Assessing California Wintertime Precipitation Responses to Various Climate Drivers
Abstract
Understanding how drivers of climate change affect precipitation remains an important area of research. Although several robust precipitation responses have been identified under continued increases in greenhouse gases (GHGs), considerable uncertainty remains. This is particularly the case at regional scales, including the West Coast of the United States and California. Here, we exploit idealized, single forcing simulations from the Precipitation Driver Response Model Intercomparison Project (PDRMIP) to address how climate drivers impact California wintertime precipitation. Consistent with recent work, GHGs including carbon dioxide and methane, as well as solar forcing, yield a robust increase in California wintertime precipitation. We also find robust California precipitation responses to aerosols but with opposite responses for sulfate versus black carbon aerosol. Sulfate aerosol increases California wintertime precipitation, whereas black carbon reduces it. Moreover, California precipitation is more sensitive to aerosols, particularly regional emissions from Europe and Asia, than to GHGs. These precipitation responses are consistent with shifts in the jet stream and altered moisture fluxes. Although the idealized nature of PDRMIP simulations precludes a formal attribution, our results suggest that aerosols can perturb precipitation and fresh water resources along the West Coast of the United States.
Key Points
- In addition to GHGs, CA wintertime precipitation increases under sulfate forcing, particularly European and Asian sulfate
- In contrast, black carbon aerosols decrease California precipitation
- California precipitation is more sensitive to aerosols than to GHGs and solar forcing
1 Introduction
Understanding how climate change impacts the hydrological cycle, including precipitation patterns and fresh water resources, remains an important societal issue. Model simulations and theoretical considerations show robust precipitation perturbations in a warmer world, including drying of the subtropics and wetting of the middle to high latitudes (Collins et al., 2013; Meehl et al., 2007). This enhancement of the pattern of precipitation minus evaporation (i.e., wet regions get wetter and dry regions drier) is largely a consequence of the increase in horizontal moisture transport under warming, due to the increase in lower-tropospheric water vapor (Held & Soden, 2006).
Although robust precipitation responses also exist at regional scales, including drying of the Mediterranean and the southwest United States (Cayan et al., 2010; Cook et al., 2015; Hoerling et al., 2012; Polade et al., 2017; Seager et al., 2010), regional precipitation responses remain relatively uncertain. This includes the West Coast of the United States, and in particular California—the fifth largest economy in the world and a major agricultural center. Although observations indicate negligible long-term changes over the entire 20th century, substantial multidecadal California precipitation variability exists (Bedsworth et al., 2018). Twenty-first century model projections, particularly those from the Coupled Model Intercomparison Project version 5 (CMIP5) (Taylor et al., 2012), indicate an increase in California wintertime precipitation in response to continued greenhouse gas (GHG) emissions (Allen & Luptowitz, 2017; Neelin et al., 2013), including an increase in extreme precipitation (Polade et al., 2017; Zecca et al., 2018) associated with atmospheric rivers (Dettinger, 2011; Hagos et al., 2016; Lavers et al., 2015). However, other seasons, particularly spring, are likely to become drier (Gao et al., 2014), indicating an intensification of the wet-dry seasonal cycle (Allen & Anderson, 2018), more dry spells and floods (Swain et al., 2018), and an increase in summertime California drought (Diffenbaugh et al., 2015).
In addition to GHGs, atmospheric aerosols are also capable of perturbing the hydrological cycle and have likely masked the expected increase in global mean precipitation due to GHGs (Liepert et al., 2004; Richardson et al., 2018; Salzmann, 2016; Wu et al., 2013). Moreover, shortwave climate drivers, like aerosols, have a larger apparent hydrological sensitivity (defined as the change in precipitation per unit change in global surface temperature) than longwave drivers, such as GHGs (Andrews et al., 2010; Liepert & Previdi, 2009; Liu et al., 2018; Samset et al., 2016). Hemispheric contrasts in aerosols have also shifted the tropical rain band, contributing to the Sahel drought that peaked in the mid-1980s (Allen et al., 2015; Ackerley et al., 2011; Biasutti & Giannini, 2006; Chang et al., 2011; Frierson & Hwang, 2012; Hwang et al., 2013; Undorf et al., 2018). Several studies also show the role of aerosols in reducing monsoon precipitation. The observed precipitation reduction in recent decades over the South and East Asia monsoon regions can be explained by the dominance of aerosol radiative effects suppressing precipitation over the expected enhancement due to increasing GHGs (Krishnan et al., 2016; Li et al., 2015; Lau & Kim, 2017; Lin et al., 2018).
The Precipitation Driver Response Model Intercomparison Project (PDRMIP) (Myhre et al., 2017) consists of a suite of idealized, single-forcing model simulations to understand how various climate drivers impact global and regional precipitation. In addition to the aforementioned studies, recent PDRMIP analyses have also shown aerosols can perturb regional precipitation patterns, including weakening of the Asian monsoon in response to sulfate aerosol (Liu et al., 2018; Samset et al., 2016). PDRMIP simulations also suggest that the increase in black carbon aerosols have contributed to Mediterranean drying (Tang et al., 2018). This signal was related to a positive North Atlantic Oscillation pattern, associated with a poleward shift of the jet stream and storm track.
Here, we leverage the PDRMIP archive to quantify how various climate drivers, including GHGs as well as aerosols, impact U.S. West Coast precipitation, focused on California. The paper is organized as follows: Section 2 describes the PDRMIP models and simulations used in this study. Results are presented in section 3, focused on the California wintertime precipitation response to various climate drivers, as well as the associated dynamical changes including atmospheric winds and moisture flux. A discussion and conclusion follow in sections 4 and 5, respectively.
2 Methods and Data
2.1 Model Simulations
The PDRMIP models and experimental design is described by Myhre et al. (2017). In summary, up to ten climate models (Table 1) performed several idealized, single-forcing simulations, including a control simulation with all anthropogenic and natural forcing agents set to present day values, a doubling of carbon dioxide (2xCO2), a tripling of methane (3xCH4), and a 2% increase in total solar irradiance (Solar+2%). Aerosol experiments include a fivefold increase in anthropogenic sulfate concentrations or emissions (5xSO4) and a 10-fold increase in anthropogenic black carbon concentrations or emissions (10xBC). Most of the PDRMIP models (seven of the 10) also performed regional aerosol experiments, including a 10-fold increase in European sulfate concentrations/emissions (10xSO4 Europe), a 10-fold increase in Asian sulfate concentrations/emissions (10xSO4 Asia), and a 10-fold increase in Asian black carbon concentrations/emissions (10xBC Asia). The European (Asian) region is defined from 35–70N and 10W to 40E (10–50N and 60–140E).
Model | Version | Resolution | Aerosol mode/size bin | Mixing state | Regional simulations | References |
---|---|---|---|---|---|---|
CanESM (E) | 2010 | 2.8 × 2.8; 35 levels | S, N, BC, OC, DU, SS | Internal | No | Arora et al. (2011) |
HadGEM2 (E) | 6.6.3 | 1.875 × 1.25; 38 levels | S(3), BC, OC, BB(3), DU(6), SS(2) | External | No | Collins et al. (2011) |
MIROC-SPRINTARS (E) | 5.9.0 | ∼1.4 × 1.4; 40 levels | S(1), BC(1), OC(1), DU(6) SS(4) | Internal and external | Yes | Takemura et al. (2005,2009) |
CESM-CAM5 (E) | 1.1.2 | 2.5 × 1.9; 30 levels | S, BC, POM, SOA, SS, DU(3) | Internal | Yes | Hurrell et al. (2013) |
ECHAM-HAM(E) | 6.3/2.2 | ∼1.8 × 1.8; 31 & 47 levels | S(4), BC(4), POM(4), SOA(20), DU(4), SS(2) | Internal and external | No | Zhang et al. (2012) |
CESM-CAM4 (C) | 1.0.3 | 2.5 × 1.9; 26 levels | S, BC(2), POM(2), SOA, DU(4), SS(4) | External | Yes | Neale et al. (2010) |
GISS-E2R (C) | E2-R | 2 × 2.5; 40 levels | S(1), N(1), BC(1), OC(1), DU(4), SS(2) | Internal and external | Yes | Schmidt et al. (2014) |
HadGEM3 (C) | GA 4.0 | 1.875 × 1.25; 85 levels | S(3), BC, OC, BB(3), DU(6), SS(2) | External | Yes | Bellouin et al. (2011) |
NorESM (C) | 1-M | 2.5 × 1.9; 26 levels | S, BC, OM, SS, DU 13 modes, 33 size bins | Internal and external | Yes | Bentsen et al. (2013) |
IPSL-CM5A (C) | CMIP5 | 3.75 × 1.875; 39 levels | S, BC, OC, DU, SS | External | Yes | Dufresne et al. (2013) |
- Note . Emission (concentration) driven models are indicated with an “E” (“C”). All models used a coupled ocean, except CESM-CAM4 and ECHAM-HAM, which implemented a slab ocean. All models use a log-normal aerosol size distribution. Microphysical aerosol interactions with clouds (aerosol indirect effects) are accounted for in all models except GISS-E2R. In addition to lacking regional aerosol simulations, ECHAM-HAM also lacks 5xSO4 and Solar+2% simulations.
- Abbreviations: BB, biomass burning; BC, black carbon; DU, dust; GA, global atmosphere; N, nitrate; OC, organic carbon; OM, organic mass; POM, primary organic matter; S, sulfate; SOA, secondary organic aerosol; SS, sea salt.
In terms of the aerosol simulations, some models are driven by changes in aerosol concentrations, whereas others are driven by changes in aerosol emissions. Concentration-driven models use identical AeroCom-based fixed concentrations in the control simulation; the anthropogenic part of these concentrations is multiplied by a factor (e.g., 10 in 10xBC experiment) to obtain the perturbation simulation. Emission-driven models use individual emissions for the control simulation; these emissions are multiplied by a factor to obtain the perturbation. Most models' control simulation is based on present-day aerosols; an exception is HadGEM2-ES, which uses year 1860 emissions for the control simulation but year 2000 emissions for the experiment (Stjern et al., 2017). In the emission-driven models, the climate response to the increase in aerosols (e.g., BC-induced warming and altered precipitation) can feedback on the aerosol concentrations (e.g., via modified aerosol wet removal), dampening or amplifying the climate response (Allen et al., 2016, 2019; Sand et al., 2015). No model includes aerosol effects on convective precipitation. GISS-E2-R is the lone model that lacks aerosol-indirect effects. All models use a dynamic ocean model, except CESM-CAM4 and ECHAM-HAM, both of which use a slab ocean.
2.2 Methods
Both coupled ocean-atmosphere and fixed sea surface temperature (SST) simulations were performed. The former give the total climate response (experiment minus control), whereas the latter give the fast response (rapid adjustments). Coupled simulations were run for 100 years, and we analyze the last 50 years. Fixed SST simulations are integrated for 15 years. Except for the effective radiative forcing (ERF) calculation, which is derived from the fixed SST simulations, all analyses are based on the coupled model simulations. Statistical significance of the ensemble mean response is based on a t test for the difference of means (experiment minus control) using the pooled variance. We also quantify the robustness of the response by the percentage of models that agree on the sign of the change. We define a “robust” response as one in which at least 70% of models agree on the sign of the response. Our definition of “robust” is consistent with Intergovernmental Panel on Climate Change's (IPCC) definition of “likely,” where 2/3 model agreement is required (Cubasch et al., 2013). Our definition of robust, however, is less stringent than IPCC's definition of “very likely,” where 9/10 model agreement is required. All model data are spatially interpolated to a 2.5 × 2.5° grid using bilinear interpolation. To maximize the use of available data, ensemble means are constructed by averaging over all available models. This implies that a slightly different mix of models constitutes the ensemble mean, depending on the experiment (e.g., only seven of the 10 PDRMIP models performed regional aerosol simulations).
3 Results
3.1 ERF
Figure S1 in the supporting information shows the ensemble mean annual mean ERF map for each experiment (see also Myhre et al., 2017). The ERF for each model and experiment is also included in Tables S1 and S2. ERF has been shown to be more representative of the eventual temperature response to climate drivers and is estimated from the top-of-the-atmosphere (TOA) radiative perturbation (change in net radiative longwave plus shortwave fluxes) from the corresponding fixed SST simulations (Forster et al., 2016). The multimodel mean ERF (and the range) is 3.72 (3.32 to 4.32) W m−2 for 2xCO2; 1.21 (0.86 to 1.49) W m−2 for 3xCH4; and 4.17 Wm−2 (4.01 to 4.40) for Solar+2%. The global aerosol simulations yield corresponding ERFs of -3.51 (-8.27 to -2.04) W m−2 for 5xSO4 and 1.01 (0.39 to 1.54) W m−2 for 10xBC. The regional aerosol simulations yield corresponding ERFs of 0.15 (0.004 to 0.40) W m−2 for 10xBC Asia; -0.74 (-1.15 to -0.45) W m−2 for 10xSO4 Asia; and -0.35 (-0.47 to -0.25) W m−2 for 10xSO4 Europe. We note larger model disagreement among global annual mean ERF for the aerosol simulations relative to the GHG/solar experiments.
3.2 Precipitation Response
Figure 1 shows the wintertime (November through March, NDJFM) ensemble mean precipitation response for several climate drivers. 2xCO2 yields a significant increase in precipitation for most of the North American West Coast, including California, with drying in Mexico and parts of the southern United States. Wintertime wetting of California in response to future increases in GHGs, as well as more idealized increases in GHGs (i.e., 1% per year CO2 increases), is consistent with prior studies based on models from the CMIP5 (Allen & Luptowitz, 2017; Allen & Anderson, 2018; Neelin et al., 2013; Zecca et al., 2018). In addition to 2xCO2, PDRMIP models also show increases in wintertime California precipitation for both 3xCH4 and Solar+2% (Figure S2).
Less is known about the possible impact of aerosols on West Coast precipitation. PDRMIP simulations show that aerosols drive significant California wintertime precipitation responses, with 10xBC leading to drying for most of the U.S. West Coast, particularly California, as well as drying of the southwestern United States and Mexico. In contrast, 5xSO4 leads to a West Coast dipole pattern of wetting (drying) south (north) of ∼40N. Mexico and Baja California experience the largest increase in precipitation. Similar precipitation responses are generally obtained when models are subdivided into concentration- versus emission-driven models (Figure S3). There are some differences, however, including a larger increase in California precipitation in response to 5xSO4 in the emission-driven models. In contrast, concentration-driven models yield a larger (and more robust) decrease in California precipitation in response to 10xBC. Some of this precipitation response contrast is due to model differences independent of the experimental design (e.g., MIROC-SPRINTARS 10xBC yields relatively large California wetting, to be discussed below).
In addition to the global aerosol simulations, PDRMIP also conducted several regional aerosol simulations, focusing on the main centers of historical aerosol emissions, Europe and Asia (unfortunately, no U.S. regional experiments were performed). 10xBC Asia drives relatively weak California drying that extends to the Four Corners region, but most of the drying is located over the Pacific Ocean. Both 10xSO4 Asia and Europe lead to significant wetting that is centered on California. Figure 2 shows the corresponding wintertime precipitation response model agreement. Except in the case of 10xBC Asia, at least 70% of the models support the aforementioned California precipitation signals, indicating a “robust” PDRMIP response. Thus, PDRMIP simulations suggest aerosols can perturb West Coast precipitation, including California.
Recall that a subset of PDRMIP models performed the regional aerosol simulations (Table 1; seven of the 10). Thus, the ensemble mean plots in Figure 1 are based on slightly different models, particularly the global versus regional aerosol ensemble mean plots. Figure S4 shows that the ensemble mean change in wintertime precipitation for 2xCO2, 10xBC, and 5xSO4 is similar using all models or when restricted to the seven models with regional aerosol simulations. Furthermore, the differing California precipitation response to 10xBC versus 10xBC Asia is not due to the different mix of models. Similar California drying is obtained under 10xBC when the ensemble mean is restricted to the same seven models used to construct the 10xBC Asia ensemble mean. The reason for this difference is that unlike most models, MIROC-SPRINTARS simulates relatively large West Coast wetting in response to BC, particularly 10xBC Asia. Reasons for this model's different behavior are unclear, but this model also simulates the opposite east Pacific circulation responses to BC (next sections). Removing MIROC-SPRINTARS from the ensemble mean results in significant California drying under 10xBC Asia (Figure S4).
Although there is a robust California precipitation response to most of the climate drivers (10xBC Asia being the exception), Figure 3 shows that for nearly all of the climate drivers, there are models that yield a California precipitation response that is opposite to the majority of the models. This includes the GHG simulations, as well as Solar+2%, where NorESM1, ECHAM-HAM, and GISS-E2-R yield drying or negligible change. The ensemble mean California precipitation response to 5xSO4 is near zero, consistent with the dipole pattern of wetting (drying) south (north) of ∼40N. HadGEM3, however, yields a very large drying trend. Although we do not find significant intermodel correlations between a model's ERF and its California precipitation response for a given experiment (not shown), we note that HadGEM3 is also an outlier in terms of the 5xSO4 ERF. At -8.27 Wm−2, it is nearly double the multimodel mean 5xSO4 ERF. For the BC simulations, the aforementioned MIROC-SPRINTARS model stands out as driving wetting, especially for 10xBC Asia, in contrast to most of the models. More consistency across models exists in the regional sulfate simulations. Figure 3 also shows similar results exist for the 95th percentile of daily wintertime precipitation. Climate drivers that yield an increase (decrease) in NDJFM California mean precipitation also yield a corresponding increase (decrease) in extreme precipitation.
We also quantify the California precipitation response for the traditionally defined boreal fall (September-October-November, SON) and spring (March-April-May, MAM) seasons (Figure S5). For MAM, 2xCO2, 3xCH4, and Solar+2% yield ensemble mean California drying (in contrast to the NDJFM wetting). Although these ensemble mean responses are not significant, 80% (78%) of the models yield drying for 2xCO2 (Solar+2%). The CO2 response is consistent with prior studies noting a “robust spring drying” of the southwestern United States, which was attributed to strengthening and expansion of the subtropical high pressure in the Pacific and Atlantic (Gao et al., 2014). 10xBC and 10xBC Asia also yield ensemble mean MAM drying, with 100% and 85% model agreement, respectively. The sulfate experiments yield ensemble mean MAM wetting, with robust responses for 5xSO4 and 10xSO4 Asia (88% and 85% model agreement, respectively).
Similar but less robust results exist for SON. This includes ensemble mean SON drying for 2xCO2, 3xCH4, and Solar+2%, as well as for 10xBC and 10xBC Asia. Ensemble mean SON wetting occurs for 5xSO4, 10xSO4 Asia, and 10xSO4 Europe. Thus, BC (SO4) experiments yield California drying (wetting) throughout the entire California wet season, including fall, winter, and spring. GHGs and solar forcing yield wetting during winter but drying during spring and fall.
Figure 4 (see also Figures S6and S7) shows the NDJFM California large-scale and convective precipitation responses. Except for 5xSO4, similar signed ensemble mean NDJFM California precipitation responses occur for both large-scale and convective precipitation. For CO2, the bulk (81%) of the ensemble mean total precipitation increase is due to an increase in convective precipitation. For CH4 and Solar+2%, the ensemble mean increase in both convective and large-scale precipitation is similar, but the convective precipitation increase is more robust (80% model agreement for both CH4 and Solar+2%) than the large-scale precipitation increase (60% and 56%, respectively).
For the aerosol experiments, however, the ensemble mean California NDJFM large-scale precipitation response tends to be larger and more robust than the corresponding convective precipitation response. For 10xBC (10xBC Asia), the ensemble mean decrease in large-scale precipitation is 66% (52%) of the total decrease. Model agreement is the same for both convective and large-scale precipitation at 80% for 10xBC and 71% for 10xBC Asia. For 10xSO4 Asia and Europe, the ensemble mean increase in large-scale precipitation is 74% of the total increase, with larger model agreement for large-scale, as opposed to convective precipitation. 5xSO4 is the lone experiment that yields opposite signed California NDJFM ensemble mean large-scale and convective precipitation responses. These responses are similar in magnitude and model agreement (e.g., 89% model agreement for the large-scale precipitation increase and the convective precipitation decrease). Similar conclusions exist between emissions- versus concentration-driven 5xSO4 models.
To summarize, California NDJFM wetting is mostly due to an increase in convective precipitation under GHG and solar forcing, particularly for CO2. In contrast, the California wintertime precipitation response under aerosol forcing is mostly due to changes in large-scale precipitation. 5xSO4 yields opposite signed changes for convective and large-scale precipitation, with the change in large-scale (convective) precipitation driving the increase (decrease) in total precipitation for southern (northern) California (Figure 1).
3.3 Sea Level Pressure and Wind Response
Figure 5 shows the wintertime ensemble mean sea level pressure (SLP) and 850-hPa wind response (Figure S8 shows the corresponding SLP response model agreement). The climate drivers that enhance California wintertime precipitation, including CO2 and sulfate, feature a deepening and southeastward shift of the Aleutian low. In turn, the 850-hPa winds show enhanced counterclockwise circulation, with anomalous southwesterly winds off the California coast. Similar responses exists for both CH4 and Solar+2% (Figure S9). In contrast, the drivers that reduce California wintertime precipitation, particularly BCx10, yield a weakening of the Aleutian low and anomalous clockwise flow, including northerly/northeasterly flow near the California coast. These changes are barotropic in nature, as they also exist in the tropospheric geopotential height response (not shown).
In addition to these near-surface atmospheric dynamical changes, the 300-hPa zonal winds—which are important for controlling the location of the storm track and steering midlatitude cyclones—also show robust responses. Figure 6 shows that CO2 drives a southward shift/southeastward extension of the jet stream (Figure S10 shows the model agreement). This response is consistent with prior studies and was suggested to promote the increase in California precipitation under continued GHG-induced warming (Chang et al., 2015; Neelin et al., 2013). PDRMIP simulations also show that similar results exist for both CH4 and Solar+2% (Figure S11). For the aerosol simulations, 5xSO4 drives a southward shift of the jet, with decreases in 300-hPa zonal winds on the poleward flank of the climatological jet and increases on the equatorward jet flank. Sulfate regional simulations, including 5xSO4 Asia and Europe, also yield an equatarward jet displacement, in addition to an eastward extension of the jet. The southward shift of the Pacific jet in 5xSO4 is larger than in the regional sulfate simulations and possibly related to U.S. sulfate emissions. In contrast to sulfate aerosol, 10xBC again leads to the opposite response, including a poleward shift of the jet stream. 10xBC Asia also leads to a poleward jet shift, but it is primarily confined to the east Pacific.
3.4 Moisture Flux Response
Figure 7 shows the moisture flux and the corresponding MFC. 2xCO2 leads to enhanced westerly/southwesterly moisture flux along the West Coast, as well as MFC (as does 3xCH4 and Solar+2%, Figure S12). 5xSO4 also shows an increase in southwesterly moisture flux and convergence for most of California and Baja California, with the opposite response poleward of ∼40N. 10xSO4 Asia and Europe lead to a similar increase in southwesterly moisture flux and convergence for California. 10xBC leads to the opposite response, and relatively weak changes exist for 10xBC Asia (except off the coast). These responses are consistent with the patterns of precipitation change and to the dynamical changes (SLP and winds) previously described.
Figure 8 shows the dynamical contribution to the change in moisture flux and its convergence (Figure S13 shows the thermodynamic contribution). Consistent with the large circulation changes off the California coast in response to the various climate drivers, most of the total moisture flux response and its convergence is due to dynamics, as opposed to thermodynamics. Similar conclusions exist for CH4 and Solar+2% (Figure S12). This highlights the importance of dynamical changes (i.e., changes in the SLP and winds) in driving the California precipitation responses. For 5xSO4, the increase in MF and MFC in southern California (where precipitation increases) is largely consistent with the dynamical component; however, the decrease in MF and MFC in northern California (where precipitation decreases) is largely consistent with the thermodynamic component.
3.5 Normalized Precipitation Response
Figure 9 shows the ensemble mean NDJFM normalized precipitation responses to the various climate drivers. Here, the change in precipitation is normalized by the ensemble mean annual mean ERF (section 3.1). Relative to CO2, as well as 3xCH4 and Solar+2% (not shown), aerosols drive a larger California precipitation response per unit ERF. In particular, California precipitation is most sensitive to regional aerosols but with opposite responses between BC and sulfate. The much larger increase in California normalized precipitation in 10xSO4 Asia and 10xSO4 Europe, relative to 5xSO4, illustrates how the relatively small sulfate forcing in Asia and Europe (relative to the global sulfate forcing) is very efficient at perturbing West Coast precipitation. This further suggests the possible importance of aerosols, particularly those emitted from Europe and Asia, in perturbing California precipitation. The relatively large response in most of the regional aerosol simulations also highlights the importance of the location of the aerosol forcing. This is consistent with prior work showing midlatitude aerosol forcing is capable of meridionally shifting the latitude of the maximum meridional temperature gradient and, in turn, the latitude of the jet stream which steers precipitation-bearing extratropical storms (Allen et al., 2012a, 2012b; Allen & Ajoku, 2016; Kovilakam & Mahajan, 2015). This will be discussed in more detail in section 4.
4 Discussion
Similar to the results presented here, others have also found an increase in U.S. West Coast wintertime precipitation, including California, in response to increasing GHGs (Allen & Luptowitz, 2017; Chang et al., 2015; Neelin et al., 2013; Simpson et al., 2015). Simpson et al. (2015) associated these precipitation changes to changes in the stationary wave field that brings wetting southerlies to the West Coast of North America (and drying northerlies to interior southwest North America). This change in the meridional wind field is caused by strengthened zonal mean westerlies in the subtropical upper troposphere, which alters the character of intermediate-scale stationary waves. El Niño Southern Oscillation (ENSO) may also play a role, as model projections feature a shift to a more El Niño-like tropical Pacific background state (Cai et al., 2015), which may favor wetter winters for California (Allen & Luptowitz, 2017; Zecca et al., 2018). Increasing GHGs yield dynamically coherent tropical and extratropical responses in CMIP5 models that are reminiscent of an El Niño-like teleconnection, including an increase in eastern tropical Pacific divergence and a poleward propagating Rossby wave, and a southeastward shift of the upper level winds and an increase in storm track activity in the east Pacific. In addition to the extratropical wind response (Figures 5 and 6), we also find an increase in eastern tropical Pacific divergence and a poleward Rossby wave response in 2xCO2 and Solar+2% (Figure 10). Models, however, may not be able to accurately simulate the tropical Pacific SST response to GHGs due to a cold bias of their equatorial cold tongues (Seager et al., 2019).
The poleward jet shift in response to BC is consistent with recent work (Allen et al., 2012b; Kovilakam & Mahajan, 2015; Shen & Ming, 2018). Allen et al. (2012b) showed that late 20th century trends in BC burden peak near the Northern Hemisphere (NH) midlatitudes, which preferentially warms the atmosphere there and decreases (increases) the baroclinicity on the equatorward (poleward) flank of the jet. This poleward shift of the latitude of maximum baroclinicity, by thermal wind balance, implies a corresponding poleward shift of the jet. A poleward jet shift also occurred in idealized simulations when a heating source was added to the midlatitude (30–60°) atmosphere (Allen et al., 2012a), as well as in response to future aerosol reductions (Allen & Ajoku, 2016). However, an equatorward jet shift occurred when heating was added to the high latitudes (60–90°) alone. Adding heat to the midlatitude and high-latitude (30–90°) atmosphere led to a weak poleward jet shift (Allen et al., 2012a). Thus, the jet shift depends on the location of the heating, with the largest poleward shift occurring in response to midlatitude heating (due to the aforementioned change in baroclinicity). More recently, Shen and Ming (2018) showed that the poleward jet shift in response to BC is due to the increase in midlatitude tropospheric stability, which results in less energetic baroclinic eddies and therefore reduced meridional energy transport in the midlatitudes.
Figure 11 shows the ensemble mean zonal mean ERF and tropospheric (850–300 hPa) temperature and zonal wind response for 10xBC, as well as the other climate drivers. Consistent with these prior studies, 10xBC features an NH lower-latitude to midlatitude (10–30N) ERF maximum, as well as an NH midlatitude (∼40N) peak in the tropospheric temperature response. There is also a reduction in the tropospheric zonal winds on the equatorward flank (20–40N) of the climatological jet maximum (thin black lines) and a corresponding increase on the jet's poleward flank (50–70N). This response implies a poleward shift of the tropospheric jet. Consistent with the large Asian contribution of BC to global emissions, similar results are obtained with 10xBC Asia. Interestingly, both BC responses also suggest a poleward jet displacement in the Southern Hemisphere, despite minimal forcing there.
The opposing PDRMIP jet shifts between sulfate and black carbon are similar to those reported in Allen and Sherwood (2011), where natural aerosols (mostly reflecting) led to an equatorward jet shift and anthropogenic aerosols (more absorbing) led to a poleward jet shift. Aerosol-induced cooling has also been shown to drive an equatorward jet shift in other studies (Fischer-Bruns et al., 2009; Ming & Ramaswamy, 2009; Ming et al., 2011). Aerosol cooling enhances the meridional temperature gradient equatorward of the NH jet but weakens it poleward, resulting in an equatorward jet shift. Aerosol-induced cooling was also found to displace the Aleutian low southeastward, which was accompanied by an equatorward displacement of the North Pacific jet and storm track (Ming et al., 2011). This was linked to stationary Rossby waves excited by the anomalous diabatic heating over the tropical east Pacific. Figure 11 shows that the sulfate simulations lead to an ERF minimum near 20–40N, a weaker relative minimum in the tropospheric temperature response just poleward of the ERF minimum, and an increase (decrease) in the tropospheric zonal winds on the equatorward (poleward) flank of the climatological jet maximum. This response implies an equatorward shift of the tropospheric jet.
An interesting distinction between the aerosol and GHG 850–300-hPa NH zonal wind response is that the aerosol jet shift is relatively zonally uniform (e.g., Figure 11), whereas the GHG response is not. This is despite the more zonally asymmetric (symmetric) aerosol (GHG) forcing, particularly in the case of the regional aerosol simulations. In fact, the equatorward jet shift due to GHGs (and Solar+2%) primarily exists in the east Pacific (Figure 6), off the coast of California; the rest of the Pacific features a poleward jet shift, consistent with increased subtropical static stability and tropopause height (Allen et al., 2012a; Chen et al., 2008; Frierson et al., 2007; Lu et al., 2008; Lorenz & DeWeaver, 2007; Yin, 2005), leaving negligible shift of the NH jet in the zonal mean (Figure 11f). This zonal asymmetry in the NH jet shift in response to GHGs and Solar+2% further supports the role of Rossby waves, which are excited by the asymmetric change in tropical Pacific divergence (Figure 10). Future PDRMIP analyses will focus more specifically on how these climate drivers impact the tropical and extratropical atmospheric circulation, including the midlatitude jets and Hadley circulation.
Shen and Ming (2018) recently showed that the ability of BC to alter atmospheric circulation, including the poleward jet shift, increases with the altitude of BC. Significant differences exist between simulated profiles of the vertical BC distribution (Koch et al., 2009; Textor et al., 2006, 2007), with climate models likely having too much BC in the upper troposphere/stratosphere (Allen & Landuyt, 2014). Causes remain uncertain but are thought to be related to wet removal (Kipling et al., 2013), convective transport (Allen & Landuyt, 2014; Park & Allen, 2015; Storelvmo, 2012), injection height (Labonne et al., 2007), and/or physical aging (Liu et al., 2011). Allen et al. (2019) showed that PDRMIP models overestimate the amount of BC atmospheric heating relative to a semiempirical estimate (Chung et al., 2016) constrained by a suite of aerosol observations, including the vertical aerosol profile from the Cloud-Aerosol Lidar with Orthogonal Polarization (CALIOP) (Winker et al., 2009). This in turn was linked to significant differences in the rapid adjustment, including clouds, surface temperature, and precipitation. This suggests the PDRMIP BC jet response may be too strong and highlights the importance of improved constraints on the simulated aerosol vertical profile. This will be evaluated during Phase 2 of PDRMIP, in which 10xBC simulations with a shortened lifetime (∼3 days, as opposed to the current multimodel mean of 9.64 days Stjern et al., 2017) will be conducted.
The experimental design of PDRMIP is idealized, which makes a formal attribution difficult. This is particularly true in the case of aerosols, where emissions have varied both spatially and temporally, which is not accounted for in PDRMIP simulations. Aerosol emissions from Europe and North America peaked in the late 1970s and have since declined substantially due to air pollution controls and clean air regulations (Allen et al., 2013; Lamarque et al., 2010; Streets et al., 2009; Wild, 2012). In contrast, aerosol emissions from Asia and India were just starting to ramp up in the late 20th century and now dominate global aerosol emissions. China, however, has recently implemented sulfur dioxide emission controls, resulting in a 75% reduction in sulfate aerosol since 2007 (Li et al., 2017). The PDRMIP regional aerosol simulations highlight the location-dependent climate response of aerosol, which does not simply scale with the global mean ERF (e.g., Figure 9). Another difficulty in using PDRMIP idealized simulations for a formal attribution is the possibility of nonlinear climate responses to aerosol forcing (Feichter et al., 2004; Ming & Ramaswamy, 2009), including dependence on the background aerosol state (Carslaw et al., 2017).
5 Conclusions
Using model simulations from PDRMIP, we have quantified how various climate drivers affect wintertime precipitation along the U.S. West Coast, focused on California. Consistent with recent work (Allen & Luptowitz, 2017; Neelin et al., 2013), GHGs including both CO2 and CH4, as well as solar forcing, drive a robust increase in California wintertime precipitation. We also find robust California precipitation responses to atmospheric aerosol forcing but with near opposite responses for absorbing (BC) versus reflecting (sulfate) aerosol. BC leads to a decrease in California precipitation, whereas sulfate leads to an increase. This wetting is particularly strong for both European and Asian sulfate.
Although a formal attribution is not possible with PDRMIP simulations, our results suggest aerosols can perturb California precipitation and that they may be important drivers of California precipitation change. This is particularly relevant over the next several decades, as aerosol emissions are expected to rapidly decline (Gidden et al., 2019). Interestingly, the offsetting tendencies of absorbing versus reflecting aerosols, combined with the relatively large natural variability of California precipitation (Deser et al., 2012), may make detection of an aerosol impact difficult. More detailed transient simulations with (and without) temporally and spatially varying aerosol emissions and precursor gases would be required to formally attribute California precipitation changes to atmospheric aerosols. Simulations currently being conducted in support of CMIP6, under the Aerosol Chemistry Model Intercomparison Project (AerChemMIP) (Collins et al., 2017) feature such 20th century transient simulations, including future projections driven by emission scenarios with weak versus strong air quality control measures, which would allow a formal attribution.
Conflict of Interest
The authors declare no competing financial interests.
Data Availability Statement
PDRMIP simulations can be accessed at https://cicero.oslo.no/en/PDRMIP.
Acknowledgments
DWP receives funding from the European Union's Horizon 2020 research and innovation programme iMIRACLI under Marie Sklodowska-Curie grant agreement No 860100. DWP also gratefully acknowledges funding from the NERC ACRUISE project NE/S005390/1.