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تعیین نقش کاربری اراضی در تولید رسوب معلق و کف بر پایۀ منشأیابی رسوب در حوضۀ طالقانی، خرم آباد | ||
نشریه علمی - پژوهشی مرتع و آبخیزداری | ||
مقاله 6، دوره 68، شماره 4، دی 1394، صفحه 751-765 اصل مقاله (920.19 K) | ||
نوع مقاله: مقاله پژوهشی | ||
شناسه دیجیتال (DOI): 10.22059/jrwm.2015.56956 | ||
نویسندگان | ||
کاظم نصرتی* 1؛ فروزان احمدی2؛ علی اکبر نظری سامانی3؛ محمد رضا ثروتی4 | ||
1دانشیار دانشکدة علوم زمین دانشگاه شهید بهشتی | ||
2دانشجوی دکتری ژئومورفولوژی- مدیریت محیطی، دانشگاه شهید بهشتی | ||
3دانشیار دانشکدة منابع طبیعی دانشگاه تهران | ||
4استاد دانشکدة علوم زمین دانشگاه شهید بهشتی | ||
چکیده | ||
پدیدة فرسایش خاک از مخربترین پدیدههایی است که موجب خسارتهای فراوان در بسیاری از مناطق میشود. از طرفی، کارایی هرچه بیشتر پروژههای حفاظتِ خاک مستلزم آگاهبودن از اطلاعاتِ تغییرات زمانی و مکانی رسوبات تولیدی در یک آبخیز است. با توجه به اینکه بخش اعظم رسوبهای خروجی از یک حوضه طی وقایع زمانی سیلابی انجام میشود، تمرکز بر منشأیابی رسوبات حملشده به هنگامِ سیلاب، اعم از بار معلق یا کف، در طراحی نوع عملیات حفاظت خاک بسیار مؤثر است. در این بررسی با تفکیک منابع رسوب در قالب کاربریهای مختلف اراضی و واحدهای سنگشناسی و با بهرهگیری از روش منشأیابی رسوب سهم هر یک از منابع رسوب در تولید رسوب حوضة آبخیز طالقانی تعیین شد. بدین منظور، در این مطالعه، 39 نمونه خاک از منابع مختلف در سطح حوضه و 19 نمونه از رسوب تولیدی حوضه (شامل 11 نمونه از رسوبات کف بستر و 8 نمونه از رواناب خروجی حوضه) برداشت شد. یازده عنصر (Fe، Mn، Mg، Zn، Cu، K، Na، P، N، C و Ca) ردیابهای اولیه در نظر گرفته شد. پس از اندازهگیری غلظت ردیابها، با استفاده از آنالیز آماری و تجزیة تابع تشخیص، ردیابهایِ Zn، C، Mg وCa به عنوان ترکیب بهینه برای منشأیابی و تفکیک کاربریهای اراضی انتخاب شدند؛ در حالی که هیچ ردیابی برای تفکیک واحدهای سنگشناسی از یکدیگر شناسایی نشد. ناتوانی در تفکیک واحدهای سنگشناسی از یک سو به دلیل فقدانِ تنوع (سه سازند) و از سوی دیگر آهکیبودن سازند تلهزنگ و تأثیر بیشتر آن در تولید بار محلول است. نتایج مطالعه نشان داد با استفاده از مدلهای چندمتغیرة ترکیبی، سهم منابع مختلف در تولید رسوب به دست آمد: کشاورزی، مرتع و جنگل بهترتیب برابر با 4/53، 4/30 و 2/16 درصد. همچنین، ردیابهای واردشده در مدل ترکیبی مبیّن تأثیر مدیریت کاربری و تفاوت بارز کاربریهای مختلف در تغییر ترکیب شیمیایی خاک است. | ||
کلیدواژهها | ||
حوضة طالقانی؛ ردیابهای شیمیایی؛ فرسایش خاک؛ منابع رسوب؛ منشأیابی رسوب | ||
عنوان مقاله [English] | ||
Determining of landuse effects on sediment yield of watershed through sediment fingerprinting technique of suspendedload and bed materials in Taleghani catchment, Khorram Abad | ||
نویسندگان [English] | ||
Kazem Nosrati1؛ Frouzan Ahmadi2؛ Ali Akbar Nazari Samani3؛ Mohammad Reza Servati4 | ||
1Department of Physical Geography, Faculty of Earth Sciences, Shahid Beheshti University, Tehran, Iran | ||
2Department of Physical Geography, Faculty of Earth Sciences, Shahid Beheshti University, Tehran, Iran | ||
3Faculty of Natural Resources, University of Tehran, Tehran, Iran | ||
4Department of Physical Geography, Faculty of Earth Sciences, Shahid Beheshti University, Tehran, Iran | ||
چکیده [English] | ||
Soil erosion is one of the most destructive phenomena which cause significant ecological changes in many areas. Soil conservation and erosion control is essential because of the irreparable damage caused by soil erosion. Soil conservation programs will not achieve until to find adequate methods of combating land degradation and ways to reduce the sediment. Therefore, we need to have enough knowledge of the sediment sources and identify places to be at high risk to soil erosion. In this study we used fingerprinting technique in the Taleghani catchment, Khorram Abad city, Lorestan Province to determine the contributions of sediment sources including agricultural, rangeland, and forest in sediment yield. In view of this, 39 soil were collected from different sources: agriculture, rangeland, forest and channel bank and 19 sediment samples including 11 samples from bed sediment and 8 samples from suspended runoff, respectively. 11 tracers including C, N, P, Na, K, Cu, Zn, Mg, Mn, Fe and Ca were selected as the primary tracers. The results showed that discriminant function analysis were selected Mg, C, Zn and Ca as the optimum set of tracers that can discriminate 3 sediment sources. Mixing model results showed that the contribution of each sediment source is 53.37, 30.37, and 16.26 percent for agriculture, rangeland, and forest, respectively. These results were consistent with the evaluation results of nitrogen and organic carbon stocks. The results of this study can be used in selecting most appropriate erosion control method the study area and generalized to similar areas. | ||
کلیدواژهها [English] | ||
Talaqani catchment, Sediment sources, Soil Erosion, Sediment fingerprinting, Geochemical tracers | ||
مراجع | ||
[1] Ahmadi, H. and Feiznia, S. (2006). Quaternary Formation, 2ed Edition, University of Tehran press, 627p.
[2] Ballantine, D., Walling, D., Collins, A. and Leeks, G. (2009). The content and storage of phosphorus in fine-grained channel bed sediment in contrasting lowland agricultural catchments in the UK. Geoderma, 151, 141-149.
[3] Blanco, H. and Lal, R. (2008). Principles of soil conservation and management, Springer Verlag, 601p.
[4] Collins, A., Anthony, S., Hawley, J. and Turner, T. (2009). The potential impact of projected change in farming by 2015 on the importance of the agricultural sector as a sediment source in England and Wales, Catena ,79, 243-250.
[5] Collins, A. and Walling, D. (2004). Documenting catchment suspended sediment sources: problems, approaches and prospects, Progress in Physical Geography, 28, 159-196.
[6] Collins, A. and Walling, D. (2007). Sources of fine sediment recovered from the channel bed of lowland groundwater-fed catchments in the UK. Geomorphology, 88, 120-138.
[7] Collins, A., Walling, D. and Leeks, G. (1997). Use of the geochemical record preserved in floodplain deposits to reconstruct recent changes in river basin sediment sources, Geomorphology, 19, 151-167.
[8] Collins, A., Walling, D., Webb, L. and King, P. (2010). Apportioning catchment scale sediment sources using a modified composite fingerprinting technique incorporating property weightings and prior information,Geoderma, 155, 249-261.
[9] Faraji, M., Ahmadi, H., Ekhtesasi, M.R., Jafari, M. and Feiznia, S. (2011). Figerprinting the sources of sand dunes using tracers and indicator minerals, case study, Journal of Range and Watershed Managment, 64 (2)1-18.
[10] Fox, J. and Papanicolaou, A. (2008). An un-mixing model to study watershed erosion processes, Advances in Water Resources, 31, 96-108.
[11] Fox, J. and Papanicolaou, A. (2008). Application of the spatial distribution of nitrogen stable isotopes for sediment tracing at the watershed scale, Hydrology, 358, 46-55.
[12] Gruszowski, K., Foster, I.D.L., Lees, J. and Charlesworth, S. (2003). Sediment sources and transport pathways in a rural catchment, Herefordshire, UK. Hydrological Processes, 17, 2665-2681.
[13] Hakimkahni, Sh. (2006). Investigation on using tracers in fluvial fine sediment sources fingerprinting (case study: in the basin of Pouldasht flood spreading system, Makoo township), Unpubl.Ph.D. thesis. University of Tehran,240 pp.
[14] Hakimkahni, Sh., Ahmadi, H., Ghayoumian, J., Feiznia, S. and Bihamta, M.R. (2006). Determinining a suitable subset of geochemical elements for Separation of lithological types of Poldasht waterspreading station basin, Iranian Journal of the Natural Resources, 60(3), 693-711.
[15] Hatfield, R.G. and Maher, B.A. (2009). Fingerprinting upland sediment sources: particle size specific magnetic linkages between soils, lake sediments and suspended sediments, Earth Surface Processes and Landforms, 34, 1359-1373.
[16] Krein, A., Petticrew, E. and Udelhoven, T. (2003). The use of fine sediment fractal dimensions and colour to determine sediment sources in a small watershed, Catena, 53, 165-179.
[17] Lal, R., Griffin, M., Apt, J., Lave, L. and Morgan, M.G. (2004). Managing Soil Carbon, Science, 304, 393.
[18] Nazari Samani, A., Wasson, R.J. and Malekian, A. (2011). Application of multiple sediment fingerprinting techniques to determine the sediment source contribution of gully erosion: Review and case study from Boushehr province, southwestern Iran, Progress in Physical Geography, 35(3), 375-391.
[19] Nosrati, K., Feiznia, S., Van Den Eeckhaut, M. and Duiker, S.W. (2011). Assessment of soil erodibility in Taleghan Drainage Basin Iran, using multivariate statistics, Physical Geography, 32, 78-96.
[20] Nosrati, K., Govers, G., Ahmadi, H., Sharifi, F., Amoozegar, M.A., Merckx, R. and Vanmaercke, M. (2011). An exploratory study on the use of enzyme activities as sediment tracers: biochemical fingerprints?, Sediment Research, 26, 136-151.
[21] Poulenard, J., Perrette, Y., Fanget, B., Quetin, P., Trevisan, D. and Dorioz, J.M. (2009). Infrared spectroscopy tracing of sediment sources in a small rural watershed (French Alps), Science of The Total Environment, 407, 2808-2819.
[22] Rutherford, P.M., McGill, W.B., Arocena, J.M. and Figueiredo, C.T. (2008). Total nitrogen, In: M.R. Carter and E.G. Gregorich (Editors), Soil Sampling and Methods of Analysis, CRC Press, Taylor & Francis Group, Boca Raton.
[23] Skjemstad, J.O. and Baldock, J.A. (2008). Total and organic carbon, In: Carter, M.R., Gregorich, E.G. (Eds.), Soil Sampling and Methods of Analysis, CRC Press, Taylor & Francis Group, Boca Raton, pp. 225-237.
[24] Smith, H.G. and Dragovich, D. (2008). Sediment budget analysis of slope–channel coupling and in-channel sediment storage in an upland catchment, southeastern Australia. Geomorphology 101, 643-654.
[25] Vanacker, V., Molina, A., Govers, G., Poesen, J. and Deckers, J. (2007). Spatial variation of suspended sediment concentrations in a tropical Andean river system: The Paute River, southern Ecuador, Geomorphology, 87, 53-67.
[26] Wallbrink, P., Martin, C. and Wilson, C. (2003). Quantifying the contributions of sediment, sediment-P and fertiliser-P from forested, cultivated and pasture areas at the landuse and catchment scale using fallout radionuclides and geochemistry, Soil and Tillage Research, 69, 53-68.
[27] Wallbrink, P.J. (2004). Quantifying the erosion processes and land-uses which dominate fine sediment supply to Moreton Bay, Southeast Queensland, Australia, Journal of environmental radioactivity, 76, 67-80.
[28] Wallbrink, P.J. and Croke, J. (2002). A combined rainfall simulator and tracer approach to assess the role of Best Management Practices in minimising sediment redistribution and loss in forests after harvesting, Forest Ecology and Management, 170, 217-232.
[29] Walling, D.E. (2005). Tracing suspended sediment sources in catchments and river systems, Science of the Total Environment, 344:159-184.
[30] Walling, D. and Collins, A. (2008). The catchment sediment budget as a management tool, Environmental Science & Policy, 11, 136-143.
[31] Walling, D., Collins, A. and Stroud, R. (2008). Tracing suspended sediment and particulate phosphorus sources in catchments, Journal of Hydrology, 350, 274-289.
[32] Walling, D.E., Owens, P.N., Waterfall, B.D., Leeks, G.J.L. and Wass, P.D. (2000). The particle size characteristics of fluvial suspended sediment in the Humber and Tweed catchments, UK. The Science of the Total Environment, 251, 205-222.
[33] Wilkinson, S., Wallbrink, P., Hancock, G., Blake, W., Shakesby, R. and Doerr, S. (2009). Fallout radionuclide tracers identify a switch in sediment sources and transport-limited sediment yield following wildfire in a eucalypt forest, Geomorphology, 110, 140-151.
[34] Youneszadeh, S. (2009). Tracing of small dam sediment inorder to sourcing and suceptibility of rocks, Unpubl. MSc. thesis. University of Tehran,174 pp.
[35] Zapata, F. (2003). The use of environmental radionuclides as tracers in soil erosion and sedimentation investigations: recent advances and future developments, Soil and Tillage Research, 69, 3-13.
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