<<

Simulation of Flows and Quality in the Using DSM2

Siqing Liu, Bob Suits

DWR, Bay Delta Office, Modeling Support Branch

2011 CWEMF Annual Meeting, February 28 –March 2 1 Topics

• Project objectives

• Aqueduct System modeled

• Assumptions / issues with modeling

• Model results –Flows / Storage, EC, Bromide 2 Objectives

Simulate Aqueduct and water quality

• 1990 – 2010 period

• DSM2 Aqueduct version calibrated by CH2Mhill

Achieve 1st step in enabling forecasting Physical System simulated

(42 miles)

(444 miles)

• East Branch to

• West Branch to Pyramid Lake (40 miles)

• Delta‐Mendota (117 miles) 4 Physical System, cont Pumping Plants Buena Vista (Check 30)

Jones Pumping Plant Teerink (Check 35)

South Bay Chrisman (Check 36)

O’Neill Pumping-Generating Edmonston (Check 40)

Gianelli Pumping-Generating Alamo (Check 42)

Dos Amigos (Check 13) Oso (West Branch)

Las Perillas (Costal branch) Pearblossom (Check 58) 5 Physical System, cont Check structures and gates

• Pools separated by check structures throughout the aqueduct system

(SWP: 66, DMC: 21 )

• Gates at check structures regulate flow rates and water surface elevation 6 Physical System, cont Turnout and diversion structures

• Water delivered to agricultural and municipal contractors through diversion structures

• Over 270 diversion structures on SWP

• Over 200 turnouts on DMC 7 Physical System, cont Reservoirs / Lakes Represented as complete mixing of water body

• O’Neill Forebay

Head boundaries

• Santa Clara Terminal Reservoir

• The Mendota Pool

• Silverwood Lake

• Pyramid Lake 3 Physical System, cont 8 Pumping Plants

• Banks Pumping Plant

• Jones Pumping Plant

• O’Neill Pumping-Generating

• Gianelli Pumping-Generating

• Pacheco

• Dos Amigos (Check 13)

• Buena Vista (Check 30)

• Teerink (Check 35)

• Chrisman (Check 36)

• Edmonston (Check 40)

• Oso (West Branch)

• Pearblossom (Check 58) 9 Assumptions / Issues with Modeling

Model Assumptions

• Check structures treated as to control water elevation

• Pipes, siphons, and treated as open channels

• Instantaneous transfer of water

• Complete and instantaneous mixing of water in reservoir

Hydraulics Issues

• Gains / Losses

• Monthly diversion data

dry-up 10 Issues with Modeling, Cont

Water Quality

• Uncertainty for Groundwater Pump‐in, Storm water Inflow

• Missing data at Banks / Jones PP for extended periods

• Data errors at Banks / Jones PP

Data Collection / Generation

• Hydraulic data compiled by Bryant Giorgi of O & M

• Water quality data compiled by Marcia Scavone‐Tansey of MWQI 11 Hydraulic Simulation of Aqueduct System

Boundary Conditions

•Flow at Banks and Jones Pumping Plants

• San Luis Reservoir Operations

• DMC and O’Neill Forebay Operations

• Diversions to South Bay Aqueduct and West Branch

• Contractor Diversions 12 Hydraulic Simulation of Aqueduct System

Output

• Flows at typical Checks

• Stages of San Luis Reservoir

Locations with measured data

• Measured flow data at SWP Checks 21, 30, 35, 40 and 58

• Storage of San Luis Reservoir 13 Model Results: Hydraulics Model Results: Hydraulics, Cont 14 Model Results: Hydraulics, Cont 15 16 Model Results: Hydraulics, Cont 17 Model Results: Hydraulics, Cont 18 Model Results: Hydraulics, Cont EC Simulation of Aqueduct System 19

Input • EC boundary at Banks (measured) and Jones PP (measured and DSM2 output)

• EC for source flows, i.e. Groundwater Pump‐in, Storm water inflow (WDL, USBR sample data)

Output

• At typical Checks

• San Luis Reservoir Available measured data

• SWP Checks 12, 13, 18, 21, 29, 41, 66

• DMC Checks 13, 21

• South Bay Aqueduct, Del Valle Check 7

• San Luis Reservoir (using Pacheco Pumping Plant) Model Results: EC 20 Model Results: EC, Cont 21 Model Results: EC, Cont 22 Model Results: EC, Cont 23 Model Results: EC, Cont 24 Model Results: EC, Cont 25 Model Results: EC, Cont 26 Model Results: EC, Cont 27 Model Results: EC, Cont 28 Model Results: EC, Cont 29 Model Results: EC, Cont 30 Model Results: EC, Cont 31 32 Bromide Simulation of Aqueduct System

Input • Br at Banks PP and Jones PP (both measured and DSM2 output)

• Br for source flows, i.e. Groundwater Pump‐in, Storm water inflow (WDL, USBR sample data)

Output • At typical Checks • San Luis Reservoir

Locations with measured data • SWP Checks 13, 29, 41, 66 • DMC Checks 12 • South Bay Aqueduct, Del Valle Check 7 • San Luis Reservoir Model Results: Bromide 33 Model Results: Bromide, Cont 34 Model Results: Bromide, Cont 35 Model Results: Bromide, Cont 36 Model Results: Bromide, Cont 37 Model Results: Bromide, Cont 38 Model Results: Bromide, Cont 38 Model Results: Bromide, Cont 40 41 Conclusions

• DSM2-Aqueduct model simulates hydraulics, EC, and bromide over historical 1990-2010 period reasonably well.

• Treating San Luis Reservoir as completely mixed is sufficient for meaningful results

• Other assumptions make sense for available information Acknowledgments

• MWQI

• DWR O&M

• Real‐time Data Forecasting (RTDF) committee

• Metropolitan Water District of