Dynamics of Muddy Rain of 15 June 2018 in Nepal - MDPI
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atmosphere Article Dynamics of Muddy Rain of 15 June 2018 in Nepal Ashok Kumar Pokharel 1,2, *, Tianli Xu 1 , Xiaobo Liu 1 and Binod Dawadi 1,3 1 Kathmandu Center for Research and Education, Chinese Academy of Sciences-Tribhuvan University, Kathmandu 44613, Nepal; xutianli@itpcas.ac.cn (T.X.); xbliu@itpcas.ac.cn (X.L.); dawadibinod@gmail.com (B.D.) 2 Weather Extreme Ltd., Incline Village, NV 89451, USA 3 Central Department of Hydrology and Meteorology, Tribhuvan University, Kathmandu 44613, Nepal * Correspondence: ashokpokharel@hotmail.com Received: 13 April 2020; Accepted: 15 May 2020; Published: 21 May 2020 Abstract: It has been revealed from the Modern-Era Retrospective analysis for Research and Applications MERRA analyses, Moderate Resolution Imaging Spectroradiometer MODIS/Terra satellite imageries, Naval Aerosol Analysis and Prediction System NAAPS model outputs, Cloud –Aerosol Lidar and Infrared Pathfinder Satellite Observations CALIPSO imageries, Hybrid Single Particle Lagrangian Integrated Trajectory HYSPLIT model trajectories, atmospheric soundings, and observational records of dust emission that there were multiple dust storms in the far western parts of India from 12 to 15 June 2018 due to thunderstorms. This led to the lifting of the dust from the surface. The entry of dust into the upper air was caused by the generation of a significant amount of turbulent kinetic energy as a function of strong wind shear generated by the negative buoyancy of the cooled air aloft and the convective buoyancy in the lower planetary boundary layer. Elevated dust reached a significant vertical height and was advected towards the northern/northwestern/northeastern parts of India. In the meantime, this dust was carried by northwesterly winds associated with the jets in the upper level, which advected dust towards the skies over Nepal where rainfall was occurring at that time. Consequently, this led to the muddy rain in Nepal. Keywords: thunderstorm; dust storm; muddy rain; transport; convection; buoyancy; turbulent kinetic energy 1. Introduction It has been found that the lofted dust from wind erosion causes environmental effects at regional and global scales. Atmospheric dust affects climate globally by altering the radiation balance of the atmosphere [1,2]. Similarly, high concentrations of dust cause negative health effects [3,4] as well as, on a regional scale, lower economic status by deteriorating visibility with an increase in the cost of visibility impairment on national parks and wilderness areas. A positive correlation has been indicated between drought years and increased dust lofting [5], whereas others indicated that the intrusion of dust into the atmosphere occurs when freshly deposited sediment caused by the intense storms becomes dried up [6]. A dust climatology study over the southwestern US mentioned that the annual mean number of dust events, the annual mean duration of dust events, and the ratio of duration to number of dust events was directly proportional to the visibility range [7]. This study also found that the higher the percentage of total seasonal precipitation, the lower the total dust events percentage in the summer and the winter, and the lower the percentage of total seasonal precipitation, the higher the total dust event percentage in the spring and the autumn. It has been stated that the capability of the wind to deflate the dust particles (erosivity), the soil’s susceptibility to entrainment (erodibility), and the supply of erodible sediment are three major controlling factors on the dust emission process [8]. It is found that the downslope winds and the Atmosphere 2020, 11, 529; doi:10.3390/atmos11050529 www.mdpi.com/journal/atmosphere
Atmosphere 2020, 11, 529 2 of 13 unbalanced adjustment processes in the lee of the mountain ranges are the terrain-induced wind storms that also lift the dust from the surface, and produce larger-scale dust aerosol mobilization, and transport [9–13]. On the other hand, there are some examples that show thunderstorms produce very strong downburst winds leading to dust storms (i.e., strong and turbulent wind events by which dust is lofted from the surface and carries clouds of fine dust, soil, and sand over a large area) [14]. In happening thus, the wall of dust created by this kind of storm can be miles long and several thousand feet high [15]. In southwest Asia, dust storm activity is also controlled by thunderstorm occurrence, lifting dust from the ground surface. Though the highest frequency of thunderstorms is during the wet months—July and August,—there is also substantial thunderstorm activity in May and June, prior to major precipitation occurrence over this region [16]. Similarly, dust storms are most frequent in the afternoon, when turbulent mixing is most pronounced, due to the abundant insolation. This was found in Mexico Basin, where events were associated with strong downdraughts generated by the convective process-dry thunderstorms [17]. As far as the thunderstorm over Nepal is concerned, lightning activity starts in March; it intensifies quickly, reaching its peak in May, while in June the activity decreases rapidly as the southwest monsoon starts [18]. Due to extreme dust storms of 28 March 2016 over Kathmandu, Nepal and its surrounding areas there was a significant reduction in visibility (2 km), effects in aviation and ground transportation, and air quality deterioration. This reveals how vulnerable Nepal is to dust storm and how severely dust storms affect Nepal. On the other hand, unfortunately there are a lack of studies about the origin of dust storms, transport and deposition of dust, and a detailed understanding of the climatological and meteorological characteristics that influence dust event frequency and dust rain dynamics in Nepal. This type of knowledge is necessary to understand the regional, local dust climatology, and the atmospheric phenomena that affect the transport and deposition of the dust in Nepal. In this regard, the study of recent muddy rain (a kind of rain which contains enough dust (e.g., desert dust) to be clearly visible. This occurs when dust and dirt particles mix with the rain [19] of 15 June 2018 in Nepal, which might have increased the pH of rain water, has become quite a newsworthy issue as it is a quite unusual activity over Nepal and its neighbors, and the dust particles can neutralize acid rain in a manner similar to the way antacids counteract excess acid in an upset stomach [20]. For example, the increased level of pH was observed in southern Corsica in 1984 when the chemistry of precipitation mixed with Saharan dust was analyzed [21]. It is to be noted here that based on the findings of previous studies increase of pH has been suspected during this particular muddy rain. However, this study does not incorporate any discussion of the possible impacts of pH caused by this particular event due to beyond the scope of the study. According to Meteorological Forecasting Division (MFD) of Nepal, there was a muddy rain over Nepal on 15 June 2018 [22], which was also observed by the public, as shown in Figure 1. They did not discuss the detailed atmospheric dynamics regarding the processes responsible for causing that muddy rain. To address these issues, this study is accomplished, which describes different processes below. As far as the previous studies of detail atmospheric dynamics of muddy rain in Nepal are concerned, no such studies have been carried out in Nepal. For the first time, this study will reveal the scientific understanding of muddy rain dynamics over Nepal. Nepal is situated between China in the north and India to the south, east and west (i.e., 26.37◦ –30.07◦ N and 80.07◦ –88.20◦ E). It is a country of tremendous geographic diversity. Elevation ranges from 59 m in Terai to Earth’s highest point, the 8848 m Mount Everest. It has a warm temperate climate with dry winters and hot summers. Average annual precipitation ranges from 160 to 5500 mm.
Atmosphere 2020, 11, 529 3 of 13 Atmosphere 2020, 11, x FOR PEER REVIEW 3 of 13 Figure Figure 1. 1. Red Red arrow arrow indicates indicates deposited deposited dust dust on on leaves leaves [23]. [23]. Methodology 2. Methodology For this study, surface meteorological data and a map of regional overview of Indian subcontinent were subcontinent werecollected fromfrom collected the Department the Department of Meteorology and Hydrology, of Meteorology and Nepal (DHM-Nepal) Hydrology, Nepal and weatherunderground.com (DHM-Nepal) [24,25]. Satellite and weatherunderground.com imagery [24,25]. from Satellite Moderate imagery ResolutionResolution from Moderate Imaging Spectroradiometer Imaging (MODIS)/Terra Spectroradiometer [26] were collected (MODIS)/Terra [26] wereand analyzed collected andin depth. analyzed Forin thedepth. synopticForscale the observational atmospheric processes analysis, the reanalysis datasets of surface synoptic scale observational atmospheric processes analysis, the reanalysis datasets of surface pressure, geopotential height, airgeopotential pressure, temperature,height, precipitable water, windprecipitable air temperature, speed and direction, water, wind andspeed verticalandmotion obtained direction, and from the Modern vertical motion Era Retrospective-Analysis obtained from the Modern for Research and Applications (MERRA) Era Retrospective-Analysis (0.50◦ × 0.67 for Research and ◦) were used to (MERRA) Applications make horizontal (0.50° ×cross 0.67°)sections were used[27].toVertical cross sections make horizontal crossof wind speed sections components [27]. Vertical cross and potential sections of wind temperature were plotted speed components and from the selected potential reanalysis temperature weredatasets. plottedAn evolution from of the the selected dust by an datasets. reanalysis aerosol modelling An evolutionsystem the1◦dust of at × 1◦ by horizontal an aerosolresolution modellingfrom the Navy system at 1°Aerosol Analysis × 1° horizontal and Prediction resolution fromSystem the Navy(NAAPS) Aerosol[28] was considered. Analysis and PredictionIn addition Systemto this, Modern-Era (NAAPS) Retrospective [28] was considered. In Analysis addition for Research to this, and Applications-2 Modern-Era Retrospective (MERRA-2) Analysis model (spatialand for Research resolution 0.5◦ × 0.625 Applications-2 ◦ ) hourly (MERRA-2) datasets(spatial model were used to analyze resolution 0.5 ×the dust hourly 0.625°) scattering aerosolwere datasets optical usedthickness to analyze(AOT)the 550 nm dust of 1 µm scattering particulate aerosol matter optical [29] over thickness this region (AOT) 550 nm of interest. of 1 μm Rawinsonde data were particulate matter [29]obtained over thisfrom theof region University interest. of Wyoming,data Rawinsonde USAwere [30]. obtained Similarly,from the dust backward trajectories the University of Wyoming, were USAanalyzed using thethe [30]. Similarly, Hybrid dust Single Particle backward Lagrangian trajectories Integrated were analyzedTrajectory using (HYSPLIT) the Hybridmodel [31]. Single To analyze Particle the vertical Lagrangian reach of Integrated dust, imageries Trajectory of Cloud-Aerosol (HYSPLIT) model [31].Lidar and Infrared To analyze Pathfinder the vertical reach Satellite of dust, Observation imageries of(CALIPSO) Cloud-Aerosol [32] were Lidaralso and taken InfraredintoPathfinder account. Satellite Observation (CALIPSO) [32] were also taken into account. 3. Results 3. Results and and Discussion Discussion 3.1. Observation 3.1. Observation of of Dust Dust Storms Storms from from Some Some Surface Surface Stations Stations Locations of Locations of surface surface stations stations close close to to the the area area of of dust dust storms storms is is shown shown inin the the regional regional overview overview ◦N of Indian subcontinent (Figure 2) [24,25]. Observational data of Safdarjung Airport, India (28.58 of Indian subcontinent (Figure 2) [24,25]. Observational data of Safdarjung Airport, India (28.58° N 77.21◦ E) 77.21° E) and and Sardar Sardar Vallabhbhai Vallabhbhai Patel Patel International Airport, India International Airport, (23.07◦ N India (23.07° 72.63◦ E) N 72.63° E) archived archived by by Weather Underground (Table 1) indicated that dust storms hit Safdarjung Weather Underground (Table 1) indicated that dust storms hit Safdarjung Airport, India at 5:45 toAirport, India at 5:45 to 8:45 a.m. (local time) on 12 June 2018 with westerly/west-northwesterly winds 8:45 a.m. (local time) on 12 June 2018 with westerly/west-northwesterly winds ranging from 6.26 to ranging from 6.26 to 8.05 8.05 msm s−1 speed; −1 speed; at 5:45 at 5:45 to 11:45 to 11:45 a.m.a.m. on 13onJune 13 June 20182018 withwith westerly westerly windwind rangingranging fromfrom 7.60 7.60 to to 9.39 9.39 m s −1 ; at 3:45 to 8:45 a.m. on 14 June 2018 with west-southwesterly wind ranging from 4.47 to ms−1 ; at 3:45 to 8:45 a.m. on 14 June 2018 with west-southwesterly wind ranging from 4.47 to 7.15 ms s−1at 7.15−1;mand ; and 3:45atto3:45 5:45toa.m. 5:45ona.m. 15 on June152018 June with 2018 west/west-southwesterly with west/west-southwesterlywinds winds ranging ranging fromfrom 6.26 6.26 to 7.60 m s −1 speed. Similarly, Sardar Vallabhbhai Patel Intl Airport, India experienced dust storms to 7.60 ms speed. Similarly, Sardar Vallabhbhai Patel Intl Airport, India experienced dust storms at −1 at 6:45 6:45 to 11:45 to 11:45 a.m.a.m.(local(local time)time) of 12 of June12 2018 Junewith 2018westerly/southwesterly/west-southwesterly with westerly/southwesterly/west-southwesterly winds ranging from 4.02 to 5.36 ms−1; at 4:15 a.m. to 11:15 p.m. (local time) of 13 June 2018 with westerly/southwesterly/west-southwesterly winds ranging from 2.68 to 6.26 ms−1; at 12:45 a.m. to
to 11:45 Westerly Safdarjung Airport, 2018 9.39 Am India 3:45 Am 14 June 4.47 to to 8:45 West-southwesterly 2018 7.15 Am 15 June 3:45 Am 6.26 to Atmosphere 2020, 11, 529 West/west-southwesterly 4 of 13 2018 5:45 Am 7.60 6:45 Am 12 June 4.02 to to −1 11:45 Westerly/Southwesterly/West-southwesterly winds ranging from 4.022018 to 5.36 m sAm ; at 4:15 5.36 a.m. to 11:15 p.m. (local time) of 13 June 2018 with westerly/southwesterly/west-southwesterly 4:15 Am winds ranging from 2.68 to 6.26 m s−1 ; at 12:45 a.m. 13 June 2.68 to to 11:15 p.m. (local time) of 14 June to 11:152018 with south-southwesterly/west-southwesterly Westerly/Southwesterly/West-southwesterly winds Sardar Vallabhbhai 2018 6.26 ranging from 2.68 to 7.15 m s−1 ; andPm at 5:45 a.m. to 5:45 p.m. (local time) of 15 June 2018 with Patel International 12:45 Am southwesterly/south-southwesterly/west-southwesterly Airport, India 14 June 2.68 to winds ranging from 2.68 to 7.70 m s−1 . Hence, to 11:15 South-southwesterly/West-southwesterly 2018 this clearly shows that there were multiple 7.15 dust storms in the far western parts of India from 12 to Pm 15 June of 2018. It is to be noted here 5:45that Am prior to these event days (e.g., 10–11 June 2018), there was 15 June 2.68 to no precipitation and the 2018 to 5:45 flow of strong wind 7.70 Southwesterly/South-southwesterly/West-southwesterly at Safdarjung Airport and Sardar Vallabhbhai Patel Pm International Airport, India. Figure 2. Observation Figure 2. Observation of of dust dust storms storms from from some some surface surface stations stations are are shown shown byby red red coloured coloured triangles triangles in the map of regional overview of Indian subcontinent [24,25]. A triangle, which is shown in the side in the map of regional overview of Indian subcontinent [24,25]. A triangle, which is shown in the side of Himalyas, represents Safdarjung Airport, India, and another triangle represents Sardar Vallabhbhai of Himalyas, represents Safdarjung Airport, India, and another triangle represents Sardar Patel International Airport, India. Rawinsonde sounding station at Ahamadabad in India is also shown by a yellow coloured star. Table 1. Surface weather data observed at two stations of India [24]. Name of Surface Date of Wind Speed Local Time Wind Direction Stations Dust Storms (m s−1 ) 12 June 2018 5:45 a.m. to 8:45 a.m. 6.26 to 8.05 Westerly/West-northwesterly Safdarjung Airport, 13 June 2018 5:45 a.m. to 11:45 a.m. 7.60 to 9.39 Westerly India 14 June 2018 3:45 a.m. to 8:45 a.m. 4.47 to 7.15 West-southwesterly 15 June 2018 3:45 a.m. 5:45 a.m. 6.26 to 7.60 West/west-southwesterly 12 June 2018 6:45 a.m. to 11:45 a.m. 4.02 to 5.36 Westerly/Southwesterly/West-southwesterly Sardar Vallabhbhai 13 June 2018 4:15 a.m. to 11:15 p.m. 2.68 to 6.26 Westerly/Southwesterly/West-southwesterly Patel International Airport, India 14 June 2018 12:45 a.m. to 11:15 p.m. 2.68 to 7.15 South-southwesterly/West-southwesterly 15 June 2018 5:45 a.m. to 5:45 p.m. 2.68 to 7.70 Southwesterly/South-southwesterly/West-southwesterly 3.2. Dust Storms and the Dust Advection The MODIS/Terra images [26] captured useful images of massive dust storms of thick dust over the far West to Northwest to North of India from 12 June to 15 June 2018, as shown in Figure 3a–d, respectively. Although these figures are not able to indicate the exact location and the time of the initiation of the dust storm, based on the earliest available images among them and observational
Vallabhbhai Patel International Airport, India. Rawinsonde sounding station at Ahamadabad in India is also shown by a yellow coloured star. 3.2. Dust Storms and the Dust Advection The MODIS/Terra images [26] captured useful images of massive dust storms of thick dust over Atmosphere 2020, 11, 529 5 of 13 the far West to Northwest to North of India from 12 June to 15 June 2018, as shown in Figure 3a–d, respectively. Although these figures are not able to indicate the exact location and the time of the initiation of the dust information, storm, it can based onthat be inferred the the earliest firstavailable lifting ofimages among dust was them and initiated observational around 26.3◦ N 73.01◦ E on information, it can be inferred that the first lifting of dust was initiated around 26.3° N 73.01° E on 12 12 June 2018 (Figure 3a). June 2018 (Figure 3a). (a) (b) (c) (d) Figure 3. Dust storms images captured by moderate resolution imaging spectroradiometer Figure 3. Dust storms images captured by moderate resolution imaging spectroradiometer (MODIS)/Terra (MODIS)/Terra (1 km(1resolution) km resolution) on 12–15 on 12–15 June ((a), June 2018 2018(b), ((a–d), respectively (c), and [26]). Pink (d), respectively colored [26]). Pink circles area show colored the area circles dustshow plume theareas dust of western plume areasto ofnorthwestern to northern western to northwestern to parts of India. northern parts of India. 3.3. Synoptic Overview from the MERRA Based on the 0.50◦ × 0.67◦ MERRA reanalysis datasets [27], a meso-α/synoptic observational analysis was carried out to find out the roles of different atmospheric processes from the surface to the mid-troposphere at different time intervals that may have generated this particular favorable muddy rain environment. The mid tropospheric synoptic overview from the MERRA shows that there was a positively tilted trough (oriented along a southwest-northeast axis) in the far western/southwestern parts of India and southwestern/southern parts of Nepal from 12 June 2018 (Figure 4a). Over time, the geopotential height consistently showed a positively tilted trough (the presence of trough indicates the condition of static instability below it, the generation of strong positive vorticity advection, and the
Atmosphere 2020, 11, 529 6 of 13 creation of differential temperature advection (i.e., upper level and low-level fronts)) with falling heights rotated cyclonically to be oriented more southern to southwestern across Nepal till 15 June 2018 (Figure 4b). On 0630 UTC of 12 June 2018 a jet at 500 hPa (causes the upper level forcing) was propagating from northwest of India to western to southern to eastern parts of Nepal, respectively, with further amplification over time; therefore, it was continuously advancing on its way, influencing the trough. The baroclinic amplification of the jet streak was consistent with the deepening of the trough at that time. Similarly, on 0000 UTC of 15 June 2018, there were a juxtaposition of the jet with lower level mesoscale jetlet between 700 and 850 hPa, referring to a possible coupling between the upper and lower level wind maxima. Due to the presence of the upper level trough and the strong jet over our region of interest it can be inferred that the combination of these lift mechanisms played significant roles for occurrence of thunderstorms leading to downburst, kicking up the dust (Figure 3a–d), and carrying the lofted dust into Nepal for causing a muddy rainfall over there. These processes are also discussed in different sub-sections below. 3.4. Evolution of the Dust by an Aerosol Modeling of Navy Aerosol Analysis and Prediction System (NAAPS) and Dust Scattering AOT by MERRA-2 The NAAPS model is an additional supporting information regarding the occurrence of dust storm data in aforesaid region of few observations. It is a 1◦ × 1◦ resolution aerosol model that depicts dust predictions at 6-h intervals [28], is also used to diagnose the beginning and subsequent multiple occurrences of dust storms over our region of interest. This model reveals the evolution of the dust, including the concentration of sulfate over the region, and it can be related to the strength and track of the dust transport over time. It is important to note that sulfate was associated with the initial emission of the dust into the atmosphere, and over time, due to the lower density associated with sulfate compared with dust it remains for a relatively long period of time in the environment. Though the concentration of sulfate is lower than the dust in the composite form of the initial emission of the total material from the surface, over time, sulfate can be recognized due to its longevity in the atmosphere more than the dust due to its lower density. Here, we analyzed the NAAPS aerosol modeling image from 0000 UTC of June 12 to 15, 2018. NAAPS shows that the strongest signal of dust and sulfate emission into the atmosphere was largely over the 20–22◦ N 68–74◦ E region at 0600 to 1800 UTC of 13 June 2018 (Figure 5a–b). At 1800 UTC of 14 June 2018 and onwards, the strength and areal extension of the dust and sulfate materials increased and mostly advected towards the northwest/north/northeast region of India and its neighbors, 22–35◦ N 68–88◦ E (Figure 5c). Similarly, MERRA-2 model shows that the dust-scattering AOT reached up to 0.874 when the intrusion of dust reached in maximum vertical height in early of 14 June 2018 in the western parts of Nepal; and over time this value was diluted [29] when the dust was advected towards the eastern parts of Nepal.
Atmosphere 2020, 11, 529 7 of 13 Atmosphere 2020, 11, x FOR PEER REVIEW 7 of 13 (a) (b) Figure Figure 4. (a) 4. (a) Geopotential Geopotential height height and and wind wind speed/direction speed/direction at 500 hPaatat500 0630hPa at on UTC 0630 UTC2018. 12 June on 12TheJune 2018.colored yellow The yellow colored circle shows thecircle flow shows thethe of jet and flow of jet and the white white dotted line indicates a trough axis from the Modern-Era Retrospective analysis for Research and Applications MERRA reanalysis dotted line indicates a trough axis from the Modern-Era Retrospective analysis for Research and Applications MERRA reanalysis with horizontal resolution of 0.5 × with horizontal resolution of ◦ [27].×The 0.67°0.5 ◦ 0.67light[27]. The blue light blue colored circlecolored circle shows the shows area thestorm of dust area of dust and the storm and the outbreak; thunderstorm thunderstorm outbreak; (b) (b) Geopotential Geopotential height and wind height and windatspeed/direction speed/direction 500 hPa at 500 hPa on 0930 UTC on on 0930 UTC 15 on June152018. JuneThe yellow 2018. The colored yellow circle shows colored theshows circle flow ofthe jet flow and the of white jet anddotted line indicates the white a trough dotted line axis from indicates the Modern-Era a trough axis from theRetrospective Modern-Era Retrospective analysis for Research analysis and Applications for Research (MERRA) and Applications reanalysis (MERRA) with horizontal reanalysis resolution of with horizontal of 0.5◦ × 0.67◦ [27]. 0.5 × 0.67°[27]. resolution
Atmosphere 2020, 11, 529 8 of 13 Atmosphere 2020, 11, x FOR PEER REVIEW 8 of 13 (a) (b) (c) Figure5.5.(a) Figure (a)Dust Dustconcentration (μg/m33) at concentration (µg/m at 0060 0060 UTC on 13 June 2018 (Green (Green and and yellow yellow show show the the dustand dust andredredshows showssulfate sulfate (horizontal (horizontal resolution of 11◦× ×1°)) resolution of 1◦ )) [28]; (b)(b) [28]; Dust Dustconcentration concentration(μg/m 3) 3) at (µg/m at1200 1200UTC UTCon on1313June June2018 2018(Green (Greenand and yellow yellowshow show the the dust dust andand redred shows shows sulfate sulfate (horizontal (horizontal resolution ◦ 1 × ◦ 1°)) [28]; (c) Dust concentration (μg/m 33) at 1800 UTC on 14 June 2018 (Green and yellow resolution 1 × 1 )) [28]; (c) Dust concentration (µg/m ) at 1800 UTC on 14 June 2018 (Green and yellow showthe show thedust dustand andred redshows showssulfate sulfate( (horizontal horizontalresolution resolution of of 11◦××1°)) 1◦ ))[28]. [28]. 3.5. 3.5.Rawinsonde RawinsondeSoundings SoundingsAnalyses Analyses To Toobserve observethe thevertical verticaltemperature temperatureand and wind wind speed/direction speed/direction profiles at different different atmospheric atmospheric pressure levels close to pressure levels close to the the time period of the muddy rainfall in Nepal, the period of the muddy rainfall in Nepal, the rawinsonde sounding rawinsonde sounding of ofAhamadabad Ahamadabad(23.06° ◦ (23.06N,N,72.63° ◦ 72.63 E)E)ininIndia Indiaobtained obtainedfrom fromUniversity UniversityofofWyoming,Wyoming,USA USA[30] [30] was was analyzed analyzedfromfrom12–1512–15June June2018 2018(Figure (Figure 6). 6). Since Since this sounding sounding stationstation is is close close to to the the possible possible dust dust sources sourceswe weexpect expectthatthatthe theinformation information regarding regarding the the vertical profiles of different different meteorological meteorological variables variablesfrom fromthese thesestations stationscould couldbe bewell wellrepresented represented in in this this analysis. sounding at analysis. A sounding at Ahamadabad Ahamadabad (23.06 ◦ NN (23.06° 72.63 ◦ E),E), 72.63° which which is close is close to theto the possible possible areaarea of a of dusta dust storm,storm, at 1200at 1200 UTC UTCof June of12, June2018 12,shows 2018 shows the likely condition of a thunderstorm because of the value the likely condition of a thunderstorm because of the value of the convective available potential energyof the convective available potential (CAPE) energy (1438 J/kg)(CAPE) and the(1438 liftedJ/kg) indexand the lifted (−9.76) at thatindex time(−9.76) at that time (i.e., responsible for(i.e., responsible lifting mechanism), for lifting mechanism), generation of the triggergeneration effect due of tothethetrigger effect presence ofdue warm to the presence air and moistureof warm air and at a lower moisture level (shown atbya lower level (shown by the value of the dew point, ◦ which is greater than the value of the dew point, which is greater than 21 C and veering directional change of wind 45 or 21 °C and veering directional ◦ change more fromof wind surface 45°toor700 more hPa,from 850surface to 700 hPato 700 hPa,was wind 850 10.3 to 700m/shPa wind (i.e., was 10.3jet) low-level m/s or(i.e., greaterlow-level in the jet) or greater observed in theand sounding), observed sounding), the presence of theand the presence trough and jet as ofdiscussed the troughinand the jet as discussed earlier in the section. Hence, earlier there wassection. Hence, there a combination of high was a combination planetary boundary of layer high (PBL) planetary boundary moisture, stronglayer (PBL) moisture, directional and wind strong shear, directional low convective and wind shear, inhibition, CAPE, low convective and lifting inhibition, mechanisms. CAPE, and lifting mechanisms.
Atmosphere 2020, 11, 529 9 of 13 Atmosphere 2020, 11, x FOR PEER REVIEW 9 of 13 Figure Figure 6. Atmospheric sounding 6. Atmospheric observed sounding observedatatAhamadabad, India Ahamadabad, India at at 1200 1200 UTCUTC onJune on 12 12 June 2018 [30]. 2018 [30]. In addition to this, the sounding, which is presented in Figure 6, is inverted and “V”-shaped and In addition to this, the sounding, which is presented in Figure 6, is inverted and “V”-shaped is also showing that the dew point depression decreased significantly with height, dry air (low RH) in and isthe also showing lower that the troposphere withdew point nearly depression saturated air (highdecreased RH) in thesignificantly with height, middle troposphere, dry air (low the presence RH) inofthe lower separating inversion troposphere the with dry air nearly saturated aloft and the moist airair (high nearRH) in the middle the surface, and the troposphere, convective the presence of inversion condensation separating level (CCL) at a highthe dry air elevation. aloftthis Hence, and the moist “V”-shaped air near sounding thethat reveals surface, there was and the convective condensation level (CCL) at a high elevation. Hence, this “V”-shaped sounding reveals a quite appropriate condition for the generation of a strong downdraft from the severe thunderstorm. For example, that there was a when quiteanappropriate inversion (also known as for condition cap)the existed from the surface generation to a certain of a strong height, heat, downdraft from the moisture, and instability could have built under this “capping” inversion. Over time, once the cap severe thunderstorm. For example, when an inversion (also known as cap) existed from the surface broke due to the addition of daytime sensible heating, then explosive convection occurred resulting in to a certain height, heat, moisture, and instability could have built under this “capping” inversion. wind gusts. This was due to the entrain of dry air aloft into the downdraft. This promoted evaporative Over time, coolingonce the cap and further broke due enhanced to the buoyancy the negative addition of ofa daytime parcel. Insensible this case, heating, thenof explosive a cold parcel air convection occurred resulting in wind gusts. This was due to the entrain surrounded by warm air descended faster than the surrounding air since the cold air was denser, of dry air aloft into the downdraft. and coolerThisairpromoted evaporative is often noticed cooling at the surface whenand further enhanced the downburst air reachesthe negativeWhen the observer. buoyancy this of a parcel.cooler air interacted In this case, a with coldtheparcel warm buoyant of air air column present surrounded by in the lower warm air troposphere, descendedasfaster indicated than the by the sounding above, there was a lifting of the dust to 740 hPa and upward surrounding air since the cold air was denser, and cooler air is often noticed at the surface when the caused by the generation of the significant amount of turbulent eddies. This turbulence was the result of the summation of downburst air reaches the observer. When this cooler air interacted with the warm buoyant air the strong wind shear and the buoyancy, as suggested by [33]. All these aforesaid processes were column present in the lower troposphere, as indicated by the sounding above, there was a lifting of consequences of the thunderstorm and its effect in Ahamadabad and its surroundings. This is consistent the dust withtothe 740 hPa andofupward observation dust storm caused observed by atthe generation Sardar of the Vallabhbhai Patelsignificant Intl Airport,amount of ◦turbulent India (23.07 N, eddies.72.63 This turbulence ◦ E), was the result of the summation of the strong wind which is very close to this sounding station in Ahamadabad, as already mentioned in the shear and the buoyancy, as suggested by [33]. All these aforesaid processes were consequences of the thunderstorm and its earlier section. effect in Ahamadabad and its surroundings. This is consistent with the observation of dust storm 3.6. Analyses of Backward Trajectory and Vertical Reach of Dust observed at Sardar Vallabhbhai Patel Intl Airport, India (23.07° N, 72.63° E), which is very close to this soundingThe station HYSPLIT in model is run with Ahamadabad, as full ensemble already set-up, in mentioned producing the earliera variety section. of parcel back trajectories [31], as shown in Figure 7. It is used here to compute air parcel trajectories and the deposition or dispersion of lofted dust from the source of dust to recipient of it (e.g., to find out where 3.6. Analyses of Backward Trajectory and Vertical Reach of Dust did the dust come from to Nepal). In other words, this is used here to establish whether a high level of dustHYSPLIT The at one location (e.g.,is model Nepal) run iswith caused fullbyensemble the transport of air contaminants set-up, producing from anotherof a variety location. parcel back For this analysis, Kathmandu (27.72◦ N, 85.32◦ E) in Nepal is considered as a recipient point. trajectories [31], as shown in Figure 7. It is used here to compute air parcel trajectories and the deposition or dispersion of lofted dust from the source of dust to recipient of it (e.g., to find out where did the dust come from to Nepal). In other words, this is used here to establish whether a high level of dust at one location (e.g., Nepal) is caused by the transport of air contaminants from another location. For this analysis, Kathmandu (27.72° N, 85.32° E) in Nepal is considered as a recipient point.
Atmosphere 2020, 11, 529 10 of 13 Atmosphere 2020, 11, x FOR PEER REVIEW 10 of 13 Figure 7. Figure Backward Trajectory 7. Backward Trajectory by the by the Hybrid Hybrid SingleLagrangian Single Particle Particle Integrated Lagrangian Integrated Trajectory (HYSPLIT)Trajectory (HYSPLIT) model [31] ending at 2300 UTC on 15 June 2018. model [31] ending at 2300 UTC on 15 June 2018. HYSPLIT back trajectories of 10 to 16 June of 2018 combined with MODIS satellite imageries have HYSPLIT back provided trajectories insight into whetherofhigh 10 to 16 June muddy of caused rain was 2018 combined with MODIS by local air pollution sources or satellite whether imageries have provided dust wasinsight blown into in thewhether highthe wind. Further, muddy backward rain was caused trajectories (Figureby local air 7) clearly inferpollution that the airsources or parcel laden with dust was transported from the western parts (between 22 ◦ N 72◦ E and 27◦ N to whether dust was blown in the wind. Further, the backward trajectories (Figure 7) clearly infer that 77◦ E) of India to Nepal (e.g., Kathmandu), as shown by the higher air currents. This also reveals the air parcel laden with dust was transported from the western parts (between 22° N 72° E and 27° that Thar desert of both Rajasthan and Gujarat states of India, which lie in the western part of India, N to 77° E) of as served India a dusttosource Nepal (e.g., in this Kathmandu), particular event. as shown by the higher air currents. This also reveals that Thar This desert of bothby is also supported Rajasthan and Gujarat CALIPSO images states [32], which of India, show that which the vertical reachlie of in dustthe waswestern 6 km part of (Figure 8a,b). This infers that when the dust India, served as a dust source in this particular event. reached such a height, the strong westerly/northwesterly current of air at that height, as discussed in an earlier section, advected dust towards the sky of Nepal, This is also supported by CALIPSO images [32], which show that the vertical reach of dust was where the precipitable water was present at that time (Figure 9), leading to muddy rain in Nepal. 6 km (Figure 8a,b). This infers that when the dust reached such a height, the strong westerly/northwesterly current of air at that height, as discussed in an earlier section, advected dust towards the sky of Nepal, where the precipitable water was present at that time (Figure 9), leading to muddy rain in Nepal.
Atmosphere 2020, 11, 529 11 of 13 Atmosphere 2020, 11, x FOR PEER REVIEW 11 of 13 Atmosphere 2020, 11, x FOR PEER REVIEW 11 of 13 (a) (a) (b) (b) Figure 8.8. (a) (a) Vertical Vertical stretch stretch of dust at 20:42:26.8 20:42:26.8 to 20:55:55.4 20:55:55.4 UTC on 13 June June 2018 captured captured by Figure Figure 8. (a) Vertical stretch ofof dust dust at at 20:42:26.8 to to 20:55:55.4 UTC UTC onon 13 13 June 2018 2018 captured by by CALIPSO CALIPSO [32]. [32]. The The red red circled circled areaarea shows shows vertical vertical reachreach of of dust; dust; (b) (b) VerticalVertical stretch stretch of dust atof dust at 20:30:08.0 CALIPSO [32]. The red circled area shows vertical reach of dust; (b) Vertical stretch of dust at 20:30:08.0 to 20:43:36.7to UTC 20:43:36.7 on 15 UTC on 15captured June 2018 June 2018by captured CALIPSO.by CALIPSO. The redshows circled area shows 20:30:08.0 to 20:43:36.7 UTC on 15 June 2018 captured byThe red circled CALIPSO. Thearea red circledvertical reach area shows vertical of dust. reach of dust. vertical reach of dust. Figure 9. Total precipitable 9. Total precipitable water water in in mm (shown (shown in legend at upper part of Figure) over Nepal Figure 9. Total precipitable water in mm (shown in legend at upper part of Figure) over Nepal (shown by a red coloured circle area) area) atat 1830 1830 UTC UTC on on 15 15 June June 2018 2018 from from the the MERRA MERRA reanalysis reanalysis with (shown by a red coloured circle area) at 1830 UTC on 15 June 2018 from the MERRA reanalysis with horizontal resolution of 0.5◦××0.67°. of 0.5 0.67◦ . horizontal resolution of 0.5 × 0.67°.
Atmosphere 2020, 11, 529 12 of 13 4. Conclusions There were big surges of dust storms in the far western parts of India, especially Ahamadabad and its surroundings, caused by thunderstorms from 12 to 15 June 2018, intermittently. There was a lifting of dust into the upper air caused by the generation of significant amount of turbulent kinetic energy as a function of strong gust wind, which had strong wind shear, and the convective buoyancy at the lower boundary layer during the descending outflow of cold air caused by the generation of a severe thunderstorm. When this lofted dust in the upper air came into contact with prevailing winds, such as northwesterly/westerly associated with the jets, as discussed in the earlier sections, upper air dust was advected towards Nepal, where rainfall was occurring, led to the muddy rain in Nepal. Hence, the study of this particular event reveals that western parts of India were dust source regions (i.e., Thar desert of both Rajasthan and Gujarat states of India, which plays a significant role as a source of emission of dust caused by the dust storms during the months of March–June every year [34]) from which dust was transported to Nepal as a long range transport. As this finding is still based on the low-resolution datasets, it would be better if it could be done on the high-resolution datasets so that the details of finer temporal and spatial processes, such as emission to transport to the deposition of dust in this particular event, could be further understood. In addition to this, there is a need for more cases in order to establish the representativeness of the event presented here. Author Contributions: Conceptualization, methodology, software, validation, formal analysis, investigation, and writing, A.K.P.; resources and project administration, T.X., X.L., and B.D. All authors have read and agreed to the published version of the manuscript. Funding: This research is funded by Kathmandu Center for Research and Education (KCRE), Chinese Academy of Sciences (CAS)—Tribhuvan University (TU). Acknowledgments: We would like to thank Tandong Yao and Tao Wang for their helpful advice and support. Also, thanks goes to Kathmandu Center for Research and Education, Chinese Academy of Sciences-Tribhuvan University, Kathmandu, Nepal for providing financial support for this study. Conflicts of Interest: The authors declare no conflict of interest. References 1. Seinfeld, J.; Carmichael, G.; Arimoto, R.; Conant, W.; Brechtel, F.; Bates, T.; Cahill, T.; Clarke, A.; Doherty, S.; Flatau, P.; et al. ACE-ASIA: Regional climatic and atmospheric chemical effects of Asian dust and pollution. Bull. Am. Meteor. Soc. 2004, 85, 367–380. [CrossRef] 2. Tegen, I. Modeling the mineral dust aerosol cycle in the climate system. Quat. Sci. Rev. 2003, 22, 1821–1834. [CrossRef] 3. Appel, B.; Tokiwa, Y.; Hsu, J.; Kothny, E.; Hahn, E. Visibility as related to atmospheric aerosol constituents. Atmos. Environ. 1985, 19, 1525–1534. [CrossRef] 4. Chan, Y.; Simpson, R.; Mctainsh, G.; Vowles, P.; Cohen, D.; Bailey, G. Sourceapportionment of visibility degradation problems in Brisbane (Australia)—Using the multiple linear regression techniques. Atmos. Environ. 1999, 33, 3237–3250. [CrossRef] 5. Okin, G.S.; Reheis, M.C. An ENSO predictor of dust emission in the southwestern United States. Geophys. Res. Lett. 2002, 29. [CrossRef] 6. Reheis, M.; Kihl, R. Dust deposition in southern Nevada and California, 1984 1989: Relations to climate, source area, and source lithology. J. Geophys. Res. 1995, 100, 8893–8918. [CrossRef] 7. Pokharel, A.; Kaplan, M. Dust Climatology of the NASA Dryden Flight Research Center (DFRC) in Lancaster, California, USA. Climate 2017, 5, 15. [CrossRef] 8. Okin, G.S.; Gillette, D.A.; Herrick, J.E. Multi scale controls on and consequences of Aeolian process in landscape change in arid and semi-arid environments. J. Arid Environ. 2006, 65, 253–275. [CrossRef] 9. Pokharel, A.; Kaplan, M.; Fiedler, S. Subtropical Dust Storms and Downslope Wind Events. J. Geophys. Res. Atmos. 2017, 122, 10. [CrossRef] 10. Pokharel, A.; Kaplan, M. Organization of dust storms and synoptic scale transport of dust by Kelvin waves. Earth Syst. Dynam. 2019, 10, 651–666. [CrossRef]
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