Investigation of Chemical Properties of Eroded Particles at Four Heights with Surface Soil

Document Type : Research Article

Authors

1 Department of Soil Science, Science and Research Branch, Islamic Azad University, Tehran, I.R. IRAN

2 Department of Soil science, Tabriz Branch, Islamic Azad University, Tabriz, I.R. IRAN

Abstract

The chemical analysis of dust particles is essential to assess the potential impacts of dust on climate, environment, soil, and health. The objective of this study is to compare the different chemical compositions of dust particles that are collected at different heights above the soil surface and the eroded soils around Lake Urmia. To trap the dust particles, the BSNE samplers were used. 14 poles were installed inside 3 ha. area and 4 samplers were installed on each pole at 0.15, 0.5, 1, and 2 m heights above the soil surface. Chemical properties such as %T.N.V, %OC, ECe, pH, and SAR of collected particles were determined. The results of variance analysis and mean comparison illustrated that there was no significant difference between the eroded soil and the particles sampled from 15 cm height among all the investigated chemical parameters. It proves that the source of the moving particles at > 0.15 m is different from the eroded soil. By elevating height above the soil surface increased, the %T.N.V, ECe, and pH decreased but the SAR and %OC increased. There was a strong negative and significant correlation between the monthly rainfall and the ECe, %T.N.V, and SAR, except for the %OC. The correlation between the speed of the strongest wind and the ECe, %OC, and SAR was positive and remarkable (P≤0.01). The pH was the only parameter that was independent of all meteorological parameters in this research. Furthermore, the SAR was the most sensitive factor to the meteorological parameters.

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Main Subjects


[1] Nachtergaele F., Food and Agriculture Organization of the United Nations (FAO), “Status of the world’s soil resources Main Report”, Chapter 6, Global Soil Status, Processes, and Trends, 101 (2015).
[2] Ekhtesasi M.R., Zare Cahokia A., “Estimation of Wind Erosion in Iran with IRF 1 and 2 Models and Strategies for Reducing Its Effects”, The Second International Congress of Geosciences, Tehran, Iran, 22 to 24 February (2016).
[3] Yunes Zadeh Jalili S., Javadian M., Tajrishi M., Taheri Sharaeni H., “Estimation of the Water Area of ​​Lake Urmia During 2013-2016 using Landsat 8 Satellite Images”, 7th National Conference on Water Resources Management of Iran. Yazd, Iran (2018).
[4] Dehgan P., Vali Zadeh S., Khosravi H., “Investigating the Factors of Drying Up of Lake Urmia and its Remediation Strategies”, Second National Conference on Water, Human and Land, Isfahan, Iran (2016).
[5] Vafayian M., Hanjari R.A., Mirzapoor Pirdosti A., “Causes of Drought in Lake Urmia”, Third National Conference on Civil Engineering and Sustainable Development of Iran, Tehran, Iran (2017).
[6] Zhang K.C., Qu J.J., Zu R.P., Fang H.Y., Temporal Variations of Sand Storms in Minqin Oasis During 1954–2000, Environmental Geology, 49: 332-338 (2005).
[7] Lak R., DarvishiKhatoni J., Mohammadi A., Paleolimnological Studies and Causes of Sudden Decrease in Water Level of Urmia Lake, Journal of Applied Geology, 7(4): 343-358 (2012).    
[9] Mirza Mustafa N., Hagen L.J., Stone L.R., Skidmore E.L., Soil Aggregate and Texture Effects on Suspension Components from Wind Erosion, Soil Sci. Soc. Am. J. 62(5): 1351-1361 (1998).
[10] Wang G., Wanquan T., Mingyuan D., Flux and Composition of Wind-Eroded Dust from Different Landscapes of an Arid Inland River Basin in North-Western China, Journal of Arid Environment, 58: 373-385 (2004).
[11] Zobeck T.M., Fryrear D.W., Chemical and Physical Characteristics of windblown sediments. II. Chemical Characteristics and Total Soil and Nutrient Discharge, Transactions of the ASAE, 29(4): 1037- 1041 (1986).
[12] Engelbrecht J.P., Stenchikov G., Parkashi P.J., Lersch T., Anisimov A., Shevchenko I., Physical and Chemical Properties of Deposited Airborne Particulates over the Arabian Red Sea Coastal Plain. Atmospheric Chemistry and Physics, 17(18): 11467-11490 (2017).
[13] Karthikeyan P., Vennila G., Subramani T., Prakas R., Aswini M. K., Assessment of heavy metals in the surface sediments of the Emerald Lake using of spatial distribution and multivariate techniques. Environmental Monitoring and Assessment, 190(668): 1-18 (2018).
[14] Goel V., Mishra S.K., Pal P., Ahlawat A., Vijayan N., Jain. S. and Sharma Ch., Influence of chemical Aging on Physico-Chemical Properties of Mineral Dust Particles: A Case Study of 2016 Dust Storms over Delhi, Environmental Pollution, 267: 115338 (2020).
[15] Attiya A.A., Jones B.G., Assessment of Mineralogical and Chemical Properties of Airborne Dust in Iraq, SN Applied Sciences, 2: 1614 (2020).
[16] Abdollahi A., Rahbani M., “Urmia Lake Drying and Solutions for Exiting the Crisis”, Second National Conference on Agriculture and Development, Tehran, Iran (2015).
[17] Bani Habib M.E., Garashi Abhari S.M.A., Evaluation of Proposed Strategies for Dealing with Lake Urmia Crisis Based on Sustainable Development Criteria, Journal of Water Resources Systems Management, 1(1): 1-12 (2017).
[18] Hasan Zadeh Y., “Investigating the Causes of Urmia Lake Water Level Reduction and Presenting Remedies”, 5th International Congress of Islamic Geographers, Tabriz, Iran (2012).
[19] Chepil W.S., The Width of Field Strips to Control Wind Erosion, Kansas Agric. Exp. Sta. Tech. Bull. 92. P: 16 (1957).
[20] Fryrear D.W., Stout J.E., Hagen L.J., Vories E.D., Wind Erosion: Field Measurement and Analysis, American Society of Agricultural Engineers, 34(1): 155-160 (1991).
[21] Fryrear D.W., A Field Dust Sampler, Journal of Soil and Water Conservation, 41(2): 117-120 (1986).
[22] Goossens D., Offer Z.Y., Wind Tunnel and Field Calibration of Six Aeolian Dust Samplers, Atmospheric Environment, 34: 1043-1057 (2000).
[23] Dong Z., Man D., Luo W., Qian G., Wang J., Zhao M., Liu S., Zhu G., Zhu S., Horizontal Aeolian Sediment Flux in the Minqin Area, a Major Source of Chinese Dust Storms, Geomorphology, 116: 58-66 (2010).
[25] Shannak B., Corsmeier U., Kottmeier Ch., Al-Azab T., Wind Tunnel Study of Twelve Dust Samples by Large Particle Size, Atmospheric Environment, 98: 442-453 (2014).
[27] Stout J.E., Fryrear D.W., The Performance of a Windblown-Particle Sampler, Transactions of the ASAE, 32(6): 2041- 2045 (1989).
[28] Sparks D.L, Page  A.L., Helmke P.A., Loeppert R.H., Soltanpour P.N., Tabatabai M.A., Johnston C.T., Sumner M.E., “Methods of Soil Analysis, Part 3, Chemical Methods,” ASA and SSSA, Madison, (1996).
[30] Shao Y., “A Model for Mineral Dust Emission”, Journal of Geophysical of Research Atmospheres, 106(17): 20239-20254 (2001).
[31] Xiao X., Yang G., “The Disasters and Prevention of Sand Storms in North-Western China”, Chinese Environmental Science Press, Beijing, 128 (1996).
 [32] Zabihi F., Esfandiari M., Dalalian M.R., Moeini A., Horizontal Flux of Suspended Particles Sampling by Big Spring Number Eight (BSNE) Sampler in Lake Urmia Area, Applied Ecology and Environmental Research, 16(2): 1313-1327 (2018).
[33] “Soil pH & Lime”, The Fertilizer Association of Ireland, In Association with Teagasc, Technical Bulletin Series No.2, Ireland. (2016).
[34] Fatubarin A., Olojugba M. R., Effect of Rainfall Season on the Chemical Properties of the Soil of a Southern Guinea Savanna Ecosystem in Nigeria, Journal of Ecology and the Natural Environment, 6(4): 182-189 (2014)
[35] Cui Y., Chen J., Zhang Y., Peng D., Huang T., Sun C., pH-Dependent Leaching Characteristics of Major and Toxic Elements from Red Mud, Int. J. Environ. Res. and Public Health, 16(11): 1-16 (2019).
[36] Karim Zadeh H.R., Jalalian A., Application of BSNE Sampler in Investigating the Vertical Distribution of Eroded Wind Sediment in the Eastern Part of Isfahan. Agricultural Sciences and Technology and Natural Resources, 6(3): 121-138 (2002). 
[37] USDA, NRCS (Natural Resources Conservation Service), Soil Electrical Conductivity, Soil Quality Kit, Guides for Educators, 1-7 https://www.nrcs.usda.gov/Internet/FSE_DOCUMENTS/nrcs142p2_053280.pdf
[38] Che Othaman N.N., Md Isa M.N., Ismail R.C., Ahmad M.I., Hui C.K., Factors that Affect Soil Electrical Conductivity (EC) Based System for Smart Farming Application, AIP Conference Proceedings 2203: 020055 (2020).
[39] Shemshaki A., Karami Gh.H., Comparison of quantity and quality changes of the Urmia lake water with Emphasis on the Southeast Bank Data. Scientific Quarterly Journal, Geoscinses, 26(103): 101-106 (2017).
[41] Taghipour M., Yaghmaeian Mahabadi N., Shabanpour M., Effect of Land Use Change on Organic Carbon Storage in Aggregates and Bulk Soil in Tootkabon Area, Guilan Province, Journal of Soil Research (Soil and Water Sciences), 33(4): 577-590 (2020). 
[42] Mansori E., Emami H., Karimi A.R., Parvizi Y., Investigating the Factors Affecting Soil Organic Carbon in a Climatic Section in Kermanshah Province, Natural Environment, 70(1): 197-210 (2017).
[43] Sheyday Karkaj E., Sepehri A., Barani H., Motamedi J., Relationship between Soil Organic Carbon Storage and some Soil Properties in the Pastures of East Azerbaijan, Journal of Rangeland Research, 11(2): 125-138 (2017).
[44] Minz S., Gara S., Gupta R. Effect of Operating Parameters, Reaction Kinetics and Comparative Assessment of Fluidized-Bed Fenton Oxidation of 4-Nitrophenol, Iranian Journal of Chemistry and Chemical Engineering (IJCCE), 40(2): 539-550 (2021).
[45] Hashemi H., Pajoum Shariati F., Delavari Ameri H., Heydarinasab A., The Effect of Instantaneous and Slow-Release Salt Stress Methods on Beta-Carotene Production within Dunaliella Salina Cells, Iranian Journal of Chemistry and Chemical Engineering (IJCCE), 40(5): 1642-1652 (2021).