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Bliss Area Sewage System. Groundwater Monitoring Pete Ganzel Washington County Department of Public Health & Environment. Agenda. System History Local Geology Collection System Treatment System MPCA Discharge Permit Monitoring Site Evaluation & Design Evaluation of Piezometer Data
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Bliss Area Sewage System Groundwater Monitoring Pete Ganzel Washington County Department of Public Health & Environment
Agenda • System History • Local Geology • Collection System • Treatment System • MPCA Discharge Permit • Monitoring • Site Evaluation & Design • Evaluation of Piezometer Data • Discussion • Questions
System Overview Historical • Big Marine Lake • Bliss, Holiday Beach Plats 1950s • Uncontrolled Flooding 70s and 80s • Flood Control • 201 Program, Individual and Collector • Cost-$1.5 Million • System in Operation Since 1987
Local Geology • St Croix Moraine • Two Glaciations • Ice Block Lake • Ice Walled Lake Sediments • Outwash • Perched Shallow Aquifer
Additional site evaluation • More rigorous analyses of • Site • Soil • Stratigraphy • Hydrogeology • 7 additional pits (10 total) • Field permeability testing • Lab characterization • Shallow soil saturation monitoring (piezometers)
Results from further site evaluation • Site 10-20’ above nearby lake • 30-40’ above Big Marine Lake • 15-30’ above springs • Depressional area on southern edge of proposed soil treatment area • Lamellae bands common (19-250 cm/d) • Saturated zone within 15’ of surface • CONCLUSIONS: • -site limitations for in-ground sewage treatment system, mounding likely an issue • -Need to assess magnitude of mounding
Assessing Mounding Magnitude • Horizontal hydraulic conductivity of overlying soils (275-500 cm/d) • Analytical modeling (Khan et al., 1976) • 22000 gpd • 350’ length x 100’ width • Vertical permeability (assumed negligible) • OUTPUT – 31.5’ mounding height • CONCLUSION: Further analysis required
Assessing Mounding Magnitude continued • Numerical modeling approach (Prickett-Lonnquist, Illinois State Water Survey) • More complex site parameters • Compared (validated) to ambient conditions and correlated to observed piezometer readings • 300 days = mounding height of 10.7’; 5 years = 11.3’ (near or at soil surface) • Re-ran model with 50% flow (11000 gpd) • Mounding height of 6.8’ (within 4’ of surface elevation)
Overall Conclusions • Site not suitable for flows, loading rates if in-ground soil treatment • Alternative treatment options investigated • Treatment of water • Infiltration rates • Lessen mounding threat to environment • Ultimately alternative treatment employed • Monitoring of separation distances/mounding
System OverviewCollection System • 75 Dwellings • Septic Tanks • Shared Step Stations • Gravity Mains • Two Main Lift Stations • Force Mains
System OverviewTreatment System • 7500 Gallon Settling Tanks • Sand Filters and Dosing Station • Drainfields and Dosing Station
MPCA Discharge Permit • Requires Licensed Operator- Class D Facility • Renewed Every 5 Years • Goal: Protecting Water Quality • Reporting • Monthly- Flow, Precipitation • Permitted 19,800 gallons per day • Quarterly- Groundwater Monitoring, Effluent Sampling
Monitoring • 9 Piezometers • Groundwater/system separation (water level) • 8 Groundwater Monitor Wells • Groundwater Quality • Nitrogen, Phosphorus, Chloride • Effluent Sampling • BOD- Biochemical Oxygen Demand • Waste Strength • VOC- Volatile Organic Compounds
VOC Monitoring • Volatile Organic Compounds • Evaporate easily, aromatic • Variable solubility in water, usually low • Solvents, Thinners, Degreasers, Fuels • Many petroleum derived or synthetic • Some Carcinogenic, Teratagenic • Air pollution-smog • Gas Chromatography • Scan for 68 compounds • Sample effluent only • RAW effluent • Sand Filter Effluent • Sample once per year in July • Not Routinely Done in Sewage Plants • Costly Test- $120 per sample, lab cost
Some Perspective • Estimated Volume • System Volume-13,000 gallons • 1300 parts per billion is 80 ml of acetone in 13,000 gallons. • 8 parts per billion is 0.5ml of p-isopropyltoluene in 13,000 gallons. • Volumes probably more because of volatilization within the collection system. • Hit and Miss catching “slugs” of contaminants with limited sampling.
Piezometer Data • Separation to Drainfield Trenches • Operation of System
Site Evaluation 1985 Included analysis of Groundwater Elevation Soil Conductivity Projected Mounding