Environmental Flows Assessment • Objective Based Flow-Setting – In certain cases, people intend to have specific pre-defined ecological, economical and social objectives for the river. • Scenario Based Flow-Setting – if water managers are able to understand and make decision on water allocations and scenarios for trade offs in managing and balancing the water demands/requirements. Building Block Methodology • Building Block Methodology – one of the most comprehensive methodology – Bottom up approach – Much detailed and can be tailored to suit local conditions – Most frequently used holistic methodology – Rigorous and well documented Building Block Methodology • Flexible to accommodate other local aspects, like religious and spiritual requirements (hence applicable for Indian rivers) • Functions well in data-rich and data-poor situations • Links to external stakeholders and public participation processes • Applicable to regulated and non-regulated river regimes • Moderate to highly resource intensive Building Block Methodology Step 1: Use a stakeholder consultation process to set objectives for the environmental condition of the river Step 2: Assess a modified flow regime that will meet those objectives Step 3: Use flow-dependent indicators (e.g. dolphins, gharial, turtles, fish, invertebrates, floodplain vegetation), non-consumptive human requirements, as well as water quality metrics and sediment transport, to identify water depths, velocities, river widths, and substrate types that will provide required habitats and conditions. Such hydraulic requirements can then be converted to hydrological (flow) requirements Step 4: Identify critical components (building blocks) of the flow regime that govern environmental conditions (e.g. dry and wet season base flows, and different-sized high flows and floods) Stage A: Scoping Task 1: Stage B: Preparation for the Assessment Initiate EFA assessment (level of detail, define methodology) Task 2: Constitution of the assessment team Task 3: Zone the study area Task 4: Habitat integrity Task 5: Site Selection Task 6: Surveys and measurements Biological Surveys Hydraulic survey Hydrological analysis Task 7: Ecological and Social Importance and Sensitivity Task 8: Define reference conditions Task 9: Define present ecological status Task 10: Define environmental objectives Geomorphological survey Water Quality analysis Social survey Stage C: EFA Setting workshop Stage E: Implementation and compliance monitoring Stage D: Negotiation Task 1: Hydrological yield analysis Task 2: Scenario analysis Task 3: Decision Objectives GANGA EFA: Promote the sustainable use of water resources in the Ganga to: - Ensure ecological integrity -Provide livelihoods - Maintain sacred values Flow Indicators Fish, Dolphins, Invertebrates, Algae, Religious rites, Livelihoods, Channel processes Habitats Activities Processes Required Hydraulics Depth Velocity Width Substrate 7 Hydrology Cubic metres per second of Water required Rishikesh • Zone I: Upper Reach (Gangotri to Rishikesh) • Zone II: Reference zone (U/S of Garhmukteshwar to Narora) • Narora Zone III: Middle Reach (Narora to Farrukhabad) Kannauj • Zone IV: Lower Reach (Kannuaj to Kanpur) Zone 1 Gangotri to Rishikesh Zone 3 Narora to Farrukhabad Zone 2 U/S of Garhmukteshwar to Narora (Reference Zone) Zone 4 Kannauj to 9 Kanpur Components 1. Hydrology - Identify and review previous hydrological modeling studies and assessment of their usability - To set up model and calibrate under existing conditions of land and water use - Examine the feasibility of different ways of modeling the past ‘natural’ and present-day flows, using observed flow data Components 2. Fluvial Geomorphology and hydraulic modeling for maintaining sustainable flows - Analysis of sediments in the river, and the assessment of the effects that will result from different flow regimes - Analyse the channel and floodplain morphology in terms of the geomorphic features, and their stability - Generate the cross section and longitudinal profile for hydraulic modelling 3. Habitat preferences of selected Aquatic species – Assess present condition in terms of the difference between the reference condition and survey results – Describe measured depths, average velocities and substratum types most commonly associated with sensitive species and families, and/or with maximum biodiversity Components 4. Economic and Livelihood objectives for Maintaining Sustainable Flows 5. Evaluate livelihood activities and its implications on environmental flows of the river Assessment of Cultural & Spiritual in stream flow required for Maintaining Sustainable Flows – Representation of the river in mythology, folklore, folk art and popular literature and art – Historical evidence of civilizations along the river, and its influence on society – Cultural, Religious, spiritual importance of the Ganga, with focus on rituals and festivals 6. Water Quality and Pollution – Generation of data on water quality parameters that is not available from any sources, but considered essential by the water quality group (samples from 30 locations) – Assessment of various types of pollution loads in different stretches/sub-stretches Arriving at E-Flows STEP 1: Hydrology and Hydraulics Cross Sections for each zone 164 ELEVATION At Kachla Ghat metres above sea level 163 162 161 160 159 158 0.0 332.1 515.5 587.0 655.5 806.4 Distance from the right bank, m 864.8 1,035.7 1,247.8 STEP 2: Flow motivations Flow recommendations based on requirements of biodiversity, Livelihoods, Culture/Spiritual needs, Geomorphology Maintenance Flows The Maintenance Flows are for "normal" years, not very wet or not very dry, here one would expect all the ecological functions and processes: fish breeding floodplain wetlands full sediment transport etc. Maintenance Flows would be equaled or exceeded during 70 years out of 100; however flows would be lower for 30 years out of 100 or in other words, 70% probability on the flow duration curve. For a long-term E-Flow, the water volume required would be at maintenance recommendations or higher for 70% of the time, and between drought and maintenance for 30% of the time. STEP 3: Calculating critical flows Critical flows • Kaudiyala: – January maintenance flow: fluvial geomorphology – August maintenance flow: biodiversity • Kachla Ghat & Bithoor: – August flows (both during maintenance and drought years): cultural and spiritual • Almost half of the critical flow recommendations were influenced by biodiversity requirements STEP 4: Calculating annual E-Flows requirements – Driest and wettest months under maintenance and drought conditions (January – driest month and August – wettest month) – E-Flows values were calculated, based on inputs from working groups, by hydrologist for other months of the year by means of interpolation – Monthly flow volumes for each month of the year for lowflow and high-flow components calculated Arriving at E-flows 165 At Kachla Ghat August - maintenance 164 August - drought metres above sea level 163 162 161 Dry Season-Normal Year Dry Season-drought 160 159 158 0.0 332.1 515.5 587.0 655.5 806.4 Distance from the right bank, m 864.8 1,035.7 1,247.8 Results: Zone 1, Maintenance Flows Site -Kaudiyala 14000 E-Flows: 72% of Mean Annual Runoff Flow Volume, MCM Present day flows could not be calculated, as flow release data from the Tehri Dam was not available 12000 72% MAR 10000 8000 6000 4000 2000 0 1 2 3 4 5 6 7 8 9 10 11 Months maintenance low maintenance high natural total 12 Results-Zone 3: Narora–Farrukhabad Maintenance Flows 14000 Site –Kachla Ghat Present day flows does not meet E-Flows requirement during the lean season Flow Volume, MCM E-Flows requirement: 45% of MAR 45% MAR 12000 10000 8000 6000 4000 2000 0 1 2 3 4 5 6 7 8 9 10 11 12 Months maintenance low maintenance high natural total Present Results - Zone 4: Kanauj- Kanpur Maintenance Flows Site EF4 – Bithur 18000 16000 Present day flows not meeting E-Flows requirements for lean months 14000 Flow Volume, MCM E-Flows: 47% of MAR 47% MAR 12000 10000 8000 6000 4000 2000 0 1 2 3 4 5 6 7 8 9 10 11 12 Months maintenance low maintenance high natural total Present Key Issues • Access to observed long term hydrological data, is critical for assessing flows and this would have considerably increased the confidence in the environmental flow assessment. • Further calibration and verification of the existing rated crosssections, and the establishment of additional cross-sections, would also increase confidence in the flow recommendations • Relationships between indicator fish, invertebrates and flow would allow more precise flow recommendations • More precise relationships between water quality parameters and flow would have allowed the prediction of the effects of recommended flows on water quality to be assessed E-flows • Not a one time flow; Regime of flows • Assess E-flows using a holistic approach: hydrology, hydraulics, fluvial geomorphology, water quality, socio-cultural-spiritual, biodiversity and livelihood • Need to be an integral part of the EIA & CIA – Bottoms up-project, sub-basin to basin level; – Existing projects – Trade-off analysis • Need to place it in the context of river basin management plan E-flows • Implementation & monitoring – Joint monitoring – Whether required releases are being made – Impacts • Adaptive process needed in E-flows assessment and implementation • The EF process should be embedded in a framework of inclusive stakeholder understanding and participation, and preferably within a broader context of IWRM Partners Facilitation: Biodiversity: Cultural/Spiritual: Livelihoods: Geomorphology: Water Quality: Hydraulics: Hydrology: Prof Jay O’Keeffe, (formerly UNESCO-IHE, Netherlands) & Dr Vladimir Smakhtin, IWMI Prof Prakash Nautiyal, Garhwal University Prof Ravi Chopra, People’s Science Institute Prof Murali Prasad, IIT Kanpur Prof Rajiv Sinha, IIT Kanpur Prof Vinod Tare, IIT Kanpur Prof A K Gosain, IIT Delhi Dr Vladimir Smakhtin, Dr Luna Bharati, IWMI THANK YOU Building Block Methodology Different EF Assessment Methodologies Assessment Method Basis Cost/time Confidence Example Look-up tables Hydrology Small Low Tennant Time Series models Hydrology Small/Medium Low IHA Rated X-Section models Hydraulics Medium Medium Intermediate (SA) Habitat Models Hydraulics/Ecology High Medium IFIM Regional Hydrology/Ecology High (initial) Medium ELOHA/Desktop Holistic Hydraulics/Ecology /Geomorph./Social/ Water Quality High High BBM/DRIFT/ Benchmarking Over 200 methodologies