Present-day radiative effect from radiation-absorbing aerosols in snow
- 1Department of Physical and Chemical Sciences, University of L'Aquila, 67100 L'Aquila, Italy
- 2Center of Excellence in Telesensing of Environment and Model Prediction of Severe Events (CETEMPS), University of L'Aquila, 67100 L'Aquila, Italy
- 3Department Information Engineering, Electronics and Telecommunications, Sapienza Università di Roma, 00185 Rome, Italy
Correspondence: Paolo Tuccella (email@example.com, firstname.lastname@example.org)
Black carbon (BC), brown carbon (BrC), and soil dust are the most important radiation-absorbing aerosols (RAAs). When RAAs are deposited on the snowpack, they lower the snow albedo, causing an increase in the solar radiation absorption. The climatic impact associated with the snow darkening induced by RAAs is highly uncertain. The Intergovernmental Panel on Climate Change (IPCC) Special Report on the Ocean and Cryosphere in a Changing Climate (SROCC) attributes low and medium confidence to radiative forcing (RF) from BrC and dust in snow, respectively. Therefore, the contribution of anthropogenic sources and carbonaceous aerosols to RAA RF in snow is not clear. Moreover, the snow albedo perturbation induced by a single RAA species depends on the presence of other light-absorbing impurities contained in the snowpack. In this work, we calculated the present-day RF of RAAs in snow starting from the deposition fields from a 5-year simulation with the GEOS-Chem global chemistry and transport model. RF was estimated taking into account the presence of BC, BrC, and mineral soil dust in snow, simultaneously. Modeled BC and black carbon equivalent (BCE) mixing ratios in snow and the fraction of light absorption due to non-BC compounds (fnon-BC) were compared with worldwide observations. We showed that BC, BCE, and fnon-BC, obtained from deposition and precipitation fluxes, reproduce the regional variability and order of magnitude of the observations. Global-average all-sky total RAA-, BC-, BrC-, and dust-snow RF were 0.068, 0.033, 0.0066, and 0.012 W m−2, respectively. At a global scale, non-BC compounds accounted for 40 % of RAA-snow RF, while anthropogenic RAAs contributed to the forcing for 56 %. With regard to non-BC compounds, the largest impact of BrC has been found during summer in the Arctic (+0.13 W m−2). In the middle latitudes of Asia, the forcing from dust in spring accounted for 50 % (+0.24 W m−2) of the total RAA RF. Uncertainties in absorbing optical properties, RAA mixing ratio in snow, snow grain dimension, and snow cover fraction resulted in an overall uncertainty of −50 %/+61 %, −57 %/+183 %, −63 %/+112 %, and −49 %/+77 % in BC-, BrC-, dust-, and total RAA-snow RF, respectively. Uncertainty upper bounds of BrC and dust were about 2 and 3 times larger than the upper bounds associated with BC. Higher BrC and dust uncertainties were mainly due to the presence of multiple absorbing impurities in the snow. Our results highlight that an improvement of the representation of RAAs in snow is desirable, given the potential high efficacy of this forcing.
In the last decades, many studies have recognized the contribution of radiation-absorbing aerosols (RAAs) to climate warming, in particular black carbon (BC), brown carbon (BrC), and dust, once deposited on the snow and ice pack (Hansen and Nazarenko, 2004; Hansen et al., 2005, 2007; Flanner et al., 2007, 2009; Bond et al., 2013; Boucher et al., 2013; Lin et al., 2014; Pitari et al., 2015a; Skiles et al., 2018). Observations show that the extent of snow coverage is declining due to global warming (Sturm et al., 2017). RAA deposition on snowy surfaces results in an enhancement of the absorbed solar radiation in snow due to the snowpack albedo reduction. This process increases melting and therefore reduces the snow duration. As a result, the alteration of runoff timing and magnitude due to the climate warming is amplified (e.g., Coppola et al., 2014), with significant impact on water resources (e.g., Painter et al., 2010; Skiles et al., 2012; Wu et al., 2018). Forcing efficacy by RAAs in snow is about 3 times larger than the forcing that results from carbon dioxide (CO2) (Flanner et al., 2007; Bond et al., 2013; Boucher et al., 2013). However, the climatic effect associated with RAAs in snow is still highly uncertain.
BC is emitted by the incomplete combustion of fossil fuel (FF), biofuel (BF), and biomass burning (BB) (Bond et al., 2013) and is characterized by high efficiency in absorbing the incoming solar radiation (Bond et al., 2013; Boucher et al., 2013). Current estimates suggest BC as the second most important climate forcing species after carbon dioxide (Gustafsson and Ramanathan, 2016). A large regional variability in BC mixing ratio in snow, ranging over 4 orders of magnitude, has been found by Warren (2019). As an example, Doherty et al. (2010) reported values of 1–4 ng g−1 in Greenland ice sheets, 4–10 ng g−1 in the Arctic Ocean, 8–14 ng g−1 in Canada, and up to 10–60 and 20–60 ng g−1 in the Russian Arctic and Scandinavia. As for middle latitudes, BC mixing ratio in snow was found to be in the range of 5–70 ng g−1 in central North America (Doherty et al., 2014) and 20–600 and 30–2000 ng g−1 in northwestern and northeastern China (Ye et al., 2012; Wang et al., 2013). The lowest BC mixing ratios in snow were found in Antarctica, being on the order of tenths of a nanogram per gram (Warren and Clark, 1990; Grenfell et al., 1994; Zatko and Warren, 2015). Currently, the best estimation of the present-day radiative forcing (RF) by BC in snow and in melting snow-free sea ice is +0.040 W m−2 (+0.01/+0.09 W m−2) and +0.012 W m−2 (+0.008/+0.017 W m−2) (Bond et al., 2013), respectively. The change in the surface temperature global average resulting from the RF exerted by BC in snow ranges from +0.06 to +0.20 K, while equilibrium change in Arctic surface temperature is estimated to be in the range of 0.50–1.6 K (Bond et al., 2013; Flanner et al., 2007).
RAAs in snow are not only represented by BC since the presence of both soil dust and absorbing organic aerosol (OA) has been observed in the snowpack. Measurements across the Arctic and central North America suggested that 20 %–50 % of the sunlight absorption in the snowpack is due to non-BC RAA particles (Doherty et al., 2010, 2014), while in the Qilian Mountains the snow particulate absorption is dominated by non-BC compounds (around 100 %), according to Wang et al. (2013).
BrC is defined as the radiation-absorbing fraction of OA (Andreae and Gelencsér, 2006; Laskin et al., 2015); it absorbs shortwave radiation with wavelengths less than 400 nm (Lukács et al., 2007; Alexander et al., 2008; Chen and Bond, 2010; Arola et al., 2011; Kirchstetter and Thatcher, 2012). Sources of such absorbing organic matter are still uncertain; observations indicate that BrC is mainly produced by BF combustion, BB, and aging of secondary organic aerosol (SOA) (Bones et al., 2010; Hecobian et al., 2010; Arola et al., 2011; Updyke et al., 2012; Lambe et al., 2013; Laskin et al., 2015; Guang-Ming et al., 2016), while other sources are represented by some aqueous-phase chemical reactions in clouds (Zhang et al., 2017). BrC treatment is poor in current atmospheric models due to lack of mass and absorption observations. For this reason, OA is commonly treated as scattering, and only few studies have investigated the climatic impact of OA as BrC (Wang et al., 2014; Lin et al., 2014; Saleh et al., 2015; Jo et al., 2016; Wang et al., 2018; Brown et al., 2018; Tuccella et al., 2020). The Intergovernmental Panel on Climate Change (IPCC) 5th Assessment Report (AR5) did not analyze the absorption of BrC in snow; however, this aspect was discussed in the IPCC Special Report on the Ocean and Cryosphere in a Changing Climate (SROCC) (Meredith et al., 2019). According to the SROCC, there is low confidence in the attribution of RF of BrC in snow. To the best of our knowledge, the global RF due to the change in OA in snow from preindustrial times was calculated by Lin et al. (2014) only, who reported estimated values ranging from +0.0011 to +0.0031 W m−2.
Soil dust is emitted from arid and semi-arid regions (Choobari et al., 2013) and from soils disturbed by anthropogenic activities (Tegen et al., 2004; Ginoux et al., 2012). The largest amount of dust in snow was found downwind from large sources (Skiles et al., 2018). Soil dust is much less absorbing than BC; however, it may dominate the RF in snow when present in very high concentrations. However, dust emissions have increased (Mahowald et al., 2010), and the dust absorption has a non-negligible effect on springtime Eurasian snow (Flanner et al., 2009; Skiles et al., 2018). Also in this case, AR5 did not assess the radiative forcing of dust in snow; however, the SROCC attributes medium confidence to snow darkening from dust (Meredith et al., 2019).
Some studies have shown that the presence of non-BC that absorbs impurities in snow reduces the influence of BC, especially in regions located downwind from large dust sources (Bond et al., 2013). Flanner et al. (2009) found that the dust deposition on the snowpack decreases the BC RF by 25 %, and, according to Bond et al. (2013), the role of dust in reducing BC RF ranges from 10 % to 40 %. Dang et al. (2017) reported regionally averaged albedo reductions due to RAAs of 0.009, 0.012, and 0.077 for fresh snow in the Arctic, North America, and China, respectively. Moreover, in the same regions, the albedo reductions caused by BC only are 0.005, 0.005, and 0.031. The same authors have also estimated an increase of 20 %–40 % in albedo perturbation in snow that did not contain non-BC RAAs. On the other hand, the presence of different light-absorbing impurities may also impact the BrC RF. Beres et al. (2020) found that the BrC deposition onto pure snow resulted in a local instantaneous RF more than twice as large with respect to a case with dark snowpack. These results highlight the importance of taking into account the concentrations in snow of BC, BrC, and mineral soil dust simultaneously.
RF by snow RAAs is also affected by other uncertainties related to emissions, snow aging, scavenging of the impurities in melting snow, parameterization for snow cover fraction (SCF), and absorption optical properties. The overall error associated with BC RF due to these single uncertainties is −73 %/+117 % (Flanner et al., 2007, 2009; Bond et al., 2013). To the best of our knowledge, there are no studies which quantify all these uncertainties for BrC and soil dust at a global scale.
In this study, we performed a multi-year simulation of the RAA mass concentration with the global chemical and transport model GEOS-Chem (Bey et al., 2001). RAA mass and their optical properties have been simulated using the most recent updates in terms of aging, size distribution, and absorption optical properties, inferred from observational constraints following our previous work (Tuccella et al., 2020). Starting from the GEOS-Chem output, we have diagnosed the mass mixing ratios of RAAs in snow and, subsequently, calculated the RF for different RAA species. In Sect. 2, we provide the description of modeling tools used in this study. In Sect. 3, the modeled RAA content in snow is compared with the available observations, and the associated RF is, therefore, calculated, taking into account the simultaneous presence of BC, BrC, and dust in the snow. Moreover, seasonal and regional differences in the RF of each species are explored. We also provide insights about the contribution of anthropogenic and carbonaceous compounds to the total RF. Finally, we discuss the uncertainties in modeling this kind of forcing associated with the assumptions of RAA optical properties, RAA mixing ratio uncertainty, snow aging, and snow cover fraction. The conclusions are given in Sect. 4.
2.1 GEOS-Chem model
Aerosol mass concentration was simulated with the GEOS-Chem global chemical and transport model, v11-01 (Bey et al., 2001, with updates documented at http://www.geos-chem.org, last access: 3 May 2021). Five years (2010 to 2014) were simulated by the model, with a grid resolution of 4∘ × 5∘ and 47 vertical levels up to 0.01 hPa. Herein, GEOS-Chem was driven by Modern Era Retrospective-analysis for Research and Application version 2 (MERRA2) with assimilation of meteorological data from the Global Modeling and Assimilation Office Goddard Earth Observing System (Rienecker et al., 2011).
BC, BrC, and dust are treated as described in Tuccella et al. (2020). BC emissions and aging were considered to be source-dependent as in Wang et al. (2014, 2018), and hydrophobic and hydrophilic BC was tracked for FF, BF, and BB sources. BrC was inferred from primary organic aerosols (POAs) and secondary organic aerosols, while dust mass concentration was simulated with a sectional approach and emitted dust size distribution following the function of Kok (2011). More details about GEOS-Chem parameterizations and RAA treatment are provided in the Supplement.
2.2 Snow albedo perturbation
The snow albedo reduction by RAAs was calculated through the parameterization of Dang et al. (2015), which is based on the Mie theory for spherical particles (Mie, 1908) and assumes that snow impurities are externally mixed with snow grains. In this scheme, the snow albedo reduction by BC is parameterized for three broadbands – all-wave, visible (VIS), and near-infrared (NIR) – by using a quadratic or cubic polynomial in the BC mixing ratio, whose coefficients are themselves quadratic in snow grain size (Re). It should be noted that the parameterization of Dang et al. (2015) was formulated assuming a size distribution and a complex refractive index for BC. Nevertheless, it can be used for BC particles with different size and refractive index by scaling the mass mixing ratio with the ratio between the mass absorption coefficient (MAC) based on our own assumptions and the coefficient used in Dang et al. (2015). The MAC of given aerosol species at a given wavelength λ is defined as
where Qext is the extinction efficiency, ω the single scattering albedo, Reff the particle effective radius, and ρ the particle density. In our work, the contribution to snow albedo reduction from soil dust and BrC was taken into account through the concept of black carbon equivalent (BCE) (Grenfell et al., 2011), following Ward et al. (2018):
[BC] being the BC-snow mixing ratio; [Dusti] the mixing ratio of dust in the dimensional ith bin; and [BrCBF], [BrCBB], and [BrCSOA] the BrC mixing ratios from BF, BB, and SOA sources, respectively. Once the BCE is calculated, the snow albedo reduction from all absorbing impurities can be estimated with the parameterization for BC proposed by Dang et al. (2015). It should be noted that the MACs that appear in the latter equation are spectrally averaged over an incident solar spectrum, which is characteristic of summer high-latitude conditions. MACs adopted in this work are discussed in the next subsections.
Dang et al. (2015) also provided a scheme for the albedo reduction in snow containing dust particles, gathered through an estimation of the BCE. However, this parameterization is not used in our work for the following reasons: first of all, the scheme is based on assumptions about the refractive index and size distribution. In particular, in the Dang's scheme a single log-normal mode for long-range-transported dust is adopted, while in our model, dust size distribution evolves over time and is not log-normal. Secondly, our simulations included the coarsest dust particles found near the sources, and this aspect could not be well represented by the size distribution adopted by Dang et al. (2015).
Snow albedo is sensitive to grain size, which depends on snow aging processes (Flanner and Zender, 2006; Flanner et al., 2007). Many studies have considered Re to be a constant, while only few works used a physical model to calculate the Re growth (Bond et al., 2013). Uncertainties in Re resulted in an error of −42 %/+58 % in RF estimation (Flanner et al., 2007). For this reason and in order to take into account Re seasonal and geographical variability, we used the exponential relationship proposed by Zhao et al. (2013) to calculate Re, starting from the snow albedo inferred from MERRA2 reanalysis. It should be noted that this is a rough approximation since the relationship of Zhao et al. (2013) was based on the snow reflectance measured near 1030 nm, while we use the snow broadband albedo in our work and experiment. Moreover, the relationship derived from the snow fields of the Heihe River Basin (China) could be inconsistent in other regions.
Finally, impurity mixing ratios in snow were calculated as the ratio between the deposition fluxes of BC, dust, and BrC simulated by GEOS-Chem and MERRA2 total precipitation flux (Kopacz et al., 2011; He et al., 2014). It should be highlighted that the impurity content in snow is not only determined by the accumulation rate from deposition processes, but it is also a function of the scavenged fraction of impurities by melting snow. According to Flanner et al. (2007), uncertainties in the scavenged fraction generate an error in BC RF estimation ranging between −31 % and +8 %.
2.3 Radiation-absorbing aerosol optical properties
In this work, we used the same set of optical properties for RAAs employed by Tuccella et al. (2020). The size distribution for BC is source-dependent according to Wang et al. (2018). The geometrical median radius was fixed to 30 and 70 nm for FF and BF–BB black carbon, while the standard deviations were 1.4 and 1.6, respectively. Following the recommendation of Bond and Bergstrom (2006), the applied refractive index was 1.95–0.79i. The BC density was assumed to be 1.8 g cm−3. Using the Mie theory (Mie, 1908), the resulting MACs at 550 nm were 6.3 and 6.2 m2 g−1 for FF and BF–BB BC, respectively.
The geometrical median radius, standard deviation and density of BrC are 90 nm, 1.6, and 1.3 g cm−3, respectively (Wang et al., 2018). The imaginary part of the BrC refractive index has been inferred starting from the MAC of BF and BB absorbing OA reported by Wang et al. (2018). More details about this calculation are provided in the Supplement. The resulting MACBrC values at 440 nm were 1.56 for BF and 3.08 and 0.92 m2 g−1 for fresh and aged BB. Two different MACBrC values for freshly emitted and aged BB were used with the aim of taking into account the blanching process of aged plumes due to the photochemical aging (Forrister et al., 2015). A MACBrC of 0.3 m2 g−1 at 440 nm was assigned to BrC-SOA, as reported in Wang et al. (2014).
Dust optical properties were also inferred as in our previous work (Tuccella et al., 2020). GEOS-Chem simulates the dust size distribution over four dimensional bins (see Sect. 2.1); however, the finer bin was split into four bins for optical calculations, as in Ridley et al. (2012). The refractive index for mineral dust particles was derived from the dataset provided by Petzold et al. (2009). Under these assumptions, Mie calculation indicates a MAC at 550 nm of 0.057 and 0.048 m2 g−1 for size ranges of 0.36–0.6 and 4.4–6.0 µm, which are representative of the dust particles lying far and close to the sources, respectively.
2.4 Numerical experiments
We carried out a series of numerical experiments in order to study the sensitivity of RAA-snow RF due to (i) the simultaneous presence of several light-absorbing impurities, (ii) their absorbing optical properties, (iii) their emissions and mixing ratios in snow, (iv) snow grain size, and (v) snow coverage fraction. The list of our experiments is reported in Table 1.
1 MACs adopted for these experiments are reported in Table 2. 2 MACs adopted for these experiments are the same as in CTRL (Table 2).
1 MACs reported here are spectrally averaged between 0.3–0.7 µm over an incident solar spectrum characteristic of summer high-latitude conditions. 2 The experiment list is reported in Table 1.
The first simulation performed represented our reference case (CTRL), where a simultaneous presence of BC and BrC is considered in the snow. The absorption enhancement (Eabs) of BC due to the “lensing effect” (Lesins et al., 2002), caused by coating of non-absorbing material, was taken into account, increasing the MAC of aged (hydrophilic) BC by a factor of 1.5, as recommended by Bond et al. (2013). We considered the CTRL simulation to be the “central” (or “mid”) absorption scenario. MACs averaged in the VIS are listed in Table 2, while those adopted for NIR are reported in Table S1 in the Supplement.
In the second simulation, the RF of each single species at a time (OSPT) in snow was calculated. The experiment main purpose was to test how much the presence of more RAAs in snow affects the RF of a single species.
The six perturbed experiments were aimed at evaluating the sensitivity of RF to the assumed absorption aerosol properties. For these experiments, we defined a “high” and a “low” absorption scenario for absorbing aerosol species. Estimation of coated Eabs is highly uncertain; recent studies have found values above the most accepted value of 1.5. Tuccella et al. (2020) reported values in the range of 1.7–1.9 for BC coated by a non-absorbing shell. According to the same authors, Eabs is 2.8–3.4 for BC coated by an absorbing shell (brown carbon). Curci et al. (2019) also estimated similar values. On the other hand, Eabs values could be lower than 1.5. As an example, Cappa et al. (2012) have observed very low values for Eabs (about 1.1). As a consequence, we applied Eabs of 1.9 and 1.1 for the BC “high-absorption” (BC-H) and “low-absorption” (BC-L) scenarios, respectively.
MAC adopted for BrC has been optimized with regional observations in the United States (Wang et al., 2018); therefore, assumed values and estimation may be inconsistent worldwide. MACs used for aged BB BrC were deduced from a limited dataset (Wang et al., 2016) that was not able to provide the most required constraints on the photochemical whitening processes (Wang et al., 2018). Moreover, it is not clear if the blanching processes affect the BF BrC. For this reason, two extreme conditions for BrC absorption have been tested. In detail, a no-whitening process for aged BB BrC was assumed in the high-absorption scenario (BrC-H), while the whitening of BF BrC is considered in the low-absorption scenario (BrC-L). In the latter one, we assumed that the MAC of aged biofuel BrC is reduced by a factor of 2.34 with respect to the CTRL run.
Soil dust absorption and its climatic impact strongly depend on the imaginary part of the refractive index (Pitari et al., 2015b; Tuccella et al., 2020), which is determined by the mineral composition of soil in the source region. Herein, we explore the sensitivity of dust absorption in the snow due to the refractive index. In particular, the dataset of Wagner et al. (2012) was exploited for the high-absorption simulation (DUST-H), while the refractive index from Sinyuk et al. (2003) was used in the low-absorption experiment (DUST-L). As shown in Table 2, the considered dust size ranges of MACs are larger by a factor of up to 3.5 in DUST-H with respect to CTRL. By contrast, MACs of DUST-L are lower by a factor of up to a 1.6 with respect to the reference simulation.
Two of the perturbed experiments were aimed at evaluating the sensitivity of RAA-snow RF to their concentration in the snowpack. The mixing ratio of absorbing impurities in the snow depends on many factors, such as emissions, deposition and precipitation rates, impurity solubility, and snow melting (Flanner et al., 2007; Bond et al., 2013). Previous studies had shown that BC absorption is underestimated in GEOS-Chem, and this was partly related to the uncertainties in both anthropogenic and biomass burning emission inventories (Wang et al., 2014; Jo et al., 2016; Tuccella et al., 2020). Data analysis and modeling revealed that current inventories underestimate the emissions from shipping and petroleum extraction in the Arctic (Tuccella et al., 2017; Law et al., 2017). On the other hand, dust emission is also uncertain. As an example, Kok et al. (2017) reported a range of values within 1000–2700 Tg yr−1 for global PM10 dust based on observational constraints. Furthermore, another uncertainty factor that affects our simulations is associated with the fraction of POA emission we assumed as BrC. In order to evaluate the impact of all these uncertainties in snow RF calculation, we perturbed the RAA mixing ratios in snowpack by doubling (BCE-H) and halving (BCE-L) the BCE.
The last two experiments were performed to test the sensitivity of RAA-snow RF to Re and SCF. As explained in Sect. 2.2, we have estimated Re with a rough method starting from the broadband snow albedo derived from MERRA2 data. In order to explore the impact of uncertainties in RAA-snow RF related to Re estimation, we multiplied (Re-H) and divided (Re-L) the snow grain radius by a factor of 2.
SCF controls the area where RAA-snow RF acts. In models, SCF is usually calculated using the snow depth (Flanner et al., 2007; Bond et al., 2013). According to Flanner et al. (2007), SCF may differ up to a factor of 2 among the various parameterizations, resulting in an uncertainty of −17 %/+8 % in BC-snow RF (Bond et al., 2013). In MERRA2, SCF fraction is parameterized as a function of the snow water equivalent (SWE) (Rienecker et al., 2011). In order to evaluate how SCF uncertainty impacts the RAA-snow RF, SWE has been multiplied (SCF-L) and divided (SCF-H) by a factor of 1.5.
2.5 Radiative transfer model
RAA-snow RF due to snow albedo reduction was calculated with the Rapid Radiative Transfer Model for General Circulation Models (RRTMG) (Iacono et al., 2008). The RRTMG was interfaced with GEOS-Chem output and MERRA2 data as described by Jo et al. (2016) and Tuccella et al. (2020). Aerosol optical properties used for the atmospheric radiative transfer were calculated using the post-processing tool FlexAOD (Curci et al., 2015, 2019).
3.1 Model evaluation
BC and BCE mixing ratios in snow diagnosed from GEOS-Chem deposition fields have been compared with the worldwide observations reported in different works. For the Arctic and North America, we used the data from Doherty et al. (2010, 2014). For China, we inferred the measurements from Ye et al. (2012) and Wang et al. (2013), while for the Himalaya and the Tibetan Plateau the observations were taken from Kopacz et al. (2011). Data for Antarctica were provided from Grenfell et al. (1994), Chylek et al. (1987), Warren and Clarke (1990), and Zatko and Warren (2015).
In Fig. 1, the scatterplot obtained from the comparison between observed and simulated BC mixing ratios in snow surface layer is reported. In addition, results from the comparison are summarized in Table S2. Model simulations were compared to the observed regional median and standard deviation, provided in the reference papers. Where this information was not available, the analysis was carried out by considering the observed regional mean, together with the minimum and maximum values measured in the region of interest. When measurements corresponded to a specific period falling within the time interval of our simulations (2010–2014), we compared the model results for the same time frame. In other cases, the 5-year average over the same months has been used
The R2 coefficient between observed and calculated BC mixing ratios was 0.84. This result indicates that the regional variability in BC in snow, spanning over 5 orders of magnitudes is reproduced by the model. Most parts of modeled values (80 %) were found to drop within a factor of 2 from the observations. This last outcome reflects the model skill in reproducing both the long-range BC transport and the impact of local major sources on the regional snow darkening. In general, the median bias of the modeled BC was −13 %.
As for the Arctic, a significant bias was found in Greenland, during summer: in this area, modeled BC is about 7 times larger than the observed median mixing ratio. As discussed in Doherty et al. (2010), BC concentration in Greenland in summertime is larger in the melting layer (around 10 cm depth) with respect to the surface as BC is left on the surface by the melted water. Since this process is missing in the calculation schemes, it likely explains the obtained model bias in this case. In eastern Russia, the modeled regional median was underestimated by a factor of 3. This bias could be related to both measurement uncertainties and model prediction. In fact, in some sites of eastern Russia, BC measurements were affected by local soil dust and assumptions about the Ångström absorption exponent (AAE), which are made for the BC and non-BC component derivation in snow samples (Doherty et al., 2010). Moreover, some samples were not representative of the regional background because they were affected by local sources from villages (domestic wood-burning) and coal-fired power plants (Doherty et al., 2010), which could not be properly resolved by GEOS-Chem given the raw resolution used in this work.
1 For this experiment, total RAA-snow RF was calculated as the sum of the single species. 2 The lower and upper bounds were calculated by adding in quadrature the RF from each experiment.
As for Antarctica, the model reproduced the observed BC amount in snowpack and sea ice, except for Simple Dome station, where the mixing ratio is underpredicted by 1 order of magnitude. A similar bias was reported by Flanner et al. (2007), although the authors had used a more advanced scheme to calculate BC content in snow. Moreover, the BC concentration measurement at Simple Dome (Chylek et al., 1987) is old (1982–1985) and may not be representative of the present-day Antarctic BC in snow, being much larger than more recent observations (0.20–0.60 ng g−1), as shown in Table 3.
The highest BC mixing ratios in snow are observed in China: the model reproduced the average magnitude of BC in snow detected in several regions of the country, with the exception of the industrial Northeast China district. In this region, predicted BC concentrations are underestimated by a factor of 3 if compared to the typical values in the range of 1000–2000 ng g−1 in snow surface (Wang et al., 2013). This area, where measurements reported by Wang et al. (2013) were collected (Table 3), hosts the highest number of industrial activities. As a consequence, the model negative bias found for this region may be another effect attributable to the adopted model resolution.
In Fig. 2, the scatterplot resulting from the comparison between observed and simulated BCE (which is defined in Eq. 2) mixing ratios in snow surface layer is shown. Numerical results are also reported in Table 3. The R2 coefficient between observed and calculated BCE mixing ratio was 0.60. As for BC, 80 % of the modeled values were within a factor of 2 from the corresponding observations, resulting in a correct simulation of BCE regional variability. The median bias between observed and of modeled BCE was −21 %: the highest BCE bias has been found in two regions of China, in particular, BCE is underpredicted by a factor of 3 in the Qilian Mountains and the northeastern industrial region. By contrast, BCE turned out to be overpredicted by a factor of 3–4 in Greenland during the summer months. In this case, the analysis of the light fraction absorption due to non-BC compounds (fnon-BC) revealed other aspects of the model skill in reproducing the RAAs in snow in terms of biases related to the emissions, transport, and assumptions made for absorbing optical properties.
In Fig. 3, a comparison between calculated and observed fnon-BC is proposed, where an R2 of 0.44 is reported as well as 90 % of the modeled values being within a factor of 2 from observations. Generally, fnon-BC was underestimated by the model, with a median bias of −17 %. The highest bias has been found for seasonal snow in North America. Furthermore, an underestimation of fnon-BC by a factor of 2 has been found in Intramountain Northwest (Rocky Mountains), the northern US Plains (North Dakota), and Canada. In this case, it should be underlined that most parts of the sites in Intramountain Northwest and the northern US Plains are characterized by thin and patchy snow and, therefore, affected by soil dust emitted by local sources (Doherty et al., 2014). This feature is not resolved by the model due to the raw resolution used. Soil dust particles also contribute to absorption in snowy Canadian sites, implying a long-range transport (Doherty et al., 2014) which is not simulated by GEOS-Chem as some local sources are probably missing in the model.
In Greenland during spring, fnon-BC was underestimated by a factor of 2. In this period, snow RAAs in this country are usually dominated by biomass burning (Doherty et al., 2010); therefore, the fnon-BC bias is likely attributable to the BrC treatment in the model. Moreover, the simulated underestimation could be associated with the POA emissions from BB as well as the absorption optical properties assumed to scale aged BB BrC mass in BCE calculation. Finally, in western Russia, the underestimation of BC resulted in a highly biased fnon-BC (factor of 1.5).
In summary, the model evaluation through worldwide observations showed a model skill in reproducing BC and BCE mixing ratios in snow. Obtained biases were mainly linked to the emissions of BC, POA, and dust emissions, while error in BCE and fnon-BC simulations was likely related to the assumptions about the RAA optical properties. A source of uncertainty in model evaluation could be represented by measurement errors. For example, according to Doherty et al. (2010), margins of error in BC and BCE measurements are related to both instrumental errors and assumptions made on the aerosol absorbing optical properties, which results in a total uncertainty estimation up to ±50 %.
3.2 Present-day global radiative forcing
In Fig. 4, the spatial pattern of the annual surface RF present-day average (2010–2014) from all RAAs, BC, BrC, and dust in snow is shown, as estimated from the CTRL run and in all-sky conditions. In the following discussion, anthropogenic RAAs were considered to be particles emitted by FF and BF sources and SOA formed by light photooxidation of aromatic compounds. BC and BrC from BB and biogenic SOA were considered to be natural. Soil dust was also considered to be a natural aerosol, even though about 20 %–25 % of the total present-day emissions are attributed to human activity (Ginoux et al., 2012); these anthropogenic dust sources were not taken into account in this analysis.
Global-average RF associated with all RAAs was +0.068 W m−2. The largest values were found in northeastern China and the Tibetan Plateau. As expected, global RAA-snow RF was dominated by BC RF, resulting in +0.033 W m−2. This value is about 18 % lower than the best estimation of 0.040 W m−2, reported by Bond et al. (2013). In Fig. S1, RF of BC, divided by source, is shown. About 80 % (+0.025 W m−2) of BC-snow RF was due to the anthropogenic sources. FF BC in snow RF acts everywhere, especially in southeastern Canada, eastern Greenland, northeastern China, and the Tibetan Plateau. BF BC showed an impact in eastern Europe, northeastern China, and the Tibetan Plateau. Eventually, BC from biomass burning occurred in Siberia and at high latitudes as a consequence of the boreal fires.
In our model, soil dust is the second light absorber in snow, having an average RF of +0.012 W m−2, which was about 3 times lower than the radiative forcing due to BC. RF of dust in snow was relevant in the Asian regions, especially downwind of the deserts and the Tibetan Plateau, where values up to +1.7 W m−2 are simulated. In some regions of Kazakhstan, Mongolia, Manchuria, the Tibetan Plateau, Pakistan, and Afghanistan, dust-snow RF is on average 2–3 times larger than what is exerted by BC. In Mongolia, dust RF is up to 4 times larger than BC.
Estimation of snow RF for BrC was +0.0066 W m−2, about 5 times lower than what was calculated for BC. Lin et al. (2014) had reported values of 0.0011–0.0031 W m−2 for RF of BrC in snow as a result of an OA emission change of 60 Tg yr−1 since preindustrial times. Starting from this RF, normalized to the emission change, the present-day RF may be estimated by using the current OA emission (124 Tg yr−1) used in Lin et al. (2014). According to this scaling, the resulting RF was 0.0020–0.0055 W m−2; therefore our estimation was above previous upper bounds. In Fig. S2, the snow RF of BrC, divided by source, is displayed. The BF BrC radiative effect was relevant in northeastern China and the Tibetan Plateau, while BB BrC was dominant at high latitudes. Based on our model, BF and BB contribution to annual BrC-snow RF was about 38 % (+0.0025 W m−2) and 47 % (+0.0031 W m−2), respectively. SOA accounts for 15 % (+0.0010 W m−2) of OA absorption, and its effect is limited at high latitudes in late spring and summer.
It should be noted that the sum of BC-, BrC-, and dust-snow RF is lower than the forcing of all RAAs. Albedo reduction does not increase linearly with the addition of RAAs because the light that penetrates in the snowpack decreases as RAA concentration increases (Dang et al., 2017). As a consequence of this non-linearity, it is not straightforward to calculate the relative contribution of each absorbing impurity to total RF. An estimation may be given through the sequential factor separation analysis (Schär and Kröner, 2017); according to this method, non-BC compounds account for about 40 % of the absorption in snow. In addition, we found that carbonaceous aerosols (BC and BrC) control about 75 % (+0.046 W m−2) of snow RF exerted by RAAs. The contribution of anthropogenic emissions to RAA absorption in snow is around 56 % (+0.031 W m−2), meaning that slightly less than half of RAA-snow forcing is due to natural sources.
Total RAA-snow RF estimated in this study is about 6–7 times lower than the direct radiative effect exerted by RAAs (+0.36 and +0.10 W m−2 for BC–BrC mixture and dust, respectively), calculated in our previous study (Tuccella et al., 2020). However, comparing RAA forcings in the atmosphere and in snow by scaling them with their efficacies (Hansen et al., 2005), they are of the same order of magnitude. Forcing efficacy for BC in snow has been estimated to be 3 times larger than the one resulting from CO2 (Flanner et al., 2007; Bond et al., 2013; Boucher et al., 2013). Assuming that the same efficacy is valid for both BrC and dust, the effective present-day RF from RAAs in snow obtained in this study is +0.20 W m−2. The atmospheric forcing estimated in Tuccella et al. (2020) may be scaled with the efficacies reported by Hansen et al. (2005), resulting in a total RAA effective forcing near +0.30 W m−2.
3.3 Present-day regional and seasonal radiative forcing
In this section, a further investigation on the regional and seasonal dependence of RAA-snow RF is proposed. To this aim, the globe has been divided into five regions, as defined in Table 4. In Fig. 5, RF values from RAAs in snow at the regional scale are represented as a function of season. The same figure also reports the relative contribution of each species to total RF.
In the Arctic, total RAA-snow RF was +0.83 and +0.59 W m−2 in spring and summer, respectively: about 40 % of this forcing was attributable to non-BC compounds. According to our model, BrC contributed 14 % of the the total absorption in spring and reached the maximum values (+0.13 W m−2) in summer, where 32 % of the overall RAA RF is concentrated. BrC RF is higher in spring, especially on the snow land of Siberia and at European high latitudes (Figs. S3, S4, S5). This forcing is linked to both BF and BB sources. During summer, BrC RF is dominated by BB as SOA accounted for about 13 % (+0.017 W m−2) of BrC forcing. By contrast, soil dust-snow RF has been found to be at a maximum in spring (+0.12 W m−2), accounting for 24 % of the total forcing, whilst its radiative impact in snow is negligible in summer. Dust RF in the Arctic is limited to the spring months during the Arctic haze transport period, reflecting the absence of significant sources at high latitudes. Arctic dust absorption in springtime is important in Siberia, while a minor impact was found in North America and sea ice (Fig. S6). Moreover, about 60 % of RAA-snow RF in the Arctic was attributable to anthropogenic sources in spring. In summer, the anthropogenic contribution dropped to 30 % as RF is dominated by BB. In fall, the calculated RAA-snow radiative effect was +0.15 W m−2, 30 % of this forcing being due to non-BC aerosols, while 65 % is determined by anthropogenic sources.
The lowest values of RAA-snow RF in the middle latitudes were found in North America, where the total RAA forcing resulted in 0.15 and 0.17 W m−2 in winter and spring, respectively. In North America, non-BC-particle snow RF was the lowest obtained in our regional analysis. BrC and dust RFs showed a peak occurrence in spring, constituting 13 % (+0.014 W m−2) and 12 % (+0.011 W m−2) of the total forcing, respectively. RAA forcing was dominated by anthropogenic sources, 94 % in winter and 77 % in spring; nevertheless, non-BC forcing is likely underestimated. As discussed in Sect. 3.2, our model underestimated fnon-BC by about a factor of 2 in North American mountain regions as local dust sources are missed in the model. As a consequence, dust forcing could be larger than the estimations we reported in our analysis. Doubling BCE attributed to dust in North America, the corresponding RF increased by about 80 %. Anthropogenic sources contributed 94 % and 77 % of the RAA forcing in winter and spring, respectively. However, anthropogenic impact should be reduced by increasing dust contribution to the forcing.
On the European continent, total RAA RF was +0.41 and +0.30 W m−2 in winter and spring, respectively. BC absorption represented slightly more than half of the total forcing. BrC forcing was dominated by BF and located in eastern regions over Europe (Fig. S4). Absorbing OA contributed about 10 % of the total forcing (+0.027 W m−2 in winter and +0.019 W m−2 in spring). The largest non-BC-compound forcing was caused by soil dust. The radiative impact of dust was relevant in eastern Europe and European Alp snowpack, where the dust-snow RF was about 30 %–40 % of the total (+0.027 and +0.019 W m−2 in winter and spring, respectively). Anthropogenic sources explained 67 % of European RAA-snow RF in winter: its contribution dropped to 58 % in spring due to a larger influence of dust.
The largest RAA-snow RF values in the middle latitudes were found in Asia. In this area, RAA RF values were +0.56 and +0.64 W m−2 in winter and spring, respectively. BrC contribution was constant (10 %, about +0.033 W m−2) between December and May. In particular, BF sources impacted the snow of northeastern China, Kazakhstan, southern Russia, and High Mountain Asia, while BB determined some impact in southern Siberia (Fig. S4). Soil dust played a key role in Asia. According to our model, dust-snow forcing was +0.10 and +0.24 W m−2 in winter and spring, respectively. Spring dust forcing was larger than BC (+0.19 W m−2) found in the same regions and constituted about a half of the total forcing. As a result, non-BC compounds gave the largest contribution (+60 %) to RAA-snow RF in Asia during spring. Dust particles caused the anthropogenic source contribution to all RAA forcing to drop from 71 % in winter, to 41 % in springtime. Moreover, it should be noted that Asiatic RAA-snow spatio-temporally averaged forcing was low in summer (+0.045 W m−2), with relevant values in the High Mountain Asia region, where it was up to 3 W m−2. About 60 % of this forcing was due to non-BC compounds, while 10 % and 50 % is produced by BrC and dust, respectively. The middle latitudes of Asia are the only regions where the snow RAAs are relevant in fall. In fall, total RAA forcing was +0.19 W m−2, and about half of this radiative effect is attributable non-BC compounds (10 % and 40 % to BrC and dust, respectively).
According to our model, the lowest RAA-snow radiative effect has been calculated in Antarctica. Here, the highest RF values have been found in winter and fall (austral summer and spring) as they were +0.14 and +0.11 W m−2, respectively. The contribution of non-BC compounds was estimated to be 20 %–30 % (10 %–20 % is due to BrC, and 10 % is from dust), while anthropogenic sources impacted 68 % and 46 % in winter and fall, respectively. The role of soil dust in Antarctica snow darkening could be underestimated in this study as dust emission from arid regions of the Southern Hemisphere calculated by our model was 65 Tg yr−1. For the same hemisphere, Ginoux et al. (2012) calculated an emission of 142 Tg yr−1, half of which is linked to anthropogenic sources. This means that dust emission in the austral hemisphere was underestimated in our simulations by a factor of 2 due to the missing dust anthropogenic sources. As a result, the presence of anthropogenic dust in the model could have increased its role in Antarctica RAA-snow RF and reduced the impact of anthropogenic compounds. Moreover, as discussed in Sect. 3.1, observations used to evaluate predicted RAA concentration in snow are obsolete and may not be representative of the current black carbon level in the Antarctica snow (see Table 3). The most recent measurements of BC, BCE, and non-BC were carried out in 2012 (Zatko and Warren, 2015) and are relative to sea ice of East Antarctica. Although our modeled RAAs in snow are in agreement with these observations, this does not imply the same in other regions of Antarctica. As a consequence, it is difficult to establish the level of uncertainty in RF associated with the snow RAA concentration calculation.
3.4 Discussion of uncertainties
In this section, the impact of RAAs in snow uncertainties on the RF is addressed. The impact of each single uncertainty was evaluated by comparing the perturbed experiments with the CTRL simulation. The results are summarized in Table 3.
First, uncertainty in BC, BrC, and dust due to the presence of multiple radiation-absorbing impurities in the snowpack has been assessed. An increasing radiative effect, with respect to CTRL, was found when RF is calculated for one species at a time (OSPT). According to our model, BC-snow RF increased by 48 % when BrC and dust are not present in the snow. This result is above the upper bound of 10 %–40 %, estimated in previous studies (Flanner et al., 2009; Bond et al., 2013), where only the role of dust was considered in modulating the BC-snow RF. BrC forcing was enhanced by 167 % when black carbon and dust are in the snowpack. This value is in line with Beres et al. (2020), where a reduction in local BrC RF of about a factor of 2 is reported, when the species is added to a dark snowpack. Finally, dust RF increased by 92 % in the OSPT simulation.
Uncertainty associated with the MAC of BC was −18 % and +16 % when an Eabs=1.1 (BC-L) and Eabs=1.9 (BC-H) are applied to the aged coated particles. The estimated range is comparable with those provided by previous works, where BC forcing uncertainty due to assumptions of its optical properties was estimated in the range ±12 % (Bond et al., 2013). BrC forcing increased by 44 % when the blanching of aged BB is missed (BrC-H). Taking into account a whitening process for BF (BrC-L), BrC-snow RF is lowered by 22 %. The uncertainty in soil dust RF associated with the refractive index was −40 % and +25 % for DUST-L and DUST-H simulations, respectively.
Uncertainties in absorbing optical properties of a given species may also affect the forcing of other RAAs deposited on the snowpack. When BC absorption was increased in the BC-H experiment, BrC and dust forcing was reduced by about 10 %. Similarly, in the BC-L simulation, the forcing of BrC and dust increased by 10 % and 5 %, respectively. Uncertainty in BrC absorption properties had a negligible effect (less than 5 %) on BC- and the dust-snow radiative effect. By contrast, the perturbation to soil dust absorption optical properties (DUST-H and DUST-L) affected BrC-snow RF by about 10 %; however, the effect on BC forcing was negligible. The estimated overall uncertainties in RF associated with the absorbing optical properties of RAAs in snow were −18 %/+17 %, −27 %/+45 %, −41 %/+25 %, and −12 %/+10 % for BC-, BrC-, soil dust-, and total RAA-snow RF.
Uncertainties related to RAA mixing ratio in snow obtained by halving (BCE-L) and doubling (BCE-H) the BCE were −36 %/+50 %, −44 %/+44 %, and −35 %/+40 % for BC, BrC, and mineral dust, respectively. The uncertainty in total RAA-snow forcing due to BCE was −36 %/+52 %.
As for uncertainties linked to Re (snow aging), we found ranges of 30 %–36 % for Re-H and 22 %–27 % for Re-L. RAA-snow RF changes due to SCF perturbation were in the range of 22 %–30 % and 11 %–20 % for SCF-H and SCF-L, respectively. The overall uncertainties in RF due to snowpack properties were −19 %/+30 %, −25 %/+40 %, −32 %/+30 %, and −31 %/+46 % for BC, BrC, dust, and total RAAs.
In summary, the estimated overall uncertainty in RF was −49 %/+77 % (0.035–0.12 W m−2), −50 %/+61 % (0.017–0.059 W m−2), −57 %/+183 % (0.0028–0.019 W m−2), and −63 %/+122 % (0.0044–0.025 W m−2) for total RAAs, BC, BrC, and dust, respectively. The total uncertainties were calculated as the root sum of single squared errors, assuming that the single uncertainties are independent. Our results indicate that the lower bounds of total uncertainty in BC, BrC, and dust were comparable. By contrast, upper bounds for BrC and dust were about 2 and 3 times larger than the one of BC. According to our calculation, this uncertainty was related to the simultaneous presence of multiple RAA species in the snowpack (OSPT experiment).
Furthermore, it has to be highlighted that RAA-snow RF can be affected by other uncertainties than what is assessed in our study. In particular, the cloud cover, which affects the incident solar radiation at the surface and RAA optical properties in snow, also depends on the microlocation of impurities (i.e., if the aerosol particles are externally or internally mixed with snow grains). In the second case, some authors estimated a BC absorption about 1.4–2.1 times larger with respect to the external mixing (Hansen and Nazarenko, 2004; Flanner et al., 2012; He et al., 2014). Another uncertainty is related to the snow grain shape: non-spherical grain assumption reduces the BC-snow RF by 20 %–40 % relative to spherical snow grains (He et al., 2014).
We presented a global modeling study to assess the present-day RF in snow due to the most relevant radiation-absorbing aerosols (BC, BrC, and dust). While BC RF in snow has been extensively studied (e.g., Bond et al., 2013; Boucher et al., 2013), the forcing from BrC and dust and associated uncertainties were not assessed in IPCC AR5. According to the IPCC Special Report on the Ocean and Cryosphere in a Changing Climate, there is low and medium confidence in the attribution of RF of BrC and dust in snow, respectively. Moreover, given that the snow albedo change is not linear with the impurity content (Flanner et al., 2009; Dang et al., 2017), RF from RAAs in snow has to be calculated simultaneously taking into account the concentrations of BC, BrC, and mineral soil dust.
Herein, we used the GEOS-Chem global chemistry and transport model to simulate BC, BrC, and dust deposition on the snowpack. The present-day radiative RF due to RAAs in snow was calculated considering the simultaneous presence in the snow of BC, BrC, and dust. BC and black carbon equivalent (BCE) mixing ratios in snow were calculated starting from simulated deposition fields and precipitation fluxes. The obtained BC and BCE concentrations in the snowpack have been validated through worldwide observations. The model was able to reproduce the observed regional variations with an R2 of 0.84 and 0.60 for BC and BCE, respectively. A total of 80 % of the modeled BC and BCE values were within a factor of 2 from the observations. The median bias for the same quantities was −13 % and −21 %. The model also reproduced the range of observed fnon-BC with an R2 of 0.44 and a median bias of −17 %.
According to the model, global-annual-mean present-day RAA-snow RF at the surface was +0.037, +0.0064, +0.013, and +0.068 W m−2 for BC, BrC, dust, and total RAAs, respectively. Non-BC compounds accounted for 40 % (+0.046 W m−2) of RAA-snow global RF, and anthropogenic RAAs contributed 56 % (+0.031 W m−2) of the forcing.
At a regional scale, RF exhibited large variability in terms of intensity and species apportionment. The largest total RAA-snow RF was found in the Arctic during spring (+0.83 W m−2) and summer (+0.59 W m−2), and 40 % of this forcing was due to non-BC compounds. In particular, non-BC spring RF is mainly due to the dust (+0.12 W m−2), while non-BC was driven by BB BrC (+0.13 W m−2) in summer. In the middle latitudes, the most relevant RAA-snow forcing was obtained in Asia, with +0.56 and +0.64 W m−2 in winter and spring, respectively. The BrC contribution was constant during winter and spring (10 %, about +0.033 W m−2), while soil dust played a key role in forcing over Asia: its radiative effect (+0.24 W m−2) was larger than the one of BC and represented 50 % of the total RAA RF in spring. RAA forcing in the High Mountain Asia region was up to 3 W m−2 in summertime, and 60 % of it is attributable to non-BC aerosols. North America exhibited the lowest RAA-snow RF (0.15 and 0.17 W m−2 in winter and spring, respectively) and the lowest non-BC contribution (about 20 %) in the middle latitudes. As for Europe, total RAA RF was +0.41 and +0.30 W m−2 in winter and spring, respectively. BC contributed slightly more than half of the total forcing. The most relevant non-BC was given by dust (30 %–40 % of the total). In Antarctica, the highest values of RF have been found in winter and fall (+0.14 and +0.11 W m−2, respectively), and the contribution of non-BC compounds was estimated to be in the range of 20 %–30 %.
In the Arctic, 60 % of springtime RF was due to anthropogenic sources, while it dropped down to 30 % in summer due to BB. In Asia, anthropogenic compounds contributed 71 % of the total forcing in winter, while the contribution was 41 % in springtime because of the presence of dust. A similar behavior has been found in Europe, while in North America RAA-snow RF was always dominated by anthropogenic emissions.
Finally, we also explored the sensitivity of RF due to the simultaneous presence of multiple RAAs in snow, absorption optical properties, uncertainties in impurity mixing ratio, snow grain size, and snow coverage. The overall uncertainty in RF associated with these factors was −49 %/+77 % (0.035–0.12 W m−2), −50 %/+61 % (0.017–0.059 W m−2), −57 %/+183 % (0.0028–0.019 W m−2), and −63 %/+122 % (0.0044–0.025 W m−2) for total RAAs, BC, BrC, and dust, respectively. These results highlight that uncertainty upper bounds of BrC and dust were about 2 and 3 times larger than the one of BC. This uncertainty was mainly due to the simultaneous presence of multiple absorbing impurities in the snow. Therefore, we may conclude that RAA-snow RF is very sensitive to the concomitant presence of more species, especially for non-BC compounds, given their minor absorption with respect to BC.
Efficacy of RF associated with BC in snow was 3 times larger than forcing from CO2 (Flanner et al., 2007; Bond et al., 2013; Boucher et al., 2013). Assuming the same efficacy for BrC and dust, effective RF exerted by RAAs in snow found in this study was +0.20 W m−2, a value comparable with the RAA effective atmospheric forcing (about +0.30 W m−2) obtained from Tuccella et al. (2020). Given that RF of RAAs in snow acts mainly on the cryosphere, it may potentially have important effects in response to the snow albedo feedback. As a consequence, a reduction in the uncertainties is desirable. According to our results, a first step to reduce uncertainties in RAA-snow RF should be an improvement of the representation of RAAs in snow within models through constraint with local and satellite observations and a better characterization of the emission inventories in current atmospheric models.
|AAE||Absorption Ångström exponent|
|AOD||Aerosol optical depth|
|BCE||Black carbon equivalent|
|DEAD||Dust Entrainment And Deposition|
|Eabs||Black carbon absorption enhancement factor|
|FlexAOD||Flexible aerosol optical depth|
|MAC||Mass absorption coefficient|
|MERRA2||Modern Era Retrospective-analysis for Research and Application version 2|
|POA||Primary organic aerosol|
|Re||Snow grain effective radius|
|RRTMG||Rapid Radiative Transfer Model for General Circulation Models|
|SCF||Snow cover fraction|
|SOA||Secondary organic aerosol|
GEOS-Chem simulations used in this study are accessible at https://doi.org/10.17605/OSF.IO/XNTR8 (Tuccella, 2020). Snow impurity measurements are available in the paper referenced in the text. The FlexAOD postprocessing tool can be provided upon request to email@example.com. RRTMG code is available at this link: http://rtweb.aer.com/rrtm_frame.html (last access: 3 May 2021; Iacono et al., 2008).
The supplement related to this article is available online at: https://doi.org/10.5194/acp-21-6875-2021-supplement.
PT and GP conceptualized the study. PT developed the methodology; PT, GC, and ER developed the software; PT performed the GEOS-Chem and radiative simulations. PT, VC, and GP performed the formal analysis. PT prepared and wrote the original draft. PT, VC, GP, ER, and GC reviewed the original draft. VC and PT administrated the project. PT, GC, and GP acquired the fund.
The authors declare that they have no conflict of interest.
The authors are grateful to the four anonymous reviewers who helped to improve the quality of the initial manuscript.
This research has been supported by the AXA Research Fund (grant no. 2016-ENV-PostDoc-University of L'Aquila) postdoctoral grant.
This paper was edited by Pedro Jimenez-Guerrero and reviewed by four anonymous referees.
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