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Santa Ana River Wasteload Allocation Model Update BASIN MONITORING PROGRAM TASK FORCE September 19, 2017 Model Development Existing WLAM (R4) WLAM Update Expanded Area 564 subareas were delineated. Each subarea consists of


  1. Santa Ana River Wasteload Allocation Model Update BASIN MONITORING PROGRAM TASK FORCE September 19, 2017

  2. Model Development Existing WLAM (R4) WLAM Update Expanded Area • 564 subareas were delineated. • Each subarea consists of • Stream segment, • Pervious land area, and • Impervious land area. • They were delineated based on: • Topography • Drainage Patterns • Types of stream channels, and • Location of gaging stations and recharge basins 9/19/2017 2

  3. Hydrologic Simulation Program Fortran - HSPF Precipitation ET Infiltration Surface Runoff Interflow Deep Streambed Percolation Percolation • Comprehensive & Physically Based, • Simulates ALL Water Cycle Components & Water Quality, • Supported & Maintained by Federal Agencies (EPA & USGS), • Established Standard Guidelines and Calibration Performance Criteria, • Windows-Based Interface with Powerful Pre- & Post- Processors, and • Software is Free. 9/19/2017 3

  4. Coupling Process of HSPF and OCWD Recharge Facilities Model (RFM) Recharge Basins SAR Diversion Prado Dam OCWD RFM Outlet Prado Inflow Step 2 & Tributary Step 1 OCWD Streamflow to HSPF RFM SAR (shown in Yellow) Streamflow Streamflow Step 3 at OCWD at SAR at HSPF RFM Outlet Santa Ana 9/19/2017 4

  5. Calibration Process • Adjust model parameters until the model provides a reasonable match between the model-simulated and measured data. • Lower zone nominal soil moisture storage, • Base groundwater recession, • Fraction of groundwater inflow to deep recharge, • Fraction of remaining ET from baseflow, • Interflow inflow parameter, • Lower zone ET parameter, • Function tables (FTABLE) which includes physical information (shape, depth, width, slope, length, Manning Factor, and materials), and infiltration rates for reaches of each sub-watershed, and • Nitrogen reaction rate coefficient. 9/19/2017 5

  6. Location of Streamflow Calibration Targets 9/19/2017 6

  7. Location of TDS/TIN Calibration Targets 9/19/2017 7

  8. Calibration Performance Criteria R 2 (Goodness-of-Fit) Type of Flow Data Calibration Performance R 2 < 0.60 Daily Flow Poor 0.60 < R 2 < 0.70 Daily Flow Fair 0.70 < R 2 < 0.80 Daily Flow Good R 2 > 0.80 Daily Flow Very Good R 2 < 0.65 Monthly Flow Poor 0.65 < R 2 < 0.75 Monthly Flow Fair 0.75 < R 2 < 0.85 Monthly Flow Good R 2 > 0.85 Monthly Flow Very Good Source: Donigian (2002) 9/19/2017 8

  9. Existing WLAM (R4) R4 – WY 1995 to 2006 100000 R 2 = 0.68 WLAM Update (HSPF) Model-Calculated Daily Streamflow, cfs 10000 Daily Streamflow 1000 100 10 1 Fair 0.1 0.1 1 10 100 1000 10000 100000 Measured Daily Streamflow, cfs SAR at HSPF – WY 2007 to 2016 MWD Crossing 100000 R 2 = 0.91 Model-Calculated Daily Streamflow, cfs 10000 1000 100 10 1 Very Good 0.1 9/19/2017 9 0.1 1 10 100 1000 10000 100000 Measured Daily Streamflow, cfs

  10. Existing WLAM (R4) R4 – WY 1995 to 2006 100000 R 2 = 0.91 WLAM Update (HSPF) Model-Calculated Monthly Streamflow, cfs 10000 Monthly Streamflow 1000 100 10 1 Very Good 0.1 0.1 1 10 100 1000 10000 100000 Measured Monthly Streamflow, cfs SAR at HSPF – WY 2007 to 2016 MWD Crossing 100000 R 2 = 0.97 Model-Calculated Monthly Streamflow, cfs 10000 1000 100 10 1 Very Good 0.1 9/19/2017 10 0.1 1 10 100 1000 10000 100000 Measured Monthly Streamflow, cfs

  11. Summary of Streamflow Calibration Performance Daily Streamflow Monthly Streamflow 2008 WLAM WLAM Update 2008 WLAM WLAM Update Gaging Station (R4) (HSPF) (R4) (HSPF) WY 1995-2006 WY 2007-2016 WY 1995-2006 WY 2007-2016 San Timoteo Ck near Loma Linda Good Fair Good Fair Warm Ck near San Bernardino Fair Fair Fair Very Good Santa Ana River at E Street Good Very Good Very Good Very Good Santa Ana River at MWD Crossing Fair Very Good Very Good Very Good Temescal Ck at Main Street Poor Fair Good Poor Chino Ck at Schaefer Avenue Fair Very Good Good Good Cucamonga Ck near Mira Loma Poor Very Good Good Very Good Santa Ana River into Prado Dam Fair Very Good Very Good Very Good Santa Ana River at Santa Ana NA Poor NA Good 9/19/2017 11

  12. Daily TDS at Santa Ana River at MWD Crossing 1,000 2008 WLAM (Mean Residual = 16.4 mg/L) WLAM Update (Mean Residual = -0.4 mg/L) 900 800 Observed 700 Model-Calculated Daily TDS, mg/L 600 500 400 300 200 100 Model-Calculated 0 Oct-94 9/19/2017 Oct-96 Oct-98 Oct-00 Oct-02 Oct-04 Oct-06 Oct-08 Oct-10 Oct-12 Oct-14 12

  13. Summary of TDS/TIN Calibration Performance TDS, mg/L TIN, mg/L 2008 WLAM WLAM Update 2008 WLAM WLAM Update Gaging Station (R4) (HSPF) (R4) (HSPF) WY 1995-2006 WY 2006-2016 WY 1995-2006 WY 2006-2016 Santa Ana River at 16.4 -0.4 -0.45 -0.40 MWD Crossing Santa Ana River 20.7 -2.0 -0.07 -0.28 below Prado Dam Santa Ana River at Imperial Highway NA 7.8 NA -0.21 near Anaheim 9/19/2017 13

  14. Summary • The WLAM was updated with recent data and recalibrated from October 1, 2006 through September 30, 2016 (Water Years 2007 through 2016). • The calibration results show: • Good to very good performance at the majority of the streamflow gages . • The streamflow calibration performance for the WLAM update is equal to or better than the 2008 WLAM at nearly all gages. • TDS/TIN residuals from the WLAM update calibration are lower than the 2008 WLAM residuals for nearly all gages. • The results indicate a satisfactory model calibration. 9/19/2017 14

  15. Major Assumptions for Waste Load Allocation Scenarios Maximum Planned 50% of Discharge Scenario Hydrology Land Use Recycled / Planned (Zero Discharge) Recycled Recycled) A X 2012 B X C X WY 1950- 2016 D X General Plan E X (2040) F X 9/19/2017 15

  16. Discharge and Reuse Data City of City of Corona EVMWD SBVMWD WMWD City of Riverside Beaumont WWTP WWTP SNRC (City WRCRW Facility WRF 1 RWQCP 001 002 Creek) Design 11.5 4 46 8 8 0 14 Max 11.4 3.30975 31.2 8 8 0 7.76 Current Ave 3.4 2.9696 26.8 0.5 4.52 0 6.44 Min 1.5 2.4232 21.8 0.5 4.5 0 5.22 Design 11.5 46 12 12 7.5 14 Discharge Max 11.5 33.8 12 12 7.5 10.3 2020 (MGD) Ave 4.6 25 0.5 7 6.4 7 Min 1.5 19 0.5 6.5 6 5.7 Design 15 46 16.8 16.8 7.5 14 Max 15 46 16.8 16.8 7.5 15.3 2040 Ave 8.5 22.5 0.5 14 6.4 10 Min 1.5 19 0.5 13 6 8.5 In house Max 7.1 1.8 0.3 0.3 0 0 only In house Current Ave 2.7 0.9 0.2 0.2 0 0 only In house Min 0 0.6 0.2 0.2 0 0 Reuse of only Recycled Water Max 10 10 0.45 0.45 7.5 7 (MGD) 2020 Ave 2.7 4 0.3 0.3 6.4 3 Min 0 1 0.2 0.2 6 0 Max 13.5 20 0.63 0.63 7.5 7 2040 Ave 3.5 16.5 0.42 0.42 6.4 3 Min 0 3 0.2 0.2 6 0 Current Discharge Permit 10 6 / 3.6 10 13 NA NA 10 12-mos. Average 5.5 / 5.2 4.34 4.5 2.5 NA NA 2.2 TIN Unknown Unkno Est. 12 mos. Average in 2040 5.5 / 5.2 10 6 2.2 wn Water Quality Current Discharge Permit 700 / 770 400 / 300 650 700 700 NA 625 (mg/L) 12-mos. Average 655 / 683 434 623 686 686 NA 529 TDS 9/19/2017 16 Unknown Unkno Est. 12 mos. Average in 2040 655 / 683 650 463 529 wn

  17. Discharge and Reuse Data EMWD IEUA City of Redlands City of San Bernardino YVWD Facility Design Max Current Ave Min Design Discharge Max 2020 (MGD) Ave Min Design Max 2040 Ave Min Max Current Ave Min Reuse of Max Recycled 2020 Ave Water Min (MGD) Max 2040 Ave Min Current Discharge Permit TIN 12-mos. Average Est. 12 mos. Average Water in 2040 Quality Current Discharge (mg/L) Permit TDS 12-mos. Average Est. 12 mos. Average in 2040 9/19/2017 17

  18. Evaluation of Wastewater Recharge in Percolation Ponds – Pilot Program • City of Redlands, • Coty of Corona, • IEUA, and • Dairy ponds in Chino-North GMZ 9/19/2017 18

  19. QUESTIONS? 9/19/2017 19

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