آرشیو

آرشیو شماره ها:
۶۱

چکیده

در پژوهش حاضر، تغییرات کاربری ارضی و تأثیر آن روی رواناب حوضه قره چای در استان همدان با استفاده از مدل SWAT تجزیه وتحلیل شده است. در این پژوهش، به منظور بررسی تأثیر کاربری اراضی بر رواناب حوضه آبخیز قره چای، از دو تصویر ماهواره ای لندست OLI-TM سال های (2001 تا 2020) استفاده شد. ابتدا تصاویر مربوطه اخذ و پیش پردازش های لازم شامل تصحیحات اتمسفری به روش FLAASH  اعمال شد. برای افزایش دقت طبقه بندی روش تلفیق تصاویر چند طیفی با تصویر پانکروماتیک[1] انجام شد و قدرت تفکیک مکانی به 15 متر ارتقا یافت. سپس طبقه بندی با استفاده از روش شیءگرا[2] و الگوریتم نزدیک ترین همسایگی صورت گرفت. از مدل SWAT برای شبیه سازی هیدرولوژیکی حوضه استفاده و از الگوریتم SUFI-2 در نرم افزار SWAT-CUP برای تحلیل حساسیت، واسنجی و اعتبارسنجی بهره گرفته شد. با توجه به حساسیت مدل به پارامتر تلفات اولیه، واسنجی مدل براساس مقادیر تلفات اولیه انجام شد. مقادیر این ضرایب برای دوره واسنجی بین 72/0 تا 90/0 و نتایج اعتبارسنجی مدل، نشان دهنده تأیید صحت واسنجی انجام شده بود. بررسی کارایی مدل با استفاده از ضرایب ناش ساتکلیف، p-factor،  Rو r-factor حاکی از قابلیت زیاد مدل در شبیه سازی رواناب است. 1. panchromatic2. object oriented

Investigating the Effects of Land Use Changes on the Runoff of Qara Chai River Basin Using the SWAT Model

The present study analyzed changes in land use and its effects on the runoff of Qara Chai Watershed in Hamadan Province using the SWAT model. To this aim, Landsat OLI-TM satellite images of the years of 2001-2020 were used. First, the relevant images were obtained and the necessary pre-processing steps, including atmospheric corrections, were applied by using the FLAASH method. To increase the classification accuracy, the multispectral images were combined with the panchromatic images and the spatial resolution was enhanced up to 15 m. Then, the classification process was done by using the object-oriented method and the nearest neighbor algorithm. The SWAT model was utilized for hydrological simulation of the basin and SUFI-2 algorithm was applied in SWAT-CUP software for conducting sensitivity analysis, calibration, and validation. Due to the sensitivity of the model to the initial loss parameter, it was recalibrated based on the initial loss values. The values ​​of the coefficients for the calibration period were between 0.72 and 0.90 and the model validation results confirmed the calibration accuracy. Assessment of the efficiency of the model by using Nash Sutcliffe coefficients, p-factor, R, and r-factor indicated its high capability for simulating the related runoff.Keywords: Land Use, Runoff, SWAT modelIntroductionLand use and its fluctuations are among the factors that affect natural cycles in ecosystems. Land use change has several effects on the hydrology of watersheds, such as changing the characteristics of peak discharge, total volume of runoff water, water quality, and hydrological balance. Changing land use and soil cover has some effects on runoff, infiltration, retention, evaporation, transpiration, etc. The runoff caused by rainfall in watersheds causes erosion and loss of surface fertile soil and finally leads to sedimentation in canals, rivers, and reservoirs of dams in addition to human and financial losses triggered by floods. Nowadays, it is possible to study land use changes through satellite images and remote sensing science The geographic information system as a suitable tool for extracting and classifying information has greatly contributed to the studies related to the effects of land use changes.SWAT model is a hydrological simulator and a continuous spatio-temporal semi-distributed model with a physical base. It has been used to simulate hydrological processes in complex and vast watersheds with regard to soil changes, land use, and weather conditions during different periods for a long time. MethodologyQara Chai Basin with an area of ​​about 11000 km2 (based on the political border) is the largest watershed in Hamadan Province. It has got the geographical coordinates of 13° 48° to 29° 49° east longitude and 12° 34° to 35° 44° north latitude. It is drained by Qara Chai River and its branches. This basin is the most flood-prone part of Hamadan Province in terms of flood situation.In the studied plan, the area of Qara Chai Catchment (​​11000 km2) was divided into 18 sub-basins. The SWAT model was used to obtain the data of the land use, soil, and slope maps and build the hydrological response units. Separate grids were introduced to the model. After introducing two maps of land use, as well as soil and slope classes, to the SWAT model, all the rasterized maps were combined and integrated to produce the hydrological reaction units of the basin. Due to the fact that the land use maps had changed in two time periods and thus had different characteristics, the hydrological response units were affected by the land use type in addition to the soil type and slope. Therefore, Therefore, the number of the hydrological reaction units changedAfter forming the basin and hydrological response units, the meteorological data required by the SWAT model were introduced to the model. Then, the output of this model was linked with SUFI-2 program in SWAT-CUP software and the important parameters of the SWAT model for the watershed were sensitized with the help of SUFI-2 algorithm for the statistical period of 2002-2021 by applying the method of one parameter at a time. The parameters, which were more sensitive, were identified and their optimal values ​​were determined. In short, the model was recalibrated for the land uses of 2001 and 2020 during the statistical periods of 2001-2008 and of 2013-2020, respectively. It was validated for the statistical period of 2009-2012. Using the statistical criteria of Nash Sutcliffe coefficient, p-factor, and r-factor both for the calibration and validation periods, the statistical analysis was done and the statistical results were checked by using the SWAT-CUP program. Results and DiscussionIn the present research, land use changes and its effects on the runoff of Qara Chai Basin were analyzed by using the SWAT model. To simulate the runoff by using the mentioned model and SUFI-2 algorithm, the effective parameters on the runoff were identified from among the 29 parameters examined in the sensitivity analysis via the sensitivity analysis technique. 14 variables were found to affect the simulation. Finally, the runoff in the Qara Chai Catchment was identified. Due to the sensitivity of the model to the initial loss parameter, it was recalibrated based on the initial loss values. Then, using the SUFI-2 algorithm, the model was calibrated and validated for the period of 2001-2020. Examining the efficiency of the model by using Nash Sutcliffe coefficients, p-factor, R, and r-factor resulted in the values between 0.72 and 0.90, which indicated the high capability of the model for simulating the runoff. The validation results of the model also confirmed the correctness of the performed calibration. To measure the influences of land use change on the amount of runoff, two SWAT models were prepared by using two separate land use maps, including those of 2001 and 2020 for Qara Chai Watershed. The results of land use changes from 2001 to 2020 showed that the most changes in land use included those of the lands without vegetation cover with an area of 2550 km2 and mixed irrigated and rainfed agriculture lands with an area of 1298.5 km2. Changes in the lands without vegetation had been decreasing and those of the lands related to the mixture of irrigated and rainfed agriculture had been increasing. Also, the least changes were related to the pastures (16.6 km2) with poor canopy coverage. ConclusionThe results related to land use changes from 2003 to 2021 showed that the most changes in land use included those related to the lands without vegetation cover and mixed irrigated and rainfed agriculture lands with the areas of 2550 and 1298.5 km2, respectively. The changes were decreasing in the lands without vegetation and increasing in the lands related to the mixture of irrigated and rainfed agriculture. Also, the least changes were related to the pastures (16.6 km2) with poor canopy cover.Due to the sensitivity of the model to the initial loss parameter, it was recalibrated based on the initial loss values. The validation results of the model showed good validity of calibration. Also, the results of this research revealed that the use of remote sensing techniques and combined images for extracting land use data provided a significant help to accurate studies of the effects of land use changes on runoff and their simulation by the SWAT model. References- Ali, M., Khan, S. J., Aslam, I., & Khan, Z. (2011). Simulation of the impacts of land-use change on surface runoff of Lai Nullah Basin in Islamabad, Pakistan. Landscape and Urban Planning, 102(4), 271-279.- Chen, Y., Xu, Y., & Yin, Y. (2009). Impacts of land use change scenarios on storm-runoff generation in Xitiaoxi basin, China. Quaternary International, 208(1-2), 121-128.- De Andrade Farias, C. W. L., Montenegro, S. M. G. L., de Assunção Montenegro, A. A., de Sousa Lima, J. R., Srinivasan, R., & Jones, C. A. (2020). Modeling runoff response to land-use changes using the SWAT model in the Mundaú watershed, Brazil. Journal of Environmental Analysis and Progress, 5(2), 194-206.- Ewen, J., & Parkin, G. (1996). Validation of catchment models for predicting land-use and climate change impacts. Method. Journal of Hydrology, 175(1-4), 583-594.- Fohrer, N., Steiner, N., & Moller, D. (2002). Multidisciplinary Trade-off Function for Land Use Option in Low Mountain Ranges Area: A Modelling Approach. Third International Conference on Water Resources and Environment Research. Dresden University of Technology, 387-391.- George, C., & James, E. J. (2013). Simulation of streamflow using soil and water assessment tool (SWAT) in Meenachil river basin of Kerala, India. Scholars Journal of Engineering and Technology, 1(2), 68-77.- Howarth, P. J., & Wickware, G. M. (1981). Procedures for change detection using Landsat digital data. International Journal of Remote Sensing, 2(3), 277-291.- Koneti, S., Sunkara, S. L., & Roy, P. S. (2018). Hydrological modeling with respect to impact of land-use and land-cover change on the runoff dynamics in Godavari River Basin using the HEC-HMS model. ISPRS International Journal of Geo-Information, 7(6), 206.- Li, K. Y., Coe, M. T., Ramankutty, N., & De Jong, R. (2007). Modeling the hydrological impact of land-use change in West Africa. Journal of Hydrology, 337(3-4), 258-268.- Li, Z., Liu, W. Z., Zhang, X. C., & Zheng, F. L. (2009). Impacts of land use change and climate variability on hydrology in an agricultural catchment on the Loess Plateau of China. Journal of Hydrology, 377(1-2), 35-42.- Melesse, A. M., & Shih, S. F. (2002). Spatially distributed storm runoff depth estimation using Landsat images and GIS. Computers and Electronics in Agriculture, 37(1-3), 173-183.- Neitsch, S. L., Arnold, J. G., Kiniry, J. R., & Williams, J. R. (2011). Soil and water assessment tool theoretical documentation version 2009. Texas Water Resources Institute.- Taia, S., Erraioui, L., Mbrenga, N. C., Chao, J., El Mansouri, B., Haida, S., & Taj-Eddine, K. (2021). Assessment of soil erosion using two spatial approaches: RUSLE and SWAT Model. In E3S Web of Conferences (Vol. 234, p. 00082). EDP Sciences.- Vaze, J., Post, D. A., Chiew, F. H. S., Perraud, J. M., Viney, N. R., & Teng, J. (2010). Climate non-stationarity validity of calibrated rainfall–runoff models for use in climate change studies. Journal of Hydrology, 394(3-4), 447-457.

تبلیغات