تعیین سهم واحدهای سنگ‌شناسی و محدوده‌های بیشینه شتاب زمین در تولید رسوب با استفاده از روش منشایابی رسوب (حوضه آبخیز تالار استان مازندران)

نوع مقاله : مقاله پژوهشی

نویسندگان

1 دانشجوی دکتری ژئومورفولوژی، گروه جغرافیای طبیعی، دانشکده علوم زمین ، دانشگاه شهید بهشتی.

2 استاد گروه جغرافیای طبیعی، دانشکده علوم زمین، دانشگاه شهید بهشتی

3 استادیار گروه برنامه ریزی و طراحی محیط زیست، پژوهشکده علوم محیطی، دانشگاه شهید بهشتی.

10.22034/gmpj.2023.413321.1452

چکیده

One of the main issues in drainage watersheds is erosion and sediment yield. Lack of proper management in this field can be environmental hazards and even a threat to human life. The purpose of this study is fingerprinting the sources of sediment yield in sub-basins 1 and 2 of Talar drainage basin in Mazandaran province.140 soil samples in first approach and 80 samples in second approach collected respectively sub-basin 1 (77) and (47), sub-basin 2 (63) and (33) of lithological units and range of peak ground acceleration and 20 drape sediment samples at the outlet sub-basins and 28 geochemical elements measured as tracers in the samples. Using the Kruskal-Wallis test and discriminant function analysis, the composite fingerprints was determined. The largest relative contribution of sediment yield based on the Bayesian un-mixing model is in the first approach (sub-basin 1 unit sandstone and conglomerate with 59.1%, sub-basin 2 unit marl and shale with 47.2%), in the second approach (sub-basin 1 unit the range of peak ground acceleration at the level (0.51-0.6) g with 50.3%, and sub basin 2 units channel bank with 64.6%). The results of this study showed that the range of peak ground acceleration have a direct effect on control of sediment yield and erosion processes. Also, division of lithological groups as sources sediment yield based on range of peak ground acceleration, which have a great impact on sediment yield, as a new approach, can be of great help in understanding sediment yield processes.

کلیدواژه‌ها


عنوان مقاله [English]

Determining lithological units contribution and ranges of peak ground acceleration in sediment yield using the sediment fingerprinting technique (Talar drainage basin of Mazandaran province)

نویسندگان [English]

  • Nafiseh Ashtari 1
  • Kazem nosrati 2
  • Salma Ommi 3
1 Faculty of Earth Sciences, Shahid Beheshti University, Tehran
2
3 Department of Environmental Planning and Design, Environmental Science Research Institute, Shahid Beheshti University,Tehran.
چکیده [English]

Extended Abstract



Introduction

Soil erosion is a global issue that causes environmental degradation.One of the factors that increase sedimentation is seismic activity and peak ground acceleration index (PGA). PGA index strongly depends on the frequency of large and small earthquakes and provides a correct measurement of the seismicity of a region. Among the results of seismic activity in rocks is the increase in weathering and sensitivity to erosion. Identifying the critical areas of the watershed in the PGA index and the role of these areas in sediment yield and soil erosion is one of the topics that has received less attention from researchers. Fingerprinting or Sediment tracing as a method with proper accuracy and high efficiency has been noticed by different researchers. In this method, the soil eroded from the sources is divided and discriminant based on the measured tracers and existing composite models. Therefore, the purpose of this research is to determine fingerprinting of sediment using uncertainty Bayesian model and to determine contribution of surface and subsurface erosion units and PGA in sediment yield in the Talar drainage basin of Mazandaran province.





Materials and Methods

The study area (2105 km^(2))is located at latitudes between 35° 44΄ and 36° 19΄ North, and at longitudes between 52° 35΄ and 53° 23΄ East. The main formations in the study area are Shemshak, Elika, Karaj, Lar. Sampling of the target sediment in each outlet of the sub-basins, 10 main drape sediments samples were taken at distances of 100 meters from the outlet of the sub-basin to the upstream side of the river. Sampling of sediment sources was done based on 4 dominant lithological units based on the largest area and sampling of the channel bank in sub-basins 1 and 2. Sampling was done from the depth of 0-5 cm in lithological units and channel bank that have suffered surface and subsurface erosion. So 140 soil samples in first approach and 80 samples in second approach collected respectively sub-basin 1 (77) and (47), sub-basin 2 (63) and (33) of lithological units and range of peak ground acceleration and 28 geochemical elements (Al-As-Ba-Be-Ca-Ce-Co-Cr-Cu-Fe-K-La-Li-Mg-Mn-Na-Ni-P-Pb-S-Sc-Sr-Ti-V-Y-Yb-Zr-Zn) measured as tracers in all samples in size fractions < 63 μm. In order to remove non-conservative tracers, standard bracket and average concentration tests were used. After identifying the conservative tracers, the significant level of each of the tracers was determined by the Kruskal-Wallis test, and finally, the composite fingerprint that have the highest power of discriminant of sediment sources was determined in the discriminant function analysis (DFA). Bayesian un-mixing model was used to estimate the relative contribution source sediment by composite fingerprints.



Findings and Discussion

The composite fingerprints in sub-basin 1, five tracer respectively, Zn, Co, Ba, Mn, Ni, and in the second approach, five tracers Ni, Zn, Co, Ba, Mn, Li were selected in DFA.

In sub-basin 2, six tracer respectively, Zn,Ba, K, P, Mn, Sc and in the second approach four tracers Ba, Pb, Ni, K were selected. The cumulative percentage of correctly classified samples in the first and second approach in sub basin 1 and 2 respectively , is (97.4% - 97.9% ), (96.8% - 100%). The relative contribution of sediment sources estimated in Bayesian un-mixing model in the corresponding uncertainty range (5-95%) in the first approach in sub-basin 1 for sandstone and conglomerate, limestone and dolomite, marl and shale, alluvial sediments and terraces , channel bank is respectively (59.1-59.1) 59.1%, (40.5-40.5) 40.5%, (0.1-0.1) 0.1%, (0.2-0.2) 0.2%, (0.1-0.1) 0.1% and for sub basin 2 (0.1-2.1) 0.7%, (5.3-7.5) 6.5%, (40.8-53.7) 47.2%, (1.4-19.3) 8.4%, (23.8-47.5) 37.2%.

In the second approach, for the PGA classes g(0.41-0.5), g(0.51-0.6) and channel bank, in sub basin 1 is (0.1-3.9) 0.9%, (46.5-54.4) 50.3% and (43.8-52.6) 48.4%, also in sub basin 2, is (0-1.4) 0.4%, (31.7-38.1) 35% and (61.3-67.6) 64.6% respectively.

In the first approach, in sub-basin 1 unit of sandstone and conglomerate with 59.1%, and in sub-basin 2 units of marl and shale with 47.2%, and in the second approach, in sub-basin 1 PGA (0.51-0.6)g with 50.3% and in sub-basin, 2 units channel bank with 48.4% have the highest relative contribution in sediment yield.

The size fractions < 63 μm show well the concentration of geochemical elements in soil and sediments. the influence of lithological units and acceleration levels on the distribution and control of geochemical elements in sediment yield is very important.

According to (Figure 1), the length of Firoozkoh and IRQ 112 faults have had a significant impact on the seismic trend in high and medium acceleration ranges.

PGA in (0.51-0.6) g (0.41-0.5) due to the frequency of large and small earthquakes, sediments and erodible rocks in sensitive slopes experience instability and displacement, which causes The conditions of mechanical and chemical weathering, crushing and weakening of rocks will eventually accelerate erosion processes and transfer sediment from the slopes to the streams over time.

Proximity to active faults such as Firouzkoh, PGA (0.51-0.6)g, proximity of erodible units especially marl and shale to the outlet of the sub basin, lateral stream erosion in PGA (0.51-0.6)g causes surface and subsurface soil erosion in the Talar drainage basin.



Conclusion

The results of this study showed that the range of PGA have a direct effect on the control of other sediment yield processes such as weathering and rock weakening. Also, the division of lithological units as sources of sediment yield based on the range of PGA, which have a great impact on sediment yield, as a new approach, can be of great help in understanding sediment yield processes.

کلیدواژه‌ها [English]

  • Sediment fingerprinting
  • Peak ground acceleration
  • Talar drainage basin
  • the Bayesian un-mixing model
احمدی، ف.، نصرتی، ک، و  حسینزاده، م م.، 1398. اثرات تغییر کاربری اراضی بر رسوبدهی حوضه کوهدشت با استفاده از تکنیک منشایابی رسوب، تحقیقات آب و خاک ایران، دوره 50، شماره 8، صص (2035- 2023).
صمدی ارغینی، ح.، فیض نیا، س، و نظری سامانی، ع ا.، 1393. بررسی سهم واحدهای سنگی در تولید رسوب با استفاده از ویژگیهای کانیشناسی و سنگشناسی، مطالعه موردی: حوزه آبخیز حسن ابدال زنجان، نشریه علمی-پژوهشی مهندسی و مدیریت آبخیز، دوره 6، شماره 3، صص (257-247).
فتحی زاد، ح.، کریمی، حاجی، و توکلی، م.، 1395. نقش حساسیت به فرسایش سازندهای زمین‌شناسی در فرسایش و تولید رسوب (مطالعه موردی: زیرحوزه های رودخانه دویرج استان ایلام)، پژوهشنامه مدیریت حوزه آبخیز، دوره ۷، شماره ۱۳، صص (208-193).
نصرتی، ک.، 1390. منشایابی رسوب بر اساس برآورد عدم قطعیت، مجله پژوهش آب ایران، دوره 5، شماره 9، صص (60-51).
نصرتی، ک. احمدی، ح، و شریفی، ف.، 1391. منشأیابی منابع رسوب: ارتباط بین فعالیت های آنزیمی خاک و رسوب، مجله علوم و فنون کشاورزی و منابع طبیعی، علوم آب و خاک، دوره 16، شماره 60 ، صص (237-226).
نصرتی، ک.، زارع، م ر، و جلالی، س.، 1398. تعیین سهم سازندهای زمین شناسی در تولید رسوب معلق با استفاده از روش منشایابی رسوب حوزه آبخیز زیارت استان گلستان، تحقیقات آب و خاک ایران، دوره 50، شماره 2، صص (387-379).
محمدی رایگانی، ز.، نصرتی، ک، 1399.کمی سازی سهم منابع رسوب معلق در طول رخداد سیلاب با استفاده از روش منشأیابی در حوضۀ کمیش، شرق کرمانشاه، مرتع و آبخیزداری مجله منابع طبیعی ایران، دوره 73، شماره 2، صص (421-405). 
Aiello, A., Adamo, M. and Canora, F., 2015. Remote sensing and GIS to assess soil erosion with RUSLE3D and USPED at river basin scale in southern Italy. Catena, 131, 174–581.
Ashtari, N., Nosrati, K., Ommi, Salma. and Collins, Adrian L., 2023. Investigating the effect of seismicity on spatial sediment sources and loads using the fingerprinting approach. Catena, 227(2), 107091, 1-14.
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-.941.
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.
Collins, A.L. and Walling, D.E., 2004. Documenting catchment suspended sediment sources: problems, approaches and prospects. Progress in Physical Geography, 28, 159 - 196.
Collins, A.L., Walling, D.E. and  Leeks, G.J.L., 1997. Source type ascription for fluvial suspended sediment based on a quantitative composite fingerprinting technique. Catena, 29(1), 1-27.
Collins, A.L. and Walling, D.E., 2002. Selecting fingerprint properties for discriminating potential suspended sediment sources in river basins. Journal of Hydrology, 261(1), 218-244.
Evrard, O., Navratil, O., Ayrault, S., Ahmadi, M., Némery, J., Legout, C., Lefèvre, I., Poirel, A., Bonté, P. and Esteves, M., 2011. Combining suspended sediment monitoring and fingerprinting to determine the spatial origin of fine sediment in a mountainous river catchment. Earth Surface Processes and Landforms, 36(8), 1072-1089.
Foster, I.D.L. and J.A. Lees., 2000. Tracers in Geomorphology: theory and applications in tracing fine particulate sediments. Conference tracers in geomorphology, 3–20.
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.
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.
Haddadchi, A., Nosrati, K. and Ahmadi, F., 2014. Differences between the source contribution of bed material and suspended sediments in a mountainous agricultural catchment of western Iran. Catena, 116, 105–113.
Hughes, A. O., Olley, J. M., Croke, J. C. and McKergow, L. A., 2009. Sediment source changes over the last 250 years in a dry-tropical catchment, central Queensland, Australia. Geomorphology, 104(3–4), 262–275.
Koons, P.O., Upton, P. and Barker, A.D., 2012. The influence of mechanical properties on the link between tectonic and topographic evolution. Geomorphology, 137(1), 168-180.
Lamba, J., Karthikeyan, K.G. and Thompson, A.M., 2015. Apportionment of suspended sediment sources in an agricultural watershed using sediment fingerprinting. Geoderma, 239-240, 25-33.
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.
Nosrati, K., 2017. Ascribing soil erosion of hillslope components to river sediment yield. Journal of Environmental Management, 194, 63-72.
Nosrati, K., Collins, L. A. and Madankan, M., 2018. Fingerprinting sub-basin spatial sediment sources using different multivariate statistical techniques and the Modified MixSIR model. Catena, 164, 32-43
Nosrati, K., Fathi, Z. and Collins, A.L., 2019. Fingerprinting sub-basin spatial suspended sediment sources by combining geochemical tracers and weathering indices. Environmental Science and Pollution Research, 26(27), 28401-28414.
Nosrati, K. and Collins, A. L., 2019. Investigating the importance of recreational roads as a sediment source in a mountainous catchment using a fingerprinting procedure with different multivariate statistical techniques and a Bayesian un-mixing model. Journal of Hydrology, 569, 506-518.
Nosrati, K., Govers, G., Semmens, B.X. and Ward, E.J., 2014. A mixing model to incorporate uncertainty in sediment fingerprinting. Geoderma, 217-218, 173-180.
Owens, P.N., Batalla, R.J., Collins, A.J., Gomez, B., Hicks, D.M., Horowitz, A.J., Kondolf, G.M., Marden, M., Page, M.J., Peacock, D.H., Petticrew, E.L., Salomons, W. and Trustrum, N.A., 2005. Fine-grained sediment in river systems: environmental significance and management issues. River Research and Applications, 21(7), 693-717.
Portenga, E. W. and Bierman, P. R., 2011. Understanding earth’s eroding surface with 10Be. GSA Today, 21(8), 4–10.
Pulley, S., Foster, I. and Antunes, P., 2015. The uncertainties associated with sediment fingerprinting suspended and recently deposited fluvial sediment in the Nene river basin. Geomorphology, 228, 303-.913.
Tiecher, T., Caner, L., Minella, J.P., Pellegrini, A., Capoane, V., Rasche, J.W.R., Schaefer, J.L. and Rheinheimer, D.S., 2017. Tracing sediment sources in two paired agricultural catchments with different riparian forest and wetland proportion in southern Brazil. Geoderma, 285,225–239.
Vanmaercke, M., Kettner, A.J., Eeckhaut, M.V.D., Poesen, J., Mamaliga, A., Verstraeten, G., Rãdoane, M., Obreja, F., Upton, P., Syvitski, J.P.M. and Govers, G., 2014a. Moderate seismic activity affects contemporary sediment yields. Progress in Physical Geography: Earth and Environment, 38(2), 145-172.
Vanmaercke, M., Obreja, F. and Poesen, J., 2014b. Seismic controls on contemporary sediment export in the Siret river catchment, Romania. Geomorphology, 216, 247-262.
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.
Walling, D. and Collins, A. L., 2008. The catchment sediment budget as a management tool, Environmental Science & Policy, 11,136-143.
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.
Zhou, M., Deng, J., Lin, Y., Belete, M., Wang, K., Comber, A., Huang, L. and Gan, M., 2019. Identifying the effects of land use change on sediment export: Integrating sediment source and sediment delivery in the Qiantang River Basin, China. Science of The Total Environment 68, 38-49.