Document Type : Research Paper

Authors

1 Master student of soil science department, Shahid Chamran University of Ahvaz, Iran

2 Assistant professor of soil science department, Faculty of Agriculture, Shahid Chamran University of Ahvaz, Ahvaz, Iran

3 Faculty member of Water Engineering Department, Agricultural Sciences and Natural Resources University of Khuzestan, Mollasani, Iran.

4 Scientific member of soil science department, Faculty of Agriculture, Shahid Chamran University of Ahvaz, Ahvaz, Iran

Abstract

Introduction
Soil degradation is a phenomenon which destructs the soil structure and mitigates its capacity for production. Among several processes that cause soil degradation, soil erosion as one of the most common forms of soil degradation leads to loss of soil surface and including on-site and off-site effects. Although soil erosion is a natural process on the earth, but destructive human activities such as burning agriculture residue, deforestation, overgrazing, and lack of proper soil conservation practices; accelerate the soil erosion and enhance the negative outcomes of erosion. Selecting and implementing of management scenarios requires assessment of soil losses from different management operations. Generally, management practices consist of structural and non-structural methods that used to reduce erosion, prevent nutrient removal, and increase soil infiltration capacity. Application of simulation models is an appropriate technique to evaluate erosional conditions. GeoWEPP is a process-based, distributed parameters and continuous simulation model of water erosion in watersheds with the possibility to simulate hillslopes and hydrographical network. Locating problems in real world usually face with a large amount of information and decision space that need to be optimized using evolutionary algorithms due to the variety of aims considered. Considering diversity of evolutionary algorithms, NSGA-II is one of the most common and a usable multiobjective evolutionary algorithm (MOEA) which is very powerful tool for solving problems with conflicting objectives. Development of simulation models along with optimization algorithms that are capable of analyzing very complex systems, have found to be very efficient in real world problems. Simulation-optimization models are powerful tools for solving problems for least cost and best performance.
Methods and materials
To predict sediment yield and runoff in the studied watershed, the GeoWEPP integrates WEPP model with TOPAZ (Topography Parameterization), CLIGEN (Climate Generation) and GIS tool (ArcGIS). The GeoWEPP model provides the processing of digital data including DEM ASCII file, soil ASCII file and landcover ASCII file. To generate climate file, the CLIGEN module which is a stochastic weather generation model was utilized. Furthermore in TOPAZ part the CSA (critical source area) and MSCL (minimum source channel length) to delineate streams and also the outlet point of studied watershed were defined using GeoWEPP linked to ArcGIS. Using the basic maps including DEM, slope, soil great groups and soil database the GeoWEPP model simulates and generates the hillslopes automatically; therefore this is an important advantage of GeoWEPP compared to WEPP model which is capable of performing the simulation of watershed components spontaneously. In this study in order to optimize the placement of Gabions, 118 channels and 5110 candidate sites for gabion construction were simulated and evaluated. For optimization process; regarding the number of objectives firstly the AHP technique was used to prioritize the effective factors on the placement of Gabions. Analytical hierarchy process is a structured technique for organizing and analyzing complicated decisions based on mathematical calculations. The AHP depicts the accurate approach for quantifying the weights of criteria and estimates the relative magnitudes of factors through pair-wise comparisons. The AHP technique includes creating hierarchical structure, prioritizing and calculating relative weights of the criteria, calculating the final weights and system results compatibility. The main criteria (objectives) for our study were minimum distance from road, minimum distance from residential area, maximum length of main channel, maximum sediment yield, maximum discharge volume and maximum volume structure. Indeed using the AHP technique it was possible to restrict the decision making space and the number of possible options, therefore simplify the optimization process. Then NSGA-II (Non-dominated Sorting Genetic Algorithm) was applied in order to find the best solutions, i.e. the Pareto front, of alternatives for optimal location of structures based on the two objectives with higher priority and distance constraint.

Results and discussion
The results of paired comparison matrix and prioritizing showed that the length of main channel in the watershed is the main effective criterion in locating Gabion structures. The first priority is considered as the most critical channel which produces the highest sediment yield; therefore the most expensive structure is established on that channel. After channel length, the volume discharge was the second priority of effective factors for gabion placement. Using the results of AHP, based on channel length and discharge volume the non-dominated sorting genetic algorithm (NSGA-II) was performed and the priority of critical channels and the specific position was determined from 1 to 35 among 5110 candidate sites for Gabion construction. Using the ArcGIS, slope map and the lowest width of the critical channels the place for gabion construction as a point was determined. Moreover the main output of GeoWEPP is the spatial distribution of sediment yield and based on this map the sediment yield was classified in the watershed. Based on this map the red color was the highest amount of sediment yield (more than 4 ton) in the watershed.
Conclusion
Results confirmed that application of simulation-optimization techniques helps to select the best sites to construct the Gabion as structural best management practice therefore is a cost-effective technique.

Keywords

  1. References

    1. Afshar, A., Scardi, M., Jirani, F. 2011. Optimal design of detention ponds in watersheds using multi-objective ant community optimization algorithm and SWAT model. Journal of Environment Science and Technology. Volume 16, Special Issue 93: 121-132. (In Persian)
    2. Ahmad, L., Verma, M. K. 2017. GIS based analytic hierarchy process in determination of suitable site for water storage. European Water, 60: 139-146.
    3. Bhuyan, S. J., Kalita, P. K., Janssen, K. A., Barnes, P. L. 2002. Soil loss prediction with three erosion simulation models. Environmental Modelling & Software (17): 137-146.
    4. Bridges, E.M., and Oldeman, L. R. 1999. Global assessment of human-induced soil degradation. J. Arid Soil Rehab., 13(4): 319–325.
    5. Coello, C.A., Lamont G.B. and Van Veldhuizen D.A. 2007. Evolutionary algorithms for solving multi-objective problems, second edition, Springer Science Business Media, LLC, 810 p.
    6. Deb, K., Pratap, A., Agarwal, S. and Meyarivan, T., 2002, A fast and elitist multiobjective genetic algorithm: NSGA-II, IEEE Transaction on Evolutionary Computation, 6(2): 182-197.
    7. Emamgholi, M., Khosravi, K., & Sedaii, N. 2015. Suitable site selections for gabion check-dams construction using analytical hierarchy process and decision-making methods. Journal of Soil Environment, 1: 35-44.
    8. Giri, S., Nejadhashemi, A. P. 2014. Application of analytical hierarchy process for effective selection of agricultural best management practices. J. Environ. Manage. 132: 165-177.
    9. Kazemi Rad, L., Haghyghy, M. 2014. Integrated Analytical Hierarchy Process (AHP) and GIS for land use suitability analysis. World Applied Sciences Journal, 32(4): 587594.
    10. , A. R., Shariatmadari, H., Naseri, H. R., Tazeh, M. 2017. Using hierarchical analysis process in watershed resource management. Journal of Soil and Water Sciences (Agriculture and Natural Sciences and Technologies). Year, 21, No. 4. (In Persian)
    11. Long-Fei, W., Le-Yuan, Shi. 2013. Simulation optimization: A review on theory and applications. Acta Automatica Sinica, Vol 39, No 11: 1958-1968.
    12. Maringanti, C. H., Chaubey, I., Popp, J. 2009. Development of a multiobjective optimization tool for the selection and placement of best management practices for nonpoint source pollution control. Water Resources Research, Vol 45: 1-15.
    13. Nearing, M. A., Foster, G. R., Lanem, L. J., and Finkner, S. C. 1989. A process-based soil erosion model for USDA-water erosion prediction project technology. Transactions of the ASAE. 32(5): 1587-1593.
    14. Nicks, A. D., Lane, L. J, Gander, G. A. 1995. Weather generator. Chapter 2 in USDA–water erosion prediction project. Hillslope profile and watershed model documentation. D.C. Flanagan M A, Nearing Eds. NSERL Report No. 10. West Lafayette, IND, USDA–ARS National Soil Erosion Research Laboratory.
    15. Pandey, A., Himanshu., K. S., Mishra, S. k., Singh, V.P. 2016. Physically based soil erosion and sediment yield models revisited. Catena (147): 596-620.
    16. Pramanik, M. K. 2016. Site suitability analysis for agricultural land use of Darjeeling district using AHP and GIS techniques. Modeling Earth Systems and Environment, 2(2): 1-22.
    17. Reis, M., Altun Aladag, I., Bolat, N, Dutal, H. 2017. Using GeoWEPP model to determine sediment yield and runoff in the Keklik watershed in Kahramanmaras, Turkey. Šumarski list, 141 (11–12): 563–569.
    18. Renschler, C. S., Flanagan, D. C., Engel, B. A., Frankenberger, J. R. 2002. GeoWEPP: The Geospatial interface to the Water Erosion Prediction Project. ASAE Paper No. 022171. St. Joseph, Mich.: ASAE. Paper No. 022171.
    19. Saaty, T. L. 1977. A scaling method for priorities in hierarchical structures. Journal of Mathematical Psychology 13: 234-281.
    20. J. H. 1975. Soil conservation, pp. 220. Englewood Cliffs, Prentice Hall, Inc. NJ.
    21. Yuksel, A., Akay, A. E., Gundogan, R., Reis, M., Centiner, M. 2008. Application of GeoWEPP for determining sediment yield and runoff in the Orcan Creek watershed in Kahramanmaras, Turkey. Sensors, 8(2): 1222-1236.