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Municipal Solid Waste Incineration

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Municipal Solid Waste Incineration Combustion Types Incineration (energy recovery through complete oxidation) Mass Burn Refuse Derived Fuel Pyrolysis Gasification ... – PowerPoint PPT presentation

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Title: Municipal Solid Waste Incineration


1
Municipal Solid Waste Incineration
2
Combustion Types
  • Incineration (energy recovery through complete
    oxidation)
  • Mass Burn
  • Refuse Derived Fuel
  • Pyrolysis
  • Gasification
  • Plasma arc (advanced thermal conversion)

3
Gasification
  • Partial oxidation process using air, pure oxygen,
    oxygen enriched air, or steam
  • Carbon converted into syngas
  • More flexible than incineration
  • More public acceptance

4
Flexibility of Gasification
5
Pyrolysis
  • Thermal degradation of carbonaceous materials
  • Lower temperature than gasification
  • Absence or limited oxygen
  • Products are gas, liquid, solid char
  • Distribution of products depends on temperature

6
Waste Incineration - Advantages
  • Volume and weight reduced (approx. 90 vol. and
    75 wt reduction)
  • Waste reduction is immediate, no long term
    residency required
  • Destruction in seconds where LF requires 100s of
    years
  • Incineration can be done at generation site
  • Air discharges can be controlled
  • Ash residue is usually non-putrescible, sterile,
    inert
  • Small disposal area required
  • Cost can be offset by heat recovery/ sale of
    energy

7
Incineration
8
Environmental Considerations
  • Tonne of waste creates 3.5 MW of energy (eq. to
    300 kg of fuel oil) powers 70 homes
  • Biogenic portion of waste is considered CO2
    neutral (tree uses more CO2 during its lifecycle
    than released during combustion)
  • Should not displace recycling

9
Waste Incineration - Disadvantages
  • High capital cost
  • Skilled operators are required (particularly for
    boiler operations)
  • Some materials are noncombustible
  • Some material require supplemental fuel
  • Public disapproval
  • Risk imposed rather than voluntary
  • Incineration will decrease property value
    (perceived not necessarily true)
  • Distrust of government/industry ability to
    regulate

10
Three Ts
  • Time
  • Temperature
  • Turbulence

11
System Components
  • Refuse receipt/storage
  • Refuse feeding
  • Grate system
  • Air supply
  • Furnace
  • Boiler

12
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13
Energy/Mass Balance
Energy Loss (Radiation)
Flue Gas
Waste
Mass Loss (unburned C in Ash)
14
Flue Gas Pollutants
  • Particulates
  • Acid Gases
  • NOx
  • CO
  • Organic Hazardous Air Pollutants
  • Metal Hazardous Air Pollutants

15
Particulates
  • Solid
  • Condensable
  • Causes
  • Too low of a comb T (incomplete comb)
  • Insufficient oxygen or overabundant EA (too high
    T)
  • Insufficient mixing or residence time
  • Too much turbulence, entrainment of particulates
  • Control
  • Cyclones - not effective for removal of small
    particulates
  • Electrostatic precipitator 
  • Fabric Filters (baghouses) 

16
Metals
  • Removed with particulates
  • Mercury remains volatilized
  • Tough to remove from flue gas
  • Remove source or use activated carbon (along with
    dioxins)

17
Acid Gases
  • From Cl, S, N, Fl in refuse (in plastics,
    textiles, rubber, yd waste, paper)
  • Uncontrolled incineration - 18-20 HCl with pH 2
  • Acid gas scrubber (SO2, HCl, HFl) usually ahead
    of ESP or baghouse
  • Wet scrubber
  • Spray dryer
  • Dry scrubber injectors

18
Nitrogen removal
  • Source removal to avoid fuel NOx production
  • T lt 1500 F to avoid thermal NOx
  • Denox sytems - selective catalytic reaction via
    injection of ammonia

19
Air Pollution Control
  • Remove certain waste components
  • Good Combustion Practices
  • Emission Control Devices

20
Electrostatic Precipitator
21
Recovery of metals from Ash
  • (Fe, Al, Cu, Zn, Cr, and Pb) concentrated in
    bottom ash mostly,
  • while Cd existed primarily in fly ash.
  • Fe, 2.69  102,
  • Al, 1.46  104,
  • Cu, 4.91  104,
  • Zn, 6.92  101,
  • Cr, 5.10  104,
  • Pb 1.85  104

22
Ash
  • Bottom Ash recovered from combustion chamber
  • Heat Recovery Ash collected in the heat
    recovery system (boiler, economizer, superheater)
  • Fly Ash Particulate matter removed prior to
    sorbents
  • Air Pollution Control Residues usually combined
    with fly ash
  • Combined Ash most US facilities
  • combine all ashes

23
Schematic Presentation of Bottom Ash Treatment
24
Ash Reuse Options
  • Construction fill
  • Road construction
  • Landfill daily cover
  • Cement block production
  • Treatment of acid mine drainage

25
Refuse Boiler
Fabric Filter
Stack
Spray Dryer
Tipping Floor
Ash Conveyer
Metal Recovery
Mass Burn Facility Pinellas County
26
Overhead Crane
27
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28
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29
Turbine Generator
30
Fabric Filter
31
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