Air Stagnation Index (ASI) to the CMIP5 global climate model ensemble. The ASI follows the ingredients-based approach of weather forecasting, wherein fundamental components of a meteorological phenomenon are identified and analysed using numerical models and/or observational datasets19. The ASI uses thresholds of daily precipitation and upper- and lower-atmospheric winds to determine when the atmosphere is likely to lack contaminant scavenging, horizontal dispersion and vertical escape capabilities4 (Methods). The daily co-occurrences of these meteorological conditions show a robust correlation with observed PM and O3 pollution days5, 6, underpin operational air quality forecasts and, when persistent, are associated with extreme air pollution episodes8, 18. We use historical and high-emission scenario (RCP8.5) CMIP5 simulations to create a multi-model ensemble projection of air stagnation occurrence (Supplementary Discussion). Our analysis examines changes in stagnation event duration, corrects model biases with six unique observational and reanalysis dataset combinations, and applies objective statistical analyses in conjunction with multi-model agreement criteria to quantify robustness of air stagnation change. Grid cell changes are considered robust if 66% of bias-corrected members pass a non-parametric permutation test at the 95% confidence level20 and 66% agree on the change direction (Methods).

Stagnant conditions are most frequent in the current climate over the tropics and sub-tropics, with areas of the western US, north Africa, central Asia and Siberian Russia exhibiting relatively high occurrence in the mid-latitudes (Fig. 1a). Regions that experience frequent stagnation but infrequent hazardous air quality, such as Siberian Russia21, confirm that the ASI measures potential impact: in the absence of human inhabitants or natural and/or anthropogenic pollutants, even ideal pollutant-accumulating meteorological conditions do not pose an air quality risk.

Figure 1: Characteristic changes in air stagnation and human exposure.
Characteristic changes in air stagnation and human exposure.

a, Mean annual baseline (1986–2005) stagnation days from the bias-corrected historical ensemble. bd, Change in mean annual stagnation days from baseline to future periods (2016–2035 (b), 2046–2065 (c) and 2080–2099 (d)). White indicates <66% of ensemble members demonstrate significant change. Grey indicates >66% of members demonstrate significant change, but <66% of members agree on change direction. Blue (decreasing) or red (increasing) shades represent ensemble-mean changes, and indicate >66% of members demonstrate significant change and >66% agree on change direction. Bar plots show logarithmic values of the ASEI, a metric that captures the potential human exposure to changes in stagnant conditions (Supplementary Table 1). Vertical axes range from 106 to 1011.5 people⋅days/year; note that above populated western US grid cells, no robust air stagnation decreases are projected in future periods (ASEI = 0).

We apply a modified version of the National Climatic Data Center ASI. A grid cell day is considered stagnant when daily-mean near-surface (10-m) wind speeds are <3.2 m s−1, daily-mean mid-tropospheric (500 mb) wind speeds are <13 m s−1, and daily-mean precipitation accumulation is <1 mm (ref. 14). The ASI does not explicitly incorporate all meteorological factors known to influence air quality: including relative humidity, temperature, turbulent mixing and orographic barriers. Consequently, ASI component threshold sensitivities may vary locally/regionally and factors in addition to, or exclusive of, air stagnation may play a substantial role in determining local/regional air quality14.

Global-warming-driven stagnation changes are explored using an ensemble of realizations from 15 modelling groups that provide requisite daily three-dimensional atmospheric fields from both historical and RCP8.5 experiments of the Climate Model Intercomparison Project Phase 5 (Supplementary Table 2). Because the ASI is reliant on absolute thresholds, systematic errors in CMIP5-simulated stagnation-relevant variables are bias corrected using an empirical quantile mapping technique14, 28, 30. To account for observational uncertainties, we use a suite of six unique reanalysis and observational dataset combinations (Supplementary Discussion). For wind correction, we use monthly NCEP-DOE R2 and ECMWF ERA-Interim reanalysis 500 mb and 10-m components. For precipitation, we use monthly University of Delaware v3.02 (UDel), Global Planetary Climatology Project v2.2 (GPCP) and Climate Prediction Center Merged Analysis of Precipitation (CMAP) data. Bias correction of the 15 CMIP5 models using six distinct combinations of observational standards forms what we refer to as the bias-corrected ensemble (90 members). For models with multiple realizations, we average all bias-corrected realizations of each model before inclusion in the ensemble mean, such that each bias-corrected version of the model receives one vote (Supplementary Discussion). All model, reanalysis and observational data are interpolated to 0.5° × 0.5°. To determine stagnation differences, the mean annual occurrence in three future RCP8.5 periods (2016–2035, 2046–2065 and 2080–2099) is compared to the baseline historical period (1986–2005). Analysis of seasonal zonal wind speeds, meridional mass transport and mid-tropospheric vertical velocity in Fig. 3 and Supplementary Figs 4–6 use monthly-scale CMIP5 data and are not bias corrected.

Bias in native CMIP5 fields varies by component, magnitude and location. Of the three ASI components, the magnitude of dry day (Supplementary Fig. 8a, e, i) and near-surface wind (Supplementary Fig. 8b, f, j) condition biases are greatest, whereas mid-tropospheric (500 mb) wind conditions show both the least bias and greatest improvement from correction (Supplementary Fig. 8c, g, k). Baseline stagnation biases are greatest over high northern latitudes, northern Australia and Amazonia, although our correction methodology substantially improves the mean occurrence (Supplementary Fig. 8d, h, l).

Extraction of a robust climate change signal from the bias-corrected ensemble follows a two-step process. First, statistical significance of the historic-to-future change in mean stagnation occurrence is assessed at each grid cell for each model using a non-parametric permutation test20. For models with multiple realizations, statistical significance is assessed by comparing the combined population of historic realizations to that of the future. The permutation test makes no assumptions with regard to the datas underlying distribution, thereby yielding greater confidence in the resulting conclusions. Following IPCC uncertainty guidance13, change is considered statistically robust if at least 66% of ensemble members demonstrate change at or above the 95% confidence level. Second, for those grid cells at which the simulated change is statistically robust, we assess ensemble member agreement in the direction of the simulated change.

If fewer than 66% of bias-corrected ensemble members exhibit change at or above the 95% confidence level, we plot the grid cell as white. If at least 66% of members exhibit change at or above the 95% confidence level, but fewer than 66% agree on the direction of the statistically significant changes, we plot the grid cell as grey. If at least 66% of members exhibit change at or above the 95% confidence level, and at least 66% agree on the direction of statistically significant changes, we consider the ASI-climate change signal robust, and plot ensemble-mean change in colour (Fig. 1). For comparison, late-century ensemble-mean air stagnation change without robustness screening is included as Supplementary Fig. 1. Stagnation changes presented in Fig. 1 and Supplementary Fig. 1 are largely in agreement with the CMIP3-based results of ref. 14. Differences are attributable to added robustness screening and changes in ensemble composition, model structure, emission scenarios and reanalysis/observational datasets.

Use of multi-model ensembles to capture model design uncertainties and create probabilistic projections of future climate outcomes has become standard practice, owing in part to the organizing efforts of CMIP. More recently, the air quality research community has adopted this protocol through independent efforts—for example, ref. 26—and under guidance from the Atmospheric Chemistry and Climate Model Intercomparison Project17. In our analysis, bias correction, consideration of the uncertainties inherent in observational standards, application of statistical rigour and establishment of multi-model agreement thresholds all provide further confidence in the multi-model probabilistic projection of the likelihood of future stagnation changes.

  1. Anenberg, S. C., Horowitz, L. W., Tong, D. Q. & West, J. J. An estimate of the global burden of anthropogenic ozone and fine particulate matter on premature human mortality using atmospheric modeling. Environ. Health Perspect. 118, 11891195 (2010).
  2. Lim, S. S. et al. A comparative risk assessment of burden of disease and injury attributable to 67 risk factors and risk factor clusters in 21 regions, 1990–2010: A systematic analysis for the Global Burden of Disease Study 2010. Lancet 380, 22242260 (2012).
  3. Silva, R. A. et al. Global premature mortality due to anthropogenic outdoor air pollution and the contribution to past climate change. Environ. Res. Lett. 8, 034005 (2013).
    URL: http://www.nature.com/nclimate/journal/v4/n8/full/nclimate2272.html
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    资源类型: 期刊论文
    标识符: http://119.78.100.158/handle/2HF3EXSE/5092
    Appears in Collections:气候变化事实与影响
    科学计划与规划
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    Daniel E. Horton. Occurrence and persistence of future atmospheric stagnation events[J]. Nature Climate Change,2014-06-22,Volume:4:Pages:698;703 (2014).
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