Abstract
How drought may change in the future are of great concern as global warming continues. In Part I of this study, we examine the uncertainties in estimating recent drought changes. Substantial uncertainties arise in the calculated Palmer Drought Severity Index (PDSI) with Penman-Monteith potential evapotranspiraiton (PDSI_pm) due to different choices of forcing data (especially for precipitation, solar radiation and wind speed) and the calibration period. After detailed analyses, we recommend using the Global Precipitation Climatology Centre (GPCC) or the Global Precipitation Climatology (GPCP) datasets over other existing land precipitation products due to poor data coverage in the other datasets since the 1990s. We also recommend not to include the years after 1980 in the PDSI calibration period to avoid including the anthropogenic climate change as part of the natural variability used for calibration. Consistent with reported declines in pan evaporation, our calculated potential evapotranspiration (PET) shows negative or small trends since 1950 over the United States, China, and other regions, and no global PET trends from 1950 to 1990. Updated precipitation and streamflow data and the self-calibrated PDSI_pm all show consistent drying during 1950–2012 over most Africa, East and South Asia, southern Europe, eastern Australia, and many parts of the Americas. While these regional drying trends resulted primarily from precipitation changes related to multi-decadal oscillations in Pacific sea surface temperatures, rapid surface warming and associated increases in surface vapor pressure deficit since the 1980s have become an increasingly important cause of widespread drying over land.
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1 Introduction
Drought is among the costliest natural disasters due to its long duration and lasting effects on agriculture and other sectors, and its low predictability among all extreme weather and climate events (Wilhite 2000; Mishra and Singh 2010). During recent years, many regions have experienced frequent severe droughts, such as the 2005 and 2010 Amazon droughts (Marengo et al. 2008; Lewis et al. 2011), the 2009–2011 winter-spring drought in southern China (Barriopedro et al. 2012; Sun and Yang 2012), the Southwest North American drought since 2010 (Peterson et al. 2012; Hoerling et al. 2012), the Horn of Africa and Sahel droughts in 2011 (Lyon and DeWitt 2012), the recent decade-long drought in Australia (McGrath et al. 2012), and the on-going record-breaking drought in California since 2012 (Williams et al. 2015). Although natural variability is often the primary cause for individual drought events, the increased frequency of severe droughts during recent years over the Americas and other regions is consistent with model-projected increases in drought frequency and severity over these regions under increasing greenhouse gases (GHGs) (Wang 2005; Burke et al. 2006; Seager et al. 2007; Sheffield and Wood 2008; Dai 2011a, 2013a; Wehner et al. 2011; Taylor et al. 2013; Feng and Fu 2013; Cook et al. 2014; Prudhomme et al. 2014; Scheff and Frierson 2015; Zhao and Dai 2015). For future drought increases, increases in atmospheric demand for moisture associated with rising temperatures (Feng and Fu 2013; Scheff and Frierson 2014) are the primary cause, with decreasing precipitation enhancing the drying over subtropical land areas (Zhao and Dai 2015). For historical drought increases since the 1970s (Dai 2011b, 2013a), decreasing precipitation is the primary cause over most areas, although increased atmospheric demand associated with rising temperatures since the 1980s is also a significant contributor. As analyzed below (section 5), these historical changes are not inconsistent with the reported declines in pan evaporation over the contiguous United States, China, India, and other regions (McVicar et al. 2012).
While all the studies mentioned above show considerable future drying in the twenty-first century, the estimated historical drying extent and magnitude since 1950 differ significantly among some studies. In particular, Sheffield et al. (2012) found only small drying over global land from 1950 to 2008 solely based on their calculated Palmer Drought Severity Index (PDSI; Palmer 1965) with the Penman-Monteith potential evapotranspiration (PET) (PDSI_pm). This is in contrast to the conclusions made by Dai et al. (2004), Trenberth et al. (2007), Dai (2011a, 2011b), and Dai (2013a), who analyzed the changes in various forms of the PDSI as well as historical precipitation and streamflow records and concluded that the warming since the 1980s has enhanced the drying over many land areas. Van der Schrier et al. (2013) concluded that different calibration periods used in calculating the PDSI can explain a portion of the differences in the estimated PDSI trends. Trenberth et al. (2014) showed that the popular Climatic Research Unit (CRU) precipitation dataset (TS 3.10.01 or older versions) used by Sheffield et al. (2012), van der Schrier et al. (2013), IPCC (2007, 2013), and many other studies (but not by Dai et al.), has a wet bias compared with other products since the 1990s due to a sharp decline in its number of rain-gauges for the recent decades. Trenberth et al. (2014) suggested that this could be a major factor for the different PDSI trends found by Dai et al. and Sheffield et al.
In this study, we further examine the uncertainties in estimating historical drying trends and the key factors that may have contributed to the different conclusions made by Sheffield et al. (2012) and by Dai et al. (2004) Dai (2011a, 2011b), and Dai (2013a). We also provide an analysis of updated precipitation and streamflow data and the calculated self-calibrated PDSI_pm (sc_PDSI_pm) to assess historical aridity trends from 1950 to 2014. Furthermore, we analyze our calculated PET to assess whether our PET and thus the sc_PDSI_pm are consistent with the reported declines in pan evaporation (McVicar et al. 2012), a proxy of PET. Here, we focus on the uncertainties in the sc_PDSI_pm associated with issues in precipitation datasets, and did not explore the impact of the uncertainties in the other forcing data mainly because there do not exist reliable data to make such an assessment. In part II of this study (Zhao and Dai 2016), the historical drought changes are compared with climate model-simulated response to historical CO2 and other external forcing.
In the following, we describe the data and method in section 2. Section 3 discusses the main sources of uncertainty in estimating historical drought changes based on the sc_PDSI_pm. An update analysis of drought changes since 1950 is presented in section 4. A summary is given in section 5.
2 Data and method
The PDSI (Palmer 1965) and its variants are one of the popular drought indices used to quantify variations and long-term changes in drought and aridity on global (Dai et al. 1998, 2004; Dai 2011a, 2011b, 2013a; van der Schrier et al. 2011, 2013; Sheffield et al. 2012) and regional scales (Zhai et al. 2010; van der Schrier et al. 2007; Wei and Wang 2013). In particular, the self-calibrated PDSI (Wells et al. 2004) with Penman-Monteith potential evapotranspiration (sc_PDSI_pm) (Dai 2011b; van der Schrier et al. 2011) overcomes some main caveats in the original PDSI, and thus is considered as a more reliable index for quantifying long-term drought changes, primarily for agricultural drought in response to global warming (Dai 2011b; Zhao and Dai 2015).
However, the calculated sc_PDSI_pm (or PDSI_pm) may contain large uncertainties due to a lack of reliable forcing data for historical precipitation, solar radiation and other near-surface meteorological fields that are needed for computing the sc_PDSI_pm (Dai 2011b). To address this problem, we first examine some key issues in calculating the sc_PDSI_pm. This includes evaluation of the existing precipitation products and a proper choice of the calibration period for computing the sc_PDSI_pm. We then compare the change patterns in the sc_PDSI_pm with observed changes in precipitation (a measure of meteorological drought) and streamflow or runoff (a measure of hydrologic drought) to assess whether the changes in these different drought measures are qualitatively consistent with each other in terms of the spatial patterns of change. Consistent change patterns among these different but physically-related drought measures can provide a more reliable assessment of historical drought trends than using one measure alone.
We updated monthly sc_PDSI_pm data to December 2014 using the method and forcing data described in Dai (2011b), with modifications described in Supplementary Materials (SM).
Drought often leads to warmer temperatures and lower relative humidity, which in turn raise PET. Higher PET enhances drought, thereby creating a positive feedback.
3 Uncertainties in historical forcing data
As mentioned in Introduction, Sheffield et al. (2012) found little drying from 1950 to 2008 over global land based on their calculated PDSI_pm using their meteorological forcing data, which were largely based on the NCEP/NCAR reanalysis data with the monthly mean T and P adjusted to match those of the CRU TS3.10. The CRU TS3.10 P contained a bug and it was soon replaced by CRU TS3.10.01 (see http://www.cru.uea.ac.uk/cru/data/hrg/#legacy). Sheffield et al. (2012) realized that there exist large uncertainties in datasets for precipitation and net surface radiation, and used four precipitation datasets (CRU TS3.10, DaiP, GPCC V4, and WilP) and two radiation estimates to generate an ensemble mean PDSI_pm and its uncertainty range. In doing so, they implicitly assumed that all the available datasets were equally likely to be true. As shown below, there is strong evidence to suggest otherwise, that is, some of the P data sets are likely to be more reliable than others and thus they should be used.
In contrast, Dai (2011b) used the DaiP, CRU T data, and observed cloudiness-based estimates of surface radiation, plus surface wind, humidity and air pressure data from the same NCEP/NCAR reanalysis. Another difference is that Dai (2011b) used a 30-year (1950–1979) period while Sheffield et al. (2012) used the whole analysis period (1950–2008) as the calibration period in calculating the PDSI. One advantage of using the whole analysis period as the calibration period, as noticed by van der Schrier et al. (2013), is that it includes all the variations and changes in the data and thus will ensure the PDSI values over the whole analysis period within a range (approx. -6 to +6) as envisioned originally by Palmer (1965), and thus Palmer’s classification ranges can be used to define various types of drought. However, because we are dealing with a changing climate with a focus on long-term changes rather than classifying drought types, we should not choose a calibration period solely based on this consideration.
The period since the 1980s has a clear warming trend that has been attributed mainly to anthropogenic forcing, rather than natural climate variations (IPCC 2007, 2013). Because of this, it is inappropriate to include this trend in the variance used to calibrate the PDSI values. Doing so would effectively reduce the PDSI value range and its trend magnitude. One extreme example would be to use the whole analysis period from 1950 to 2099 as the calibration period in computing the PDSI for model-simulated historical and future climates. This would effectively reduce the future PDSI change magnitude (with little effect on its temporal evolution) and be equivalent to assume the 1950–2099 mean as the norm that we should calibrate with. Obviously, that is incorrect.
As shown by van der Schrier et al. (2013), using different calibration periods may account for some of the PDSI trend differences between Dai (2011b) and Sheffield et al. (2012), while the discontinuity error around 2004/2005 in Dai (2011b)’s forcing data is unlikely to be a major factor. To further quantify the effects of these issues, we compare the global-mean time series of the sc_PDSI_pm from Dai (2011b) and that without the discontinuity error (Fig. 1a), and the sc_PDSI_pm calculated separately with 1950–1979 (as in Dai 2011b) and 1950–2008 (as in Sheffield et al. 2012) as the calibration period for the different precipitation cases (Fig. 1b). It is clear that the difference caused by the discontinuity error around 2005, which is similar to that shown in Sheffield et al. (2012), changes the overall trend from 1950 to 2008 only slightly from about −0.8 to −0.9 change per century, with both being statistically significant. Thus, while this error may have slightly enhanced (by ~10 %) the drying trend in the sc_PDSI_pm used by Dai (2011b), it certainly has no effect on the downward trend up to 2004 and also cannot explain the difference between the results of Dai (2011b) and Sheffield et al. (2012), who essentially discarded the results of Dai (2011b) using this discontinuity error as the main reason.
As expected, using 1950–2008 (instead of 1950–1979) does reduce the variation range and trend magnitude of the sc_PDSI_pm, but only slightly, e.g., from −0.75 to −0.68 change per cerntury for the DaiP case (Fig. 1b). Thus, the difference in the calibration period is also not a major factor, although we consider 1950–1979 as a better choice based on the arguments presented above.
As shown in Sheffield et al. (2012) and Trenberth et al. (2014), large uncertainties exist in current estimates of historical precipitation changes over global land due to sparse observations and data quality issues (Dai et al. 1997). In particular, the CRU TS 3.10 and TS 3.10.01 datasets had poor gauge coverage since the 1990s, with only about 1500 gauges after year 2000. In comparison, GPCC V6 has ~10,000 gauges after 2000 (see Fig. 1 of Trenberth et al. 2014). The GPCP v2.2 (used in DaiP) has similar raingauge coverage as the GPCC product. Fig. S1 in SM illustrates the large differences in the rain-gauge density and coverage between CRU TS3.10.01 and GPCC V6. The use of vastly more observations in GPCC V6, instead of filling the gaps with data from far away stations or with 1961–1990 climatology (as done in the CRU TS datasets), should greatly improve the reliability of the GPCC V6 data, especially for the recent decades. In fact, with improved raingauge coverage, the updated CRU TS3.21 P data show lower global-mean land precipitation since the 1990s than the CRU TS3.10.01 and are closer to GPCC V6 and GPCP v2.2 (Trenberth et al. 2014). The fact that adding more gauges to CRU TS3.10.01 makes it closer to GPCC V6 and GPCP v2.2 suggests that the estimates from GPCC V6 and GPCP v2.2 are likely to be closer to the truth than the CRU TS3.10.01 (while CRU TS3.10 P should not be used). Unfortunately, GPCC does not release its station data to the scientific community.
Another way to evaluate the various precipitation products is to compare their correlations (or the correlations of the PDSI derived from the P products) with physically related but independently measured quantities, such as soil moisture, streamflow, and GRACE satellite-observed water storage changes (Swenson 2012), as we have done previously (e.g., Dai et al. 2004; Dai 2011b). Fig. S2 in SM shows an example of such comparison, with Fig. S2a showing the GRACE vs. sc_PDSI_pm monthly anomaly correlation during April 2002–December 2012 for DaiP (i.e., GPCP v2.2) case and the difference from Fig. S2a in the other panels for the GPCC V6, CRU TS3.22, and WilP cases. It is clear that the correlations are strong (r ≥ 0.6) and similar among the four products over the central and eastern U.S., Europe and other areas with good gauge coverage, thus confirming the reliability of the water storage variations represented by the GRACE data. However, over Africa, South America, central and South Asia, and other regions with poor gauge coverage (Fig. S1), the CRU TS3.22 (similar for CRU TS3.10.01), WilP and even the GPCC V6 product generally show lower correlations than the GPCP data. One exception is central Africa (south of the equator) where the CRU and WilP data show higher correlations with the GRACE data. Despite this, Fig. S2 suggests that recent variations and changes in global land precipitation since the 1990s are likely to be more reliable in the GPCP v2.2 and GPCC V6 datasets than the CRU TS 3.10.01 and CRU TS3.22 (and the WilP) datasets, simply because the rain-gauge coverage is too poor in the latter datasets for the recent decades. Thus, it is unwise to simply treat these P datasets equally and use the ensemble mean of the PDSI_pm derived from them as the best estimate, as is done in Sheffield et al. (2012).
As shown by Trenberth et al. (2014), the wet bias in the CRU TS3.10.01 P data since the 1990s resulted in considerably higher global-mean sc_PDSI_pm for the recent decades compared with the cases using the DaiP, GPCC V6, and WilP P data. Figure 1b further shows that the updated CRU TS3.22 (with more gauges but still substantially fewer than GPCC V6, Trenberth et al. 2014) makes the sc_PDSI_pm closer to the other cases and the 1950–2010 drying trend becomes statistically significant as with the other cases.
Significant differences also exist in other forcing data between ours (Fig. S3 in SM) and those of Sheffield et al. (2012). In particular, global-land downward surface solar radiation in Sheffield et al. (2012) shows a large decline (~4Wm−2) from about 1970 to 1976, and their surface wind speed also shows spurious variations with different variance before and after around 1980 and a downward trend (see their Fig. S5), although surface observations (which often contain spurious discontinuities) do show some stilling (McVicar et al. 2012). These large changes in solar radiation and surface wind speed should both reduce evapotranspiration and thus increase PDSI_pm for the recent decades. In contrast, our cloudiness-based estimate of solar radiation and the 20CR wind data (Fig. S3) do not contain such large long-term changes. We realize that our solar radiation estimates do not include the effects of aerosol changes; however, the large drop in the early 1970s and other long-term changes in Sheffield et al.’s solar radiation estimates do not match the evolution of aerosol-induced radiative forcing (Myhre et al. 2013), which shows increasing cooling effects globally from 1950 to 1990 but declining effects after 1990. The 20CR (Compo et al. 2011) assimilated observed surface pressure and sea surface temperatures (SSTs) (while surface observations besides SSTs were not assimilated in the NCEP/NCAR reanalysis), thus the 20CR surface winds are likely to be reliable for air pressure-induced changes, but unable to account for land surface and other changes.
4 An updated analysis of drought trends since 1950
The calculated sc_PDSI_pm (a measure of agricultural drought) is just one of many drought measures available (Dai 2011a). The conclusions made by Dai et al. (2004); Dai (2011a, 2011b) and Dai (2013a) were based not only on the PDSI trends, but also changes in observed precipitation (a measure of meteorological drought) and streamflow (a measure of hydrologic drought). Figure 2 compares trend maps for 1950–2012 using the DaiP precipitation data (broadly similar for GPCC V6 and CRU TS 3.22), runoff inferred from downstream streamflow gauge records (Dai et al. 2009; Dai 2016), and our sc_PDSI_pm (based on the DaiP and other forcing data described in section 2). The focus here is on the broad spatial patterns of the trends, as these are physically related but different variables. Some similarity is expected between the P and sc_PDSI_pm change patterns since the P data are a major driver of the sc_PDSI_pm, which also includes the effects of other meteorological fields (Fig. S3). However, the runoff changes are derived from independently measured streamflow rates. Thus, consistent trend patterns between the P and runoff or the sc_PDSI_pm and runoff would suggest that the change patterns in both fields are likely to be real, as the chance for the errors in P and streamflow to induce similar trend patterns is low.
Although some regional disagreements are evident between the P and runoff changes (Fig. 2), e.g., over Siberia where the runoff increases may have partly resulted from reduced evapotranspiration and thawing permafrost (Adam and Lettenmaier 2008), overall the three different measures of drought all suggest widespread drying from 1950 to 2012 over Africa, East and South Asia, eastern Australia, central South America, southern Europe and the Middle East, and eastern and western Canada; while wetting trends are apparent the central U.S., northern Europe, Argentina, northwestern Australia, and some other regions (Fig. 2). As shown previously (Dai 2013b; Dong and Dai 2015), precipitation trends since the 1950s (and especially since the 1990s) over southwestern North America, eastern Australia, southern Africa, Argentina, and other regions are strongly influenced by the decadal to multi-decadal oscillations in Pacific sea surface temperatures (SSTs), namely the Inter-decadal Pacific Oscillation (IPO), which is a natural mode of internal climate variability (Liu 2012). Thus, many of the regional trends shown in Fig. 2 have partly resulted from natural climate variations such as the IPO, rather than entirely being caused by recent global warming.
The drying trend in the sc_PDSI_pm (Fig. 2c) is more widespread (over 9.259 × 107 km2) than the decreasing precipitation trend (Fig. 2a, over 8.467 × 107 km2), as precipitation only reflects the supply of water to the surface while sc_PDSI_pm also accounts for changes in atmospheric demand for moisture from the surface. With rising surface air temperatures (Fig. S3a), atmospheric demand for moisture increases during the most recent decades (Fig. S3f), which leads to drier surfaces as reflected by the sc_PDSI_pm trend (Fig. 2c). This drying effect from rising temperatures is shown more clearly in Fig. 3, in which the globally (60oS-75oN) averaged sc_PDSI_pm from two cases is compared: one includes all changes (red line) and the other includes all but the temperature and vapor pressure changes (blue line). The difference between these two cases illustrates the direct impact of surface warming and the associated increases in surface vapor pressure deficit (VPD, Figs. S3-S6) on the sc_PDSI_pm mainly through their influences on PET.
Figure 3 shows that the recent increases in T and VPD have enhanced the downward trend in global-mean sc_PDSI_pm from −0.29/century (significant at the 5 % level) to −0.76/century (significant at the 1 % level) and the upward trend in global drought area from 14.5 % to 21.2 % per century (both significant at the 1 % level). Global drought areas have increased from about 20 % (of global land area) during 1950–1979 to about 30 % since the late 1990s, with an increasingly large contribution from the effect of surface warming and VPD increases (Fig. 3b). The VPD increases derived from the CRU data are qualitatively consistent with those projected by CMIP5 models under a warming climate (Scheff and Frierson 2014; Zhao and Dai 2015). Thus, the large surface warming and the associated VPD increases since the 1980s have substantially enhanced the drying over global land and increased the drought areas during the last thirty years.
Given the well-documented influences of ENSO- (Dai and Wigley 2000) and IPO-related (Dai 2013b; Dong and Dai 2015) SST variations on land precipitation and temperature, we expect significant influences of SSTs on land aridity. To further quantify this, we performed a maximum covariance analysis (MCA, Bretherton et al. 1992) of the 13-point smoothed monthly SST and sc_PDSI_pm fields from 1920 to 2014 to extract the statistically associated leading patterns in the SST and sc_PDSI_pm fields. The first mode for SST shows a temporal evolution that is strongly correlated with the global-mean surface temperature (r = 0.99, blue line in Fig. 4a), with the SST pattern (Fig. 4c) showing warming over almost all oceans from 1920 to 2014. Thus, this mode represents global warming. The associated mode for sc_PDSI_pm also shows a time series (red line in Fig. 4a) that is highly correlated with the global-mean surface temperature (r = 0.90). However, the spatial pattern for this mode in sc_PDSI_pm (Fig. 4d) contains large internal variations that are also reflected in its trend map (Fig. 2c), and it does not match well the sc_PDSI_pm change pattern in response to GHG-induced warming (Zhao and Dai 2015). Dai (2013a) suggested that this mis-match on regional scales is likely due to large sampling noise in the MCA mode; that is, the GHG-induced drying trend is not yet detectable on regional scales given the large internal variability, although it is also possible that some of the CMIP5 change patterns may be incorrect, thereby contributing to the discrepancies.
The second MCA mode (Figs. 4b, 4e-f) represents the ENSO- and IPO-related SST variations primarily in the Pacific, since its temporal coefficients are highly correlated with the Niño3.4 SST index (blue line in Fig. 4b) and its SST pattern (Fig. 4e) resembles the typical ENSO and IPO mode (Dai 2013b; Dong and Dai 2015). After averaging the data with 9-year running mean, the MCA2 (Fig. S7) shows that multi-decadal sc_PDSI_pm variations, which affect its long-term trends, are most pronounced over Southwest North America, central South America, and the Middle East (with drier conditions when the eastern Pacific is cooler than normal), and also over West Africa, parts of eastern Asia and northern North America (with drier conditions when the eastern Pacific is warmer than normal). Interestingly, Australia, southern Africa and northern South America show muted response to multi-decadal SST anomalies compared with those shown in Fig. 4f.
In particular, MCA2 induces an apparent downward trend since the early 1990s associated with the IPO phase change (Figs. 4b and S7b). This apparent trend represents a cooling (warming) in the central and eastern Pacific (western Pacific) during the last 20 years (Figs. 4e and S7e), and a drying trend since the 1990s over many land areas such as Southwest North American, central and southern South America, the Middle East and northern Africa (Fig. S7f). The sc_PDSI_pm patterns shown in Fig. 4f are broadly consistent with the ENSO- and IPO-induced precipitation anomaly patterns (Dai and Wigley 2000; Dong and Dai 2015). Thus, the second MCA mode for sc_PDSI_pm (Figs. 4b and 4f) represents the impacts of ENSO- and IPO-induced SST variations on land aridity and drought, and these impacts are large for many regions in dark blue or red color in Fig. 4f.
5 Comparison with pan evaporation trends
To assess whether our estimated PET trends (and thus the PDSI trends) are consistent with previously reported trends in pan evaporation (Epan, McVicar et al. 2012), we show the trend maps for PET and its key drivers in Figs. S4-S6 for three different periods from 1950 to 2012, 1955–2000, and 1980–2012 (so that the PET trends can be roughly compared with the Epan trends over various periods). These figures show that our estimated PET trends are negative or close to zero over most of the contiguous U.S. for all the three periods (consistent with the Epan trends), near-zero over most China (except its Northeast) from 1955 to 2000, and positive from 1980 to 2012 over most China (consistent with the positive Epan trends for 1992–2007 from study #19 in Table 5 of McVicar et al. 2012). The positive PET trend over Northeast China results mainly from the positive net radiation trend in our forcing data (Fig. S5), which is likely unrealistic as increasing air pollution has dimmed surface solar radiation over that region but this effect was ignored here. Over India, our estimated PET trend from 1980 to 2012 is negative or close to zero except northern India, where our PET shows positive values. Over Australia and New Zealand, our PET shows mostly negative or near zero trends from 1955 to 2000, but large positive trends from 1980 to 2012 over northern and central Australia. Globally, our land PET does not show a clear upward trend before the 1990s (Fig. S3f).
Wang et al. (2012) calculated the PET using station weather reports and the Penman-Monteith equation, and showed that PET during 1982–2008 over Asia, North America and Europe exhibits mostly decadal variations rather than monotonic trends, and that water vapor deficit has the largest influence on PET. Given the uncertainties in our forcing data (especially solar radiation) and the broad consistency between our PET and the Epan trends (and the PET of Wang et al. 2012), we conclude that our estimated PET is consistent with most of the reported Epan trends. Thus, our PDSI drying trends since 1950, which are supported by the precipitation and runoff trends (Fig. 2), are consistent with most of the reported Epan trends. Since the trend in global PET up to the 1990s is small (Fig. S3), the PDSI drying trends since 1950 result mainly from precipitation decreases (Fig. 2), although increasing PET since the 1990s is also a significant contributor for the recent period.
6 Summary
We have examined the main uncertainty sources in estimating historical drying trends based on sc_PDSI_pm or PDSI_pm, and evaluated the sc_PDSI_pm trend with observed changes in precipitation and runoff for assessing historical drought changes. The main findings are summarized as follows.
-
1)
The GPCC V6 and GPCP v2.2 precipitation data sets are likely to be more reliable than other (including CRU) datasets for estimating global land precipitation changes for the period since the 1990s, primarily due to the fact that too few rain-gauges were included in the other datasets for the recent decades.
-
2)
Updated records of precipitation, streamflow and the calculated sc_PDSI_pm show spatially consistent patterns of drying during 1950–2012 over most Africa, East and South Asia, southern Europe, eastern Australia, and many parts of the Americas. They confirm the findings by Dai et al. (2004); Dai (2011a, 2011b) and Dai (2013a), while the “little drying” conclusion made by Sheffield et al. (2012) solely based on their calculated PDSI_pm is likely influenced by spurious changes in their precipitation, radiation and wind forcing data.
-
3)
Our estimated PET trends are broadly consistent with most of the reported trends in pan evaporation (McVicar et al. 2012), with negative or small trends over the United States, China and many other regions and no trends in global-mean PET from the 1950s to the 1980s. However, since the 1980s, rapid warming and associated VPD increases have significantly enhanced drying over global land. These drying effects are consistent with climate model projections, even though the effects of man-made aerosols were not included in our forcing data.
-
4)
An MCA analysis suggests that Pacific SST variations associated with ENSO and IPO, respectively, have large influences on multi-year variations and multi-decadal trends in drought over many land areas, such as southwestern North America, South America, West and South Asia, southern and northern Africa, southern Europe, and Australia. This large internal variability still dominates over GHG-induced drought trends over these regions.
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Acknowledgments
We thank J. Scheff, G. van der Schrier and another anonymous reviewer for constructive review comments. This study was supported by the National Key Basic Research Program of China (Grant No.2012CB956203), the U.S. National Science Foundation (Grant #AGS-1353740), U.S. Department of Energy’s Office of Science (Award #DE-SC0012602), and the U.S. National Oceanic and Atmospheric Administration (Award #NA15OAR4310086).
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This article is part of a Special Issue on “Decadal Scale Drought in Arid Regions” edited by Zong-Liang Yang and Zhuguo Ma.
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Dai, A., Zhao, T. Uncertainties in historical changes and future projections of drought. Part I: estimates of historical drought changes. Climatic Change 144, 519–533 (2017). https://doi.org/10.1007/s10584-016-1705-2
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DOI: https://doi.org/10.1007/s10584-016-1705-2