Biomass-burning-induced surface darkening and its impact on regional meteorology in eastern China
Biomass burning has attracted great concerns for the emission of particular matters and trace gases, which substantially impacts air quality, human health, and climate change. Meanwhile, large areas of dark char, carbon residue produced in incomplete combustion, can stick to the surface over fire-prone areas after open burning, leading to a sharp drop in surface albedo, so-called “surface darkening”. However, exploration into such surface albedo declines and the radiative and meteorological effects is still fairly limited. As one of the highest-yield agricultural areas, eastern China features intensive straw burning every early summer, the harvest season for winter wheat, which was particularly strong in 2012. Satellite retrievals show that the surface albedo decline over fire-prone areas was significant, especially in the near-infrared band, which can reach −0.16. Observational evidence of abnormal surface warming was found by comparing radiosonde and reanalysis data. Most sites around intensive burned scars show a positive deviation, extending especially in the downwind area. Comparisons between “pre-fire” and “post-fire” from 2007 to 2015 indicated a larger temperature bias of the forecast during the post-fire stage. The signal becomes more apparent between 14:00 and 20:00 LT. Weather Research and Forecasting model coupled with Chemistry (WRF-Chem) simulations suggest that including surface darkening can decrease model bias and well-captured temperature variation after burning at sites in fire areas and their adjacent area. This work highlights the importance of biomass burning induced albedo change in weather forecast and regional climate.
Biomass burning (BB) refers to open or quasi-open combustion of plants or organic fuels, including forest fires, savannah fires, peat burning, and crop residue burning in fields (Andreae, 1991; Andreae and Merlet, 2001; Fearnside, 2000; Thompson, 1996). Intensive BB events occur across the world every year and pose great threats to life and the property of human beings (Bowman and Panton, 1994; Duncan et al., 2003; Kaiser et al., 2012; Streets et al., 2003; Uhl and Kauffman, 1990). Apart from this, BB has received widespread attention due to air pollution, health threats, and climate change caused by the large amount of particulate matter, trace gases, and greenhouse gases it releases (Chan and Yao, 2008; Chang and Song, 2010; Chen et al., 2017; Crutzen and Andreae, 1990; Crutzen et al., 1979; Hansen et al., 2005; Haywood and Ramaswamy, 1998; Hobbs et al., 1997; Langmann et al., 2009; Podgorny et al., 2003). However, the impact of BB is much more than that. BB can directly destruct vegetation covers and affect soil properties over fire-prone areas (Certini, 2005), and it is considered as one of the most important factors influencing the global terrestrial ecosystem (Fearnside, 2000).
Since open BB tends to occur directly on land surface, vegetation covers will be destructed, and the underlying surface properties will be affected straightway (Certini, 2005; Myhre et al., 2005). Among them, surface albedo is highly sensitive to BB (Jin and Roy, 2005). Due to the cover of black charcoal produced in incomplete combustion, sharp surface albedo decline can be observed over fire-prone areas, which has been proven on several kinds of vegetation covers, including savannah and forest (Govaerts et al., 2002; Jin and Roy, 2005; Myhre et al., 2005; Roy and Landmann, 2005). This kind of “surface darkening” can last for about 1 week or even longer if it is dryer and calmer, before char materials are removed by weathering and vegetation starts to regenerate (Amiro et al., 2006; Beringer et al., 2003; Bremer and Ham, 1999; Trigg and Flasse, 2000; Tsuyuzaki et al., 2008; Veraverbeke et al., 2012). The magnitude of such surface albedo decline depends on fire intensity and can be up to half of pre-fire values (Veraverbeke et al., 2012). Decreased surface albedo enhances the capacity of fire-affected surface to absorb solar radiation under clear-sky conditions, perturbing the surface energy budget and the process of land–atmosphere interaction, and then modifying local or even regional circulation (Gatebe et al., 2014). These changes in meteorological parameters will be important for weather and air quality forecast (Ding et al., 2013a; Yang et al., 2019; Zhang et al., 2016).
Though restrictions have been imposed, severe and large-scale BB events still occurred frequently all over the world in recent years (Abatzoglou and Williams, 2016; Nolan et al., 2020). Moreover, threats from global fire activities are still increasing dramatically with climatic and anthropogenic drivers (Marlon et al., 2009; Pechony and Shindell, 2010; Van Der Werf et al., 2006). These facts emphasize the urgent need for further research on the impact of BB, to improve the human ability to predict future weather and climate (Hansen et al., 2005). Globally, BB events occur with significant seasonal variations and distinct regional characteristics (Duncan et al., 2003; Hao and Liu, 1994; Kaiser et al., 2012; Streets et al., 2003; Uhl and Kauffman, 1990). It is noteworthy that agricultural burning is still very common in many developing countries, mainly during post-harvest periods, for the purpose of clearing farmland and providing ash fertilization for the crop rotation (Gao, 2002; Ravindra et al., 2019; Tipayarom and Kim Oanh, 2020). However, exploration into such fire-induced decreased surface albedo and its radiative and meteorological effects is still fairly limited.
As for China, with the world's top-ranked crop production across the world, about 122 Tg of crop residue is burned on site annually (Yan et al., 2006). Eastern China, especially the middle and lower reaches of the Yellow River and Yangtze River, features a large plain area and dense population with high agricultural production (Li et al., 2016). Eastern China has been characterized by intensive straw burning every June, the harvest season for winter wheat (He et al., 2007; Huang et al., 2012a, 2018; Li et al., 2016; Yang et al., 2013; Yin et al., 2019). After revolution in rural fuel structure, farmers, who are eager to deal with tons of wheat straw, always resort to burning on site rather than taking it as fuel (Lu et al., 2011; Yan et al., 2006; Zhu et al., 2019). Hence, the wheat straw burning is exceedingly dense in both time and space (Huang et al., 2012b; Yang et al., 2008). This phenomenon not only poses alarming threats to air quality and human health (Ding et al., 2016; Nie et al., 2015) but also brings great challenges to weather and climate forecast (Ding et al., 2013b; Huang et al., 2016; Wang et al., 2018; Xu et al., 2018; Zhou et al., 2018).
Based on years of satellite fire counts in eastern China, the most severe straw burning happened in June 2012 (Huang et al., 2012b). The most concentrated area of burning in eastern China is the Yellow–Huai River area (YHR), which connects the middle and lower reaches of the Yellow River and Yangtze River. YHR is the major wheat-producing area in China (Lei and Yuan, 2013). An extremely typical pollution episode was triggered by BB emissions from YHR in June 2012, during which a yellow haze blanketed the Yangtze River Delta (YRD) (Ding et al., 2013a; Huang et al., 2012b; Xie et al., 2015). The intensive BB events and the resulting heavy pollution put weather forecast in trouble, during which a series of meteorological anomalies were observed, such as air temperature changes and precipitation redistribution (Ding et al., 2013a; Gao et al., 2018; Huang et al., 2016). On one hand, these anomalies have been partly attributed to aerosols, particularly absorbing aerosols like black carbon (BC), considering the interaction between air quality and meteorology (Huang et al., 2016). On the other hand, the fire-induced decreased surface albedo and its radiative and meteorological effects on a regional scale should not be ignored (Myhre et al., 2005). The striking spectral contrast between dark charcoal deposits over burned surface and bright ripe wheat could cause distinct physical signals, so-called surface darkening (Govaerts et al., 2002; Pereira et al., 1999). The influence of such surface albedo decline on the local and regional energy budget can be significant (Jin and Roy, 2005), especially in summer when solar radiation is extremely strong. It could be another key issue that needs to be well understood so as to figure out the meteorological anomalies during the burning season. Since many developing areas are still carrying out large-scale agricultural burning, better understanding of such fire-induced albedo change and its meteorological effects is of great significance for weather and climate forecast (Ravindra et al., 2019).
In this study, signals of surface albedo decline induced by crop residue burning in eastern China were found based on satellite retrievals, defined as surface darkening. The magnitude and spatial distribution of the declines were investigated combining fire counts by Moderate Resolution Imaging Spectroradiometer (MODIS) based on straw burning in June 2012. Temperature anomalies after BB were also explored using long-term site observations from 2007 to 2015 in eastern China, and comparisons were made between two statuses: “pre-fire” and “post-fire”. Moreover, with the aid of the Weather Research and Forecasting model coupled with Chemistry (WRF-Chem model), decreased surface albedo over fire-prone areas were taken into consideration in the simulation targeting temperature anomalies in June 2012. The further impact of surface darkening on the radiation budget, energy reallocation in the Earth–atmosphere system, and meteorology were discussed on a local and regional scale, which is of assignable climatological significance and should not be neglected.
2.1 Fire counts and surface albedo
The intensity of fire counts and the magnitude of surface albedo decline induced by crop residue burning were analysed based on standard MODIS products provided by NASA (Giglio and Justice, 2015a, b; Vermote, 2015).
The MODIS Surface Reflectance product (MOD09A1) provides an estimate of the surface spectral reflectance of MODIS bands 1 through 7 at a horizontal resolution of 500 m and uses the Bidirectional Reflectance Distribution Function (BRDF) database to better constrain the different threshold used (Schaaf et al., 2002). Wavelengths of the seven MODIS spectral narrowbands range relatively from 0.62 to 0.67, 0.84 to 0.87, 0.46 to 0.48, 0.54 to 0.56, 1.23 to 1.25, 1.63 to 1.65, and 2.11 to 2.15 µm. The narrowband albedo can be converted to specified broadband albedo for shortwave and near-infrared broadband through valid algorithms (Liang, 2001; Liang et al., 2003). It has been corrected for atmospheric conditions such as gases, aerosols, and Rayleigh scattering. The dataset is updated every 8 d, for selecting one value from all acquisitions in an 8 d composite period for each pixel unit. The criteria for grid cell value selection include cloud conditions and solar zenith angle.
The MODIS Thermal Anomalies/Fire Daily L3 Global product (MOD/MYD14A1) consists of daily surface thermal anomaly data obtained by Terra and Aqua satellites with spatial resolution of 1 km (Giglio et al., 2009, 2013, 2016; Hawbaker et al., 2008), and fire counts with low confidence were got rid of for quality control. The “fire count” described in the following part indicates the central location of MODIS pixels with surface thermal anomalies. The actual geographic size of the pixel varies depending on the angle at which a satellite scans. When counting the number of pixels in the target region, the pixels are abstracted into points on a two-dimensional plane.
2.2 Temperature observation and forecast
To obtain the surface meteorological conditions, meteorological observations of air temperature at 2 m height were acquired from the Integrated Surface Dataset from the US National Centers for Environmental Information (NCEI). The temperature observations were used to compare with the US National Centers for Environmental Prediction (NCEP) global final analysis data (FNL) with a spatial resolution which is updated every 6 h, and they were also applied for verification and analysis of numerical simulations.
The radiosonde data at Xuzhou (34.28∘ N, 117.15∘ E; WMO station number 58027) were collected from the University of Wyoming (http://weather.uwyo.edu/upperair/sounding.html, last access: 28 December 2019), which is the only sounding site in the YHR area. The radiosondes were launched twice a day (08:00 and 20:00 LT) and made measurements both on the mandatory pressure levels (e.g. surface, 1000, 900, and 850 hPa) and additional key levels. They measure vertical profiles of atmospheric parameters like air temperature and water mixing ratio.
2.3 Experiment design and model configuration
Version 3.6.1 of WRF-Chem, an online-coupled chemical transport model, was employed in this study, in which multiple physical and chemical processes are depicted, including emission, transport, mixing, and chemical transformation of trace gases and aerosols simultaneously with meteorology (Grell et al., 2005). In order to take fire-induced albedo change into consideration and figure out the impact of surface darkening on the radiation budget and meteorology in eastern China, a pair of parallel experiments in WRF-Chem with surface albedo as a variable were designed: in the control (CTL) experiment, a default value of monthly surface albedo in the model was adopted, while in the ABD experiment we applied satellite-detected albedo decline over fire-prone areas. In particular, the fire-affected grids were extracted out by a certain threshold of fire count density in June 2012, and the surface albedo decline in each grid is defined as the difference between MODIS-detected surface albedo post-fire and pre-fire based on the satellite data analysis in Sect. 3.1. In YHR, most fire from wheat straw is characterized by short-lived and incomplete smoldering (Huang et al., 2016). The relationship between the fire radiative power (FRP) and fire sizes varies at a global scale, and FRP of such straw burning is much weaker than grassland fires in North American (Laurent et al., 2019). Based on the MODIS Thermal Anomalies product (MOD/MYD14A1), the average maximum FRP for the most severe burning area in June 2012 is almost less than 0.02 kW m−2, the energy disturbance of which is much smaller than the continuous radiative disturbance of surface albedo decline in summer. Consequently, the heat released by fire was not treated in the model.
The domain is centred at 33.0∘ N, 115.0∘ E with a grid resolution of 20 km covered the eastern China and its surrounding areas. The initial and lateral boundary conditions of meteorological variables are obtained from NCEP FNL, which updates every 6 h. MIX, a mosaic Asian anthropogenic emission inventory developed by Tsinghua University (Li et al., 2017), and the Fire Inventory from NCAR (FINN), providing high-resolution global emission estimates from open burning (Wiedinmyer et al., 2011), were applied in WRF-Chem as anthropogenic and BB emissions, respectively. The simulations were conducted for the time period of 2–18 June 2012 and split into eight independent 72 h runs for the meteorological fields, while the chemical outputs from the preceding run were used as the initial conditions for the following run. Only the last 48 h results of each run were kept for analysis, and the first 7 d were regarded as the model spin-up period for atmospheric chemistry, so as to allow the model to reach a state of statistical equilibrium under the applied forcing (Berge et al., 2001; Lo et al., 2008).
The main configurations for WRF-Chem physical and chemical processes in both CTL and ABD experiment are listed in Table 1. A new version of the rapid radiative transfer model for general circulation model applications (RRTMG) was employed to depict the radiative transfer process for both shortwave and longwave radiation (Iacono et al., 2008; Mlawer et al., 1997). The Noah land surface scheme (Ek et al., 2003) was used to describe the land–atmosphere interactions, implemented with the MYJ boundary Layer scheme (Janjic, 1994) to describe the diurnal evolution of the planet boundary layer (PBL). As for cloud and precipitation processes, the new Grell–Freitas cumulus ensemble parameterization (Grell and Freitas, 2014) along with Lin microphysics (Lin et al., 1983) accounting for six forms of hydrometers was employed. Moreover, since the experiments were designed on the basis of MODIS products, the MODIS surface classification options of the International Geosphere–Biosphere Programme (IGBP) was adopted to keep consistency.
3.1 Fire-induced surface albedo change
In 2012, About 160 Tg of crop residue was burned, and 36 % of the total fires were recorded on farmland, the majority of which occurred in June, the harvest season for wheat (Li et al., 2016). YHR, the major wheat-producing area in China, is located in the vast flat plain in eastern China. Figure 1a shows the daily number of satellite fire counts in YHR, where cropland, especially wheat, dominates the vegetation cover (Gong et al., 2019; Lei and Yuan, 2013; Van Der Werf et al., 2010). The limited duration of agricultural fire combined with the low temporal resolution of MODIS may increase the difficulty of signal capture and lead to underestimation of fire counts (Chang and Song, 2009, 2010; Giglio et al., 2009; Randerson et al., 2012; Yin et al., 2019). As illustrated in Fig. 1a, severe and intensive BB events happened in mid–early June, especially 7–13 June, a tense and busy period in the crop cycle for harvest of wheat and sowing of maize. Among them, burning on 13 June is the most serious. Black charcoal deposits produced in highly intensive open straw burning would adhere to exposed soil and bound surface albedo over a period of time before removal of the char by natural process or regeneration of vegetation (Veraverbeke et al., 2012). The strong spectral contrast between dark burned surface and original bright, dry ripe wheat cover can cause distinct physical signals (Govaerts et al., 2002; Pereira et al., 1999).
Understanding the saliency and persistence of signals is important for estimation of albedo change amplitude and further analysis of its radiative and meteorological effects. The signals of surface darkening were a relatively short duration of about 1 week and much more sensitivity in shortwave near-infrared bands (Trigg and Flasse, 2000). Considering higher resolution and better depiction of narrowband satellite observations, and the outstanding capacity of the near-infrared band to separate the signals between vegetation and charcoal (Jin and Roy, 2005; Trigg and Flasse, 2000), the shortwave near-infrared band (0.84–0.87 µm) was chosen. Figure 1b and c show the surface albedo distribution before and after the severe burning separately, based on the MODIS Surface Reflectance product (MOD09A1), which updates every 8 d and has ruled out the interference of clouds. Data on 1 June have not been adopted because of too few valid data. For the shortwave near-infrared band, the decrease induced by fire is about 0.30 to 0.14, almost half of original values. The immediate surface albedo decline after fire can be attributed to the large-scale replacement of ripe wheat with black charcoal over fire-prone areas, so-called “burned scar”. Char materials strongly absorb the incoming solar radiation, causing a significant decline of the reflection-to-incoming-solar-radiation ratio (Veraverbeke et al., 2012), and this could disturb surface radiation balance at a level that cannot be ignored (Jin and Roy, 2005), which needs further exploration.
The total satellite-detected fire counts with high-confidence from 24 May to 17 June, the highly intensive straw burning period, are shown in Fig. 2a. Combined satellite-derived surface albedo changes of the same time period in the shortwave near-infrared broadband at fire locations are shown in Fig. 2b. As illustrated, the fire counts are fairly concentrated, especially in the northern part of Anhui (AH) province, an agricultural area mainly dominated by winter wheat (Yan et al., 2006). Correspondingly, extensive negative values in Fig. 2b demonstrate substantial signals of surface albedo decline over fire-prone areas in June 2012. For the near-infrared broadband, the declines range from −0.16 to −0.02. In addition, the surface albedo declines show obvious spatial heterogeneity and have a larger decline margin in northern AH than Jiangsu (JS). The effect of fire surface albedo is complex, determined by combustion completeness, fire intensity, pre-fire land cover structure, and underlying soil reflectance (Roy and Landmann, 2005). Here, the burning in AH was indeed more severe, which is consistent with the satellite fire detection. Though the surface albedo product applied here has ruled out cloud interference, inevitable noise from cloud shadow still exists, as reflected in the scattered positive values in the north-western region in Fig. 2b.
To better understand the signals of agricultural-fire-induced surface albedo decline and provide a basis for the following numerical experiments, frequency distributions of surface albedo decline in the near-infrared (0.7–2.5 µm) and short-wave (0.25–2.5 µm) broadband are shown in Fig. 3, to clarify the magnitude of surface albedo decline. The sample size of fire counts is 9477 pixels, consistent with the sample of those marked in Fig. 2a. Surface albedo change in most fire-affected pixel changes is distributed in the negative region, while the noise in the positive region corresponds to the positive values in the north-western area in Fig. 2b owing to cloud shadows. The frequency distribution of both the near-infrared and shortwave broadband shows two apexes, which is in accordance with the spatial heterogeneity of fire in AH and JS. Peak values for the shortwave band are distributed between −0.02 and −0.06, and for the near-infrared band between −0.06 and −0.10. Since nearly half of the solar energy that reaches the surface is at wavelengths longer than 0.7 µm, albedo change in the near-infrared band is rather significant for the energy budget of the surface (Hartmann, 1994). Consequently, to better characterize the surface albedo decline in aspects of both spatial distribution and scope in the severely burned area, the difference of the satellite-derived surface albedo in the shortwave near-infrared band was adopted as the albedo decline between the parallel experiments over fire-prone areas.
3.2 Observational evidence on surface warming in the post-fire period
Surface albedo is defined as the fraction of the downward solar flux density that is reflected by the surface, directly determining the absorptivity of the surface (Hartmann, 1994). In other words, when the flux of downward solar radiation reaching the surface is the same, more solar radiation will be absorbed by surface with decreased albedo. Without green plants to photosynthesize over fire-prone areas, the immediate fire-induced increase in radiation absorption is used to heat the ground primarily and then warm the near-surface atmosphere (Andrews, 2010; Wallace and Hobbs, 2006), leading to the signal of surface warming. What is more, straw burning in YHR bursts in summer, when solar radiation is the strongest and the response of surface albedo can be the fiercest. Hence, the air temperature observations over fire-prone areas after BB were investigated.
Near-surface air temperature observations at meteorological sites were compared with FNL data in 2012. Refer to Fig. 1a: burning in YHR is the most severe on 13 June, while 18 June is the end date of the wheat straw burning “season” in 2012. Temperature bias at 2 m height in the observational network at 20:00 LT on 13 and 18 June is shown in Fig. 4, filled according to the value of observation minus FNL. In addition, fire counts on the day and accumulated during the past 5 d, so-called burned scars, are marked. The scattered positive values of temperature bias in Fig. 4 show that observational temperature at those sites is higher than predictions from the forecast model with only a small fraction of assimilated observations. Most sites around intensive burned scars shows a positive deviation, which is an abnormal signal of surface warming, extending especially in the downwind direction.
In fact, intensive straw burning occurred in YHR every June, during the post-harvest period of wheat, over the past 20 years before the launch of strict regulations in recent years (Li et al., 2016; Yin et al., 2019), which stress the significance of understanding the signals of surface warming after BB from the perspective of climatology.
Xuzhou (XZ) station (marked in Fig. 4), the only radiosonde observatory located in the most intensive fire-prone area in YHR. The radiosonde observations at XZ from 2007 to 2015 were compared with FNL data in the PBL. The sample of days was selected out according to burning conditions in each year and has been classified into specific statuses: pre-fire and post-fire. Post-fire days must be within 5 d after a severe burning, while pre-fire days must be among the 5 d before fire but not within 5 d after a previous fire. Only days under clear-sky conditions were selected. The statistical distribution of temperature bias on different isobaric levels at 20:00 LT in the two statuses is shown in Fig. 5a and b. Temperature bias was defined as the value of radiosonde observation minus FNL data. As illustrated, temperature biases are mostly positive on the lower levels in both two statuses, and absolute values of post-fire are larger than pre-fire. Combined with Fig. 5c, this means observations post-fire have a bigger positive deviation from forecast results, a signal of abnormal warming post-fire. In addition, with regards to the vertical profile of bias post-fire (Fig. 5b), deviations on lower levels tend to be bigger and more positive than those on higher levels. A larger absolute value of deviation means lower predictability of temperature post-fire. Radiosonde data update 2 times a day, at 08:00 and 20:00 LT, and only patterns at 20:00 LT are shown here since no significant difference exists between the two statuses at 08:00 LT. After accumulation of absorbed radiation during the daytime, the change of thermal states near the ground level can be notable by 20:00 LT. The abnormal warming signal tends to be more obvious near the surface, which can be explained by the enhancement of surface heat absorptivity caused by decreased surface albedo.
For the same sample of days in 2007–2015, the diurnal variation of 2 m temperature bias between site observations and FNL in the two statuses is shown in Fig. 6. Negative values of deviation at 08:00 and 14:00 LT show that FNL tends to overestimate temperature during daytime and underestimate at night. It is noteworthy that the absolute values of deviations post-fire are always larger than those pre-fire no matter during the day or night. With regard to the median values, deviations post-fire gradually surpass over those pre-fire between 14:00 and 20:00 LT, consistent with the warming signal revealed by radiosonde analysis at 20:00 LT. The continuous uptrend during the daytime demonstrates a needed response time of heat accumulation, which may be attributed to the radiative effect of surface darkening (Andrews, 2010; Myhre et al., 2005). Thus, the signal of abnormal warming becomes more apparent between 14:00 and 20:00 LT, with the gradual accumulation process.
3.3 Improved temperature simulation by considering surface albedo change
As mentioned earlier, fire-induced surface albedo change and observational evidence of abnormal surface warming were substantial in eastern China. However, the radiative effects on meteorology and the underlying physical images of surface warming have not been figured out yet, which should resort to model simulation. In existing studies, radiative effects of albedo changes over burned scars were investigated on land covers like boreal forests (Lyons et al., 2008) and savannas (Jin and Roy, 2005; Myhre et al., 2005), but few of them were conducted on open agricultural fire in farmlands. Exploration into the disturbance of surface albedo decline induced by agricultural BB using model simulation can be meaningful for improving weather and climate forecast of regions with large-scale BB events. Hence, WRF-Chem experiments targeting surface albedo change induced by agricultural BB in eastern China were conducted. The most severe episode, which happened in June 2012, was selected as the case. Surface albedo set in the two parallel experiments, CTL and ABD, is shown in Fig. 7a and b. Figure 7c shows the surface albedo difference between the two experiments, which is defined as the difference between MODIS-detect surface albedo post-fire (17 June) and pre-fire (24 May) in each grid. Model results were compared with site observational air temperature in concentrated fire-prone areas (Fig. 8a) and their southern adjacent area, YRD (Fig. 8b). In Fig. 8, the ABD experiment shows an increase in temperature and enjoys a better fit with observations at both sites in the afternoon and evening compared to the CTL experiment. Temperature anomalies can be simulated to some extent, after considering the decreased surface albedo caused by BB.
The local surface energy budget at Bengbu is shown in Fig. 9. Bengbu is located in the fire-affected area with decreased albedo. As shown in Fig. 9a, upward shortwave radiation at the surface reduces a lot, while only a little change exists in downward shortwave radiation reaching the surface. The smaller ratio of solar radiation reflected to the atmosphere by the surface can be attributed to surface albedo decline. Accordingly, with more solar radiation absorbed by the surface, the ground will be heated and the surface temperature will be higher in the ABD experiment (Fig. 9b). Higher surface temperature would give rise to larger upward heat flux, thereby heating the atmosphere near the surface by vertical mixing (Stull, 1988). So the local radiation budget change induced by surface albedo change would directly influence the near-surface air temperature and cause an abnormal warming signal over fire-prone areas in the afternoon and evening with a certain lag.
Meanwhile, the temperature influence of fire-induced albedo change is also obvious in adjacent areas like LK (Lukou) (Fig. 8b), located in YRD. Some other stations in YRD also show similar patterns. Local temperature can be affected by various factors such as local radiation budget change and advection transport caused by thermal disturbance. As illustrated in Fig. 10a, surface warming shows up in the upwind area of LK station, which indicates influence of warm advection. According to Fig. 10b and c, sharp decrease in low cloud water contents was found in the upwind area in the ABD experiment. Low clouds, effective reflectors of solar radiation (Hartmann, 1994), would cause large perturbations to the surface radiation budget. In Fig. 10d, downward shortwave radiation reaching the surface in the ABD experiment reduces quit a lot due to reflection and occlusion of low clouds. The additional heat by decreased albedo over fire-prone areas would increase the surface temperature, change both sensible heat flux and latent heat flux, and then change the vertical velocity in the boundary layer and even disturb the process of cloud formation (Stull, 1988). Thus, surface albedo declines near fire locations also have great impacts on areas where surface albedo was barely changed, by disturbance to cloud formation and advection transmission.
These burned scars can remain over the surface for about 1 week under rainy conditions, or even longer if dryer and calmer (Trigg and Flasse, 2000). The length of the period allows for the process of local radiative accumulation and disturbance in regional circulation, and it influences the temperature over both fire-prone areas and adjacent areas.
To figure out surface albedo change induced by biomass burning and its impact on regional meteorology in eastern China, an investigation into the relationship between surface albedo change and temperature anomalies was conducted based on meteorological observations and satellite retrievals, combined with WRF-Chem simulations. This study focuses on the intensive wheat straw burning that occurred every early summer in the YHR area, the major wheat-producing area in eastern China. A typical and severe burning episode in 2012 was chosen to be the study case.
Fire-induced surface darkening over fire-prone areas was verified based on satellite retrievals. A large area of surface albedo decline is shown over fire-prone areas in YHR. It also shows obvious spatial heterogeneity and has a larger decline margin in AH, where fire counts are more concentrated and the burning is much more severe. For the near-infrared broadband, the absolute surface albedo decline ranges from −0.16 to −0.02, which can be an obvious signal on a regional scale and cause large radiative disturbance. Peak values of reduction in the shortwave broadband (0.7–2.5 µm) range between −0.06 and −0.02, and those in the near-infrared broadband (0.25–2.5 µm) range between −0.10 and −0.06.
Evidence of abnormal surface warming was found in eastern China. Most sites around intensive burned scars show a positive deviation in June 2012, an abnormal signal of surface warming which extends especially in the downwind direction. Comparisons were made between the statuses of pre-fire and post-fire under clear-sky conditions, based on multi-year temperature observations from 2007 to 2015. Observations post-fire have a bigger positive deviation from forecast results at 20:00 LT, especially on lower levels. This kind of abnormal surface warming signal post-fire will lead to lower predictability of temperature. In terms of diurnal variation, the signal becomes more apparent between 14:00 and 20:00 LT, with the accumulation of absorbed radiation.
To explore the direct radiative effects and the potential regional meteorological impacts of surface albedo change, WRF-Chem experiments targeting the surface albedo change induced by agricultural BB in eastern China were carried out. The ABD experiment shows an increase in temperature and enjoys a better fit with observations in concentrated fire-prone areas and its southern adjacent area compared to CTL, especially in the afternoon and evening. Surface albedo change over fire-prone areas influences the surface temperature through both direct local radiation budget change and indirect disturbance in cloud formation and advection transmission.
This study shows that either human or naturally induced biomass burning will not only influence the weather and regional climate by emission of aerosols and trace gases. The change in surface albedo could also cause significant impacts at a regional scale during the post-fire periods, particular in regions with strong solar radiation. This kind of short-term disturbance should be considered in future weather, climate, and air quality forecast models.
Meteorological datasets used in this work can be acquired from https://rda.ucar.edu/datasets/ds083.2/ (National Centers for Environmental Prediction et al., 2000), http://weather.uwyo.edu/upperair/sounding.html (University of Wyoming, 2019), and https://www7.ncdc.noaa.gov/CDO/cdoselect.cmd (Smith et al., 2011). The MODIS dataset can be obtained from the Level-1 and Atmosphere Archive & Distribution System (LAADS) Distributed Active Archive Center (DAAC), located in the Goddard Space Flight Center in Greenbelt, Maryland (https://ladsweb.nascom.nasa.gov; Giglio and Justice, 2015a, b; Vermote, 2015).
RT and XH led the manuscript writing. RT and DZ conducted the data analysis and model simulations. AD contributed to the research design.
The authors declare that they have no conflict of interest.
The numerical modelling was conducted on computing facilities at the High Performance Computing Centering (HPCC) at Nanjing University.
This research has been supported by the National Natural Science Foundation of China (grant nos. 91544231, 41922038, 91744311, and 41422504) and the International Cooperation project of Jiangsu Provincial Science and Technology Agency (BZ2017066).
This paper was edited by Leiming Zhang and reviewed by three anonymous referees.
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