Impacts of oak deforestation and rainfed cultivation on soil redistribution processes across hillslopes using 137Cs techniques

被引:19
作者
Ayoubi, Shamsollah [1 ]
Sadeghi, Nafiseh [1 ]
Afshar, Farideh Abbaszadeh [2 ]
Abdi, Mohammad Reza [3 ]
Zeraatpisheh, Mojtaba [4 ,5 ]
Rodrigo-Comino, Jesus [6 ,7 ]
机构
[1] Isfahan Univ Technol, Coll Agr, Dept Soil Sci, Esfahan 8415683111, Iran
[2] Univ Jiroft, Coll Agr, Dept Soil Sci, Kerman, Iran
[3] Univ Isfahan, Fac Sci, Dept Phys, Esfahan 8174773441, Iran
[4] Henan Univ, Henan Key Lab Earth Syst Observat & Modeling, Kaifeng 475004, Peoples R China
[5] Henan Univ, Coll Environm & Planning, Kaifeng 475004, Peoples R China
[6] Univ Trier, Dept Phys Geog, Trier, Germany
[7] Univ Valencia, Dept Geog, Soil Eros & Degradat Res Grp, Valencia, Spain
关键词
Land-use change; Soil redistribution; Topographical changes; Radionuclide; Rainfed farming; Deforestation; LAND-USE CHANGES; CALCAREOUS SOILS; SEMIARID REGION; EROSION RATES; PHYSICAL-PROPERTIES; MAGNETIC MEASURES; ORGANIC-MATTER; CENTRAL ZAGROS; COVER CHANGES; CARBON;
D O I
10.1186/s40663-021-00311-1
中图分类号
S7 [林业];
学科分类号
0829 ; 0907 ;
摘要
Background As one of the main components of land-use change, deforestation is considered the greatest threat to global environmental diversity with possible irreversible environmental consequences. Specifically, one example could be the impacts of land-use changes from oak forests into agricultural ecosystems, which may have detrimental impacts on soil mobilization across hillslopes. However, to date, scarce studies are assessing these impacts at different slope positions and soil depths, shedding light on key geomorphological processes. Methods In this research, the Caesium-137 (Cs-137) technique was applied to evaluate soil redistribution and soil erosion rates due to the effects of these above-mentioned land-use changes. To achieve this goal, we select a representative area in the Lordegan district, central Iran. Cs-137 depth distribution profiles were established in four different hillslope positions after converting natural oak forests to rainfed farming. In each hillslope, soil samples from three depths (0-10, 10-20, and 20-50 cm) and in four different slope positions (summit, shoulder, backslope, and footslope) were taken in three transects of about 20 m away from each other. The activity of Cs-137 was determined in all the soil samples (72 soil samples) by a gamma spectrometer. In addition, some physicochemical properties and the magnetic susceptibility (MS) of soil samples were measured. Results Erosion rates reached 51.1 t center dot ha(- 1)center dot yr(- 1) in rainfed farming, whereas in the natural forest, the erosion rate was 9.3 t center dot ha(- 1)center dot yr(- 1). Magnetic susceptibility was considerably lower in the cultivated land (chi(hf) = 43.5 x 10(- 8) m(3)center dot kg(- 1)) than in the natural forest (chi(hf) = 55.1 x 10(- 8) m(3)center dot kg(- 1)). The lower soil erosion rate in the natural forest land indicated significantly higher MS in all landform positions except at the summit one, compared to that in the rainfed farming land. The shoulder and summit positions were the most erodible hillslope positions in the natural forest and rainfed farming, respectively. Conclusions We concluded that land-use change and hillslope positions played a key role in eroding the surface soils in this area. Moreover, land management can influence soil erosion intensity and may both mitigate and amplify soil loss.
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页数:14
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