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EVALUATION OF ALTERNATIVE INSTREAM-FLOW CRITERIA AND WATER-SUPPLY DEMANDS ON GROUND-WATER DEVELOPMENT OPTIONS IN THE BIG RIVER AREA, RHODE ISLAND. U.S. Geological Survey R.I. Water Resources Board. MISSION.
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EVALUATION OF ALTERNATIVE INSTREAM-FLOW CRITERIA AND WATER-SUPPLY DEMANDS ON GROUND-WATER DEVELOPMENT OPTIONS IN THE BIG RIVER AREA, RHODE ISLAND U.S. Geological SurveyR.I. Water Resources Board
MISSION • Provide actionable information and detailed ground-water withdrawal strategies that the RIWRB and public suppliers may use to maximize withdrawals while minimizing the probability of adverse effects caused by these withdrawals in the basin.
ACTIONABLE INFORMATION • WHAT DO YOU NEED TO KNOW? Streamflow (probable) – Depletion = Probable Risk • WHEN DO YOU NEED TO KNOW IT? In Time to Affect Depletion • HOW DO YOU RESPOND? • Go to Alternate Withdrawal Plan • WHAT LIMITS RESPONSE? WSSMP Minimum Service Limit Volumes
Develop DSS to Provide: • Estimated “Natural” Streamflow Record • Ground-water flow model • Actual Streamflow record(s) • Historical Streamflow Analysis • Response coefficients • Withdrawal plans • Drought Projection • Hydrologic predictors • Withdrawal plans
Estimated “Natural” Streamflow Record • Use • Response Coefficients from Ground-Water Model • Withdrawal Records • Calculate Streamflow Depletion • Back Out Estimated “Natural” Streamflow • Extend Estimated “Natural” Streamflow Record beyond withdrawal records by MOVE.1/MOVE.3
Results: Ground-Water Withdrawals for Different Instream-Flow Criteria
Average Annual Ground-Water Withdrawals For Alternative Instream-flow Criteria
Information • Information and publications are available at URL: • http://ma.water.usgs.gov/projects/BigRiver.htm
Transient Model: Potential Results • Understand impacts of withdrawals on streamflow depletion during drought: Streamflow depletion during drought caused by withdrawals Streamflow during drought with no withdrawals Streamflow during drought with current withdrawals - = • Understand gains in streamflow when drought plan implemented: Effect of demand management on streamflow depletion Streamflow during drought with current withdrawals Streamflow during drought with demand management - = • Evaluate effectiveness of demand-management practices • Use results to constrain optimization • Other comparisons that can be made between simulation results?
Stream Depletion i Well j Stream Site k Preceeding months t Month *Note response coefficients should sum to almost 1 at the outlet of a closed basin. Reductions in ground water ET caused by drawdown account for some water Also, If a well gets water from a neighboring basin the depletions will not equal withdrawals
RHODE ISLAND DROUGHT MANAGEMENT PLAN: WHERE Normal Annual Precipitation Approximate location of the study area
What is Basin Safe Yield? Safe Yield = Natural Streamflow ± Alterations - Flow to maintain ecosystem • Calculation of safe yield requires knowledge of: • Natural, unaltered streamflow (estimated) • Streamflow resulting from alterations in the basin (estimated) • Flow to maintain ecosystem (specified)
Example of Basin Safe-Yield Graphical output • Natural flows or flow statistics • Altered (existing) flows • Target Flows • Effects of a particular withdrawal • Basin characteristics • Safe-yield estimate or appropriate safe-yield statistics Tabular Output Natural flow regime Log Streamflow, log Q Existing flow regime Target FDC Safe yield Exceedence probability*, in percent * Percent time streamflow exceeds a given level at a specified location
Reservoir water balance and firm yield Water in storaget= Storaget-1+ Inflowst – Outflowst • Precipitation • Surface inflow • Ground-water inflow • Evaporation • Other withdrawals • Drinking-water yields • Required releases • Uncontrolled releases (spills) • Loss to ground-water The firm yield of a reservoir is the maximum drinking-water yield that can be withdrawn without the complete depletion of available storage. Illustration by: C. Mendelsohn, USGS
Summary: The DSS is a Useful Tool • Provides quantitative forecast (probabilities) • Gives the RIWRB a method to report risks of low flows (decision makers decide based on risk) • Demonstrates/validates the need for conservation based on lagged depletions • Dynamic • The tool is applicable for various conditions • Forecasts can be modified as the situation evolves • Linked to management measures • User friendly • Based on proven methods