Tools for Accurate Sewer Metering and Billing
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1 Tools for Accurate Sewer Metering and Billing May 20, 2008 Tim Prince Chief Engineer Oakland County Drain Commissioner O&M Division Robert Czachorski Orchard, Hiltz & McCliment Livonia, Michigan
2 The Clinton-Oakland Sewage Disposal System Collect sewage from about 250,000 people in 11 Cities, Villages and Townships (CVTs) for conveyance to the Detroit System for Disposal City of Auburn Hills Independence Township Lake Orion Village Oakland Township Orion Township Oxford Township Oxford Village City of Rochester City of Rochester Hills Waterford Township West Bloomfield Township Oakland County Wayne County City of Detroit!
3 COSDS District Map of the Oxford (Twp and Village) Outside COSDS System Independence Orion Lake Orion Oakland Auburn Hills Rochester Waterford Pontiac (not in system) Rochester Hills West Bloomfield
4 1996 Management Agreement Prior to 1996, it was recognized that the system had more capacity than originally allocated to the CVTs due to routing and travel time effects A study was done to determine how much excess capacity was available 1996 agreement allocated the capacity to CVTs and stipulated monthly penalties for exceeding capacities Using this capacity pushed the system and necessitated better tracking of flows to ensure adequate system performance and tracking of CVT peak flows
5 The Goal: Change the Billing System from REU-Based to Flow-Based Customer REUs 5 #1 Total Flow #2 Total Flow 4 Rain 1.0 #1 3,520 Flow (cfs) 3 Rain (in) #2 8, /1 3/3 3/5 3/7 3/9 3/11 3.0
6 The Challenge: Flow Metering is Not an Exact Science Even flumes are not perfect 60 Flow 0 50 Rain 1 Dye testing helps, but still leaves discrepancies These tools alone are not enough Flow (cfs) Rain (inches) 10 There are millions of dollars on the line 0 5/20/04 5/22/04 5/24/04 5/26/04 5/28/04 5 6
7 Objectives of the Reporting System Enforce the COSDS 1996 Management Agreement, which allows for purchase capacity exceedances Bill based on more equitable methodology Encourage incentives for I/I control & reduction Proactively meet the State SSO Policy Serve as a diagnostic tool for system performance
8 Key Success Factors The right consultant Robust metering system Community interaction Technical flow review toolbox
9 The Right Consultant Steering committee formed and participated in selection QBS process used for selection OHM Selected Primary differentiator: value added tools for wet weather modeling Versatility on both technical abilities and communication with public officials
10 Robust Metering System Needed to accomplish more accurate billing More direct metered districts (22 new meters) Brought the total to 61 billing meter sites Parallel AV meters at flumes experiencing surcharging (6 new meters) * * 23% incrementally metered
11 Old Directly Metered Areas Incremental Areas New Directly Metered Areas
12 Community Interaction Steering committee participation Quarterly COSDS Meetings Individual community one-on-one meetings Mock-bills computed for one year Project web site established
13 Billing Flow Review Toolbox
14 Billing Components Volumetric component - requires good understanding of dry weather flows Peak flow component - requires accuracy in metering system during wet weather flows Volumetric Formula 30 Maximum Assignment Capacity 25 + Direct metered districts 20 Purchase Capacity + Incremental Districts Flow (cfs) Interceptor I/I Adjustment 5 = CVT Billed Flow 0 7/15/05 7/16/05 7/17/05 7/18/05 7/19/05
15 Billing Flow Review Tools 1. Dye testing - accurate metering 2. Mass flow balance - accurate allocation of incremental flow 3. Wet weather flow editing - fill in gaps during wet weather when a meter fails 4. Hydraulic routing - accounting for routing and travel time for accurate peak flow bills 5. Interceptor I/I - accurate identification and allocation
16 Tool #1 - Dye Testing Procedures / methodology How it was used - applied as a constant factor Dye testing periodically updated (annually) Flow (cfs) Original Flow Dye Corrected Flow Dye Test Point 5 0 7/1/05 7/2/05 7/3/05 7/4/05 7/5/05 7/6/05 7/7/05 7/8/05 7/9/05 7/10/05 7/11/05
17 Dye Results at Outlet (all flows dye corrected) Metered Upstream Flows 3.26 cfs 1020 to Meter 1001 = 40.7 cfs Flow from 1001 and 1020 should 35.7 cfs 42.1 cfs balance with = cfs 1000 Investigation into 1001 later uncovered an issue with the dye test set-up.
18 Tool #2 - Mass Flow Balance Flows averaged for an entire quarter Dye factors applied as a constant factor Local Direct Meters 1.3 cfs (126 gpcd) cfs (100 gpcd) Incremental: 0.3 cfs (17 gpcd) Per capita flows computed for direct and incremental areas Incremental flows suggest ELPS is high Local Direct Meters 5.7 cfs (85 gpcd) ELPS cfs (103 gpcd) Incremental: 2.4 cfs (270 gpcd) 3.0 cfs (95 gpcd)
19 Tool #2 - Mass Flow Balance Reduced ELPS by 10%, which greatly improves the incremental balance Criteria developed for allowable minor changes Local Direct Meters 1.3 cfs (126 gpcd) cfs (100 gpcd) Incremental: 1.3 cfs (149 gpcd) Significant numerical changes reviewed by mass flow balance team Review of ELPS meters in field showed SCADA scaling issue Local Direct Meters 5.7 cfs (85 gpcd) ELPS cfs (103 gpcd) Incremental: 1.4 cfs (149 gpcd) 3.0 cfs (95 gpcd)
20 Tool #3 - Wet Weather Editing Wet weather flows are very important because of peak component to the billing system Flow meters are more prone to issues and failure during peak flow events Accurate editing tool desired to fill in gaps during periods of meter failure or inaccuracy Two independent methods used to edit wet weather flows: meter correlations and the antecedent moisture model
21 Antecedent Moisture Effects on Wet Weather Flows
22 The Antecedent Moisture Model Based on system identification techniques from aerospace control systems and digital signal processing Continuous modeling approach as opposed to an event based model for I/I Separate models for inflow and infiltration vary continuously Model at each time step adjusted based on antecedent rainfall and temperature
23 Antecedent Moisture Accurately Simulates Dry and Wet Conditions
24 25 20 Meter 1315 Wet Data Editing Flow (cfs) /15/05 7/16/05 7/17/05 7/18/05 7/19/05 7/20/05 Two methods used to review data Flow (cfs) Meter 1315 Primary is meter correlation to adjacent meters Secondary is antecedent 0 7/15/05 7/16/05 7/17/05 7/18/05 7/19/05 7/20/05 moisture model
25 Tool #4 - Incremental Districts Hydraulic Routing EXTRAN hydraulic model used for routing Model accounts for routing & travel time effects Incremental hydrograph uniquely determined through iterative identification process
26 Tool #5 - Interceptor I/I Needs to be properly allocated to the system Nighttime Minimum Flows at Meter Minimum Daily (cfs) M1000 (cfs) Can not be directly measured from metering data Flow (cfs) /1/06 8/11/06 8/21/06 8/31/06 9/10/06 9/20/06 9/30/06 Use meter outlet meter (1000) nighttime flows as indicator of interceptor I/I Captures the variations in time in interceptor I/I Interceptor I/I in Reaches 1-6 (gal/day per inch-mile) Interceptor I/I Correlation in gpdim Meter 1000 Nighttime Flow
27 Tool Development Conclusions Flow meters are not perfect - some editing and corrections are needed for use in billing Dye testing alone will not initially result in adequate mass flow balance - other tools needed It is critical to involve the full team in reviewing numeric edits: data processors and field staff Belt and Suspenders - two methods to edit wet weather flows provides confidence in bills Billing system provided more value than just bills: system diagnostics & proactive SSO control
28 Billing System Conclusions Recognize that sewage flow metering is not an exact science But remember the objectives: Bill based on more equitable methodology Enforce the operating agreements Serve as a diagnostic tool for system performance Encourage incentives for I/I control & reduction Proactively meet the State SSO Policy Flow metering meets the objectives better than prior REU methodology
29 Questions?
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