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Denver Water’s Preparation for the Stage 2 Disinfectant By-Product Rule Bruce Hale (DW) Steve Lohman (DW) Arnold Strasser (DW) Edward Koval (B&V) Important Stage 2 features • New Distribution System (DS) definitions • Locational Running Annual Average (LRAA) MCLs • Significant Excursions • Phased compliance • Initial Distribution System Evaluation (IDSE) Finding new Stage 2B monitoring sites w/ IDSE • Under “early schedule”, IDSE results due 2 yrs from promulgation • See EPA Stage 2 Guidance Manuals http://www.epa.gov/safewater/stage2/index.html IDSE options • Standard Monitoring Program (SMP) • System-specific Study (SSS) Denver Water stats • • • • • 3 Surface water treatment plants (WTPs) Max. treatment capacity: 710 MGD, chloramine Max. day: 500 MGD Base day: 120 MGD Total “combined” pop. served: ~1.1 million, ~50% in over 60 consecutive systems • Water may be served from any operating WTP to any part of “combined” DS • Any, or all WTPs may operate at the same time Denver will opt for a SSS IDSE • DW combined system too complex for SMP • DW has computer model to assist w/ site selection – Water age provided by model, main factor influencing DBPs from respective WTPs • DW already has much data IDSE is intended to uncover Routine DS monitoring programs • Regulatory DBP (HAA/THM) monitoring: 12 sites, monthly • VOC monitoring: 9 sites, 8 times/year • Sp. Conductance checks: 20 sites, weekly • Regulatory total chlorine monitoring: ~ 500 samples/month What months have highest historical DS DBPs? Annual TTHM profile (monthly avg. of all DS data points) 60 conc. (ug/L) 50 40 2000 2001 2002 2003 30 20 10 0 Jan Feb Mar Apr May Jun Jul Month Aug Sep Oct Nov Dec Monthly DS Max. TTHM profile 100 90 80 conc. (ug/L) 70 60 2000 2001 2002 2003 50 40 30 20 10 0 Jan Feb Mar Apr May Jun Jul Aug Sep Oct Nov Dec Month Hypothetical LRAA w/ monthly DS Max values 80 70 TTHM HAA5 50 40 30 20 10 Year 03 20 03 20 03 20 02 20 02 20 02 20 01 20 01 20 01 20 00 20 00 20 00 0 20 conc. (ug/L) 60 Rationale for evaluating sites with a single sample event • Unable to identify “typical” DS operations • Sample when all plants in service • Sample when DBPs are high, to make differences between sites more evident • Historical data available for context • Sites chosen & evaluated with “all-pipes” model (APM) Key APM products • At any DS location, percent composition by water source (WTP) • Water age at any DS location. APM Validations –Extended Period Simulations (EPS) • Hydraulic validation: max day • Water Age validation: base load day • Source trace validation: 3 potentially high DBP production days Basis for choosing IDSE sample sites • Prior knowledge: – Foothills WTP produces highest DBPs – Foothills WTP treats the most water & has largest service area – HAAs & THMs trend the same in the DS • APM’s water age representation • APM’s source water identification September 9, 2003 Water Age Analysis Moffat WTP Marston WTP Foothills WTP September 9, 2003 Foothills WTP Source Trace Moffat WTP Marston WTP Foothills WTP September 9, 2003 Moffat WTP Source Trace Moffat WTP Marston WTP Foothills WTP How many sites will DW’s SSS cover? • Under the “DS entry point” scenario: 24 • Under the “population-based” scenario: 32 Distribution of 32 sample sites using SMP guidelines • 1 “first customer” site for each WTP • Priority given to sites likely served by Foothills WTP –9 –5 –5 –4 Max residence sites Avg residence sites Sites of max residence w/ blends Sites of avg residence w/ blends • 2 Max residence sites each, from Moffat and Marston WTPs Distribution of 32 sample sites (cont.) • 2 Avg residence sites each, from Moffat and Marston WTPs • Blends of Moffat and Marston insignificant • ~50% are new sites not used in DW monitoring programs • No Stage 1 sites DW tests SSS strategy in Aug, 2004 • 32 sites sampled on one day • All sites tested for HAAs & THMs • Field tests at each site – Specific conductance – Total chlorine – Temperature Moffat WTP Marston WTP Foothills WTP Conductivity vs TTHM DS sites w/ TTHM < Platte WTP effluents 80 2 TTHM (ug/L) R = 0.9197 60 40 20 0 0 50 100 150 200 Specific conductance 250 300 350 HAA5 vs TTHM (all sites) 60 HAA5 (ug/L) 50 2 R = 0.8192 40 HAA5 max 30 TTHM max 20 10 0 0 20 40 60 TTHM (ug/L) 80 100 Chlorine vs HAA5 DS sites w/ mostly Foothills WTP effluent 2 Foothills’ first customer Cl2 (mg/L) 1.6 1.2 0.8 0.4 0 0 20 40 HAA5 (ug/L) 60 Study Conclusions • Study was successful – Reflected bias towards Foothills’ DS – Found some sites with high DBPs • Level of TTHM LRAA MCL was exceeded at one site only, and not at all for HAA5 • No site exceeded proposed excursion levels • Confirmed THMs and HAAs act similarly • The ratio of Foothills water is the main influence on DBPs at any single site. Acknowledgements Royce Bennett Rhonda Birdnow Fred Sanchez Janice Vaughn Greg Zempel