Evaluation of Environmental Flows in a River using Eco-hydrology and Hydraulic Methods based on the Natural Flow Regime (Case study: Darerud River, Aras Basin)

Document Type : Research Article

Authors

1 Department of Irrigation and Reclamation Engineering, College of Agriculture and Natural Resources, University of Tehran, Karaj, Iran

2 Department of Irrigation & Reclamation Engineering, University of Tehran, Karaj Campus, Karaj 3158777871, IRAN

Abstract

Objective: This study presents an integrated framework for environmental flow assessment by combining ecohydrological and hydraulic methods based on the reconstructed natural flow regime.
 
Method: Long-term hydrometric records from the Darerud River at the Moshiran hydrometric station were analyzed. The natural flow regime was first reconstructed, after which environmental flows were estimated using the Tennant, Modified Tennant, Tessman, Aquatic Base Flow, Flow Duration Curve (FDC), Flow Duration Curve Shifting (FDC-Shifting), Desktop Reserve Model (DRM), Range of Variability Approach (RVA), hydraulic Wetted Perimeter, and Water Quality methods.
 
Results: The observed mean annual discharge of the Darerud River at the Moshiran station is 11.8 m³/s, whereas the reconstructed natural flow regime yields a mean annual discharge of 21.6 m³/s. Using the Tennant method, the required environmental flow is 2.2 m³/s during the first six months of the water year, and 6.5 m³/s for the next six months. In contrast, the Modified Tennant, Tessman , Flow Duration Curve Shifting (FDC-Shifting), and Desktop Reserve Model (DRM) methods produce distributed monthly environmental flows that reflect the natural seasonal flow regime. The corresponding mean annual environmental flows are 4.7, 10.7, 7.5, and 7.6 m³/s. The Aquatic Base Flow, Flow Duration Curve (FDC), hydraulic method (wetted perimeter curve slope), hydraulic method (maximum curvature), and water quality methods estimate constant environmental flows of 8.3, 6.3, 12.5, 8.9, and 8.1 m³/s, respectively. The Range of Variability Approach (RVA), however, presents a yearly flexible environmental flow range between 9.6 and 27.6 m³/s, rather than prescribing a single discharge value.
 
Conclusions: The Modified Tennant, FDC-Shifting (Class D), DRM (Class B/C) methods are considered to be more reasonable approaches for the Darerud River. These three methods present the mean annual environmental flows of 4.7, 7.5, and 7.6 m³/s, respectively, corresponding to 22%, 35%, and 35% of the mean annual natural flow regime. The Spearman rank correlation coefficients are 0.99, 0.98, and 0.92, respectively. These three methods represent seasonal environmental flow variability in consistent with the hydrological characteristics of the natural river system. The findings of this study provide a flexible scientific tool for river management and the conservation of flow-dependent ecosystems in the Darerud watershed.

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Main Subjects


  • Acreman, M. C., & Dunbar, M. J. (2004). Defining environmental river flow requirements – A review. Hydrology and Earth System Sciences, 8(5), 861–876.
  • Annear, T., Chisholm, I., Beecher, H., Locke, A., & et al. (2004). Instream Flows for Riverine Resource Stewardship: Revised Edition. Instream Flow Council, Cheyenne, Wyoming.
  • Arthington, A. H., Bhaduri, A., Bunn, S. E., Jackson, S. E., Tharme, R. E., Tickner, D., Young, B., Acreman, M., Baker, N., Capon, S., et al. (2018). The Brisbane Declaration and Global Action Agenda on Environmental Flows (2018). Frontiers in Environmental Science, 6, 45.
  • Bunn, S. E., & Arthington, A. H. (2002). Basic principles and ecological consequences of altered flow regimes for aquatic biodiversity. Environmental Management, 30(4), 492–507.
  • Ghasemi, A., Valinassab, T., & Mohammadpour, M. (2022). Use of hydrological and ecohydrological methods for the assessment of river environmental flow to protect aquatic animals and aquatic ecosystem. Iranian Scientific Fisheries Journal, 31(4), 107-119. [in Persian]
  • Hughes, D. A., & Hannart, P. (2003). A desktop model used to provide an initial estimate of the ecological instream flow requirements of rivers in South Africa. Journal of Hydrology, 270(3–4), 167–181.
  • Hughes, D. A., & Münster, F. (2000). Desktop Reserve Model: A rapid assessment method for determining environmental flow requirements of rivers. Water Research Commission Report No. TT 120/00. Pretoria, South Africa: Water Research Commission.
  • Jabarian Amiri, B. (2017). Determining the environmental flow of rivers in Ardabil province. Applied research plan. Ardabil Province Regional Water. Ministry of Energy. [in Persian]
  • Jabbarian Amiri, B., Kharazi Bahri, B., & Khayyat Rostami, B. (2018). Comparing three approaches to determine environmental flow for Harou river in Ardabil province. Journal of Natural Environment, 71(2), 139–150. [in Persian]
  • Khan, I., Zakwan, M., Pulikkal, A.K., Lalthazula, R. (2024). “Environmental flow assessment for the Musi River, India.” Environment, Development & Sustainability, 10(19): 1–15.
  • Lar consulting engineers. (2012). Environmental impact assessment studiy: Amart dam plan. Ardabil Province Regional Water Joint Stock Company. Ministry of Energy. [in Persian]
  • Madani, K. (2014). Water management in Iran: What is causing the looming crisis? Journal of Environmental Studies and Sciences, 4(4), 315–328.
  • Mostafazadeh, R., Azizi Mobsar, J., & Mirzaei, S. (2025). Comparison of temporal changes in flow regime components in two natural and affected by dam construction rivers in Ardabil Province. Hydrogeomorphology, 12(42), 137–155. [In Persian]
  • Naderi, M., Zakerinia, M., & Salari Jazi, M. (2020). Ecosystems Protecting of Gharasoo River based on Regulation of Environmental Flow Regime using Hydrological Methods, 11(1), 118–136. [in Persian]
  • Nasiri Khiavi, A., Mostafazadeh, R., Esmali-Ouri, A., Ghafarzadeh, O., & Golshan, M. (2019). Changes in environmental flow components under the effect of Sabalan Dam in the Qarehsou River of Ardabil Province. Journal of Watershed Management Research, 10(19), 85–94.[in Persian]
  • Nilsson, C., Reidy, C. A., Dynesius, M., & Revenga, C. (2005). Fragmentation and flow regulation of the world's large river systems. Science, 308(5720), 405–408.
  • Poff, N. L., Allan, J. D., Bain, M. B., et al. (1997). The natural flow regime. BioScience, 47(11), 769–784.
  • Rauf, M., & Ali Oghli, S. (2021). Estimation of environmental flow in the Balikhloo Chay River and assessment of the impacts of Yamchi Dam operation on the hydrological and environmental flow regime. Journal of Natural Environment, 15(1), 163–171. [in Persian]
  • Richter, B. D., Baumgartner, J. V., Powell, J., & Braun, D. P. (1996). A method for assessing hydrologic alteration within ecosystems. Conservation Biology, 10(4), 1163–1174.
  • Richter, B. D., Baumgartner, J. V., Wigington, R., & Braun, D. P. (1997). How much water does a river need?. Freshwater Biology, 37(1), 231–249.
  • Richter, B. D., Warner, A. T., Meyer, J. L., & Lutz, K. (2003). A collaborative and adaptive process for developing environmental flow recommendations. River Research and Applications, 19(5–6), 497–514.
  • Sedghi-Asl, M., Poursalehan, S.J. (2025). “Hydro-environmental flow classification of rivers (case study: Beshar River, Iran).” Ecological Indicators, 178.
  • Setayeshi Nasaz, H., Asghari Saraskanroud, S., Mostafazadeh, R., & Madadi, A. (2024). Assessment of changes in the hydrological flow regime and environmental flow components (EFCs) in the Khiav Chay River over a 30-year period. Hydrogeomorphology, 10(37), 25–43. [In Persian]
  • Smakhtin, V. U., & Anputhas, M. (2006). An Assessment of Environmental Flow Requirements of Indian River Basins. Colombo, Sri Lanka: International Water Management Institute (IWMI).
  • Smakhtin, V. U., Revenga, C., & Döll, P. (2006). Taking into account environmental water requirements in global-scale water resources assessments. IWMI Working Paper 42, International Water Management Institute, Colombo, Sri Lanka.
  • Smakhtin, V., Revenga, C., & Döll, P. (2004). A pilot global assessment of environmental water requirements and availability. Water International, 29(3), 307–317.
  • Tchobanoglus, G., Burton, F. and H.D. Stensel. 2003. Wastewater engineering: Treatment and reuse. American Water Works Association Journal, 95(5), p.201.
  • Tennant, D. L. (1976). Instream flow regimens for fish, wildlife, recreation and related environmental resources. Fisheries, 1(4), 6–10.
  • Tessman, S. A. (1980). Environmental assessment, technical appendix E: Environmental use sector reconnaissance elements of the western Dakotas region of South Dakota study. S. Fish and Wildlife Service.
  • Tharme, R. E. (2003). A global perspective on environmental flow assessment: Emerging trends in the development and application of environmental flow methodologies for rivers. River Research and Applications, 19(5–6), 397–441.
  • Vogel, R. M., & Fennessy, M. S. (1994). Flow-duration curves I: New interpretations and confidence intervals. Journal of Water Resources Planning and Management, 120(4), 485–504.
  • Vörösmarty, C. J., McIntyre, P. B., Gessner, M. O., et al. (2010). Global threats to human water security and river biodiversity. Nature, 467(7315), 555–561.
Volume 13, Issue 2
June 2026
Pages 1241-1267
  • Receive Date: 31 March 2026
  • Revise Date: 07 May 2026
  • Accept Date: 15 June 2026
  • First Publish Date: 22 June 2026
  • Publish Date: 22 June 2026