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J Environ Health Sci Eng. 2014; 12: 9.
Published online 2014 January 7. doi:  10.1186/2052-336X-12-9
PMCID: PMC3898600

Dust storm simulation over Iran using HYSPLIT

Abstract

Particulate matters have detrimental effects on human health, environment and economic. This pollutant may emit from anthropogenic or natural sources. On global scale, main proportion of natural particulate matter release to the atmosphere because of wind erosion from arid and semi-arid regions. Recently, the amount of dust coming from Arabian countries has dramatically increased, especially dust storms that are affecting western and even central parts of Iran. This phenomenon has caused a lot of environmental problems. Dust source identification and trajectory simulation using numerical techniques are the main aims of this study. HYSPLIT (Hybrid Single Particle Lagrangian Integrated Trajectory) model dust module and trajectory simulation are utilized in this research and two case studies are investigated (in May and June 2010). The base of the HYSPLIT dust module is the PM10 dust storm emission algorithm for desert land use. This methodology is applied to estimate hotspots and trajectories. Due to the results, dust storms started on May 17th and June 7th because of high wind shear (>8.5 m/s) from the western Syrian Desert. The source region limited to 32.50 °N to 33.80 °N and 38.00 °E to 38.80 °E coordinates. Dust plumes lifted and dispersed towards the east and southeast of the sources and reached Ahvaz on May 18th and June 8th. The average of PM10 concentration in these dates reached 625 and 494 equation M1 on Ahvaz monitoring stations, respectively. Moreover, the results gained from the model for dust motion simulation are similar to the MODIS satellite images.

Keywords: Dust storms, Dust sources, Trajectory, PM10, HYSPLIT, MODIS satellite images

Introduction

Dust storms and wildfires in natural resources can be the considerable sources of suspension dust [1]. On global scale, most of the dust emission comes from arid and semiarid areas [2]. The main dust source areas are located in arid climates (with annual rainfall under 200–250 mm) in the so-called ‘dust belt’ [3]. The ‘dust belt’ extends from the west coast of North Africa, the Middle East, central and south Asia to China (Figure 1) [4].

Figure 1
Dust belt in SCIAMACHYa absorbing aerosol index [5]. (Figure courtesy of M. de Graaf).

There are many drawbacks with the dust phenomenon such as environmental, socio-economic, human health, climate and microclimate problems [6]. Some of these issues are discussed as follows.

Wind-blown dust is an effective factor for the transport of pathogens and pollutants [7,8] and also can influence air quality downwind of dust source regions by reducing visibility, soiling property and causing illnesses [9,10]. Inhalation of dust particles can cause heart beat irregularities, heart attacks and respiratory problems, severe and chronic headaches, severe allergies and skin diseases [11].

Particles such as mineral dust, by absorbing ultraviolet radiation can inhibit smog production, having profound implications in the control of air pollution in urban areas [12]. Furthermore, the interactions between wind-blown dust and anthropogenic pollutants aggravate the generation of secondary aerosols [13].

Dust particles have a significant effect on climate, acting both directly (by scattering and absorbing radiation) and indirectly (by changing the optical properties of clouds) on the Earth’s radiation balance [14]. Absorption and scattering of solar radiation caused by dust events may affect air temperatures [15]. In another way Dust fertilization (including iron and phosphorus) of poor nutrient marine environments can increase formation of phytoplankton and can influence the global cycle of carbon [16].

Different Techniques have been developed to identify dust hotspots and pathways. Numerical modeling, trajectory analysis, Remote sensing and satellite imagery, dust observations and metrological data analysis, mineral tracers and geological models can be applied as the principal tools used to research dust events [4,6,17-20].

In Iran a few studies have been carried out to determine dust sources, trajectories, contribution of dust to urban PM10 concentrations and temporal and spatial coverage of dust by using modeling techniques [21]. It should be mentioned that most of the conducted studies on these issues used satellite images and meteorological data analysis [22,23]. Most of the Dust storms in Iran are coming from the western and southern neighboring countries and they affect western and central regions of Iran [6].

In this research, the most high risk city of Iran namely Ahvaz, is chosen as the case study. According to WHO database [24], Ahvaz with 372 equation M2 annual mean of concentration of particulate matter is the first polluted city in the world. Finding the dust sources and the trajectories which cause the dust in Iran (specially the cities of Ahvaz and Tehran) has a significant importance. Therefore, this research uses numerical modeling techniques to study meteorological parameters, sources and trajectories of suspended particles of dust storms from wind erosions events. Surly, the results aim to control and reduce the amount of pollutions.

Materials and methods

Study area

Study area for dust injection to the atmosphere investigated using HYSPLITb model including parts of Saudi Arabia, Iraq, Syria and Jordan. This area limited to 20 °N −36.30 °N and 37 °E - 50 °E coordinates. Only desert land-use areas participate in the dust module and model omits the other land uses automatically by definition of this algorithm. Figure 2 shows the desert land-use considered for dust emission in the present study.

Figure 2
Dust sources regions defined in HYSPLIT dust module.

HYSPLIT model description

The HYSPLIT model uses puff or particle approaches to compute trajectories, complex dispersion and deposition. The model computation method is a combination of Eulerian (concentrations are calculated for each grid cell using integration of pollutant fluxes at every grid cell interface due to advection and diffusion) and Lagrangian (concentrations are computed by summing the contribution of each pollutant “puff” that is advected through the grid cell as represented by its trajectory) approaches.

The model utilizes meshed meteorological data on one of three conformal map projections (Polar, Lambert and Mercator). The dispersion model requires meteorological data fields that can be obtained from archives or from forecast model outputs and the datasets should be formatted for input to HYSPLIT [25,26].

The accuracy of the model is considerably dependent on the meteorological data resolution [27], For this study, we used GDASc meteorological data provided by U.S NOAA.

In HYSPLIT dust module, PM10 dust injections are estimated using as mass source algorithm [28].

equation M3
(1)

where F is the vertical mass flux of dust that is obtained from the friction velocity u*, a threshold friction velocity u*t, (required for initiation of dust emission), and a coefficient K (s/m) that depends on the surface soil texture. The friction velocity varies in space and time. However, the threshold velocity and soil texture coefficient vary only in space and related to the soil, land-use characteristics and surface roughness. In this study, the model is used over domain where detailed soil characteristics are not available and revised version of the dust module for vertical mass flux is replaced as Equation (1) [29].

equation M4
(2)

Based on these algorithms PM10 is emitted from desert land-use, when the wind velocity exceeds from local friction velocity and this parameter is defined as:

equation M5
(3)

Where z 0ns is the aerodynamic roughness length for non-saltating conditions, z is the wind measurement height and Von Karman’s constant k is assumed to be 0.4 [17].

In this research, dispersion simulation is done over the study area with HYSPLIT dust module. A horizontal domain of 30° × 30° with resolution of 0.05* × 0.05* and a vertical level of 100 meters above ground level is considered in dispersion model. Pollutant concentrations are sampled in every time step and are averaged over every 12 h. The turbulence mixing is computed using a diffusivity approach based on vertical stability estimates and the horizontal wind field deformation. The puff dispersion is assumed to be linear function of time. Ground level concentrations are calculated as average of the lowest 100 m within each horizontal grid cell. HYSPLIT dust storm modeling done for 0.25° × 0.25° resolution for desert dust sources and a total of 100,000 particles or puffs are released during one release cycle with a maximum of 50,000 particles permitted to be carried at any time during the simulation. Release mode is sampled with 3-dimensional (3-D) particle horizontal and vertical option.

The trajectory calculation in any Lagrangian model is based on the following the particle or puff. Therefore, once the basic meteorological data (U, V and W) has been processed and interpolated to the model grid. Trajectories can be computed to test the advection components of the model. The advection is computed from the average of the 3-D velocity vectors for the initial-position P(t) and the first-guess position P’(t + Δt). The velocity vectors are linearly interpolated in both space and time [25,26].

The first guess position is

equation M6
(4)

and the final position is

equation M7
(5)

In this study back trajectory simulations were used for determining source of dust storms and motion direction of dust plume over Middle East and Iran. Back trajectories started from Ahvaz (31.24 °N, 48.49 °E) and Tehran (35.42 °N, 51.25 °E) at the time of dust arrival. For HYSPLIT trajectory setting, four trajectory tracking levels including 500, 1000, 2000 and 3000 m are considered and also the top of model assumed to be 10,000 m.

Turbulence, wind fields and mixing depth values are used as inputs for dispersion model.

Results and discussion

First, the meteorological parameters surveyed in desert areas and the results showed that high wind velocity and mixing height caused to inject and lift the dust to the atmosphere, respectively. Second, dust hotspots determined in Syrian deserts and motion of dust simulated over study area using meteorological fields. The results are discussed in details as follows.

Two case studies are simulated in this research. These dust storms occurred on May 17th -20th and June 7th - 10th, 2010. In these two periods of time, PM10 concentration dramatically exceeded the ambient air quality standards (50 equation M8). Table 1 Shows PM10 concentrations in three air quality stations of Ahvaz during these periods [30].

Table 1
PM 10 concentrations in Ahvaz air quality stations (equation M9)

Meteorogical fields

Meteorological fields and flow patterns are analyzed in the 3-D model grid. Meteorological simulation indicates the development of diurnally varying local flow pattern. The wind fields at 10 m above the ground surface at 9 UTC on May 17th (a) and 12 UTC on June 7th 2010 (b) are shown in Figure 3. As illustrated in the figure, the main flow pattern was westerly and northwesterly in dust region around midday. This pattern rarely changed in the course of the day.

Figure 3
Wind fields over study area at the time of dust injection starting on (a) May 17th and (b) June 7th.

Table 2 shows the case studies’ meteorological parameters in dust hotspots area at the time of injection. As indicated in Table 2, these parameters are approximately similar in two assessed dust events. The wind speed is the most important parameter that influences particulate matter advection and dispersion and planetary boundary layer height (PBLH) Causes particulates dispersing in vertical direction. In these events PBLH was above 2000 m and dust dispersed effectively in vertical direction.

Table 2
Surface metrological parameters for two dust events in source areas

Dust module modeling results

May dust event was started at about 9 UTC on May 17th from west of syrian desert and dust injected for about 15 hours. Main hotspots derived by model for case studies are shown in Table 3. Dust plume spreaded in northwesterly direction and reached to Ahvaz in noontime of May 18 and increased PM10 concentration in the city to 496 equation M10 reported by DOE. Dust storm reached to Tehran on May 19th at 6 UTC and air quality of Tehran drastically was affected by air borne particles. The avarege of PM10 concentration of Tehran was 343 equation M11.

Table 3
Dust hotspots resulted by HYSPLIT dust module

In the second case study, when wind speed exceeded 10.34 m/s in Syrian Desert (Syria and Jordan region) at 12 UTC on June 7th, dust storm started and dust emitted for about 12 hours. This event affected western part of Iran, especially Khuzestan province. Dust plumes reached to Ahvaz at the beginning of the June 8th. The average of PM10 concentration reached to 625 equation M12 in the Ahvaz monitoring stations during the day. Figures 4 and and55 show results of dust storm modeling for May (17 May (a), 18 May (b), 19 May (c) and 20 May (d)) and June (7 June (a), 8 June (b), 9 June (c) and 10 June (d)) dust events, respectively.

Figure 4
Modeling results for concentration PM10 of averaged 0 – 100 m in May, (a) 17, (b) 18, (c) 19 and (d) 20 May.
Figure 5
Modeling results for concentration of PM10 averaged 0 – 100 m in June, (a) 7, (b) 8, (c) 9 and (d) 10 June.

Trajectory results

In this research, Horizontal and vertical pathways of dust parcel are simulated using trajectory approach. For May dust event, according to the arrival time of dust storms to Ahvaz and Tehran, back trajectory simulation started at 6 UTC on May 18th for Ahvaz and 6 UTC on May 19th for Tehran. The source of dust storm was located in west and north of Syrian Desert. Trajectory simulation began at 12 UTC on June 8th for Ahvaz and 12 UTC on June 9th for Tehran for June case study. This trajectory modeling showed that Source of early June dust storm was in western Syrian Desert and near the border of Syria, Jordan and Saudi Arabia. Figure 6 shows backward trajectory plots of Tehran and Ahvaz (Ahvaz at 6 UTC 18 May (a), Tehran at 6 UTC 19 May (b), Ahvaz at 12 UTC 08 June (c) and Tehran at 12 UTC 09 June (d)).

Figure 6
HYSPLIT Back trajectory simulations. (a) Ahvaz on May 18th, (b) Tehran on May 19th, (c) Ahvaz on June 8th, (d) Tehran on June 9th.

In the first case in May, studying arrival altitudes in Tehran and Ahvaz indicates that vertical distribution of dust in Tehran was 1000 and in Ahvaz was about 2000–3000 m. in the second case in June; height of dust plume was up to 2000 m above ground surface.

For supporting HYSPLIT results, MODISf satellite images have been used in this study. MODIS plays a significant role on earth observations of dust events which can identify dust storms using optical satellite images based on the radiation and scattering characteristics of particles. Temporal and spatial coverage computed by HYSPLIT was significantly similar to MODIS images. Figures 7 and and88 demonstrate MODIS images for case studies over study area provided by NASA rapid response imagery [31].

Figure 7
MODIS satellite images for May dust storm. (a) 17, (b) 18, (c) 19 and (d) 20 May.
Figure 8
MODIS satellite images for June dust storm. (a) 7, (b) 8, (c) 9 and (d) 10 June.

According to Figure 7, on May 17th, dust appeared in Syria and after passing over Iraq gradually moved to the western and central parts of Iran. Also Figure 8 shows that dust storm on June 7th after covering large regions of Iraq reached Khuzestan province and finally circulated towards the Persian Gulf and Arabian Peninsula.

In this study, MODIS images confirmed the results of HYSPLIT dust modeling and it was detected that dust plumes had a circulating motion while moving towards eastern parts of Middle East.

Conclusion

In this research source identification and trajectory simulation of two dust storms over Iran which was caused by wind erosion are studied. The HYSPLIT model dust module was applied to a western Middle East deserts. However, the results clarified that both of dust events simulated started from Syrian Desert in similar coordinates. Due to the high shear wind speed and mixing height, dust was released from desert land-use and dispersed horizontally and vertically over the study area. In addition, strong winds transported the dust through large areas of Iraq and Kuwait reaching the significant parts of Iran in about 48 hours. Backward trajectory simulation from Tehran and Ahvaz confirmed dust sources derived by dust module. At end, dust motion in MODIS images were compared to the output of HYSPLIT simulation which showed same trends.

Endnotes

aScanning Imaging Absorption Spectro-Meter for Atmospheric Cartography

bHybrid Single-Particle Lagrangian Integrated Trajectory

cGlobal Data Assimilation System

dZonal component of wind

eMeridional component of wind

fModerate Resolution Imaging Spectro radiometer

Competing interests

The authors declare that no conflict of interest.

Authors’ contributions

All authors read and approved the final manuscript.

Acknowledgments

The authors gratefully acknowledge the technical support provided by Dr. Majid Azadi (Atmospheric Science and Meteorological Research Center) and Mr. Hossein Vahidi (Academic Center for Education, Culture and Research).

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