Seasonal variation and light absorption property of carbonaceous aerosol in a typical glacier region of the southeastern Tibetan Plateau
- 1State Key Laboratory of Cryospheric Science, Northwest Institute of Eco-Environment and Resources, Chinese Academy of Sciences, Lanzhou 730000, China
- 2Atmospheric Sciences and Global Change Division, Pacific Northwest National Laboratory (PNNL), Richland, WA 99352, USA
- 3Collaborative Innovation Center of Atmospheric Environment and Equipment Technology, Jiangsu Key Laboratory of Atmospheric Environment Monitoring and Pollution Control, School of Environmental Sciences and Engineering, Nanjing University of Information Science and Technology, 219 Ningliu Road, Nanjing 210044, China
- 4CAS Center for Excellence in Tibetan Plateau Earth Sciences, Beijing 100101, China
- 5University of Chinese Academy of Sciences (UCAS), Beijing 10049, China
- 6Institute for Climate and Global Change Research, School of Atmospheric Sciences, Nanjing University, Nanjing 210093, China
- 7Collaborative Innovation Center of Climate Change, Jiangsu Province, China
- 8Department of Geography, National University of Singapore, 1 Arts Link, Singapore 117570, Singapore
- 9College of Earth Environmental Sciences, Lanzhou University, Lanzhou 730000, China
- 10College of Geography and Environmental Science, Northwest Normal University, Lanzhou 730030, China
Correspondence: Shichang Kang (firstname.lastname@example.org) and Hailong Wang (email@example.com)
Deposition and accumulation of light-absorbing carbonaceous aerosol on glacier surfaces can alter the energy balance of glaciers. In this study, 2 years (December 2014 to December 2016) of continuous observations of carbonaceous aerosols in the glacierized region of the Mt. Yulong and Ganhaizi (GHZ) basin are analyzed. The average elemental carbon (EC) and organic carbon (OC) concentrations were 1.51±0.93 and 2.57±1.32 µg m−3, respectively. Although the annual mean OC ∕ EC ratio was 2.45±1.96, monthly mean EC concentrations during the post-monsoon season were even higher than OC in the high altitudes (approximately 5000 ) of Mt. Yulong. Strong photochemical reactions and local tourism activities were likely the main factors inducing high OC ∕ EC ratios in the Mt. Yulong region during the monsoon season. The mean mass absorption efficiency (MAE) of EC, measured for the first time in Mt. Yulong, at 632 nm with a thermal-optical carbon analyzer using the filter-based method, was 6.82±0.73 m2 g−1, comparable with the results from other studies. Strong seasonal and spatial variations of EC MAE were largely related to the OC abundance. Source attribution analysis using a global aerosol–climate model, equipped with a black carbon (BC) source tagging technique, suggests that East Asia emissions, including local sources, have the dominant contribution (over 50 %) to annual mean near-surface BC in the Mt. Yulong area. There is also a strong seasonal variation in the regional source apportionment. South Asia has the largest contribution to near-surface BC during the pre-monsoon season, while East Asia dominates the monsoon season and post-monsoon season. Results in this study have great implications for accurately evaluating the influences of carbonaceous matter on glacial melting and water resource supply in glacierization areas.
Carbonaceous aerosols play an important role in Earth's climate system and energy budget (Bond et al., 2007, 2013; Schuckmann et al., 2016). It has sophisticated/complex effects on the human health and living species (Jerret et al., 2005), visibility (Park et al., 2003), atmospheric radiative balance (Bond et al., 2013; Schuckmann et al., 2016), and the surface albedo of snow and ice (Gertler et al., 2016; Kaspari et al., 2014; Niu et al., 2017a, b). Carbonaceous aerosol is an aggregate of thousands of species with various thermal, physicochemical, and optical properties (Andreae and Gelencsér, 2006; Cheng et al., 2011a). In the atmosphere, carbonaceous aerosols affect the radiative balance by absorbing and scattering solar radiation and affecting the properties of clouds (IPCC, 2013; Lohmann and Feichter, 2005; Carslaw et al., 2010). In the cryosphere, deposition of carbonaceous matter on snow and glaciers reduces the surface spectral albedo (snow darkening) (Flanner et al., 2009; Doherty et al., 2013; Qian et al., 2015; Niu et al., 2017a) and accelerates snow/glacial melting (Hansen and Nazarenko, 2004; Xu et al., 2009a).
Carbonaceous matter in smoke from biomass burning and fossil fuel combustion has been identified as the typical atmospheric pollutant since the historical period (Brimblecombe, 1987). Recently, scientific attention has shifted from the role of carbonaceous matter as an atmospheric pollutant to its influence as one of the driving factors of climate change (Andreae, 1995; Andreae and Gelencsér, 2006; Hansen et al., 2005; Ramanathan et al., 2005). Some model simulations proposed that the radiative forcing of black carbon (BC) is comparable to that of methane (Chung and Seinfeld, 2005; Jacobson, 2004), suggesting that BC may be the second most important warming agent (only after CO2) in terms of direct radiative forcing (Jacobson, 2001). Ding et al. (2016) found that BC particles play a key role in modifying and heating the planetary boundary layer (PBL) and enhancing the haze pollution, called the “dome effect” of BC, and suggested an urgent need for reducing BC emissions to mitigate the extreme haze pollution in megacities in China. In addition, high concentrations of absorbing aerosols (e.g., BC, brown carbon, and/or dust) over eastern China during winter and spring were found to be the major reason for the observed recent warming trend (Yu et al., 2001). BC in snow can increase the surface air temperature by approximately 1.0 ∘C over the Tibetan Plateau (TP) and reduce spring snow cover (Qian et al., 2011). Generally, sampled carbonaceous aerosols can be divided into elemental carbon (EC) and organic carbon (OC) using the thermal-optical reflectance (TOR) method (Cao et al., 2010; Chow et al., 1993). EC is also known as BC when measured using optical methods or in aerosol–climate modeling studies (e.g., Cheng et al., 2011a; Ming et al., 2013; Xu et al., 2009b; Wang et al., 2014, 2015). Moreover, in the low-latitude and high-elevation areas, extensive incoming solar radiation and large amount of carbonaceous aerosol deposited on snowpack and glaciers result in surface albedo reduction and the retreat of glaciers in the TP, and this further affects Asian hydrological cycle and monsoon climate (Qian et al., 2011; Qu et al., 2014; Li et al., 2016a). This is closely related to water resources for a large population of local habitants in South Asia (Ramanathan et al., 2005, 2007). Therefore, it is rather important and necessary to carry out carbonaceous aerosol studies in glacierization regions.
The mass absorption efficiency (MAE, m2 g−1) is a typical parameter characterizing the optical (or light-absorbing) properties of aerosols. For EC particles, it is determined by the mass concentration (µg m−3) and absorption coefficient (babs, Mm−1) of EC (Liousse et al., 1993; Cheng et al., 2011b), where babs is the cross section of EC available to absorb light (Bond and Bergstrom, 2006; Knox et al., 2009). MAE of EC is usually estimated using quartz-filter-based methods, which detect the change in the light transmittance through a quartz filter due to the presence of EC particles (Sharma et al., 2002; Knox et al., 2009; Cheng et al., 2011a). Bond and Bergstrom (2006) suggested a mass-normalized MAE of 7.5±1.2 m2 g−1 at 550 nm for uncoated EC particles. However, Ram and Sarin (2009) studied the babs and MAE of EC in aerosols sampled at three typical sites in India, and they found a distinct spatiotemporal variability in babs and EC MAE on a regional scale. Discrepancies are sometimes inevitable for the filter-based techniques related to aerosol–filter interactions (Cheng et al., 2011a; Sandradewi et al., 2008). Moreover, the MAE of EC can be largely influenced by the aerosol mixing state (Bond et al., 2006; Doran et al., 2007; Jacobson, 2001; Schnaiter et al., 2005). It was proposed that non-carbon species (e.g., sulphate, nitrate) can increase the MAE value of EC (Knox et al., 2009) because the coating by other components can focus light into the EC core of the particle (Bergstrom et al., 1982; Cheng et al., 2011a). Enhancement of MAE by coating can be described in terms of absorption amplification that is largely independent of coating thickness (Schnaiter et al., 2005; Knox et al., 2009). Therefore, it is quite necessary to make a further analysis on EC MAE to reduce the uncertainties in evaluating light absorption of carbonaceous aerosols.
Recently, in addition to EC, it has been recognized that certain OC components in carbonaceous aerosol can also absorb light (Andreae and Gelencsér, 2006; Cheng et al., 2011a). However, light absorption by OC has not yet been taken into consideration in many climate models, e.g., various versions of the Community Earth System Model (CESM) (Flanner and Zender, 2006; Wang et al., 2013; Qian et al., 2015; Liu et al., 2016), which causes certain uncertainties in precisely evaluating climate/radiative forcing of carbonaceous aerosol in the atmosphere and snow/ice. The radiative forcing of carbonaceous aerosol remains one of the great challenges in climate simulation (Jacobson, 2001; IPCC, 2013).
In this study, total suspended particulates (TSP) were simultaneously collected at two remote stations on the Yulong Snow Mountain (abbreviated Mt. Yulong), in the southeast fringe of the TP. Small-scale spatial and seasonal variations of atmospheric carbonaceous matter are examined, and the corrected EC MAE is calculated to evaluate the light-absorbing property of carbonaceous aerosol in the typical glacierization area. Cloud-Aerosol Lidar with Orthogonal Polarization (CALIOP) is used to retrieve total attenuated backscatter and subtype information of smoke plumes to help in the source attribution of carbonaceous aerosols in Mt. Yulong.
2.1 Study area and TSP sampling
The study area, Mt. Yulong (26∘59′–27∘17′ N, 100∘04′–100∘15′ E), is the southernmost glaciated mountain in the Eurasian continent (Fig. 1). The Baishui glacier (27∘06′ N; 100∘11′ E) on Mt. Yulong is a typical temperate glacier that has large energy fluxes, particularly at lower snow-covered elevations. The climate of Mt. Yulong is typically affected by the Indian summer monsoon and East Asian summer monsoon (Nie et al., 2017) in the monsoon season (June–September) and characterized by other three distinct seasons: post-monsoon (October–November), winter (December–February), and pre-monsoon (March–May) season (Chen et al., 2015; Cong et al., 2015b; Bonasoni et al., 2010; Niu et al., 2013). Annual precipitation in Mt. Yulong occurs considerably (∼80 %) in the monsoon season (Fig. 2). There is little precipitation in winter when the westerly jet dominates (Liu et al., 2017).
One of the TSP sampling sites is at the elevation of 4510 , which is close to the location of the upper station (27∘06′ N, 100∘11′ E) of the tourism cableway on Mt. Yulong. Ganhaizi (GHZ) basin, the other TSP sampling site (27∘06′ N, 100∘15′ E), is located on the east side and at the foot of Mt. Yulong, at an elevation of 3054 It is separated from the urban area. However, it becomes an increasingly popular tourist destination, with a geological museum and a golf course. Moreover, there is a spacious parking lot and a tourist dining center in GHZ. Besides the major emissions from tourist vehicles, there are some other limited pollution sources, such as agricultural waste burning, biomass burning (open fire), and crustal aerosols (Niu et al., 2014, 2016) near the study sites. These two sampling sites are located on the southeast fringe of the TP, away from urban areas, and thus considered as typical remote areas in the Northern Hemisphere (Li et al., 2016a) and ideal observation areas for atmospheric environment in the glacierization region.
The TSP samples analyzed in this study were collected from December 2014 to December 2016 at these two sites using a particulate sampling apparatus (TH150-A, Wuhan Tianhong Instruments Group). The sampling apparatuses were placed 15 m above the ground, away from the surface dust and any specific pollutant sources. The quality assurance of this apparatus (TH150-A) is demonstrated by the difference between the manually calculated volume of gas and the automatically recorded value. The volume of air was usually calculated automatically by the apparatus. The air (and suspended particulates) was sampled at a flow rate of 100 L min−1 with an accuracy of ±2.5 %, and each sample was collected for 24 h using a Thomas pump (2628TE32, America). The sampling interval for each TSP sample was 6 days. The number of aerosol samples collected at Mt. Yulong and GHZ was 117 and 120, respectively. The collected TSP samples were loaded on 90 mm (in diameter) pre-combusted (heating at 550 ∘C for 6 h in an oven) quartz fibre filters (Whatman Corp.).
After sampling, the quartz filters were wrapped with an aluminum foil and were kept in a refrigerator at 4 ∘C in the Yulong Snow Mountain Glacier and Environmental Observation Research Station of the Chinese Academy of Sciences in Lijiang city and then were transported to the State Key Laboratory of Cryospheric Science, Northwest Institute of Eco-Environment and Resources in Lanzhou for chemical analysis.
2.2 Sample analysis
OC and EC on the quartz filters were analyzed using a Desert Research Institute (DRI) model 2001 thermal-optical reflectance carbon analyzer (Atmoslytic Inc., Calabasas, California) to determine the EC mass and optical attenuation (ATN) (Chow et al., 2001, 2004; Cheng et al., 2011a; Li et al., 2016b; Niu et al., 2017a). We adopted the improved US Interagency Monitoring of Protected Visual Environments (IMPROVE) – a thermal-optical reflectance protocol (Niu et al., 2017b). Every filter was analyzed for a portion of carbon in a 0.502 cm2 punch. A temperature peak (550∘) was designed to reduce the measuring time that EC exposed in the catalyzing atmosphere. The applied heating conditions permitted the separation of EC portions in the O2 (2 %) and helium (98 %) atmosphere and OC portions in a helium atmosphere (Wang et al., 2015; Niu et al., 2017a). The residence time of each heating step was determined by the stabilization of the carbon signal.
2.3 Calculation methods of ATN, MAE, and POC
2.3.1 ATN calculation
The ATN is calculated based on the transmittance signal during the filter analysis, defined as
where I0 and I are the transmittance signal after and before the thermal-optical analysis (Ram and Sarin, 2009). Lights passing through a particle-loaded and a blank filter were simultaneously measured in the determination of ATN by the (thermal-optical reflectance) carbon analyzer. ATN determined by the carbon analyzer is similar to the Aethalometer (Cheng et al., 2011a). Previous studies have demonstrated that the ATN of blank quartz fibre filters averaged 0.00±0.01, suggesting that the ATN of loaded quartz filter could generally be ascribed to the existence of light-absorbing carbon (Yang et al., 2009; Cheng et al., 2011a).
2.3.2 MAE calculation
The mass absorption efficiency (MAE) is calculated as
where ECs (µg C cm−2) is the filter loading amount of EC, which is directly measured from the thermal optical analysis. The filter-based determination of light absorption has many artifacts, though the various scattering effects can be properly corrected by an empirical factor, C. A value of C=3.6 was proposed for the internally mixed atmospheric aerosol when employing the thermal-optical analysis method in several studies (Weingartner et al., 2003; Doran et al., 2007; Ram and Sarin, 2009; Cheng et al., 2011a). The same empirical factor was also used in the optical measurement by the Aethalometer (Ram and Sarin, 2009). There are many factors (e.g., measurement methods, mixed states) accounting for the discrepancy of MAE. The corrected equation of the MAE calculation (i.e., corrected for the multiple scattering effects) performed in this study has greatly diminished the uncertainties (around 15 %). By converting previously published MAE values (Ram and Sarin, 2009) to the equivalent MAE, Cheng et al. (2011a) have found that the equivalent MAE was much lower in the regions severely affected by biomass burning (e.g., Allahabad, India).
The dependence of light attenuation detected at 632 nm on EC loading (ECs) is shown in Fig. 3 to identify the artifact relevant to filter-based measurements. As a result, ATN and ECs correlate well (R2=0.83) with a slope (K) of 0.08 m2 g−1 and an intercept (b) of 0.35 m2 g−1 for our samples at the Mt. Yulong sampling site. Strong correlation (R2=0.62) between ATN and ECs also exists for the GHZ sampling site, with K=0.08 m2 g−1 and b=0.45 m2 g−1. Strong dependence of ATN on ECs has been found in the present study, and artifacts associated with filter-based method was not identified and thus can be neglected.
2.3.3 Primary OC (or POC) calculation
where (OC ∕ EC)min is the minimum OC ∕ EC ratio in a specific set of data, the same sets of samples as used in this study. OCpri indicates the POC content.
2.4 Model experiment
We use a global aerosol–climate model, the Community Atmosphere Model version 5 (CAM5), equipped with a BC (or EC) source tagging technique (Wang et al., 2013, 2014; Zhang et al., 2015) to help estimate the source attribution of BC in the Mt. Yulong area. The four-mode modal aerosol scheme of CAM5 recently developed by Liu et al. (2016) is used here, in which BC and primary OC particles are emitted into a primary-carbon mode. Then they grow through condensation of gas-phase precursors (e.g., sulfuric and organic gases) and move to the accumulation size mode, where hygroscopic aerosol particles, including carbonaceous aerosols, are subject to wet removal by precipitation.
The CAM5 experiment is conducted for 5 years (2010–2014) at a horizontal grid spacing of and 30 vertical levels. The sea surface temperatures and sea ice concentrations are prescribed with observations, and winds are constrained with reanalysis from NASA Modern-Era Retrospective Analysis for Research and Applications (MERRA) (Rienecker et al., 2011; Ma et al., 2013). Monthly mean anthropogenic and open fire emissions (Hoesly et al., 2018; van Marle et al., 2017), including primary OC and BC, used in the simulation come from the recently released datasets for the Coupled Model Intercomparison Project Phase 6 (CMIP6), which are only available up to year 2014. Therefore, the model experiment is not designed to simulate the 2-year observations of aerosols in TP, but rather for a recent time period (2010–2014) to estimate the mean source attributions and seasonal variations of near-surface BC concentrations.
3.1 Characteristics of the carbonaceous aerosols
Temporal variations of carbonaceous matter measured from Mt. Yulong are shown in Fig. 4. Distinct seasonal differences presented during the sampling time period. The winter season and post-monsoon season had higher concentrations of carbonaceous matter in the TSP during the 2 years, which is consistent for EC, OC, and POC. However, the OC ∕ EC ratio showed an opposite seasonal contrast. Monsoon season in 2016 had the lowest carbonaceous matter contents in the 2-year time period (Fig. 4), whereas the concentrations of OC, EC, and POC in the monsoon and pre-monsoon season in 2015 presented relatively high and low values, respectively. This is uncharacteristic, compared to the general seasonal variations of atmospheric chemistry (Kang et al., 2004, 2007; Niu et al., 2013, 2016). It is quite likely that frequent rainfall events with occasional dust (e.g., Dong et al., 2011; Niu et al., 2014) from anthropogenic activities (Shrestha et al., 2000) during the monsoon in 2015 are responsible for this unusual phenomenon (i.e., relatively high content in monsoon season in 2015). Note that the minimum value of the OC ∕ EC ratio is used in the POC calculation. It varies greatly among different seasons (i.e., 0.38, 0.71, 0.42, and 0.35 for winter, pre-monsoon, monsoon, and post-monsoon in Mt. Yulong, respectively), so seasonal minimum values are used to estimate POC concentrations in the corresponding seasons.
In comparison to Mt. Yulong, the trends of carbonaceous matter from the GHZ basin presented more distinct seasonal variations (Fig. 5); i.e., the monsoon season regularly had the lowest concentrations of EC, OC, and POC. The OC ∕ EC ratio was consistently opposite to that; e.g., higher values of OC ∕ EC appeared in monsoon seasons. The lower ratio of OC ∕ EC in the other seasons (winter, pre-monsoon, post-monsoon) was probably due to the less photochemical production of secondary organic compounds as coating material on EC particles (Knox et al., 2009; Cappa et al., 2012). In addition, seasonal changes in EC and OC sources (e.g., biomass burning vs. fossil fuel combustion) might play an important role for the variations of OC ∕ EC ratios. Obviously higher EC and OC concentrations were found in the post-monsoon season at the Mt. Yulong site and in the winter season at the GHZ site (Figs. 4 and 5) when wet removal by precipitation is inefficient. This suggests the importance of seasonal changes in sources (Carrico et al., 2003; Cong et al., 2015b; Wan et al., 2017). In addition, the OC ∕ EC ratio was usually employed to evaluate the combustion fuel sources. Previous studies reported that the global mean of OC ∕ EC by biomass burning was higher than fossil fuel burning (Bond et al., 2004; Cao et al., 2010; Liousse et al., 1996). Seasonal differences in vehicle emissions from touring buses and private vehicles in the GHZ basin might have played an important role in the seasonal variations of OC ∕ EC ratios.
Table 1 summarizes statistical results of EC, OC, and POC concentrations in atmospheric aerosol from Mt. Yulong. The annual mean EC concentration was 1.53±1.49 µg m−3, with the sampled values ranging from 0.02 to 6.83 µg m−3 during the study period (December 2014–December 2016). The post-monsoon season had the highest EC content of 3.51±1.20 µg m−3, ranging from 1.22 to 5.80 µg m−3. The annual average OC concentration was 1.65±1.14 µg m−3, with the lowest concentrations in the monsoon season (1.34±0.90 µg m−3) and the highest concentrations in the post-monsoon season (OC: 2.57±1.30 µg m−3). Similar seasonal differences were also found in other areas such as Lumbini, Nepal (Wan et al., 2017); Nepal Climate Observatory – Pyramid (NCO-P) (Bonasoni et al., 2010); Kanpur, India (Ram et al., 2012); and Delhi, India (Mandal et al., 2014). Moreover, monthly averaged EC and OC concentrations were analyzed for Mt. Yulong (Fig. 6). It shows that from the monsoon season to the post-monsoon season (particularly from September to December), EC concentrations were higher than that of OC. A large amount of biomass burning emissions in the high atmosphere (around 5000 ) in Mt. Yulong were probably transported from distant source regions which can be determined by the analysis of CALIOP retrievals and source apportionment of carbonaceous aerosols (see Sect. 3.4). In addition, we performed the trajectory analysis with the HYSPLIT model. From the monsoon season to the post-monsoon season, the trajectories of air mass reaching the sampling location changed much. In the monsoon season, the air mass (and pollutants) mainly originated from southwest and southeast monsoons, while in the post-monsoon season it mainly came from the west (Fig. 7). The annual mean OC ∕ EC ratio was found to be highest in the monsoon season and lowest in winter. The aging process of EC (or soot) resulting from photochemical oxidation by molecular O2 and the photooxidation of OC (Han et al., 2012) were likely involved and increased the OC ∕ EC ratio. Photochemical reaction can change their physical and chemical properties from the original molecule of the substance (alkyne C-H (≡C-H) and aromatic C-H (Ar-H)) (Kirchner et al., 2000; Cain et al., 2010). When this occurs, these molecules tend to form a new structure by combining with each other or with other molecules (carbonyl C=O and ether C−O) (Daly and Horn, 2009; Cain et al., 2010; Nieto-Gligorovski et al., 2008), which may change the state of OC, EC, or OC ∕ EC ratios. The photochemical oxidation by O2 under sunlight is an important aging process for EC (Han et al., 2012). Statistical results of EC, OC, and POC concentrations in aerosol from the GHZ site are shown in Table 2. The annual average EC concentration, 1.50±0.90 µg m−3, is comparable with that from Mt. Yulong (1.53±1.49 µg m−3). However, the annual average concentration of OC, 3.50±1.50 µg m−3 was significantly higher than that from Mt. Yulong. Remote sources are likely to have a similar impact on aerosols over the two sites that are fairly close to each other. Therefore, the additional OC in the GHZ basin was more likely contributed by local sources such as fossil fuel (vehicle) emissions associated with the frequent and intense tourism activities, which is totally different from that of Mt. Yulong. Maximum seasonal mean EC and OC concentration occurred in the winter season (EC: 2.42±0.74 µg m−3, OC: 4.09±1.70 µg m−3) in the GHZ basin, and their lowest concentrations conventionally occurred in the monsoon season (EC: 0.75±0.30 µg m−3, OC: 2.80±0.80 µg m−3). The seasonal variation of carbonaceous aerosols found in the GHZ basin was different from that found in Mt. Yulong. It is likely related to the distinct elevation difference (nearly 1500 m) and different amount of local human activities (here mainly referring to tourism-related activities) between the Mt. Yulong and the GHZ sampling sites. The GHZ site location is close to a parking lot for private vehicles and touring buses and a visitor service center that involves food cooking. These tourism activities can contribute to local emissions of carbonaceous aerosols and precursor gases for OC (Borrego et al., 2000; Cong et al., 2015a; Shi et al., 2017). However, we don't have direct observational evidence to support this.
The OC ∕ EC ratios at the two sites were relatively low, and they have distinct seasonal variations and spatial differences over the Mt. Yulong region. The annual average value was 2.06±3.38 for Mt. Yulong, with the highest value occurring in the pre-monsoon season (3.67±5.70) and the lowest value in the post-monsoon season (0.79±0.40) (Table 1). Monthly variation of the average OC ∕ EC ratio was determined by the relative concentrations of EC and OC in aerosol; for example, the lowest OC ∕ EC ratio occurring in post-monsoon was due to substantially high EC concentrations in that season (Fig. 6). The annual mean OC ∕ EC ratio in samples from the GHZ basin was 2.90±1.80, while the monsoon season had the highest value (4.40±2.00) and the winter season had the lowest value (1.93±1.58) (Table 2). Previous studies suggested that OC ∕ EC ratios from biofuel and biomass burning emissions are generally higher than those from fossil fuel combustion (Cao et al., 2013; Ram et al., 2012; Cong et al., 2015b; Wan et al., 2017). Strong photochemical reactions (due to extensive solar radiation) (Fig. 2) and tourism activities in the monsoon season (is the peak season for tourism) were likely the main factors that result in relatively high OC ∕ EC ratios in GHZ. In addition, high OC ∕ EC ratios are closely related to the OC concentration (2.80±0.80 µg m−3) in the monsoon season in the GHZ site (Table 2) when extensive photochemical processes occurred (e.g., Antony et al., 2011; Schneidemesser et al., 2009).
3.2 Optical properties of EC
The corrected MAE values of EC at 632 nm (calculated using the equation in Sect. 2.3.3) were 7.38±1.01 and 6.25±0.46 m2 g−1 for Mt. Yulong and GHZ samples, respectively. The EC MAE has distinct seasonal variations, with the peak of EC MAE values in the pre-monsoon and monsoon seasons at Mt. Yulong and GHZ, respectively (Fig. 8). The high MAE values suggest an enhancement of MAE (or absorption amplification) by external coating with OC (Cheng et al., 2011a; Knox et al., 2009; Schnaiter et al., 2005). Strong seasonal and spatial differences of EC MAE values in Mt. Yulong and GHZ largely related to OC abundance. Furthermore, correlation analysis among MAE and OC, ECs concentrations, OC ∕ EC and POC ∕ OC ratios in Mt. Yulong, and GHZ aerosols were performed. Strong correlations were found between EC MAE and the OC ∕ EC and POC ∕ OC ratios (R2=0.55 and 0.40, respectively, p<0.01) as well as ECs (R2=0.58, p<0.01) in Mt. Yulong aerosol (Fig. 9), while the coefficient of determination R2=0.57 (p<0.01) for MAE and the OC ∕ EC ratio, R2=0.47 (p<0.01) for MAE and POC ∕ OC ratio, and R2=0.69 (p<0.01) for MAE and ECs in GHZ aerosol (Fig. 10). As expected, correlation between MAE and OC is weak for aerosols at Mt. Yulong (R2=0.18, p<0.01) and GHZ (R2=0.11, p<0.01). The strong correlations between MAE and the OC ∕ EC and POC ∕ OC ratio appear to be influenced by the abundance of OC and other particulates (e.g., sulfate) (Omar et al., 1999). The availability of POC for external coating is responsible for the variations of mean EC MAE (Knox et al., 2009). Values of atmospheric EC MAE are also dependent on the extent of internal-mixing of the EC with other substances (Cappa et al., 2012; Schnaiter et al., 2005). Atmospheric EC light absorption is linearly proportional to the EC concentration since EC particles are small enough (Schwarz et al., 2013).
Many previous studies have quantified the EC MAE values at various sites (Bond and Bergstrom, 2006; Cheng et al., 2011a; Knox et al., 2009; Ram and Sarin, 2009; Li et al., 2016c). However, large uncertainties exist among different calculation approaches. Measurement methods of ATN and ECs (various temperature protocols) definitely affect the EC MAE (Cheng et al., 2011a, b; Li et al., 2016c). In addition, brown carbon (BrC) appearing in the particle mixture can decrease the EC MAE (Jeong et al., 2004; Hecobian et al., 2010). BrC is less absorptive compared with pure EC (Cheng et al., 2011a). BrC emitted from biomass burning has considerably lower MAE values (Jeong et al., 2004), whereas coating by organic aerosol or mixing state can enhance the MAE values (Knox et al., 2009; Zhang et al., 2008). Higher absorption cross sections result from coating processes in the atmosphere (Andreae and Gelencsér, 2006; Bond et al., 2013). EC particles in aerosol, due to condensation processes and/or cloud processing, acquire non-absorbing coatings (mainly sulfate and OC), which lead to absorption enhancements (Andreae and Gelencsér, 2006; Fuller et al., 1999; Schnaiter et al., 2005).
3.3 Controls of carbonaceous matter components
Our results show that carbonaceous matter (EC, OC) in aerosol exhibited a discernable small-scale spatial variation between Mt. Yulong and GHZ. In addition to the elevation difference, other potential factors such as the greater number of tourism activities near GHZ than at Mt. Yulong could partly account for the difference.
In addition, inter-annual differences of carbonaceous aerosol from Mt. Yulong and GHZ were also distinct (Fig. 11). The annual mean concentrations of carbonaceous matter collected in 2016 were lower than those in 2015 for the two sites (Fig. 11a and b), which could be partly due to the strict mitigation measures that improved the local atmospheric environment in the Mt. Yulong region. For example, the amount of soot emissions (2.44 Tg C) in 2016 were reduced by 21.76 % compared to 2015 in the Yunnan province (http://www.zhb.gov.cn/, last access: 12 October 2017), where Mt. Yulong locates. Other factors likely contributed to the inter-annual difference as well. The amount of precipitation is important to determine aerosol wet removal from the atmosphere during the transport (e.g., Wang et al., 2013). The stronger precipitation in 2016 than in 2015 at Mt. Yulong and GHZ (Fig. 11a and b) partly explains the smaller carbonaceous aerosols mass concentrations in 2016. The average OC ∕ EC ratios also decreased in 2016 compared to 2015, whereas the mean POC ∕ OC ratios have no obvious difference between the 2 years in both Mt. Yulong and GHZ (Fig. 11).
We also compare atmospheric EC concentrations in Mt. Yulong with other (results derived from TSP samples) interested areas. It shows that EC concentrations in Mt. Yulong aerosol were relatively low and, among the compared values, most of EC concentrations were within the range of 1.0–2.5 µg m−3 (Fig. 12), while some of values were extremely low (close to 0.5 µg m−3) or high (above 6.0 µg m−3). The low EC concentrations were typically found in the TP, e.g., QOMS (i.e., Qomolangma Station for Atmospheric and Environmental Observation and Research, Mt. Everest; Cong et al., 2015b), pre-monsoon season in Mt Yulong, whereas the EC concentrations in Agra, India (6.1±0.83 g m−3) (Pachauri et al., 2013) were almost 3-fold higher than the values found in Mt. Yulong. Agra and Lumbini have been identified as regions in the world that are highly affected by biomass burning (Wan et al., 2017). A large amount of carbonaceous aerosols emitted from those regions can reach Mt. Yulong by crossing the Himalayas (e.g., Lüthi et al., 2014), which substantially influence the Mt. Yulong region.
3.4 Source apportionments of carbonaceous aerosols
Aerosol vertical distributions from CALIOP retrievals often reveal that the smoke plume could reach approximately 6 km (Fig. 13), which is higher than most of the mountains and mountain glaciers in the Himalaya regions. Some typical CALIOP–CALIPSO (Cloud-Aerosol Lidar and Infrared Pathfinder Satellite Observations) transects, having strong backscattering signal (i.e., 532 nm total attenuated backscatter), show spatially continuous atmospheric pollutant layers from the ocean all the way to Mt. Yulong (Fig. 13), indicating a penetration of smoke plume into the TP. Carbonaceous aerosol is an important anthropogenic driving force of the observed changes in the high elevations (>5000 ) and remote regions (such as the TP and Himalayas region) (Lau et al., 2010; Ramanathan and Carmichael, 2008). It was reported that the pre-monsoon season is the major vegetation-fire period in the foothill areas of the southern Himalayas (Vadrevu et al., 2012; Putero et al., 2014), and the winds surrounding the Himalayas and TP could facilitate the transport of carbonaceous matter from South Asia to the Himalayas (Cong et al., 2015a; Dong et al., 2017b; Lau et al., 2010).
We analyzed the CAM5 model results to quantify the source attributions of BC in the Mt. Yulong area. BC emissions from each of the four source regions in the surrounding area (i.e., South Asia, East Asia, Middle East, and Southeast Asia) are explicitly tracked. Figure 14 shows the annual and seasonal mean relative contributions from the tagged source regions. The two sampling sites are located in the same model grid box, as marked in the figure. The modeled near-surface BC is predominately (more than 90 %) from South Asia and East Asia. East Asia has a dominant contribution in the monsoon, post-monsoon and winter seasons, while South Asia dominates in the pre-monsoon season (Table 3). As discussed by Wang et al. (2015), circulation patterns during the monsoon and non-monsoon seasons largely determine the seasonal variations in the transport of aerosols from the different major sources to the southeastern TP. Strong precipitation during the monsoon season can substantially remove atmospheric BC during the transport, especially from South Asia. Although smoke plumes can sometimes be lifted over the natural block of the Himalayas, they provide relatively less important contributions to the surface than to the upper-level BC concentrations. According to our climate model results, emissions (2010–2014) from East Asia, including local sources accounted for in the emission dataset, show a dominant contribution to the near-surface BC at the Mt. Yulong sites during the monsoon (78 %) and post-monsoon (68 %) seasons, as well as the winter season (53 %). The seasonal changes in source apportionment also have implications on the cause of variations in OC ∕ BC ratios over the southeastern TP (e.g., Wang et al., 2015).
Carbonaceous aerosols from the Mt. Yulong region and GHZ basin were measured to investigate the small-scale spatiotemporal variations and light-absorbing properties. Results of the first 2 years of continuous observations show that the annual mean EC and OC aerosol concentrations were 1.51±0.93 and 2.57±1.32 µg m−3, respectively.
Concentrations of carbonaceous matter displayed distinct seasonal differences, with the lowest content found in the monsoon season and the highest concentration in winter season. Monthly mean EC concentrations from the monsoon to post-monsoon season were higher than OC, which shows a large impact from biomass burning emissions in the Mt. Yulong region. The seasonal differences of carbonaceous matter found in the GHZ basin were different with that in Mt. Yulong; distinct elevation differences and different degrees of human (or tourism-related) activities between the two sites were the main reasons for the discrepancy. Furthermore, high carbonaceous matter associated with OC in the GHZ basin was mainly contributed from vehicle emissions. Therefore, there was a discernable spatial difference in the concentrations of carbonaceous matter in this glacierized region. Moreover, inter-annual differences of carbonaceous aerosols in Mt. Yulong and GHZ were also distinct. The annual mean concentrations of carbonaceous matter in 2016 were lower than those in 2015, partly indicating the improvement of local air quality in the Mt. Yulong region.
The annual mean OC ∕ EC ratio was 2.45±1.96 in Mt. Yulong, with the highest value in the monsoon season (4.4±2.0) and the lowest in the post-monsoon season (0.79±0.4). Strong photochemical reactions and local tourism activities in the monsoon season were likely the main factors resulting in relatively high OC ∕ EC ratios in the Mt. Yulong region, particularly in the GHZ basin.
EC MAE was quantified using a thermal-optical carbon analyzer and was measured at 632 nm under the quartz-filter-based method. The corrected mean EC MAE at 632 nm was 6.82±0.73 m2 g−1 in the Mt. Yulong region, comparable with the results in other studies. The strong correlations were found between EC MAE and POC ∕ OC, OC ∕ EC, and ECs in aerosol. Obvious seasonal variations and the discernable spatial difference of EC MAE in the study area were largely related to the OC abundance. The enhancement of MAE was mainly due to external coating of the OC and/or mixing state (internally mixed).
To quantitatively estimate the source apportionment of EC (or BC) in the Mt. Yulong area, we used a global aerosol–climate model, in which BC emissions from four regions (i.e., South Asia, East Asia, Middle East, and Southeast Asia) are explicitly tracked. The 5-year (2010–2014) mean results show that East Asia has the largest contribution (52 %) to the annual mean near-surface BC concentration in this area, followed by South Asia (43 %). There is a significant seasonal variation in the source apportionment. East Asia shows a dominant contribution to the near-surface BC in the monsoon and post-monsoon seasons, while South Asia shows a dominant contribution to the near-surface BC in the pre-monsoon season.
The supplement related to this article is available online at: https://doi.org/10.5194/acp-18-6441-2018-supplement.
The EC and OC data are provided in the Supplement.
The authors declare that they have no conflict of interest.
This article is part of the special issue “Study of ozone, aerosols and radiation over the Tibetan Plateau (SOAR-TP) (ACP/AMT inter-journal SI)”. It is not associated with a conference.
This work was supported by the National Natural Science Foundation of China (41601071, 41721091, 41630754) and the Key Research Program
for Frontier Science of Chinese Academy of Sciences (QYZDJ-SSW-DQC039); the independent program of SKLCS (SKLCS-ZZ-2017) and the
Chinese Academy of Sciences (CAS) Light of West China Program (Y62992);
and the China Postdoctoral Science Foundation (2016T90963, 2015M582725)
and Jiangsu Key Laboratory of Atmospheric Environment Monitoring and Pollution Control (KFK1509). Rudong Zhang acknowledges support from NSFC (41605041), Jiangsu Provincial Science Fund (BK20160621),
Fundamental Research Funds for the Central Universities (020714380020) and International Postdoctoral Exchange Fellowship
(20160046). Hailong Wang and Yun Qian acknowledge support from the US Department of Energy (DOE), Office of Science, Biological and
Environmental Research as part of the Earth System Modeling program. The Pacific Northwest National Laboratory (PNNL) is operated for
the DOE by the Battelle Memorial Institute under contract DE-AC05-76RLO1830. The model simulations were performed using PNNL Institutional
Edited by: Xiaobin Xu
Reviewed by: two anonymous referees
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