Document Type : Research Paper
Authors
1 Gorgan University of Agricultural Sciences and Natural Resources, Gorgan, Iran
2 Islamic Azad university of Gorgan, Young researchers and elite club, Golestan, Iran.
Abstract
Introduction. Soil is an essential part of the environment. It is important for the production of food and other crops. Soil erosion and sedimentation are complicated and least well-known environmental problems worldwide (Mahmoodabadi et al, 2014). Recently, the application of compounds that modify and improve soil quality and also reduce soil erodibility has been more thoroughly researched. These compounds are known by the common name of soil amendments with a relatively high variety such as gypsum, basanite, zeolite, chemical amendments, organic additives, a variety of chemical, biological and composite polymers, soiltac, fungi, polyvinyl acetate, vermicompost and cattle manure, biochar, straw mulching and cyanobacteria and bacteria (Behzadfar et al, 2017). The objective of this study was to investigate the influence of bentonite clay and slope gradient on runoff and sediment concentration and some hydraulic Characteristics in the Loess soil using a rainfall simulator.
Materials and Methods The experiments were conducted using a rainfall simulator at the Soil Erosion and Conservation Laboratory, Gorgan University of Agricultural Sciences and Natural Resources, Iran. The soil used for the experiments is taken from the surface layer (0-30 cm depth) of loess lands from Golestan province (37° 55ʹ N and 55° 29ʹ E). The soil sample at first was air-dried, thoroughly mixed and then crushed to pass through 10 mm sieve size. Experiments were done as factorial based on completely random design with three replications. The factors were the bentonite clay at four level (0, 2, 5 and 10 % weight) and slope steepness at three level (10, 20 and 30%). In all experiments, each soil sample was put in the flume, then was saturated from the bottom for 24 h. Afterwards, the drainage water was removed out of the tray, and the experiment lasted for 45 min. For each rainfall event, the sediment-laden overland flow was sampled at selected time intervals and volumetrically measured. The sediment-laden overland flow was sampled at several time intervals and the sediment concentration was determined . The sediment in the collected samples was allowed to settle, separated from the water, and dried in an oven at 105 °C for 24 h. The sediment concentration was determined as the ratio of dry sediment mass to sampled runoff volume for each time interval.Different hydraulic parameters including flow depth, shear stress, stream power, and unit stream power were measured.
Results and Discussion The result showed that the sediment concentration decreased with increasing levels bentonite at all slopes. At 10 % slope steepness, the mean sediment concentration varied 32.48 in the control treatment to 24.67 kg m-3 at level 3 bentonite treatment. At 30% slope the corresponding value were 474.52 and 224.14 kg m-3. Therefore, with increasing slope steepness the sediment concentration increased. Totally, the use of bentonite at level 10 % weight could decrease 46% of sediment concentration in comparison with control treatment. Defersha and Melesse (2012) found that rain intensity and slope gradient had significant influences on sediment concentration. Slope gradient is important as more soil particles are splashed down-slope than up-slope (Dunne et al. 2010; Grismer 2012). According to Fig. 2, the obtained flow depth was 1.92×10−4, 1.92×10−4, 1.92×10−4 and 1.92×10−4 m for 0, 2, 5, 10% clay treatment, respectively. Also, the depth flow ranged from 3.6×10− 4 to 1.96×10−4 m on 10 to 30 % slopes. Totally, the depth of flow decreased with increasing slope steepness for all treatments. In fact, due to higher flow velocities at steeper slopes, shallower flow depths were achieved. Statistical analysis (Table 2) confirmed a significant positive main effects of application levels of bentonite and slope on shear stress, power flow and unit power flow. The clay treatment showed significant reductions ranging from 2 to 50% compared to the control treatment for all slopes. Unit stream power varied from 0.0084 to 0.0095 ms-1, 0.0176 to 0.0241 ms-1 and 0.030 to 0.057 ms-1 for 10, 20 and 30 % slope, respectively. Totally, with increasing slope steepness, all the hydraulic parameters, except flow depth, increased. While with increasing percentage of bentonite clay, shear stress and depth flow and stream power, decreased. Consequently, the maximum values were observed at the steepest slope (30 %) and control treatment (0%).
Conclusion Based on the results obtained during the present study, it can be concluded that the bentonite can be considered as an effective modifier of soil physicochemical properties leading to better performance in soil and water conservation in loess lands.
Keywords: Bentonite, Simulator Rain, Slope, Sediment Concentration, Hydraulic Characteristics
Keywords
- Abudi, I., Carmi, G., and Berliner, P. 2012. Rainfall simulator for field runoff studies. Journal of Hydrology. 454: 76-81.
- Ayoubi, S., Feizi, Z., Mosaddeghi, M.R., and Besaltpour, A.A. 2018. Investigating the application of biochar, bentonite clay and polyvinyl acetate polymer on some mechanical properties of sand deposits. Scientific Journal Management System. 41(2): 83-97.
- Behzadfar, M., Sadeghi, S.H., Khanjani, M.J., and Hazbavi, Z. 2017. Effects of rates and time of zeolite application on controlling runoff generation and soil loss from a soil subjected to a freeze-thaw cycle. International Soil and Water Conservation Research. 5(2): 95-101.
- Boroghani, M., Mirnia, S.K., Vahhabi, J., and Ahmadi, S.J. 2014. Investigation of nanozeolite effects on soil erosion decreasing using FEL3 rainfall simulator. Journal of Watershed Management Research. 5 (9): 95-106. (in Persian with English abstract)
- Cao, L., Zhang, K., Dai, H., and Liang, Y. 2015. Modeling interrill erosion on unpaved roads in the loess plateau of China. Land Degradation & Development. 26(8): 825-832.
- Catt, J. 2001. The agricultural importance of loess. Earth-Science Reviews. 54(1-3): 213-229.
- Defersha, M.B. and Melesse, A.M. 2012. Effect of rainfall intensity, slope and antecedent moisture content on sediment concentration and sediment enrichment ratio. 90: 47-52.
- Dunne, T., Malmon, D.V., and Mudd, S.M. 2010. A rain splash transport equation assimilating field and laboratory measurements. Journal of Geophysical Research: Earth Surface.115(1): 18-28.
- Foroumadi, M. and Vaezi, A.R. 2018. Flow Characteristics and Rill Erodibility in Relation to the Rainfall Intensity in a Marl Soil. Iran-Watershed Management Science & Engineering. 12: 11-22. (in Persian with English abstract).
- Fu, S., Liu, B., Liu, H., and Xu, L. 2011. The effect of slope on interrill erosion at short slopes. 84(1-2): 29-34.
- Gailani, J., Jin, L., McNeil, J., and Lick, W., 2001. Effects of Bentonite Clay on Sediment Erosion Rates. Army Engineer Waterways Experiment Station Vicksburg MS Engineer Research.
- Gee, G.W. and Or, D. 2002. 2.4 Particle-size analysis. Methods of soil analysis. Part. 4(598): 255-293.
- Giménez, R. and Govers, G. 2002. Flow detachment by concentrated flow on smooth and irregular beds. Soil Science Society of America 66(5): 1475-1483.
- Grismer, M. 2012. Standards vary in studies using rainfall simulators to evaluate erosion. California Agriculture. 66(3): 102-107.
- Hubert, C., 2004. The Hydraulics of Open Channel Flow: An Introduction. Elsevier Butterworth-Heinemann.
- Hui-Ming, S. and Yang, C.T. 2009. Estimating overland flow erosion capacity using unit stream power. International Journal of Sediment Research. 24(1): 46-62.
- Iserloh, T., Fister, W., Seeger, M., Willger, H., and Ries, J. 2012. A small portable rainfall simulator for reproducible experiments on soil erosion. Soil and Tillage Research. 124: 131-137.
- Iserloh, T., Ries, J., Arnáez, J., Boix-Fayos, C., Butzen, V., Cerdà, A., Echeverría, M., Fernández-Gálvez, J., Fister, W., and Geißler, C. 2013. European small portable rainfall simulators: A comparison of rainfall characteristics. 110: 100-112.
- Kamei, T., Ahmed, A., and Shibi, T. 2012. Effect of freeze–thaw cycles on durability and strength of very soft clay soil stabilised with recycled Bassanite. Cold Regions Science and Technology. 82: 124-129.
- Kheirabadi, H., Mahmoodabadi, M., Jalali, V., and Naghavi, H. 2018. Sediment flux, wind erosion and net erosion influenced by soil bed length, wind velocity and aggregate size distribution. 323: 22-30.
- Kheirfam, H., Sadeghi, S.H., Homaee, M., and Darki, B.Z. 2017. Quality improvement of an erosion-prone soil through microbial enrichment. Soil and Tillage Research. 165: 230-238.
- Kinnell, P. 2010. Comment on" A new splash and sheet erosion equation for rangelands". Soil Science Society of America Journal. 74(1): 340.
- Knapen, A., Poesen, J., Govers, G., Gyssels, G., and Nachtergaele, J. 2007. Resistance of soils to concentrated flow erosion: A review. Earth-Science Reviews. 80(1-2): 75-109.
- Kumar, A. and Saha, A. 2011. Effect of polyacrylamide and gypsum on surface runoff, sediment yield and nutrient losses from steep slopes. Agricultural Water Management. 98(6): 999-1004.
- Lassu, T., Seeger, M., Peters, P., and Keesstra, S.D. 2015. The Wageningen rainfall simulator: Set‐up and calibration of an indoor nozzle‐type rainfall simulator for soil erosion studies. Land Degradation & Development. 26(6): 604-612.
- Leh, M., Bajwa, S., and Chaubey, I. 2013. Impact of land use change on erosion risk: an integrated remote sensing, geographic information system and modeling methodology. Land Degradation & Development. 24(5): 409-421.
- Levy, G., Levin, J., and Shainberg, I. 1995. Polymer effects on runoff and soil erosion from sodic soils. Irrigation Science. 16(1): 9-14.
- Mahmoodabadi, M., Ghadiri, H., Rose, C., Yu, B., Rafahi, H., and Rouhipour, H. 2014. Evaluation of GUEST and WEPP with a new approach for the determination of sediment transport capacity. Journal of Hydrology. 513: 413-421.
- Mandal, D. and Sharda, V. 2013. Appraisal of soil erosion risk in the Eastern Himalayan region of India for soil conservation planning. Land Degradation & Development. 24(5): 430-437.
- Meyer, L., Rainfall simulators for soil erosion research, in Soil erosion research methods, Routledge. 83-104.
- Mi, J., Gregorich, E.G., Xu, S., McLaughlin, N.B., Ma, B., and Liu, J. 2017. Effect of bentonite amendment on soil hydraulic parameters and millet crop performance in a semi-arid region. Field Crops Research. 212: 107-114.
- Morgan, R.P.C. 2009. Soil erosion and conservation. John Wiley & Sons.
- Nearing, M., Norton, L., Bulgakov, D., Larionov, G., West, L., and Dontsova, K.M. 1997. Hydraulics and erosion in eroding rills. Water Resources Research. 33(4): 865-876.
- Page, A. 1965. Methods of soil analysis. Part 2. Chemical and microbiological properties. American Society of Agronomy, Soil Science Society of America. pp. 181-223.
- Refahi, H.G. 2006. Water erosion and conservation. University of Tehran, Iran, 671p. (In Persian).
- Sadeghi, S. and Hazbavi, Z. 2016. Watershed health assessment based on soil loss using reliability, resilience and vulnerability framework. in Proceedings of 19th PSSST Annual Meeting and Scientific Conference, Legaspi City, Albay.
- Sadeghi, S.H., Hazbavi, Z., and Harchegani, M.K. 2016. Controllability of runoff and soil loss from small plots treated by vinasse-produced biochar. Science of the Total Environment. 541: 483-490.
- Sadeghi, S.H., Hazbavi, Z., Younesi, H., and Bahramifar, N. 2016. Trade-off between runoff and sediments from treated erosion plots and polyacrylamide and acrylamide residues. 142: 213-220.
- Sajjadi, S.A. and Mahmoodabadi, M. 2015. Sediment concentration and hydraulic characteristics of rain-induced overland flows in arid land soils. Journal of Soils and Sediments. 15(3): 710-721.
- Sepaskhah, A. and Bazrafshan-Jahromi, A. 2006. Controlling runoff and erosion in sloping land with polyacrylamide under a rainfall simulator. Biosystems Engineering. 93(4): 469-474.
- Sirjani, E. and Mahmoodabadi, M. 2012. Study on flow erosivity indicators for predicting soil detachment rate at low slopes. International Journal of Agricultural Science, Research and Technology. 2(2): 55-61.
- Sirjani, E. and Mahmoodabadi, M. 2014. Effects of sheet flow rate and slope gradient on sediment load. Arabian Journal of Geosciences. 7(1): 203-210.
- Walkley, A. and Black, I.A. 1934. An examination of the Degtjareff method for determining soil organic matter, and a proposed modification of the chromic acid titration method. Soil Science. 37(1): 29-38.
- Wang, H.Q., Zhao, Q., Zeng, D.H., Hu, Y.L., and Yu, Z.Y. 2015. Remediation of a magnesium‐contaminated soil by chemical amendments and leaching. Land Degradation & Development. 26(6): 613-619.
- Zhang, K., Zhang, W., Tan, L., An, Z., and Zhang, H. 2015. Effects of gravel mulch on aeolian transport: a field wind tunnel simulation. Journal of Arid Land. 7(3): 296-303.
- Zhu, X., Risse, L., McCutcheon, S., Tollner, E., Rasmussen, T., and West, L. 2010. Laboratory investigation of rill erosion on compost blankets under concentrated flow conditions. Transactions of the ASABE. 53(4): 1077-1086.