Investigating Marl Formation and their Dominant Land use and Erosion in Kermanshah Province

Document Type : Research Paper

Authors

1 Department of Soil Conservation and Watershed Management, Kermanshah Agricultural and Natural Resources Research and Education Center, Agricultural Research, Education and Extension Organization (AREEO), Kermanshah, Iran

2 2Department of Soil Conservation Soil Conservation, Soil Conservation and Watershed Management Research Institute, Agricultural Research, Education and Extension Organization (AREEO), Tehran, Iran

3 Department of Geography, Faculty of Literature and Humanities, Razi University, Kermanshah, Iran

4 4Department Education, Kermanshah Agricultural and Natural Resources Research and Education Center, Agricultural Research, Education and Extension Organization (AREEO), Kermanshah, Iran

Abstract

Land use/cover change at the geological marl formations, especially the conversion of forest and rangeland areas to rain-fed lands and subsequent improper tillage practice has led to severe soil erosion and sedimentation, soil moisture lost, dust-blown, global warming, and water pollution. The current study aims to prepare the spatial distribution of marl formation in Kermanshah province in Iran and to assess dominant land-use, plant cover, slope, and erosion features using satellite image (SPOT 2000) and field survey. The field data have been analyzed through ArcGIS software. The results of this study reveal that there are eight major marls formations in Kermanshah province including Amiran, Aghajari, Gachsaran, Gurpi, Talezangh, Kashkan, Pabdeh, and Mishan occupying about 24.21 % of province areas. Among these formations, three formations including Amiran, Kashkan, and Aghajari are the most vulnerable to degradation due to topographic conditions, high solubility, and improper land-use practices. The sensitive facies of Amiran and Kashkan Formations are more prominent in the forest and rain-fed areas with hill slope conditions. In these areas, deforestation, illegal charcoal extraction, improper agricultural and non-agricultural activities resulted in the dissolution of sensitive layered and consequently landslide incidents. Thus during each effective rainfall occurrence, there is severe erosion and siltation deliver fresh sediment in lower drainage systems affecting road, brigs, and farmlands. In gentle slope, this process causes head-cut and gully development. Aghajari formation, which covers a wide range of winter pastures in Kermanshah province, has a high potential of dissolution due to its mineralogical and soil properties increasing soil erosion and sediment yield. It is concluded that severe land use/cover change at marl formation of Zagros areas are the factors sensitive to soil erosion, sedimentation and flood hazard as well as the solution of serous crises such water deficiency and desertification.
Extended Abstract
1-Introduction
 Geological Marl formations and their deposits are more sensitive to degradation and soil erosion factors. The considerable areas of Zagros regions in Iran comprise marl formations dominated by forest and rangeland land uses. These marls are different condition of topography and land use/cover, while they are characterized by high level of clay and slit contents and dominant swell-shrink clay minerals. Thus, the soils originated from these marl formations are vulnerable to plant cover degradation causing severe erosion, sediment and flood hazards. Landus in marly areas are forest and rangeland, hence; converting them to rain-fed areas and subsequently improper human practices such as heavy tillage and civil activities cause gully erosion and other soil erosion features, landslide occurrences, soil moisture lost and organic carbon emission. However, survey on marl formations in terms of land use/cove and dominant soil erosion at local scale are necessary steps to control environmental hazards, especially erosion, sediment, flood as well as drought, dust and water shortage managements in watersheds of west and east west of Iran. The present study aims to determinate the marl formation areas and to make a map for their distribution recognizing, some important local features like erosion in Kermanshah province (a part of upper Karkheh catchment) in Iran which were carried out during 2017-2020.  
2-Materials and Methods
 This research conducted in Kermanshah province comprising verity of geological formations mainly marl deposits which are the hilly and plain topography. In other to achieve this research, the border of each marl formation was mapped using basal geological map and field verification. Next the dominant erosion feature was determined using satellite image (SPOT), but the land use was mapped through Landsat 8 (2015). Finally, field survey carried out for exploring details of land use and erosion features using GPS. The soil erosion features were inter-rill, rill, gully and landslide. Furthermore, land use was forest, rangeland and agricultural areas.  The spatial distribution and area of main erosion feature and land use within each marl formation was mapped using ArcGIS.
3-Results and Discussion
The findings reveal that there are eight major marl formations in Kermanshah province including Amiran, Aghajari, Gachsaran, Gurpi, Talezangh, Kashkan, Pabdeh, and Mishan occupying approximately 603 million ha (24.21 % of province areas).Among these formations, three formations of Amiran, Kashkan, and Aghajari are the most vulnerable to degradation due to higher area, topographic conditions, high solubility, and improper land-use practices. Field verification showed that solubility phenomenon in both Kaskan and Amiran formations is considerable where, forest and rangeland are degraded or rain-fed areas is subjected to up-down the slope tillage practice. They are more sensitive to land use change and field survey showed severe inter-rill, rill and landslide incidence where subjected to converting forest, tillage practice, charcoal extraction and improper civil activities. In some areas, that forest is wholly cleared, after each effective rainfall occurrence, fresh sediment from hill slope of Amiran and Kashkan damage the road, bridge, riverside and lowland agricultural areas. Moreover, in plane areas, dissolve phenomenon contributes to head-cut activity developing of gully erosion. For instance, in Bujan area (SW Kermanshah city), sever tunneling erosion and landslide are delivered the fresh sediment comprising greenish clay and slits fractions during rainfall. This sediment moves down through runoff in parallel to slope furrow of tillage at the rain-fed lands. Consequently, this sediment contaminates surface water, accelerates local flood hazard and covers farmlands in lower parts. It can be said that the deforestation rate is less visible in this province. Therefore, as one of the upstream branches of Karkheh basin, it has a key origin of flood occurrence and sediment yield and its accelerating damages in Lorestan (Pol-e Dokhtar) and Khuzestan provinces. This destruction continues in an astonishing way, away from improper management and monitoring. Aghajari formation, which covers a wide range of winter pastures in Ghasr-e-shirin, has a high potential of dissolution phenomenon due to its mineralogical and soil properties increasing soil erosion and sediment yield. It is more vulnerable, where subjected to land use change, particularly converting rangeland to irrigation lands.
4-Conclusion
According to findings, most of the marl formations in Kermanshah province have more outcrops in the upper and middle parts of watersheds and continue in Lorestan, Ilam and Khuzestan provinces which induces same conditions for environmental hazards such as floods, soil erosion and dust phenomena. The reason for the destruction of these marl formations is the change in land use, especially the conversion of forests and rangeland to rain-fed areas causing various forms of erosion, including dissolution, rill, gully and landslides. Field studies reveal that most facies of these marl formations contain clay, silt and shale with thin to medium sandstone layers. Due to mineralogical property and high amounts of clay and silt fractions as well as topographic factors, they are prone to dissolution, erosion and landslides hazard, which are increased by land use change in forest and rangeland areas, vegetation destruction and improper tillage practice. In this condition, fine-grained sediments reach the drainage system during rainfall time. The consequencs of this process, in addition to sediment, are the flood hazard, water shortages impacting proper management of such crises in the Zagros regions. In Qasr-e-shirin areas, extensive land use change at Aghajari formation not only causes soil erosion, sediment and flood problems, but also potentially is the dust blown origin due to the prevailing wind direction (from east to west), that can affect Kermanshah, Lorestan, Hemedan and Markazi province of Iran.

Keywords


References
Bernatek-Jakiel, A. & Poesen, J. (2018). Subsurface erosion by soil piping: Significance and research needs. Earth-Science Reviews185, 1107-1128.
Blanco, H. & Lal, R. (2008). Principles of soil conservation and management (Vol. 167169). New York: Springer.
Borchardt, G. (1989). Smectites. Minerals in soil environments1, 675-727.
Darvishzadeh, A. (1991). Iran geology. Lahore: Nashre-Danesh Publishing Company (In Persian).
Ebrahimzadeh, S., Bazrafshan, J. & Ghorbani, Kh. (2013). Comparative Study Between Satellite and Ground-based Drought Indices Using Change Vector Analysis Technique (Case Study of Kermanshah Province). Journal of Water and Soil, 27 (5), 1034-1045 (In Persian).
Feiznia, S., Heshmati, M., Ahmadi, H. & Ghodosi, J. (2008). Investigation of gully erosion in Marly Agha-Jari formation in Zagross (Case study: Ghasre-Shirin, Kermanshah). Iranian Academic J. Pajouhesh and Sazandegi, 20 (1), 32-40 (In Persian).
Gheitury, M., Heshmati, M. & Ahmadi, M. (2019). Longterm Land use Change Detection in Mahidasht Watershed, Iran. Ecopersia7 (3), 141-148.
Ghobadi, M.H, Rafiei, B., Heydari, M., Mousavi, S. & Sfandiari, M. (2014). The geochemistry and provenance of Aghajari sandstones in Khouzestan province. Applied Sedimentology, 2 (3), 48-61 (In persian).
Haghgow, K., Rostami, N., Heshmati, M. & Faramarzi, M. (2017). Investigation of Desertification Potential Using IMDPA Model (Case Study: The Gandomban Plain, Qasr-e-Shirin). Geography and Sustainability of Environment, 7 (1), 21-33 (In Persian).
Heshmati, M. & Geitouri, M. (2018). Land-use Change; Achilles heel to Overcoming the Environmental Crisis, Process and Impacts. Geography and Sustainability of Environment, 8 (1), 89-105 (In Persian).
Heshmati, M., Arifin, A., Shamshuddin, J. & Majid, N. M. (2012). Predicting N, P, K and organic carbon depletion in soils using MPSIAC model at the Merek catchment, Iran. Geoderma175, 64-77.
Heshmati, M., Gheitouri, M., Parvizi, Y. & Hosini, M. (2015). Effect of converting forest to rainfed lands on spatial variability of soil chemical properties in the Zagros forest, western Iran. Ecopersia3 (4), 1161-1174.
Heshmati, M., Gheitouri, M., Sheikhvaisi, M., Arabkhedri, M. & Hosini, M. (2017). Combating the Forest Mortality Crises in Zagros Regions, Iran through Adaptive Approaches Solutions. Journal of Geography and Environmental Hazards6 (3), 125-141(In Persian).
James, G. A. & Wynd, J. G. (1965). Stratigraphic nomenclature of Iranian oil consortium agreement area. AAPG bulletin49 (12), 2182-2245.
Kamali, K., Zehtabian, G., Mesbahzadeh, T., Arkhazloo, H. S., Arabkhedri, M. & Moghaddamnia, M. (2020). Evaluation of the Soil Sustainability Indices in Desert Areas (Case study: Rangeland and Agriculture fields of Semnan). Range and Watershed Management, 73 (1), 183-198 (In Persian).
Karam, A., Ranjbar, M., Eftekhari, M. & Yaghoob Nejad, N. (2014). Classification of Morph climatic Zones of Kermanshah Province Using Cluster Analysis Method. Geography, 11 (39), 234-255 (In Persian).
Karimi-Bavandpoor, A., Hajihosaini, A. & Shahandi, M. (1999). Geological Map of Kermanshah: 1:100,000 Series: 5458. Tehran: Geological Survey of Iran Publisher (In Persian).
Karlen, D. L., Tomer, M. D., Neppel, J. & Cambardella, C. A. (2008). A preliminary watershed scale soil quality assessment in north central Iowa, USA. Soil and Tillage Research99 (2), 291-299.
Kosmas, C., Tsara, M., Moustakas, N., Kosma, D. & Yassoglou, N. (2006). Environmentally sensitive areas and indicators of desertification. In Desertification in the Mediterranean Region. A Security Issue, (pp. 525-547). Springer, Dordrecht.
Lutenegger, A. J. & Cerato, A. B. (2001). Surface area and engineering properties of fine-grained soils. In: Proceedings of the Fifteenth International Conference on Soil Mechanics and Geotechnical Engineering, Istanbul, Turkey, 27-31 August 2001. Volumes 1-3 (pp. 603-606). AA Balkema.
Miall, A. D. & Postma, G. (1997). The geology of fluvial deposits, sedimentary facies, basin analysis and petroleum geology. Sedimentary Geology110 (1), 149.
Mohseni, H., Toulabi, M., Yosefi Yeganeh, B., Khodabakhsh, S. (2014). Organic geochemistry of the Amiran Formation in the Amiran anticline, SW of Lorestan. Applied Sedimentology, 2 (4), 75-89 (In persian).
Mutiee, H. (1993). Zagros Stratigraphy (1), In: E. Hoshmandzadeh, (Eds.), Tehran: Geology of Iran, Geological Survey of Iran (In Persian).
Nael, M., Khademi, H. & Hajabbasi, M. A. (2004). Response of soil quality indicators and their spatial variability to land degradation in central Iran. Applied soil ecology27(3), 221-232.
Nasiri, Y., Mahboubi, A., Moussavi-Harami, S. R. & Yousefi, B. (2013). Cyclic Sedimentation of the Amiran Formation for Subsurface Characterization in the Zagros fold–thrust belt (Application of Markov Chain Method in depositional sequences interpretation). Journal of Tethys1 (2), 113-127.
Nemati Paykani, M. & Jalilian, N. (2013). Medicinal plants of Kermanshah province. Taxonomy and Biosystematics, 4 (11), 69-78 (In Persian).
Owliaie, H. R., Abtahi, A. & Heck, R. J. (2006). Pedogenesis and clay mineralogical investigation of soils formed on gypsiferous and calcareous materials, on a transect, southwestern Iran. Geoderma134 (1-2), 62-81.
Parvizi, Y., Gheitury, M. & Heshmati, M. (2015). Capability of hillslope version of WEPP model in prediction of runoff and soil erosion dynamic in different type of semi-arid rangeland. Journal of Range and Watershed Management, 67 (4), 501-513 (In Persian).
Parvizi, Y., Heshmati, M. & Gheituri, M. (2017). Intelligent approaches to analysing the importance of land use management in soil carbon stock in a semiarid ecosystem, west of Iran. Ecopersia5 (1), 1699-1709.
Rostami, F., Feiznia, S., Aleali, M., Heshmati, M. & Yousefi Yegane, B. (2019). Erodibility and sedimentation potential of marly formations at the watershed scale. Global Journal of Environmental Science and Management5 (3), 383-398.
Rust, B. R. (1978). Depositional models for braided alluvium. In: A. D. Miall, (Ed.), Fluvial sedimentology. Canadian Society of Petroleum Geologists Memoir, 5, 605-626.
Shahbazi, K., Salajagheh, A., Jafari, M., Ahmadi, H., Nazarisamani, A. & Khosrowshahi, M. (2017). Comparative Assessment of Gully Erosion and Sediment Yield in Different Rangelands and Agricultural Areas in Ghasr-e-Shirin, Kermanshah, Iran. Journal of Rangeland Science7 (3), 296-306.
Sokouti, R., Mahdian, M. H. & Farshad, A. (2009). The effects of physical and chemical properties of marl derived soils on the erosion forms and rates. In: Goldschmidt Conference Abstracts. A (Vol. 1246).
Vaezi, A. R. & Foroumadi, M. (2018). Flow characteristics and rill erodibility in relation to the rainfall intensity in a marl soil. Iranian Journal of Watershed Management Science and Engineering, 12 (40), 11-22 (in Persian).
Vaezi, A. R., Hasanzadeh, H. & Mohammadi, M. H. (2013). Runoff variations in the soil textures samples in the plot scale under the same rainfall events. Iranian Journal of Soil and Water Research, 44 (3), 243-253 (in Persian).
Wani, P. P. & Sudi, R. (2006). Gully control in SAT watershed. International Crops Research Institute for the Semi-Arid Tropics2 (1), 28.
Wright, V. P. (2007). Calcrete. Geochemical sediments and landscapes, 10-45.
Zarei Sahmie, R., Yousefi Yeganeh, B., Zamanian. H. & Moazmi Godarzi, F. (2012). Study of sedimentary environment and geochemistry of Kashkan formation. Advanced Applied Geology, 1 (1), 48-62 (In Persian).
Zolfaghari, H. (2006). Study of natural seasons in Kermanshah province. Geographical Researches, 20 (1), 90-106 (In Persian).