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Lagoon & Stabilization Pond Sizing Calculator - Facultative, Aerated, and Storage Lagoon Checks

Size wastewater lagoons based on BOD loading, climate zone & detention time requirements

Check facultative, aerated, and storage lagoon planning inputs from entered flow, influent BOD, climate zone, geometry, and storage period. Outputs include local area, volume, detention, earthwork, and aeration placeholders, plus source warnings for state criteria, permit limits, site data, liner requirements, and qualified review.

Pro Tip: Climate loading rows are only a screening input. Verify the current state design standard, permit basis, measured wastewater strength, seasonal discharge window, soil and groundwater data, and qualified process review before using any lagoon number for design, funding, construction, or compliance.

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Lagoon & Stabilization Pond Sizing Calculator

How It Works

  1. Enter Screening Inputs

    Input flow rate, influent BOD concentration, optional effluent target, and population context. Use measured plant or planning-flow data where available.

  2. Select Lagoon Type and Climate

    Choose facultative, aerated, or storage lagoon and select a climate zone. Treat the local loading rows as placeholders until current state criteria are verified.

  3. Configure Cell Layout

    Set number of cells, operating depth, freeboard, and side slope ratio. Confirm cell arrangement, hydraulics, liner, and berm requirements with project sources.

  4. Review Planning Results

    Review surface area, volume, detention, local range flags, approximate cell dimensions, earthwork calculator, and source warnings before any design use.

Built For

  • Small towns screening early lagoon wastewater options
  • Engineers comparing preliminary expansion scenarios before source reconciliation
  • Operators sanity-checking entered flow and BOD assumptions for further review
  • Rural communities framing questions for lagoon versus mechanical treatment planning
  • Project teams collecting source gaps before a formal design submittal

Assumptions

  • Organic loading rates are local screening bands and are not represented as current state-approved criteria
  • Influent BOD and TSS are user-entered and assumed constant (no seasonal or diurnal variation applied)
  • Lagoon operating depth follows local screening ranges only
  • Side slope ratios are user-selectable and must be verified against geotechnical, liner, safety, and reviewing-authority criteria
  • Multi-cell configurations assume equal cell sizing and do not model actual series hydraulics, baffling, or short-circuiting
  • Earthwork volume is estimated from prismoidal formula using top and bottom dimensions with the selected side slope
  • Evaporation and seepage losses are not included in the hydraulic detention time calculation

Limitations

  • Does not model algae growth, DO profiles, ammonia, nutrients, TSS, pH, or seasonal treatment performance
  • Wind-induced mixing effects and thermal stratification in deep lagoons are not modeled
  • Does not evaluate liner requirements (clay, HDPE, GCL) based on site soil permeability and groundwater protection standards
  • Odor potential from overloaded primary cells or anaerobic conditions is not assessed
  • Does not account for sludge accumulation over time, which reduces effective volume and treatment capacity
  • Setback distances, floodplain, groundwater protection, liner approval, and permit conditions are jurisdiction-specific and not calculated here

References

  • EPA-WASTEWATER-POND-SYSTEMS-2011 - EPA pond-system design and operations source pointer
  • TEN-STATES-WASTEWATER-2014-SOURCE - Ten States wastewater standards source pointer; current state adoption must be verified
  • EPA-SECONDARY-TREATMENT-STANDARDS-2026 - EPA secondary-treatment regulatory context
  • WEF-MOP8-7TH-SOURCE - licensed wastewater design reference pointer only
  • NRCS-POND-LINING-COMPACTED-SOIL-520-SOURCE - liner and seepage warning context
  • State design standards and permit conditions vary; verify with the reviewing authority

Frequently Asked Questions

The local screen calculates BOD loading as flow (MGD) × BOD (mg/L) × 8.34, then divides by the midpoint of the selected local climate loading band. That is not a state-approved design criterion; verify current state standards, permit basis, measured wastewater data, and professional review.
The facultative path screens area from organic loading. The aerated paths screen volume from local detention-time bands and add a placeholder oxygen-transfer horsepower estimate. Actual process design and aerator selection require current references, equipment data, redundancy, electrical review, and permit requirements.
It gives a planning footprint from square cell approximations, freeboard, side slope, and a local berm allowance. It does not include roads, structures, setbacks, buffers, floodplain, liner areas, sludge handling, access, odor controls, or site-specific grading.
Disclaimer: This calculator provides preliminary sizing estimates. Actual lagoon design must comply with your state design standards, which vary significantly by jurisdiction. Factors including groundwater protection, soil permeability, setback distances, and wildlife impact must be evaluated by a licensed professional engineer.

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