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Landfill Gas Case Study: Lessons Learned and Design Considerations

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Northwest corner has relatively low gas production ... Landfill gas in older portion of landfill is trapped beneath lined areas ... – PowerPoint PPT presentation

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Title: Landfill Gas Case Study: Lessons Learned and Design Considerations


1
Landfill Gas Case Study Lessons Learned and
Design Considerations
  • Lori A. Winters and Sean C. Paulsen
  • MWIA/ESD 2009 Solid Waste Conference

2
Discussion Outline
  • Chronology of Events
  • Response Activities
  • Future Plans and Steps
  • Lessons Learned

3
In the Beginning
  • Groundwater Monitoring Data and Results
  • Dissolved iron and manganese
  • Other inorganic constituents
  • Landfill Gas Monitoring Results
  • Methane levels increase along western boundary
  • Unable to tune field to control LFG

4
Redox Sensitive Parameters
  • Redox sensitive parameters generally unreliable
    for monitoring
  • Field sampling variability
  • Well construction materials
  • Landfill construction

Dissolved Iron
Dissolved Manganese
5
Inorganic Indicators
  • Conservative parameters more reliable for
    landfill impacts
  • Not influenced by oxidation processes
  • PROBLEM only indicate leachate impact

Chloride
Dissolved Potassium
Nitrogen-Ammonia
Dissolved Sodium
6
10,000 Foot View
  • Iron and manganese initially increased along
    north
  • Oldest portion of the landfill in northwest
    corner
  • Focus initial investigation on northwest

Zone of initial increases2004-2005
7
Landfill Gas Contours
Percent Methane in Landfill Gas Extraction Wells
8
Landfill Gas Contours
Percent Oxygen in Landfill Gas Extraction Wells
9
Results of Contouring
  • Northwest corner has relatively low gas
    production
  • Oxygen levels in northwest corner are relatively
    high
  • Pulling harder will create NSPS or plant problem
  • Lack of gas wells in central portion of landfill
  • Other potential sources for LFG?

10
10,000 Foot View (Part 2)
  • Iron and manganese begin to increase along south
    landfill boundary
  • No migration issues along south unable to
    control west
  • Change the focus of the investigation
  • Relationship between the two areas?

Zone of initial increases2004-2005
Zone of later increaseslate 2007
11
Redox Sensitive Parameters
  • Redox sensitive parameters generally unreliable
    for monitoring
  • No VOCs or gas parameters
  • Added dissolved methane analyses

Dissolved Iron
Dissolved Manganese
12
Groundwater Contour
  • Channel Fill Aquifer stretches between two zones
    where methane detected
  • Geology is an old stream channel
  • Need to determine potential as a migration pathway

13
Hydrogeologic Investigation
Cross-Section Location Map
14
Hydrogeologic Investigation
  • Two aquifer zones Channel Fill and Outwash
    Aquifer
  • Channel Fill Aquifer also extends between west
    and south boundaries
  • Clay lined cells in north and central portion of
    landfill

Unsaturated zone
East-West Cross-Section
15
Hydrogeologic Investigation
  • Cells 1 and P are double-composite lined cell
  • Cells N and O recompacted clay liner
  • Is the construction of composite cells over clay
    lined cells adding to the problem?

North-South Cross-section
16
Piggyback Liner
Area with CompactedClay Liner
Area of PiggybackOverliner
Gas Well Location Map with Piggyback Liner Areas
17
Problems
  • Older, clay lined areas are overlain by composite
    lined cells gas collection system essentially
    abandoned during construction
  • Landfill gas in older portion of landfill is
    trapped beneath lined areas
  • Rules dont allow penetration of piggyback liner
  • Due to pressure build-up, landfill gas in older
    cells moving through clay liner into subsurface

18
Response Actions
  • Source area appears to be central portion of
    landfill
  • Met with MDEQ to discuss options
  • Complete pilot boring using hollow stem auger and
    split spoon samples
  • Locate depth of piggyback liner
  • Monitor methane levels
  • Grab samples to determine moisture content of
    waste material

19
Response Actions (cont.)
  • Install first round of piggyback wells
  • Single well only bentonite seal at and above
    piggyback liner
  • Install dual extraction wells
  • One above and one below liner
  • Install out-of-waste collectors on west side

20
Completion of Pilot Borings
  • Piggyback liner settled an average of 10
  • Waste material located above piggyback liner very
    dry
  • Waste material below piggyback liner variable
    moisture
  • Incr. moisture content incr. gas production

21
Dual Gas Well Detail
  • Both wells constructed of Schedule 80 PVC
  • Ten foot thick bentonite seal placed at piggyback
    liner 5 above and below
  • 1 to 3 stone backfill placed around slotted
    portion
  • Minimum 2 between slots and seal

22
Installation of Dual Gas Wells
  • Six dual wells total of ten piggyback wells
  • Two wells installed in each 36 diameter boring
  • 6 well is shallow installed above liner
  • 8 well is deeper below liner

23
Install Out-of-Waste Collectors
  • Continued control issues with subsurface landfill
    gas levels along western boundary
  • Methane concentrations further indicate source is
    not northwest corner, but newer waste
  • Installed 3 out of waste collectors along western
    boundary to control methane
  • Collectors have been successfully controlling gas
    for approx. 2.5 months
  • Condensate sump critical and very active

24
Out-of-Waste Collectors
  • Three wells along west perimeter to intersect
    Channel Fill
  • 200 foot spacing
  • 3 PVC well with 2 well head
  • Condensate sump is the key to system operation

25
Next Steps
  • Continue Gas Extraction from New Gas Wells
  • Since new wells, gas production increased from
    1400 to 1900 scfm
  • Half of the difference from piggyback wells
  • May need additional piggyback wells?
  • Continue Out-of-Waste Collection
  • Maintain gas levels along landfill boundary
  • Continue Monitoring Sensitive Parameters
  • Dissolved iron and manganese
  • Dissolved methane

26
Landfill Gas Contours
Percent Methane in Landfill Gas Extraction Wells
27
Chemistry Changes
  • Since install of new wells, diss. iron levels
    have stabilized or decreased
  • Diss. methane has stabilized or decreased
  • Diss. methane typically responds first, and
    inorganics follow

Dissolved Iron
Dissolved Methane
28
Lessons Learned
  • Normal leachate indicators may not identify gas
    issues
  • Redox sensitive parameters function well as
    landfill gas indicators
  • Source isnt always obvious think big picture
  • If gas is potential source, include dissolved
    methane testing VOCs dont always show up
  • No quick fix issues take time to resolve

29
Lessons Learned (cont.)
  • Plan for gas extraction before installing
    piggyback liners
  • Passive vs. active
  • Tweak dual well design
  • Re-evaluate function of piggyback liners
  • Some states dont require piggyback liners
  • The gas is where the moisture is
  • Condensate sump critical to out-of- waste
    collectors

30
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