T7 Incineration

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    Thermal Treatment/Disposal:

    Incineration

    Chapter 12

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    Activity

    Why use incineration?

    What are the drawbacks?

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    Regulations

    Historical perspective

    HW incinerators vs. cement kilns and light

    aggregate kilns and industrial boilers andfurnaces

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    General Schematic

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    Other Thermal Processes

    Plasma arc pyrolysis

    Microwave discharge

    Advanced electrical reactor In situ vitrification

    Wet air oxidation

    Supercritical water oxidation Calcination

    Thermal desorption

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    Classifications of Incinerators

    Grate

    Open rack

    Stationary or moving

    Air circulation

    Large and irregular

    wastes

    Hearth Solid plate

    Variety of waste

    Suspension

    Sand or alumina bed

    fluidized with air

    Relatively uniformfeed size

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    Typical Process Flow Diagram

    Waste

    Storage

    Pre-processing/blending

    Incineration Flue Gas

    Pollution

    Control

    Ash Stabilization

    Landfill

    Effluent

    POTW

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    3 Ts

    +Excess O2

    Combustion Requirements

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    Typical Excess Air Reactions

    CHCl+ O2

    + N2

    CO2

    + H2

    O+ HCl+

    O2+ N2+ heat

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    Flue Gas Quench

    Cool to:

    500 - 700oF for spray dryer

    180oF for low-temperature equipment

    Air or water

    Concurrent or counter-current flow

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    Air Pollution Control

    Pollution:

    Particulates (including 10 priority metals)

    Acid gases

    Systems

    Wet

    Dry

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    Trial Burn

    Test incinerator

    Principal organic hazardous constituents

    (POHCs) destruction and removal

    efficiencies (DREs)

    HCl

    Particulates

    CO

    Metals

    Dioxin and furans

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    POHC DRE

    At least 99.99% on all selected POHCs

    during trial burn

    100in

    outinW

    WWDRE

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    HCl Emissions

    Emission no greater than larger of

    4 lb/h or 1% of HCl in stack gas

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    Emissions Example

    Example 12-2 (p. 746)

    Does incinerator performance meet

    requirements?

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    CO Emissions

    100 ppm by volume as a 60-minute rolling

    average corrected to 7% O2

    on a dry basis

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    CO and Particulate Example

    Example 12-11 (p. 804)

    w

    YY wetdry

    1

    dry

    mcY

    PP

    21

    14

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    Combustion Efficiency

    At least 99.99%

    1002

    2

    COCO

    CO

    CC

    C

    CE

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    Dioxin and Furan Emissions

    0.4 ng/dscm

    or0.0001%

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    PCBs

    At least 99.9999% DRE for liquid

    Dwell time of 2 s at 1200 100 oC and 3% EA in stack

    gas

    OR

    Dwell time of 1.5 s at 1600 100 oC and 2% EA in stack

    gas

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    Design

    Example 12-7 (p. 765)