Document Type : Research Paper

Authors

1 Assistant Professor, Soil Protection and Watershed Management Department, Fars Agricultural and Natural Resources Research and Education Center

2 Assistant Professor, Desert Research Division, Research Institute of Forests and Rangelands, Agricultural Research Education and Extension Organization (AREEO), Tehran, Iran

10.22092/ijrdr.2025.134291

Abstract

Abstract
Background and objective
The phenomenon of dust storms results from a combination of natural and human-induced factors and has serious impacts on health, agriculture, transportation, and water resources. Strong winds can detach fine particles from dry soils, leading to the formation of dust storms that transport these particles over long distances. Consequently, dust storms have become a local, regional, and global challenge. In southwestern Iran, the average number of dusty days over the past 50 years has ranged between 27 and 75 days per year. Due to its geographical and climatic conditions, Fars Province is affected by both internal and external dust sources. Land-use changes, consecutive droughts, and geological characteristics are among the key factors contributing to the expansion of this phenomenon. Considering the geological conditions of Fars Province, the presence of abandoned agricultural lands, the drying of wetlands, and land-use changes, the dust phenomenon holds particular significance. The objective of this study is to examine the distribution and introduce the physicochemical properties of surface soils in dust-producing areas through the analysis of land-use documents, meteorological and geological data, remote sensing, field visits, and laboratory investigations. Additionally, this research aims to provide a foundation for further studies and desertification control projects.
Materials and methods
In this study, dust source areas were identified and classified using maps of desert regions, geology, land use, and vegetation cover within a GIS environment. Sampling points were then determined using a 2×2 km grid method over these source areas. Two soil samples were collected from each point: a 2-kg sample from the 0 to 30 cm depth for physicochemical tests and a 20-kg sample for wind erosion testing. The physicochemical tests included measuring pH, electrical conductivity (ECe), ionic compositions, cation exchange capacity (CEC), saturated moisture percentage (SP), gypsum content, and soil texture. Additionally, a wind tunnel test was conducted to evaluate wind erosion. Finally, to examine the relationship between soil properties of the source areas and wind erosion, the data obtained were analyzed using charts and tables.
Results
Five major dust source areas have been identified in Fars Province, including Bakhtegan-Neyriz, Maharloo-Sarvestan, Shahrpir-Zarindasht, Dezhgah-Farashband, and Khonj-Larestan. These dust hotspots are located in the central, eastern, and southern parts of the province and are primarily affected by rangeland degradation, drought, and wetland desiccation. Land-use analysis in these areas indicates that 65% of the land consists of degraded rangelands, 19% comprises dried wetlands, and 16% includes abandoned agricultural lands and rainfed farms. The threshold wind erosion speed in these hotspots ranges between 8 and 10 meters per second. Moreover, the correlation between erosion intensity and increasing wind speed in most of these areas is between 80% and 99%, highlighting their high sensitivity to atmospheric changes and rising wind speeds.
Wind tunnel experiments indicate that the highest wind erosion occurred in Dezhgah-Farashband, where at a wind speed of 25 meters per second, the erosion rate reached 15.76 kg per square meter per minute. The soil texture in these dust source areas mainly consists of loam, sandy loam, and loamy sand. The soil pH varies between 7.5 and 8.5, while electrical conductivity ranges from 0.41 to 157.7 dS/m. A correlation study between soil wind erosion and parameters such as salinity, acidity, sodium content, organic matter, and soil texture (sand, silt, clay) indicates a weak correlation between wind erosion and salinity, particularly in saline soils. However, in non-saline soils, a positive and significant correlation (66.7%) exists. Conversely, a positive and significant correlation is observed between wind erosion and sand content, while a negative correlation is found with silt and clay content.
Discussion
The study reveals that the wind erosion threshold velocity varies across different locations, primarily depending on the physical and chemical properties of the soil. In areas with coarser soil textures, and relatively higher silt proportions (e.g., the Dezhgah-Farashband dust resources), a lower wind speed is required to initiate wind erosion and transport soil particles; thus, the threshold wind erosion velocity is lower. Conversely, in areas with higher clay content and lower silt content (e.g., parts of the Khonj - Larestan and the Shahrpir-Zarindasht dust resources), a higher wind speed is necessary to initiate wind erosion. The wind erosion threshold velocity across all study ranged from 7 to 10 meters per second. The Dejgah-Farashband dust resource exhibits the highest dust production due to its soil composition. Conversely, the Shahrpir-Zarindasht dust resource is more resistant to wind erosion due to its heavier soil texture. Furthermore, increased soil salinity reduces particle cohesion, potentially lowering the wind erosion threshold velocity. This study indicates that soil salinity, pH, and organic matter content can influence both the wind erosion threshold velocity and dust production.
Conclusion
The dust hotspots in Fars Province, including Neyriz-Bakhtegan, Maharloo-Sarvestan, Shahrpir-Zarindasht, Dezhgah-Farashband, and Khonj-Larestan, are influenced by a combination of environmental factors. The most significant of these include the drying of wetlands (particularly Bakhtegan, Abadeh Tashk, and Maharloo), extensive rangeland degradation, and unfavorable soil characteristics such as loamy texture, high salinity, and low organic carbon content. Although high wind speeds (with an erosion threshold of 8 to 10 m/s) play a crucial role in erosion within these areas, the extent of windborne sediment transport and dust production is significantly influenced by soil texture and the percentage of clay and silt. For instance, the Shahrpir-Zarindasht hotspot exhibits lower erosion due to its fine-grained soil texture. Therefore, a comprehensive and targeted management approach, focusing on wetland restoration, vegetation improvement, and soil rehabilitation, is essential to mitigate the adverse impacts of dust storms.
 

Keywords

References

Abbasi, F., 2021. Particulate matter crisis and its effects on regional security. Journal of Geography and Human Relations, 12, 601-619. [In Persian]. https://doi.org/10.22034/gahr.2021.276411.1516
Aghanabati, A., 2004. Geology of Iran. Organization of Geology and Mineral Exploration of the country.
Amir Azadi, A. R., & Jafari, M., 2020. Prioritization and identification of dust centers in Fars province. Geography, 18(64), 64–78. [In Persian]. https://civilica.com/doc/1411943
Azadeslamiyeh, M. R., Kalantari, S., Shirmardi, M., & Tazeh, M., 2017. Investigating the effect of salinity on the threshold wind erosion velocity (Case study: Meybod) [Conference paper]. In Proceedings of the 4th National Conference on Wind Erosion and Dust Storms (Yazd, Iran). https://civilica.com/doc/714416
Chatrenour, M., Norouzi, A., Farrokhian Firouzi, A., and Landi, A., 2020. Investigating soil properties in susceptible areas of dust production in Khuzestan province by visible and wave-near infrared spectroscopy. Journal of Watershed Engineering and Management, 12(3), 670–685. https://doi.org/10.22092/ijwmse.2019.123907.1570
Cornelis, W. M., and Gabriels, D., 2003. The effect of surface moisture on the entrainment of dune sand by wind: an evaluation of selected models. Sedimentology, 50(4), 771-790. https://doi.org/10.1046/j.1365-3091.2003.00577.x
Dargahian, F. and Lotfi Nasab Asl, S., 2019. Temporal and spatial changes and precipitation trends in watersheds leading to dust centers in Khuzestan province. Iranian Nature, 5(3), 59-67. [In Persian]. https://civilica.com/doc/1890626
Food and Agriculture Organization of the United Nations. 2020., Standard operating procedure for soil calcium carbonate equivalent: Titrimetric method. Rome, Italy: FAO. ttps://www.fao.org/documents/card/en/c/ca7152en
Geodata., 2024. SOL UFHSD. www.geodatas.ir/product/sol-ufhsd
Ghahari, G., Hosseinimarandi, H. and Saif, M., 2019. Monitoring of climatic factors affecting the intensification of the phenomenon of dust and sand dune (wind erosion) in Fars province. Fars Agriculture and Natural Resources Research and Education Center. [In Persian].
Hosseinimarandi, H., Ghahari, G., Mesbah, S.H., and Abbasi, H., 2022. Monitoring the dust sources of sand dunes in Fars Province (The project final report) (Report No. 0-09-09-09-135-961571). Fars Agricultural and Natural Resources Research and Education Center. [In Persian].
Jalali, N., Iranmanesh, F., and Davoodi, M., 2017. Identification on dust storm sources and their affecting areas in south-west provinces of Iran, using MODIS image. Watershed Engineering and Management, 9(1), 318-331. [In Persian]. https://doi.org/10.22092/ijwmse.2017.112374
Jooybari, S. A., Pirovan, H., Rezaei, P., and Gholami, H., 2022. Investigating and analyzing the concentration of heavy metals and indicators of sediment pollution in Handijan dust center, Khuzestan province. Scientific-Research Journal of Watershed Engineering and Management, 41(3), 312-331. [In Persian]. https://doi.org/10.22092/ijwmse.2021.353711.1884
Katorani, S., Ahmadi, M., and Dadashi Rudbari, A., 2024. Spatial distribution and trends of dust particles in West Asia and their relationship with land use changes. Iranian Journal of Water and Soil Research, 55(8), 1415-1432. https://doi.org/10.22059/ijswr.2024.374563.669685
Li, X., Zhang, L., and Li, J., 2017. Application of waste iron in wet flue gas desulfurization. Environmental Science and Pollution Research, 24(3), 2269–2278. doi: 10.1007/s11356-024-35646-z
Meshkat, M. A., Daneshvar, M. R., Ekhtesasi, M. R., and Dashtkian, K., 2006. Mapping of degradation of vegetative cover,wind erosion and salt affected soils in some of of the yazd-ardekan plain. Range and Desert Research of Iran, 13(1), 10-16. [In Persian].
Mohamadkhan, Sh., Abravesh, S., Sarvati, M., & Gharudi Tali, M., 2021. Origin of aeolian sediments based on geochemical traces by sedimentary fingerprinting method [In Persian]. Geographical Studies of Dry Areas, 12(46), 17–30. Retrieved from https://jargs.hsu.ac.ir/article_161553
Naeimi, M., Eftekhari, A., Khalifehzadeh, R., Dargahian, F., and Zandifar, S., 2022. Dust mitigation by the application of treated sewage effluent (TSE) in Iran. Scientific Reports, 12(1), 15521. [In Persian]. doi: 10.1038/s41598‑022‑19331‑0
Nivar, M., and Baghery, M., 2020. Spatial analysis of observational rainfall in Fars province and its projection using the CanESM5 climatic model output. Journal of Climate Research, 7(2), 57-70. https://nivar.irimo.ir/article_212718.html
Nikolay, S. K., Natalia, E. K., Dmitry, V. V., Ksenia, S. N., and Alexander, V. R., 2021. Physicochemical properties of road dust in Moscow. Science of The Total Environment, 762, 143081. DOI: 10.1016/j.scitotenv.2020.143081
Noorzadeh Haddad, M., & Bahrami, H., 2015. Investigating the relationship of fine dust concentration with surface moisture and soil size distribution using a portable wind erosion simulator in the desert areas of western Khuzestan province. Geographical Explorations of Desert Areas, 3(1), 60–72. [In Persian].
Noorzadeh Haddad, M., & Landi, A., 2018. Mineralogy study and sensitivity of fine dust production sources to gravel cover in the soil surface: A case study of western lands of Khuzestan province. Ahar Geographical Space Quarterly, 18(64), 61–74. [In Persian]. http://geographical-space.iau-ahar.ac.ir/article-1-2270-fa.html
Omidvar, K., and Omidi, Z., 2013. Analysis of dust phenomenon in the south and central regions of Fars province. Geographical Researches of Desert Areas, 1(1), 1-10.
Shao, Y., 2008. Integrated Wind-Erosion Modelling. In Y. Shao (Ed.), Physics and Modelling of Wind Erosion (pp. 303-360). Springer. doi.org/10.1007/978-1-4020-8895-7_9
U.S. Department of Agriculture (USDA)., 2017. Soil survey manual (Soil Survey Division Staff; Soil Conservation Service, Handbook No. 18). U.S. Department of Agriculture.
Vafaeinezhad, A., Kheirkhah Zarkesh, M. M., Ahmadi Dahka, F., and Fallah Zazouli, M., 2014. Monitoring of dust haze phenomenon using remote sensing and GIS and its synoptic analysis: Case study of 18 June 2012 dust haze. Geographical Data, 23(91), 69-80. https://sid.ir/paper/253173/en
World Meteorological Organization (WMO)., 2017. Dust storm or sandstorm. In International Cloud Atlas. World Meteorological Organization.
Yamani, M., Lak, R., Gorabi, A., Shahbazi, R., and Shabani Iraqi, A., 2014. Analysis of the potential of wind erosion and dust phenomena through the application of wind circulation patterns in the Damghan basin. Journal of Marine Science and Technology, 23(91), 69-80. https://magazine.hormozgan.ac.ir/article-1-536-fa.html
Zhang, G., Li, L., Tang, W., Liu, L., Shi, P., Han, X., & Dai, J., 2023. Wind erosion from crusted playa surfaces by no saltation and with saltation: A comparison through laboratory wind tunnel experiments. International Soil and Water Conservation Research. Advance online publication. https://doi.org/10.1016/j.iswcr.2022.10.007
Zulfaqari, H., Masoompour, J., Shaygan Mehr, Sh., and Ahmadi, M., 2018. Observational survey of dust storms in the western regions of Iran during the years 2014 to 2018. Journal of Geography and Environmental Planning, 22(3), 17-45. [In Persian]. https://sid.ir/paper/153296/fa