225
    .APPENDTX
    B
    Continuous
    Emission
    Monitoring
    Systems
    for
    Mercury
    Section
    1.1
    Applicability
    The
    provisions
    of
    this
    Appendix
    apply
    to
    sources
    subject
    to 35
    III
    Admin.
    Code
    Part
    225
    mercury
    (Hg)
    mass
    emission
    reduction
    program.
    Section
    1.2
    General
    operating
    requirements
    a)
    Primary
    Equipment
    Performance
    Requirements.
    The
    owner
    or
    operator
    must
    ensure
    that
    each
    continuous
    mercury
    emission
    monitoring
    system
    required
    by
    this
    Appendix
    meets
    the
    equipment,
    installation,
    and
    performance
    specifications
    in Exhibit
    A to
    this
    Appendix
    and
    is maintained
    according
    to the
    quality
    assurance
    and
    quality
    control
    procedures
    in
    Exhibit
    B
    to this
    Appendix.
    b)
    Heat
    Input
    Rate
    Measurement
    Requirement.
    The
    owner
    or operator
    must
    determine
    and
    record
    the heat
    input
    rate,
    in
    units
    of
    mmBtu!hr,
    to
    each
    affected
    unit
    for
    every
    hour
    or
    part
    of
    an
    hour
    any
    fuel
    is combusted
    following
    the procedures
    in
    Exhibit
    C
    to
    this
    Appendix.
    c)
    Primary
    equipment
    hourly
    operating
    requirements.
    The
    owner
    or
    operator
    must
    ensure
    that
    all
    continuous
    mercury
    emission
    monitoring
    systems
    required
    by
    this
    Appendix
    are
    in
    operation
    and
    monitoring
    unit
    emissions.
    at
    all
    times
    that
    the
    affected
    unit
    combusts
    any
    fuel
    except
    during
    periods
    of calibration,
    quality
    assurance,
    or preventive
    maintenance,
    performed
    pursuant
    to
    Section
    1.5
    of
    this
    Appendix
    and
    Exhibit
    B
    to this
    Appendix,
    periods
    of
    repair,
    periods ofbackups
    of
    data
    from
    the data
    acquisition
    and
    handling
    system,
    or
    recertification
    performed
    pursuant
    to
    Section
    l.4.of
    this
    Appendix.
    1)
    The
    owner
    or
    operator
    must
    ensure
    that
    each
    continuous
    emission
    monitoring
    system
    is
    capable
    of
    completing
    a minimum
    of
    one
    cycle
    of operation
    (sampling,
    analyzing,
    and
    data
    recording)
    for
    each
    successive
    15-minute
    interval.
    The
    owner
    or
    operator
    must
    reduce
    all
    volumetric
    flow,
    CO
    2
    concentration,
    02
    concentration,
    and
    mercury
    concentration
    data
    collected
    by
    the
    monitors
    to
    hourly
    averages.
    Hourly averages
    must
    be
    computed
    using
    at
    least
    one
    data
    point
    in
    each
    fifteen
    minute
    quadrant
    of an
    hour,
    where
    the
    unit
    combusted
    fuel
    during
    that
    quadrant
    of
    an
    hour.
    Notwithstanding
    this
    requirement,
    an
    hourly
    average
    may
    be
    computed
    from
    at
    least
    two
    data
    points
    separated
    by
    a minimum
    of
    15
    minutes
    (where
    the
    unit
    operates
    for
    more
    than
    one
    quadrant
    of
    an
    hour)
    if
    data
    are
    unavailable
    as
    a
    result
    of
    the
    performance
    of
    calibration,
    quality
    assurance,
    or
    preventive
    1

    maintenance;activities’pursuantto
    Sectiôn’L5of
    this
    Appendix
    and
    Exhibit
    B
    to
    this
    Appendix,
    or
    backups
    of
    data
    from the
    data
    acquisition
    and
    handling
    system,
    or
    recertification,
    pursuantto
    Section 1.4
    to
    thisAppendix
    The
    owner
    or
    operator
    must
    use
    all
    valid
    measurements
    or
    data
    points
    collected
    during an
    hour
    to
    calculate
    the
    hourly
    averages.
    All
    data
    points
    collected
    during an
    hour
    must
    be,
    to
    the
    extent
    practicable,
    evenly
    spaced
    over the
    hour.
    2)
    Failure
    of a
    CO
    2
    oLQ2
    emissions
    concentration
    monitor,
    mercury
    concentration
    monitor,
    flow
    monitor,
    or
    a
    moisture
    monitor
    to
    acquire
    the
    minimum
    number
    of
    data
    points
    for
    calculation
    of
    an
    hourly
    average
    in paragraph
    (c)(
    1)
    of
    this
    Section
    must
    result
    in the
    failure
    to
    obtain
    a
    valid
    hour
    of
    data
    and
    the
    loss
    of
    such
    component
    data for
    the
    entire
    hour.
    For
    a
    moisture
    monitoring
    system
    consisting
    of
    one
    or
    more
    oxygen
    analyzers
    capable
    of
    measuringQ
    2
    on
    a
    wet-basis
    and
    a
    dry-basis,
    an
    hourly
    average
    percent
    moisture
    value
    is
    valid
    only
    if
    the
    minimum
    number
    of
    data
    points
    is acquired
    for
    both
    the
    wet-and
    dry-basis
    measurements.
    d)
    Optional
    backup
    monitor
    requirements.
    If
    the
    owner
    or
    orator
    chooses
    to
    use
    two
    or
    more
    continuous
    mercury
    emission
    monitoring
    systems,
    each
    of
    which
    is
    capable
    of
    monitoring
    the
    same
    stack or
    duct
    at
    a
    specific
    affected
    unit,
    or
    group
    of
    units
    using
    a
    common
    stack,
    then
    the
    owner
    or
    operator
    must
    designate
    one
    monitoring
    system
    as
    the
    primary
    monitoring
    system,
    and
    must
    record
    this
    information
    in
    the
    monitoring
    plan, as
    provided
    for
    in
    Section
    1.10
    of
    this
    Appendix.
    The
    owner
    or
    operator must
    designate
    the
    other
    monitoring
    system(s)
    as
    backup
    monitoring
    system(s)
    in
    the
    monitoring
    plan.
    The
    bàcku
    monitoring
    system(s)
    must
    be
    designated
    as
    redundant
    backup monitoring
    system(s),
    non-redundant
    backup
    monitoring
    system(s),
    or
    reference method
    backup
    system(s),
    as
    described
    in
    Section
    1.4(d)
    of
    this
    Appendix.
    When
    the
    certified
    primary
    monitoring
    system
    is
    operating
    and
    not
    out-of-control
    as
    defined
    in
    Section
    1.7
    of
    this
    Appendix,
    only
    data
    from
    the
    certified primary
    monitoring
    system
    must
    be
    reported
    as
    valid,
    quality-assured
    data.
    Thus,
    data
    from
    the
    backup
    monitoring
    system
    may
    be
    reported
    as
    valid,
    quality-assured
    data
    only
    when
    the
    backup
    is
    operating
    and
    not
    out-of-
    control
    as
    defined in
    Section
    1.7
    of
    this
    Appendix
    (or
    in the
    applicable
    reference
    method
    in
    appendix
    A
    of 40
    CFR60,
    incorporated
    by
    reference
    in
    Section
    225.140)
    and
    when
    the
    certified
    primary
    monitoring
    system is
    not
    operating
    (or
    is
    operating
    but
    out-of-control).
    A
    particular
    monitor
    may
    be
    designated
    both
    as
    a certified
    primary
    monitor
    for
    one
    unit
    and
    as
    a
    certified
    redundant
    backup
    monitor
    for
    another
    unit.
    e)
    Minimum
    measurement
    capability
    requirement.
    The
    owner
    or
    operator
    must
    ensure
    that
    each
    continuous
    emission
    monitoring
    system
    is
    capable
    of
    accurately
    measuring,
    recording,
    and
    reporting
    data,
    and
    must
    not
    incur
    an exceedance
    of
    the
    full
    scale
    range,
    except
    as
    provided
    in
    Section
    2.1.2.3
    of
    Exhibit
    A to
    this
    Appendix.
    2

    f).
    Operator must
    record
    and
    the
    designated
    representative
    must
    report
    the.
    hourly,
    daily,
    quarterly,
    and
    annual
    information
    collected
    under
    the
    requirements
    as
    specified
    in
    subpart
    G
    of 40
    CFR
    75,
    incorporated
    byreference,in
    Section
    225.140,
    and
    Section
    1
    .1 F
    through 1.13
    of
    this
    Appendix.
    Section
    1.3
    Special
    provisions
    for
    measuring
    mercury
    mass
    emissions
    using
    the
    excepted
    sorbent
    trap
    monitoring
    methodology
    For
    an
    affected
    coal-fired
    unit
    under
    .35.111
    Admin.
    Code.
    Part
    225
    if
    the.
    owner
    or
    operator elects
    to
    use
    sorbent
    trap
    monitoring
    systems
    (as
    defined
    in
    Section
    225.130) to
    quantify
    mass
    emissions,
    the
    guidelines
    in
    paragraphs
    (a)
    through
    (1)
    of this
    Section
    must
    be
    followed
    for
    this
    excepted
    monitoring
    methodology:
    a)
    For
    each
    sorbent
    trap
    monitoring
    system
    (whether
    primary
    or
    redundant
    backup),
    the
    use
    of
    paired
    sorbent
    traps,
    as
    described
    in Exhibit
    D
    to this
    Appendix,
    is
    required:
    b’)
    Each
    sorbent
    trap
    must
    have
    a
    main
    section,
    a backup
    section,
    and
    a
    third
    section
    to
    allow
    spiking
    with
    a calibration
    gas of
    known mercury
    concentration,
    as
    described
    in
    Exhibit
    D to
    this
    Appendix:
    c)
    A
    certified
    flow
    monitoring
    system
    is
    required;
    d)
    Correction
    for
    stack
    gas
    moisture
    content
    is
    required,
    and
    in some
    cases,
    a
    certified
    O2or
    Q2
    monitoring
    system
    is
    required
    (see
    Section
    1.1
    5(a)(4));
    e)
    Each
    sorbent trap
    monitoring
    system
    must
    be
    installed
    and
    operated
    in
    accordance
    with
    Exhibit
    D
    to
    this
    Appendix.
    The
    automated
    data.acguisition
    and
    handling
    system
    must
    ensure
    that
    the
    sampling
    rate
    is
    proportional
    to
    the
    stack
    gas
    volumetric
    flow
    rate.
    f)
    At
    the
    beginning
    and
    end
    of
    each
    sample
    collection
    period,
    and
    at
    least
    once
    in
    each
    unit
    operating
    hour
    during
    the
    collection
    period,
    the
    gas
    flow
    meter
    reading
    must
    be
    recorded.
    g)
    After
    each
    sample
    collection
    period,
    the
    mass
    of
    mercury
    adsorbed
    in
    each
    sorbent
    trap
    (jn
    all
    three
    sections)
    must
    be
    determined
    according
    to the
    applicable
    procedures
    in
    Exhibit
    D
    to
    this
    Appendix.
    h)
    The
    hourly
    mercury
    mass
    emissions
    for
    each
    collection
    period
    are
    determined
    using
    the
    results
    of
    the
    analyses
    in
    conjunction with
    contemporaneous
    hourly
    data
    recorded
    by
    a
    certified
    stack
    flow
    monitor,
    corrected
    for
    the
    stack
    gas
    moisture
    content.
    For
    each
    pair
    of
    sorbent
    traps
    analyzed,
    the
    average
    of
    the
    two
    mercury
    concentrations
    must
    be
    used
    for
    reporting
    purposes
    under
    Section
    1.18(f)
    to
    this
    Appendix.
    Notwithstanding
    tlils
    3

    requirement,
    if,
    due
    to
    circumstances
    beyond
    the
    control
    of the
    owner
    or
    operator,
    one
    of.
    the
    paired
    traps.is
    accidentally
    lost,
    damaged,
    or
    broken
    and
    cannot.
    be
    analyzed, the..
    results
    of
    the analysis
    of
    the
    other
    trap
    may
    be
    used
    fr
    reporting
    purposes,
    provided
    that
    the
    other
    trap
    has
    met
    all
    of the
    applicable
    quality-assurance
    requirements
    of
    this
    part.
    i)
    All
    unit
    operating
    hours
    for
    which valid
    mercury
    concentration
    data
    are
    obtained
    with
    the
    primary
    sorbent
    trap
    monitoring
    system
    (as
    verified
    using
    the
    quality
    assurance
    procedures
    in
    Exhibit
    D
    to this
    Appendix)
    must
    be
    reported
    in
    the electronic
    quarterly
    report
    under
    Section
    1.18(f) .to this
    Appendix.
    For.hours
    in
    which
    data
    from
    the
    primary
    monitoring
    system
    are
    invalid,
    the
    owner
    or
    operator
    may,
    in
    accordance
    with
    Section
    1.4(d)
    to this
    Appendix,
    report
    valid
    mercury
    concentration
    data
    from:
    A
    certified
    redundant
    backup
    CEMS
    or sorbent
    trap
    monitoring
    system;
    a certified
    non-redundant
    backup
    CEMS
    or
    sorbent
    trap
    monitoring
    system;
    or
    an applicable
    reference
    method
    under
    Section
    1.6
    to
    this
    Appendix.
    j)
    Initial
    certification
    requirements
    and
    additional
    quality-assurance
    requirements
    for
    the
    sorbent.trap.monitoring
    systems
    are
    found
    in
    Section
    L4(c)(7),
    in
    Section
    6.5.6
    of
    Exhibit
    A
    to
    this
    Appendix,
    in
    Sections
    1.3
    and
    2.3
    of Exhibit
    B
    to this
    Appendix,
    and
    in
    Exhibit
    D
    to
    this
    Appendix.
    k)
    During
    each
    RATA
    of a
    sorbent
    trap
    monitoring
    system,
    the
    type
    of sorb
    ent
    material
    used
    by
    the
    traps
    must
    be
    the
    same
    as
    for
    daily
    operation
    of
    the
    monitoring
    system.
    A
    new
    pair
    of
    traps
    must
    be
    used
    for
    each
    RATA
    run.
    However,
    the
    size
    of
    the
    traps
    used
    for
    the
    RATA
    may
    be
    smaller
    than
    the
    traps
    used
    for
    daily
    operation
    of
    the
    system.
    1)
    . Whenever
    the
    type
    of
    sorbent
    material
    used
    bythetraps
    is changed,.
    the
    owner
    orroperator
    must
    conduct
    a
    diagnostic
    RATA
    of the
    modified
    sorbent
    trap
    monitoring
    system
    within
    720
    unit
    or
    stack
    operating
    hours
    after
    the.
    date
    and
    hour
    when
    the
    new
    sorbent
    material
    is
    first
    used.
    If
    the
    diagnostic
    RATA
    is
    passed,
    data
    from
    the
    modified
    system
    maybe
    reported
    asquality-assured.
    back
    to the
    date
    andhour
    when.
    the
    new
    sorbent
    material
    was
    first
    used.
    If
    the
    RATA
    is
    failed,
    all
    data
    from
    the
    modified
    system
    must
    be
    invalidated,
    back
    to
    the
    date
    and
    hour
    when
    the
    new
    sorbent
    material
    was
    first
    used,
    and
    data
    from
    the
    system
    must
    remain invalid
    until
    a
    subsequent
    RATA
    is
    passed.
    If
    the
    required
    RATA
    is
    not
    completed
    within
    720
    unit
    or
    stack
    operating
    hours,
    but
    is passed
    on
    the
    first
    attempt,
    data
    from
    the
    modified
    system
    must
    be
    invalidated
    beginning
    with
    the
    first
    operating
    hour
    after
    the
    720
    unit
    or stack
    operating
    hour
    window
    expires
    and
    data
    from
    the
    system
    must
    remain
    invalid
    until
    the
    date
    and
    hour
    of
    completion
    of
    the
    successful
    RATA.
    Section
    1.4
    Initial
    certification
    and
    recertification
    procedures
    a)
    Initial
    certification
    approval
    process.
    The
    owner
    or
    operator
    must
    ensure
    that
    each
    continuous
    mercury
    emission
    monitoring
    system
    required
    by
    this
    Appendix
    meets
    4

    the
    iitiaI c&ifiation•requirementsof
    this
    SeôtiOn;
    In
    addition,
    whenever’the
    owner
    or
    operator
    installs
    a
    continuous
    mercury
    emission
    monitoring
    system
    in
    order
    to
    meet
    the
    reqriirmentsof
    Sections
    1.3
    of
    this
    Appendix
    and
    40
    CFR
    Sections
    75.11
    through
    75.14
    and
    75
    .16
    through
    75.18,
    incorporatedby
    reference
    in
    Section
    225.140,
    where
    no
    continuous
    emission
    monitoring
    system
    was.
    previously
    installed,
    initial
    certification
    is
    required.
    1)
    Notification
    of
    initial
    certification
    test
    dates.
    The
    owner
    or
    operator
    or
    designated
    representative
    must
    submit
    a
    written
    notice
    of
    the
    dates
    of
    initial
    certification
    testing at
    the
    unit
    as
    specified.
    in
    40
    CFR
    75.61
    (a)(
    1),
    incorporated
    by
    reference
    in
    Section
    225.140..
    2)
    Certification
    application.
    The
    owner
    or
    operator
    must
    apply
    for
    certification
    of
    each continuous
    mercury
    emission
    monitoring
    system.
    The
    owner
    or
    operator
    must
    submit
    the
    certification
    application
    in
    accordance
    with
    40
    CFR
    75.60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    and
    each
    complete
    certification
    application
    must
    inolude
    the
    information
    specified
    in
    40
    CFR
    75.63,
    inCorporated
    by
    reference
    in
    Section
    225.140.
    3)
    Provisional
    approval
    of
    certification
    (or
    recertification)
    applications.
    Upon
    the
    successful
    completion
    of
    the
    required
    certification
    (or
    recertification)
    procedures
    of
    this
    Section,
    each
    continuous
    mercury
    emission
    monitoring
    system
    must
    be
    deemed
    provisiànally
    certified
    (or
    recertified)
    for
    use
    for
    a period
    not
    to
    exceed
    120
    days following
    receipt
    by
    the
    Agency
    of
    the
    complete
    certification
    (or
    recertification)
    application
    under paragraph
    (a)(4) of
    this
    Section.
    Data
    measured
    and
    recorded
    by
    aprovisionally
    certified
    (or
    recertified)
    continuous
    emission
    monitoring
    system,
    operated
    in
    accordance
    with
    the
    requirements
    of
    Exhibit
    B
    to
    this
    Appendix,
    will
    be
    considered
    valid
    quality-assured
    data
    (retroactive
    to
    the
    date
    and
    time
    of
    provisional
    certification
    or
    recertification),
    provided
    that
    the
    Agency
    does
    not
    invalidate
    the
    provisional
    certification
    (or
    recertification)
    by
    issuing
    a
    notice
    of
    disapproval
    within
    120
    days
    of
    receipt
    by
    the
    Agency
    of
    the
    complete
    certification
    (or
    recertification)
    application.
    Note
    that
    when
    the
    conditional
    data
    validation
    procedures
    of
    paragraph
    (b)(3)
    of
    this
    Section
    are
    used
    for
    the
    initial certification
    (or
    recertification)
    of
    a
    continuous
    emissions
    monitoring
    system,
    the
    date
    and
    time
    of
    provisional
    certification
    (or
    recertification)
    of
    the
    CEMS
    may
    be
    earlier
    than
    the
    date and
    time
    of
    completion
    of
    the
    required
    certification
    (or
    recertification)
    tests.
    4)
    Certification
    (or
    recertification)
    application
    formal
    approval
    process.
    The
    Agency
    will
    issue
    a
    notice
    of
    approval
    or
    disapproval
    of
    the
    certification
    (or
    recertification)
    application to
    the
    owner or
    operator
    within
    120
    days
    of
    receipt
    of
    the
    complete
    certification
    (or
    recertification)
    application. In
    the
    event
    the
    Agency
    5

    does
    not
    issue
    such
    a
    notice
    within
    120
    days
    of
    receipt,
    each
    continuous
    emission
    monitoring
    system
    which
    meets the
    performance
    requirements
    of
    this
    part
    and
    is
    included
    in
    the
    certification
    (or
    recertification)
    applicationwill
    be
    deemed
    certified
    (or
    recertified) for
    use
    under
    35
    IliAdmin.
    Code
    Part
    225.
    A)
    Approval
    notice.
    If
    the
    certification
    (or
    recertification)
    application
    is
    complete
    and
    shows
    that
    each
    continuous
    emission
    monitoring
    system
    meets
    the performance
    requirements
    of
    this
    part,
    then
    the
    Agency
    will
    issue
    a
    notice
    of
    approval
    of
    the
    certification
    (or
    recertification)
    application
    within
    120
    days
    of
    receipt.
    B)
    Incomplete
    application
    notice.
    A
    certification
    (or
    recertification)
    application
    will
    be
    considered
    complete
    when
    all
    of
    the
    applicable
    information
    required
    to
    be
    submitted
    in
    40
    CFR
    75.63,
    incorporated
    by
    reference
    in
    Section
    225.140,
    has
    been received
    by
    the
    Agency.
    If
    the
    certification
    (or
    recertification)
    application
    is
    not
    complete,
    then
    the
    Agency
    will
    issue
    a notice
    of
    incompleteness
    that
    provides
    a
    reasonable•
    timeframe
    for
    the
    designated
    representative
    to
    submit
    the
    additional
    information
    required
    to
    complete
    the
    certification
    (or
    recertification)
    application.
    If
    the
    designated
    representative
    has
    not
    complied
    with
    the
    notice
    of
    incompleteness
    by
    a
    specified
    due
    date,
    then
    the
    Agency
    may
    issue
    a
    notice
    of
    disapproval
    specified
    üñder
    paragraph
    (a)(4)(C)
    of
    this
    Section.
    The
    120-day
    review
    period
    will
    not
    begin
    prior
    to
    receipt
    of
    a
    complete
    application.
    C)
    Disapproval
    notice.
    If
    the
    certification
    (or
    recertification)
    application
    shows
    that
    any
    continuous
    emission
    monitoring
    system
    does
    not
    meet
    the
    performance
    requirements
    of
    this
    part, or
    if
    the
    certification
    (or
    recertification)
    application
    is
    incomplete
    and
    the
    requirement
    for
    disapproval
    under
    paragraph
    (a)(4)(B)
    of
    this
    Section
    has
    been
    met,
    the
    Agency
    must issue
    a
    written
    notice
    of
    disapproval
    of
    the
    certification
    (or
    recertification)
    application
    within
    120
    days
    of
    receipt.
    By issuing
    the
    notice
    of
    disapproval,
    the
    provisional
    certification
    (or
    recertification)
    is
    invalidated
    by
    the
    Agency,
    and
    the
    data
    measured
    and
    recorded
    by
    each
    uncertified
    continuous
    emission
    or
    opacity
    monitoring
    system
    must
    not
    be
    considered
    valid
    quality-assured
    data
    as
    follows:
    from the
    hour
    of
    the
    probationary
    calibration
    error
    test
    that
    began
    the
    initial
    certification
    (or
    recertification)
    test
    period
    (if
    the
    conditional
    data validation
    procedures
    of
    paragraph
    (b)(3)
    of
    this
    Section
    were
    used
    to
    retrospectively
    validate
    data)
    or
    from
    the
    date
    and
    time
    of
    completion
    of
    the
    invalid
    certification
    or
    recertification
    tests
    (if
    the
    conditional
    data
    validation
    procedures
    of
    paragraph
    (b)(3)
    of
    this
    Section
    were
    not
    used).
    The
    owner
    or
    operator
    6

    must
    follow
    the
    procedures
    forioss
    of
    initial
    certification
    in
    paragraph
    (a)(5)
    of
    this
    Section
    for
    each
    continuous
    emission
    or
    opacity
    monitoring
    sytetii
    which
    is
    disapproved
    for
    initial
    certification.
    For
    each
    disapproved
    recertification,
    the
    owner
    or
    operator
    must
    follow
    the
    procedures
    of
    paragraph
    (b)(5)
    of
    this
    Section.
    5)
    Procedures
    for
    loss
    of
    certification.
    When
    the
    Agency
    issues
    a notice
    of
    disapproval
    of a
    certification
    application
    or
    a notice
    of
    disapproval
    of
    certification
    status
    (as
    specified
    in
    paragraph
    (a)(4)
    of
    this
    Section),
    then:
    A)
    Until
    such
    time,
    date,
    and
    hour
    as
    the
    continuous
    mercury emission
    monitoring
    system
    can
    be
    adjusted,
    repaired,
    or replaced
    and
    certification
    tests
    successfully
    completed
    (or,
    if the
    conditional
    data
    validation
    procedures
    in
    paragraphs
    (b)(3)(B)
    through
    (b)(3)(I)
    of
    this
    Section
    are
    used,
    until
    a
    probationary
    calibration
    error
    test
    is passed following
    corrective
    actions
    in
    accordance
    with
    paragraph
    (b)(3)(B)
    of
    this
    Section),
    the
    owner
    oroperator
    must
    perform
    emissions
    testing
    pursuant to
    Section
    225.239.
    B)
    The
    designated
    representative
    must
    submit
    a
    notification
    of
    certification
    retest
    dates as
    specified
    in
    Section
    225.250(a)(3)(A) and
    a
    new
    certification
    application
    according
    to
    theprocedures
    in
    Section
    225.250(a)(3)(B);
    and
    C)
    The
    owner
    or
    operator
    must
    repeat
    all
    certification
    tests
    or other
    requirements
    that
    were
    failed
    by
    the
    continuous
    mercury
    emission
    monitoring
    system,
    as
    indicated
    in
    the
    Agency’s
    notice
    of
    disapproval,
    no
    later
    than
    30
    unit
    operating
    days
    after
    the
    date
    of
    issuance
    of
    the
    notice
    of
    disapproval.
    b)
    Recertification
    approval
    process.
    Whenever
    the
    owner
    or
    operator
    makes
    a
    replacement,
    modification,
    or
    change
    in
    a
    certified
    continuous
    mercury
    emission
    monitoring
    system
    that
    may
    significantly
    affect
    the
    ability
    of
    the
    system
    to
    accurately
    measure
    or
    record
    the
    gas
    volumetric
    flow
    rate,.mercury
    concentration,
    percent
    moisture,
    or
    to
    meet
    the
    requirements
    of
    Section
    1.5
    of this
    Appendix
    or Exhibit
    B
    to
    this
    Appendix,
    the
    owner
    or
    operator
    must
    recertify
    the
    continuous
    mercury
    emission
    monitoring
    system,
    according
    to
    the
    procedures
    in
    this
    paragraph.
    Examples
    of changes
    which
    require
    recertification
    include: replacement
    of
    the
    analyzer;
    change
    in location
    or
    orientation
    of
    the
    sampling
    probe
    or site;
    and
    complete
    replacement
    of
    an
    existing
    continuous
    mercury
    emission
    monitoring
    system.
    The
    owner
    or
    operator
    must
    also
    recertify
    the
    continuous
    emission
    monitoring
    systems for
    a unit
    that
    has
    recommenced
    commercial
    operation
    fo1lowing
    period
    of
    long-term
    cold storage
    as
    defined
    in
    Section
    225.130.
    Any
    change
    to
    a
    flow
    7

    monitor
    or
    gas
    monitoring
    system
    for
    which
    a
    RATA
    is
    not
    necessary
    will
    not
    be
    considered
    a
    recertification
    event.
    In addition,
    changipg
    the
    polynomial
    coefficients
    or
    K
    factor(s)
    of a
    flow
    monitor
    will
    require
    a
    3-1badRATA,
    but
    is
    not
    considered
    to
    be a
    recertification
    event;
    however,
    records
    of
    the
    polynomial
    coefficients
    or
    K
    factor(s)
    currently
    in
    use
    must
    be
    maintained
    on-site
    in
    a
    format
    suitable
    for
    inspection.
    Changing
    the
    coefficient
    or
    K
    factor(s)
    of amoisture
    monitoring
    system
    will
    require
    a RATA,
    but
    is
    not
    considered
    to
    be
    a
    recertification
    event;
    however, records
    of
    the
    coefficient
    or
    K
    factor(s)
    currently
    in use
    by
    the
    moisture
    monitoring
    system
    must
    be maintained
    on-site
    in
    a format
    suitable
    for
    inspection.
    In
    such
    cases,
    any
    other
    tests
    that
    are
    necessary
    to
    ensure
    continued
    proper operation
    of
    the
    monitoring
    system
    (e.g.,
    3-load
    flow
    RATAs
    following
    changes
    to flow
    monitor polynomial
    coefficients,
    linearity
    checks,
    calibration
    error
    tests,
    DAHS
    verifications,
    etc.)
    must
    be
    performed
    as
    diagnostic
    tests,
    rather
    than
    as
    recertification
    tests.
    The
    data
    validation
    procedures
    in paragraph
    (b)(3)
    of
    this
    Section
    must
    be
    applied
    to
    RATAs
    associated
    with
    changes
    to
    flow
    or
    moisture
    monitor
    coefficients,
    and
    to
    linearity
    checks,
    7-day
    calibration
    error
    tests,
    and
    cycle
    time
    tests,
    when
    these
    are
    required
    as
    diagnostic
    tests.
    When
    the
    data
    validation
    procedures
    of
    paragraph
    (b)(3)
    ofthis
    Section
    are
    applied
    in
    this
    manner,
    replace
    the.word
    “recertification”
    with
    the word
    “diagnostic.”
    1)
    Tests
    required.
    For
    all
    recertification
    testing,
    the
    owner
    or
    operator
    must
    complete
    all
    initial
    certification
    tests
    in paragraph
    (c)
    of
    this
    Section
    that
    are
    applicable
    to
    the
    monitoring
    system,
    except
    as Otherwise
    approved
    by
    the
    Agency.
    For
    diagnostic
    testing
    after
    changing
    the
    flow
    rate
    monitor
    polynomial
    coefficients,
    the
    owner
    or
    operator
    must
    complete
    a 3-level
    RATA.
    For
    diagnostic
    testing
    after
    changing
    the
    K factor
    or mathematical
    algorithm
    of
    a moisture
    monitoring
    system,
    the
    owner
    or operator
    must
    complete
    a RATA.
    2)
    Notification
    of recertification
    test
    dates.
    The
    owner,
    operator,
    or
    designated.
    representative
    must
    submit
    notice
    of
    testing
    dates
    for
    recertification
    under
    this
    paragraph
    as
    specified
    in
    40
    CFR
    75.61
    (a)(
    1
    )(ii),
    incorporated
    by
    reference
    in
    Section
    225.140,
    unless
    all
    of
    the tests
    in paragraph
    (c)
    of
    this
    Section
    are
    required
    for
    recertification,
    in
    which
    case
    the
    owner
    or
    operator
    must
    provide notice
    in
    accordance
    with
    the
    notice
    provisions
    for
    initial
    certification
    testing
    in
    40
    CFR
    75.61(a)(1)(i),
    incorporated
    by
    reference
    in
    Section
    225.140.
    3)
    Recertification
    test
    period
    requirements
    and
    data
    validation.
    The
    data
    validation
    provisions
    in
    paragraphs
    (b)(3)(A) through
    (b)(3)(I)
    of
    this
    Section
    will
    apply
    to
    all
    mercury
    CEMS
    recertifications
    and
    diagnostic
    testing.
    The
    provisions
    in
    paragraphs
    (b)(3)(B)
    through
    (b)(3)(I)
    of
    this
    Section
    may
    also
    be applied
    to
    initial
    certifications
    (see
    Sections
    6.2(a).
    6.3.1(a),
    6.3.2(a),
    6.4(a)
    and
    6.5(f)
    of
    Exhibit
    A
    to
    this
    Appendix)
    and
    may
    be
    used
    to
    supplement
    the
    linearity
    check
    and
    RATA
    8

    data
    validatiónprocedures
    in
    Sèctions2.2.3(b)
    and
    2.3.2(b)
    of
    Exhibit
    B
    to
    this
    Appendix.
    A)
    The
    owner
    or
    operator
    must
    report
    emission
    data
    using
    a reference
    method
    or
    another
    monitoring
    system
    that
    has
    been
    certified
    or
    approved
    for
    use
    under
    this
    part,
    in the
    period
    extending
    from
    the hour
    of
    the
    replacement,
    modification,
    or
    change
    made
    to
    a
    monitoring
    system
    that
    triggers
    the
    need
    to
    perform
    recertification
    testing,
    until
    either:
    the
    hour
    of
    successful
    completion
    of
    all
    of the
    required
    recertification
    tests;
    or
    the
    hour
    in
    which
    a probationary
    calibration
    error
    test
    (according
    to
    paragraph
    (b)(3)(B)
    of
    this
    Section)
    is performed
    and
    passed,
    following
    all
    necessary
    repairs,
    adjustments,
    or
    reprogramming
    of the
    monitoring
    system.
    The
    first
    hour
    of
    quality-assured
    data
    for the
    recertified
    monitoring
    system
    must
    either
    be
    the
    hour
    after
    all
    recertification
    tests
    have
    been
    completed
    or,
    if
    conditional
    data
    validation
    is
    used,
    the
    first
    quality-assured
    hour
    must
    be
    determined
    in
    accordance
    with
    paragraphs
    (b)(3)(B)
    through
    (b)(3)(I)
    of
    thisSection.
    Notwithstanding
    theserequirements,
    if the
    replacement,
    modification,
    or
    change
    requiring
    recertification
    of
    the
    CEMS
    is
    such
    that
    the
    historical
    data
    stream
    is
    no
    longer
    representative
    (e.g.,
    where
    the
    mercury
    concentration
    and
    stack
    flow
    rate
    change
    significantly
    after
    installation
    of a
    wet
    scrubber),
    the
    owner
    or operator
    must
    estimate
    the
    mercury
    emissions
    over
    that
    timeperiod
    and
    notify
    the
    Agency
    within
    15
    days
    of
    the
    replacement,
    modification,
    or
    change
    requiring
    recertification
    of the
    CEMS.
    B)
    Once
    the
    modification
    or changeto
    the
    CEMS
    has been
    completed
    and
    all
    of
    the associated
    repairs,
    component
    replacements,
    adjustments,
    linearization,
    and
    reprogramming
    of the
    CEMS
    have
    been
    completed;
    a
    probationary
    calibration
    error
    test
    is
    required
    to
    establish
    the
    beginning
    point
    of
    the.recertification
    test
    period.
    In
    this
    instance,
    the
    first
    successful
    calibration
    error
    test
    of the
    monitoring
    system
    following
    completion
    of
    all
    necessary
    repairs,
    component
    replacements,
    adjustments,
    linearization
    and
    reprogramming
    must
    be
    the probationary
    calibration
    error
    test.
    The
    probationary
    calibration
    error
    test
    must
    be
    passed
    before
    any
    of
    the
    required
    recertification
    tests
    are
    commenced.
    C)
    Beginning
    with
    the
    hour
    of commencement
    of
    a
    recertification
    test
    period,
    emission
    data
    recorded
    by
    the
    mercury
    CEMS
    are
    considered
    to
    be
    conditionally
    valid,
    contingent
    upon
    the
    results
    of
    the
    subsequent
    recertification
    tests.
    9

    D)
    Each
    required
    recertification
    test’
    must
    be completed
    no
    later
    than
    the
    following
    number
    of
    unit
    operating
    hours
    (or
    unit
    operating
    days)
    after
    the
    probationary
    calibratkrn
    error
    testthat
    initiates
    the test
    period:
    i)
    For
    a
    linearity
    check
    and/or
    cycle
    time
    test,
    168
    consecutive
    unit
    operating
    hours,
    as
    defined
    in
    40
    CFR
    72.2,
    incorporated
    by
    reference
    in Section
    225.140,
    or,
    for
    CEMS
    installed
    on
    common
    stacks
    or
    bypass
    stacks,
    168
    consecutive
    stack
    operating
    hours,
    as
    defined
    in
    40CFR
    72.2:
    ii)
    For
    a
    RATA
    (whether
    nonnal-load
    or multiple-load),
    720
    consecutive
    unit
    operating
    hours,
    as defined
    in
    40
    CFR
    72.2,
    incorporated
    by
    reference
    in Section 225.140,
    or,
    for
    CEMS
    installed
    on
    common
    stacks
    or bypass stacks,
    720
    consecutive
    stack
    operating
    hours,
    as defined
    in
    40
    CFR
    72.2;
    and
    iii)
    For a
    7-day
    calibration
    error
    test,
    21 consecutive
    unit
    operating
    days,
    as
    defined
    in
    40
    CFR
    72.2,
    incorporated
    by
    reference
    in
    Section
    225.140.
    E)
    All recertification
    tests
    must
    be performed
    hands-off.
    No
    adjustments
    to
    the
    calibration
    of
    the
    mercury
    CEMS,
    other
    than
    the
    routine
    calibration
    adjustments
    following
    daily
    calibration
    error
    tests
    as
    described
    in
    Section
    2.1.3
    of
    Exhibit
    B to
    this
    Appendix,
    are
    permitted
    during
    the
    recertification
    test
    period.
    Routine
    daily
    calibration
    error
    tests
    must
    be
    performed
    throughout
    the
    recertification
    test
    period,
    in
    accordance.with
    Section 2.1.1
    of Exhibit
    B
    to this
    Appendix.
    The
    additional
    calibration
    error
    test
    requirements
    in
    Section
    2.1.3
    of
    Exhibit
    B to
    this
    Appendix,
    must
    also
    apply
    during
    the
    recertification
    test
    period.
    F)
    If all
    of
    the required
    recertification
    tests
    and
    required
    daily
    calibration
    error
    tests
    are
    successfully
    completed
    in
    succession
    with
    no
    failures,
    and
    if
    each
    recertification
    test
    is
    completed
    within
    the
    time
    period
    specified
    in
    paragraph
    (b)(3)(D)(i),
    (ii),
    or
    (iii)
    of
    this
    Section, then
    all
    of the
    conditionally
    valid
    emission
    data
    recorded
    by
    the mercury
    CEMS
    will
    be
    considered
    quality
    assured,
    from
    the
    hour
    of commencement
    of
    the
    recertification
    test
    period
    until
    the hour
    of
    completion of
    the
    required
    test(s).
    G)
    If
    a
    required
    recertification
    test
    is
    failed
    or
    aborted
    due
    to
    a
    problem
    with
    the
    mercury
    CEMS,
    or
    if
    a
    daily
    calibration
    error
    test
    is
    failed
    during
    a
    recertification
    test
    period,
    data
    validation
    must
    be
    done
    as follows:
    10

    i)
    If
    any
    required
    recertification
    test
    is failed,
    it must
    be
    repeated,.
    If
    any
    recertification
    test
    other
    than
    a 7-day
    calibration
    error
    test
    is
    failed
    or
    aborted
    due
    to
    a problem
    with
    the mercury
    CEMS,
    the
    original
    recertification
    test period
    is ended,
    and
    a new
    recertification
    test period
    must
    be
    commenced
    with
    a
    probationary
    calibration
    error
    test.
    The
    tests
    that
    are
    required
    in the
    new
    recertification
    test
    period
    will
    include
    any tests
    that
    were
    required
    for
    the
    initial
    recertification
    event
    which
    were
    not•
    successfully
    completed
    and
    any recertification
    or diagnostic
    tests
    that
    are
    required
    as
    a
    result
    of changes
    made
    to
    the monitoring
    system
    to
    correct
    the
    problems
    that
    caused
    the
    failure
    of
    the
    recertification
    test.
    For
    a 2-
    or 3-load
    flow
    RATA,
    if
    the relative
    accuracy
    test
    is
    passed
    at one
    or
    more
    load
    levels,
    but
    is
    failed
    at
    a
    subsequent
    load
    level,
    provided
    that
    the
    problem
    that
    caused
    the
    RATA
    failure
    is
    corrected
    without
    re-linearizing
    the
    instrument,
    the
    length
    of the
    new
    recertification
    test
    period
    must
    be
    equal
    to
    the
    number
    of unit
    operating
    hours
    remaining
    in
    the
    original
    recertification
    test
    period,
    as
    of
    the hour
    of failure
    of the
    RATA.
    However,
    if
    re-linearization
    of the
    flow
    monitor
    is
    required
    after
    a flow
    RATA
    is
    failed
    at
    a
    particular
    load
    level,
    then
    a
    subsequent
    3-load
    RATA
    is
    required,
    and
    the
    new
    recertification
    test
    period
    must
    be
    720
    consecutive
    unit
    (or
    stack)
    operating
    hours.
    The new
    recertification
    test
    sequence
    must
    not
    be
    commenced
    until
    all
    necessary
    maintenance
    activities,
    adjustments,
    linearizations,
    and
    reprogramming
    of
    the
    CEMS
    have
    been
    cornpleted
    ii)
    Ifa
    linearity
    check,
    RATA,
    or
    cycle
    time
    test is
    failed
    or
    aborted
    due
    to a
    problem
    with
    the
    mercury
    CEMS,
    all
    conditionally
    valid
    emission
    data
    recorded
    by
    the
    CEMS
    are
    invalidated,
    from
    the
    hour
    of
    commencement
    of the
    recertification
    test
    period
    to
    the
    hour
    in
    which
    the test
    is
    failed
    or aborted,
    except
    for the
    case
    in
    which
    a
    multiple-load
    flow
    RATA
    is
    passed
    at one
    or
    more
    load
    levels,
    failed
    at
    a subsequent
    load
    level,
    and
    the
    problem
    that
    caused
    the
    RATA
    failure
    is corrected
    without
    re-linearizing
    the
    instrument.
    In
    that
    case,
    data invalidation
    will
    be
    prospective,
    from
    the
    hour
    of
    failure
    of the
    RATA
    until
    the commencement
    of
    the
    new
    recertification
    test
    period.
    Data
    from
    the CEMS
    remain
    invalid
    until
    the
    hour
    in which
    a new
    recertification
    test
    period
    is
    commenced,
    following
    corrective
    action,
    and
    a
    probationary
    calibration
    error
    test
    is
    passed,
    at
    which
    time
    the
    conditionally
    valid
    status
    of
    emission
    data
    from
    the
    CEMS
    begins
    again;
    11

    iii)
    If
    a
    7-day
    calibration error
    test
    is
    failed
    within
    the
    recertification
    test
    period,
    previously-recorded
    conditionally
    valid
    émissión
    data
    from
    the mercury
    CEMS
    are not
    invalidated.
    The
    conditionally
    valid
    data
    status
    is
    unaffected,
    unless
    the calibration
    error
    on
    the
    day
    of
    the failed
    7-day
    calibration
    error
    test
    exceeds
    twice
    the
    performance
    specification
    in
    Section
    3
    of Exhibit
    A
    to
    this
    Appendix,
    as described
    in
    paragraph
    (b)(3)(G)(iv) of this
    Section.
    iv)
    If a
    daily
    calibration
    error
    test
    is
    failed
    during
    a
    recertification
    test
    period
    (i.e.,
    the
    results
    of
    the
    test
    exceed
    twice
    the
    performance
    specification
    in
    Section
    3 of
    Exhibit
    A
    to this
    Appendix),
    the
    CEMS
    is
    out-of-control
    as
    of
    the
    hour
    in
    which
    the
    calibration
    error
    test
    is
    failed.
    Emission
    data
    from
    the
    CEMS
    will
    be
    invalidated
    prospectively
    from
    the
    hour
    of the
    failed
    calibration
    error
    test
    until
    the
    hour
    of
    completion
    of
    a
    subsequent
    successful
    calibration
    error
    test
    following
    corrective
    action,
    at which
    time
    the
    conditionally
    valid
    status
    of data
    from
    the
    monitoring
    system
    resumes.
    Failure
    to perform
    a
    required
    daily
    calibration
    error
    test
    during
    a
    recertification
    test
    period
    will
    also
    cause
    data
    from
    the
    CEMS
    to
    be
    invalidated prospectively,
    from
    the hour
    in which
    the
    calibration
    error
    test
    was
    due
    until
    the
    hour
    of
    completion
    of a
    subsequent
    successful
    calibration
    error
    test.
    Whenever
    a
    calibration
    error
    test
    is
    failed
    or
    missed
    during
    a recertification
    test
    period,
    no
    further
    recertification
    tests
    must
    be
    performed
    until
    the
    required
    subsequent
    -calibration
    error
    test
    has
    been
    passed,
    re-establishing
    the
    conditionally
    valid
    status
    of
    data
    from
    the monitoring
    system.
    If
    a
    calibration
    error
    test
    failure-
    occurs
    while
    a
    linearity
    check-or
    RATA
    is
    still
    in
    progress,
    the
    linearity
    check
    or RATA
    must
    be
    re
    started.
    v)
    Trial
    gas
    injections
    and
    trial RATA
    runs
    are permissible
    during
    the
    recertification
    test
    period,
    prior
    to commencing
    a linearity
    check
    or
    RATA,
    for
    the purpose
    of optimizing
    the
    performance
    of
    the
    CEMS.
    The
    results
    of
    such gas
    injections
    and
    trial
    runs
    will
    not
    affect
    the
    status
    of
    previously-recorded
    conditionally
    valid
    data
    or
    result
    in
    termination
    of
    the
    recertification
    test period,
    provided
    that
    they meet
    the
    following
    specifications
    and
    cOnditions:
    for
    gas
    injections,
    the
    stable,
    ending
    monitor
    response
    is
    within
    +-5
    percent
    or
    within
    5
    ppm
    of the
    tag
    value
    of
    the
    reference
    gas;
    for
    RATA
    trial
    runs,
    the
    average
    reference
    method
    reading
    and
    the
    average
    CEMS
    reading
    for
    the
    run
    differ
    by
    no
    more
    than +-lO%
    of
    12

    the
    average
    referencemethod
    value
    or
    +-15
    ppm,
    or
    +-1.5%
    HQ
    or
    +-O.02
    lb/mmBtu
    from
    the
    average
    reference
    method
    value,
    as
    applicable;
    no
    adjustments
    to
    the calibration
    f
    the
    CEMS
    are
    made
    following
    the
    trial
    injection(s) or
    run(s),
    other
    than
    the
    adjustments permitted
    under
    Section
    2.1.3
    of
    Exhibit
    B to
    this
    Appendix
    and
    the
    CEMS
    is
    not
    repaired,
    re-linearized
    or
    reprogrammed
    (e.g.,
    changing
    flow
    monitor
    polynomial
    coefficients,
    linearity
    constants,
    or
    K-factors)
    after
    the
    trial
    injection(s)
    or
    run(s).
    vi)
    If the
    results
    of
    any trial
    gas
    injection(s)
    or
    RATA
    run(s)
    are
    outside
    the limits
    in paragraphs
    (b)(3)(G)(v) of
    this
    Section
    or
    if
    the CEMS
    is
    repaired,
    re-linearized,
    or
    reprogrammed
    after
    the
    trial
    injection(s)
    or
    run(s),
    the
    trial
    injection(s)
    or
    run(s)
    will
    be
    counted
    as
    a
    failed
    linearity
    check
    or
    RATA
    attempt.
    If this
    occurs,
    follow
    the procedures
    pertaining
    to failed
    and
    aborted
    recertification
    tests
    in paragraphs
    (b)(3)(G)(i)
    and
    (b)(3)(G)(ii)
    of
    this
    Section.
    H)
    If
    any
    required
    recertification
    test is
    not completed
    within
    its
    allotted
    time
    period,
    data
    validation
    must
    be done
    as follows.
    For
    a
    late
    linearity
    test,
    RATA,
    or cycle
    time
    test
    that
    is
    passed
    on
    the
    first
    attempt,
    data
    from
    the
    monitoring
    system
    will
    be
    invalidated
    from
    the
    hour
    of
    expiration
    of
    the
    recertification
    test
    period
    until the
    hour
    of
    completion
    of the
    late
    test. For
    a
    late
    7-day
    calibration
    error
    test,
    whether
    or
    not it
    is passed
    on
    the
    first
    attempt,
    data
    from
    the
    monitoring
    system
    will
    also
    be invalidated
    from
    the
    hour
    of
    expiration
    of
    the
    recertification
    test
    period
    until
    the
    hour
    of
    completion
    of the
    late
    test.
    For a
    late linearity
    test,
    RATA,
    or cycle
    time
    test
    that
    is failed
    on
    the
    first
    attempt
    or
    aborted
    on
    the
    first
    attempt
    due to
    a
    problem
    with
    the
    monitor,
    all conditionally
    valid
    data
    from
    the
    monitoring
    system
    will
    be considered
    invalid
    back
    to
    the
    hour
    of
    the
    first
    probationary
    calibration
    error
    test
    which
    initiated
    the
    recertification test
    period.
    Data
    from
    the
    monitoring
    system
    will
    remain
    invalid
    until
    the hour
    of
    successful
    completion
    of the
    late
    recertification
    test
    and
    any
    additional
    recertification
    or diagnostic
    tests
    that are
    required
    as a
    result
    of
    changes
    made
    to the
    monitoring
    system
    to correct
    problems
    that caused
    failure
    of
    the
    late
    recertification
    test.
    I)
    If
    any required
    recertification
    test
    of
    a
    monitoring
    system
    has
    not
    been
    completed
    by
    the end
    of
    a
    calendar
    quarter
    and
    if data
    contained
    in
    the
    quarterly
    report
    are.
    conditionally
    valid
    pending
    the results
    of
    test(s)
    to
    be
    completed
    in a
    subsequent quarter,
    the
    owner
    or operator
    must
    indicate
    13

    this
    by
    meansofasuitableconditionailyvaliddataflag
    in
    the
    electronic
    quarterly
    report,
    and
    notification
    within
    the
    quarterly
    report
    pursuant
    to
    225;29Ob)(
    l)(),
    for
    that
    quarter.
    The
    owner
    or operator
    must
    resubmit
    the
    report
    for
    that
    quarter
    if
    the
    required
    recertification
    test
    is
    subsequently
    failed.
    If
    any
    required
    recertification
    test
    is
    not
    completed
    by
    the
    end
    of
    a
    particular
    calendar
    quarter
    but
    is
    completed
    no
    later
    than
    30
    days
    after
    the
    end
    of
    that
    quarter
    (i.e.,
    prior
    to
    the
    deadline
    for
    submitting
    the
    quarterly
    report
    under
    40
    CFR
    75.64,
    incorporated
    by
    reference
    in Section
    225.140),
    the
    test
    data
    and
    results
    may
    be
    submitted
    with
    the
    earlier
    quarterly
    report
    even
    though
    the
    test
    date(s)
    are
    from
    the
    next
    calendar
    quarter.
    In
    such
    instances,
    if
    the
    recertification
    test(s)
    are
    passed
    in
    accordance
    with
    the
    provisions
    ofparagraph
    (b)(3)
    of
    this
    Section,
    conditionally
    valid
    data
    may
    be reported
    as
    quality-assured,
    in
    lieu
    of
    reporting
    a
    conditional
    data
    flag.
    In
    addition,
    if
    the
    owner
    or
    operator
    uses
    a conditionally
    valid
    data
    flag
    in
    any
    of
    the
    four
    quarterly
    reports
    for
    a
    given
    year,
    the
    owner
    or
    operator
    must
    indicate
    the
    final
    status
    of
    the
    conditionally
    valid
    data
    (i.e.,
    resolved
    or
    unresolved) in
    the
    annual
    compliance
    certification
    report
    required
    under
    40
    CFR
    72.90
    for that
    year.
    The
    Agency
    may
    invalidate
    any
    conditionfly
    valid
    data
    that
    remains
    unresolved
    at the
    end
    of
    a particular
    calendar
    year.
    4)
    Recertification
    application.
    The
    designated
    representative
    must
    apply
    for
    recertification
    of each
    contihuous
    mercury
    emission
    monitoring
    system.
    The
    owner
    or
    operator
    must
    submit
    the
    recertification
    application
    in
    accordance
    with
    40
    CFR
    75.60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    and
    each
    complete
    recertification
    application
    must
    include
    the
    information
    specified
    in
    40
    CFR
    75.63, incorporated
    by
    reference
    in
    Section
    225.140.
    5)
    Approval
    or
    disapproval
    of
    request
    for
    recertification.
    The
    procedures
    for
    provisional
    certification
    in
    paragraph
    (a)(3)
    of
    this
    Section
    apply
    to
    recertification
    applications.
    The
    Agency
    will
    issue
    a
    notice
    of
    approval,
    disapproval,
    or
    incompleteness
    according
    to the
    procedures
    in
    paragraph
    (a)(4)
    of
    this
    Section.
    Data
    from
    the
    monitoring
    system remain
    invalid
    until
    all
    required
    recertification
    tests
    have
    been
    passed
    or
    until
    a
    subsequent
    probationary
    calibration
    effor
    test
    is
    passed,
    beginning
    a new
    recertification
    test
    period.
    The
    owner
    or
    operator
    must
    repeat
    all
    recertification
    tests
    or
    other
    requirements,
    as indicated
    in the
    Agency’s
    notice
    of disapproval,
    no
    later
    than
    30
    unit
    operating
    days
    after
    the
    date
    of
    issuance
    of
    the
    notice
    of
    disapproval.
    The
    designated
    representative
    must
    submit
    a
    notification
    of the
    recertification
    retest
    dates,
    as
    specified
    in
    40
    CFR
    75.61(a)(l)(ii),
    incorporated
    by
    reference
    in
    Section
    225.140,
    and
    must
    submit
    a
    new
    recertification
    application
    according
    to
    the procedures
    in
    paragraph
    (b)(4)
    of
    this
    Section.
    14

    c)
    Initial certification
    and
    recertification
    procedures.
    Prior
    to
    the
    applicable
    deadline
    in
    35
    Ill
    Admin.
    Code
    225.240(b),
    the
    owner
    or.
    operator
    must
    conduct
    initial certification
    tests
    and
    in
    accordance
    with
    40CFR75.63,
    incorporated
    by
    reference
    in
    Section
    225.140.
    the
    designated
    representative
    must
    submit an
    application
    to
    demonstrate
    that
    the
    continuous
    emission
    monitoring
    system
    and
    components
    thereof
    meet
    the
    specifications
    in
    Exhibit
    A
    to
    this
    Appendix.
    The
    owner
    or
    operator
    must
    compare
    reference
    method
    values
    with
    output
    from
    the
    automated
    data
    acquisition
    and
    handling
    system
    that
    is
    part
    of
    the
    continuous
    mercury
    emission
    monitoring
    system
    being
    tested.
    Except
    as
    otherwise
    specified
    in
    paragraphs
    (b)(1),
    (d),
    and
    (e)
    of
    this
    Section,
    and
    in
    Sections
    6.3.1
    and
    6.3.2
    pfxhibit
    A
    to this
    Appendix,
    the
    owner
    or
    operator
    must
    perform
    the
    following
    tests
    for
    initial
    certification
    or.recertification
    of
    continuous
    emissionmonitoring
    systems
    or
    components
    according
    to the
    requirements
    of
    Exhibit
    B
    to
    this
    Appendix:
    1)
    For
    each
    mercury
    concentration
    monitoring
    system:
    A)
    A
    7-day
    calibration
    error test;
    B)
    A
    linearity check,
    for
    mercury
    monitors,
    perform
    this
    check
    with
    elemental
    mercury
    standards;
    C)
    A
    relative
    accuracy
    test
    audit
    must
    be
    done
    on a
    jig/scm
    basis;
    D)
    A bias
    test;
    B)
    A
    cycle
    time
    test;
    F)
    For
    mercury
    monitors
    a
    3-level
    system
    integrity
    check,
    using
    a
    NIST
    traceable
    sourceof
    oxidized mercury,
    as
    described
    in Section
    6.2
    of
    Exhibit
    A
    to this
    Appendix.
    This
    test
    is
    not
    required
    for
    a
    mercury
    monitor
    that
    does
    not
    have
    a converter.
    2
    For
    each
    flow
    monitor:
    A)
    A
    7-day
    calibration
    error
    test;
    B)
    Relative
    accuracy
    test
    audits,
    as
    follows:
    i)
    A
    single-load
    (or
    single-level)
    RATA
    at
    the
    normal
    load
    (or
    levefl,
    as
    defined
    in
    Section
    6.5.2.1(d) of
    Exhibit
    A
    to
    this
    Appendix,
    for
    a
    flow
    monitor
    installed
    on
    a
    peaking
    unit
    or
    bypass
    stack,
    or
    for
    a
    flow
    monitor
    exempted
    from multiple-level
    RATA
    testing
    under
    Section
    6.5.2(e)
    of
    Exhibit
    A
    to this
    Appendix;
    15

    ii)
    For
    all
    other
    flow
    monitors,
    a
    RATA
    at
    each of
    the
    three
    load
    lvels
    (or
    perating
    levels)
    corrsponding
    to
    the
    three
    flue gas
    velocities
    described
    in
    Section
    6.5.2(a)
    of
    Exhibit
    A
    to
    this
    Appendix;
    C)
    A
    bias
    test
    for
    the
    single-load
    (or
    single-level)
    flow
    RATA
    described
    in
    paragraph
    (c)(2)(B)(i)
    of
    this
    Section:
    and
    D)
    A
    bias
    test
    (or
    bias
    tests)
    for
    the
    3-level
    flow
    RATA
    described
    in
    paragraph
    (c)(2)(B)(ii) of this
    Section,
    at
    the
    following
    load
    or
    operational
    level(s):
    i)
    At
    each
    load
    level
    designated
    as
    normal
    under
    Section
    6.5.2.1(d)
    of
    Exhibit
    A
    to this
    Appendix,
    for
    units
    that
    produce
    electrical
    or
    thermal
    output,
    or
    ii)
    At
    the
    operational
    level
    identified
    as
    normal
    in
    Section
    6.5.2.1(d)
    of
    Exhibit
    A
    to this
    Appendix,
    for units
    that
    do
    not
    produce
    electrical
    or thermal
    output.
    3)
    FOr
    each
    diluent
    as
    monitor
    used
    only
    to
    monitor
    heat input
    rate:
    A)
    A
    7-day
    calibration
    error
    test:
    B)
    A linearity
    check;
    C)
    Arelative
    accuracy
    test
    audit,
    where,
    for
    an
    02
    monitor
    used
    to
    determine
    cQ2
    concentration,
    the
    CO,
    reference
    method
    must
    be
    used
    for
    the
    RATA;
    and
    D)
    A cycle-time
    test.
    4)
    For
    each
    continuous
    moisture
    monitoring
    system
    consisting
    of
    wet-
    and
    dry-basis
    Q
    analyzers:
    A)
    A
    7-day
    calibration
    error
    test
    of each
    O7analvzer:
    B)
    A
    cycle
    time
    test
    of each
    07
    analyzer:
    C)
    A
    linearity
    test
    of
    each
    02
    analyzer:
    and
    16

    D)
    A
    RATA.
    directly
    comparing
    the
    percent
    moisture
    measured
    by
    the
    monitoring
    system
    to
    a
    reference
    method.
    5)
    For
    each
    continuous
    moisture sensor:
    A
    RATA,
    directly
    comparing
    the
    percent
    moisture
    measured
    by
    the
    monitor
    sensor
    to
    a
    reference
    method.
    6)
    For
    a
    continuous
    moisture
    monitoring
    system
    consisting
    of
    a
    temperature
    sensor
    and
    a
    data
    acquisition
    and
    handling
    system
    (DAHS)
    software
    component
    programmed
    with
    a
    moisture
    lookup
    table:
    A
    demonstration
    that
    the
    correct
    moisture
    value
    for
    each
    hour
    is
    being
    takea
    from
    the
    moisture lookup
    tables
    and
    applied
    to
    theemission
    calculations.
    At
    a minimum,
    the
    demonstration
    must
    be
    made
    at
    three
    different
    temperatures
    covering
    the
    normal
    range
    of
    stack
    temperatures
    from
    low
    to
    high.
    7)
    For
    each
    sorbent
    trap
    monitoring
    system,
    perform
    a
    RATA,
    on
    a ig/dscm
    basis,
    and
    a bias
    test.
    8)
    For
    the
    automated
    data
    acquisition
    and
    handling
    system,
    tests
    designed
    to
    verify
    the
    proper
    computation
    of
    hourly
    averages
    for
    pollutant
    concentrations,
    flow
    rate,
    pollutant
    emission
    rates,
    and
    pollutant
    mass
    emissions.
    9)
    The
    owner or
    operator
    must
    provide
    adequate
    facilities
    for
    initial
    certification
    or
    recertification
    testing
    that
    include:
    A)
    Sampling
    ports
    adequate
    for
    test
    methods
    applicable
    to
    such
    facility,
    such
    that:
    i)
    Volumetric
    flow
    rate,
    pollutant
    concentration,
    and
    pollutant
    emission
    rates
    can
    be
    accurately
    determined
    by
    applicable
    test
    methods
    and
    procedures:
    and
    ii)
    A
    stack
    or
    duct
    free
    of
    cyclonic
    flow
    during
    performance
    tests
    is
    available,
    as
    demonstrated
    by
    applicable
    test
    methods
    and
    procedures.
    B)
    Basic
    facilities
    (e.g.,
    electricity)
    for
    sampling
    and
    testing
    equipment.
    d)
    Initial
    certification
    and
    recertification
    and
    quality assurance
    procedures
    for
    optional
    backup
    continuous
    emission
    monitoring
    systems.
    1)
    Redundant
    backups. The
    owner
    or
    operator
    of an
    optional
    redundant
    backpp
    CEMS
    must
    comply
    with
    all
    the
    requirements
    for
    initial
    certification
    and
    17

    recertificationaccordingto
    the
    procedures
    specified
    in
    paragraphs
    (a),
    (b),
    and
    (c)
    of
    this
    Section.
    The
    owner
    or
    operator
    must
    operate
    the
    redundant
    backup
    CEMS
    during
    all
    periods
    of
    unit
    operation,
    except
    for
    periods
    of
    calibration,
    quality
    assurance,
    maintenance,
    or repair.
    The
    owner
    or
    operator
    must
    perform
    upon
    the
    redundant
    backup
    CEMS
    all
    quality
    assurance
    and
    quality
    control
    procedures
    specified
    in
    Exhibit
    B
    to this
    Appendix,
    except
    that
    the
    daily
    assessments
    in
    Section
    2.1
    of
    Exhibit
    B to
    this
    Appendix
    are
    optional for
    days
    on
    which
    the
    redundant
    backup
    CEMS
    is
    not
    used
    to
    report
    emission
    data
    under
    this
    part.
    For
    any
    day
    on
    which
    a redundant
    backup
    CEMS
    is
    used
    to report
    emission
    data,
    the
    system
    must
    meet
    all
    of
    the
    applicable
    daily
    assessment
    criteria
    in
    Exhibit
    B
    to
    this
    Appendix.
    2)
    Non-redundant
    backups.
    The
    owner
    or
    operator
    of an
    optional
    non-redundant
    backup
    CEMS or
    like-kind
    replacement
    analyzer
    must
    comply
    with
    all
    of
    the
    following
    requirements
    for
    initial
    certification,
    quality
    assurance,
    recertification,
    and
    data
    reporting:
    A)
    Except
    as
    provided
    in
    paragraph
    (d)(2)(E)
    of
    this
    Section,
    for
    a
    regular
    non-redundant
    backup
    CEMS
    (i.e.,
    a
    non-redundant
    backup
    CEMS
    that
    has
    its
    own
    separate
    probe,
    sample
    interface,
    and
    analyzer),
    or
    a non-
    redundant
    backup
    flow
    monitor,
    all
    of
    the
    tests
    in
    paragraph
    (c)
    of
    this
    Section
    are
    required
    for
    initial, certification
    of
    the
    system,
    except
    for
    the
    7
    day
    calibration
    error
    test.
    B)
    For
    a
    like-kind
    replacement
    non-redundant
    backup
    analyzer
    (i.e.,
    a non-
    redundant
    backup
    analyzer
    that
    usesthe same
    probe
    and
    sample
    interface
    as
    a primary
    monitoring
    system),
    no
    initial certification
    of
    the
    analyzer
    is
    required.
    C)
    Each
    non-redundant
    backup
    CEMS or
    like-kind
    replacement
    analyzer
    must
    comply
    with
    the
    daily
    and
    quarterly
    quality
    assurance
    and
    quality
    control requirements
    in
    Exhibit
    B
    to
    this
    Appendix
    for
    each
    day
    and
    quarter
    that
    the
    non-redundant
    backup
    CEMS
    or
    like-kind
    replacement
    analyzer
    is
    used
    to
    report
    data,
    and
    must
    meet
    the
    additional
    linearity
    and
    calibration
    error
    test
    requirements
    specified
    in
    this
    paragraph.
    The
    owner
    or
    operator must
    ensure that
    each
    non-redundant
    backup
    CEMS
    or
    like
    kind
    replacement
    analyzer
    passes
    a
    linearity
    check
    (for
    mercury
    concentration
    and
    diluent
    gas
    monitors)
    or
    a calibration
    error
    test
    (for
    flow
    monitors)
    prior
    to each
    use
    for
    recording
    and
    reporting
    emissions.
    When
    a
    non-redundant
    backup
    CEMS
    or
    like-kind
    replacement
    analyzer
    is
    brought
    into
    service,
    prior
    to
    conducting
    the
    linearity
    test,
    a probationary
    calibration
    error
    test
    (as
    described
    in
    paragraph
    (b)(3)(B)
    of
    this
    Section),
    18

    which*ill
    begin
    a
    period
    of
    conditkrnally
    valid
    data,
    may
    be
    perfonned
    in
    order
    to
    allow
    the
    validation
    of
    data retrospectively,
    as
    follows.
    Conditionally
    valid
    data
    from
    the
    CEMS
    or
    like-kind
    replacement
    analyzer
    are
    validated
    back
    to
    the
    hour
    of
    completion
    of
    the probationary
    calibration
    error
    test
    if
    the following
    conditions
    are
    met:
    if
    no
    adjustments
    are
    made
    to
    the CEMS
    or like-kind
    replacement analyzer
    other
    than
    the
    allowable
    calibration
    adjustments
    specified
    in
    Section
    2.1.3
    of
    Exhibit
    B
    to
    this
    Appendix
    between
    the
    probationary
    calibration
    error
    test
    and
    the
    successful
    completion
    of the
    linearity
    test;
    and
    if
    the linearity
    test
    is
    passed
    within
    168
    unit
    (or
    stack)
    operating
    hoursof
    the
    probationary
    calibration
    error
    test.
    However,
    if the
    linearity
    test
    is
    performed
    within
    168
    unit
    or
    stack
    operating hours
    but
    is
    either
    failed
    or
    aborted
    due
    to a
    problem
    with
    the CEMS
    or like-kind
    replacement
    analyzer,
    then
    all
    of
    the
    conditionally
    valid
    data
    are
    invalidated
    back
    to the
    hour
    of the
    probationary
    calibration
    error
    test,
    and data
    from
    the
    non-redundant
    backup
    CEMS
    or from
    the
    primary
    monitoring
    system
    of
    which
    the
    like-kind
    replacement
    analyzer
    is
    a
    part
    remnin
    invalid
    until
    the hour
    of
    cbmpletionof
    a
    successful
    linearity
    test. Notwithstanding
    this requirement,
    the conditionally
    valid
    data
    status
    may
    be
    re-established
    after
    a failed
    or
    aborted
    linearity
    check,
    if
    corrective
    action
    is
    taken
    and
    a calibration
    error
    test
    is subsequently
    passed.
    However,
    in
    no
    case
    will
    the
    use
    of
    conditional
    data
    validation
    extend
    for
    more
    than
    168
    unit
    or
    stack
    operating
    hours
    beyond
    the
    date
    and
    time
    of
    the
    original
    probationary
    calibration
    error
    test
    when
    the
    analyzer
    was
    brought
    into
    service.
    D)
    For
    each
    parameter
    monitored
    (i.e.,
    CO
    2
    Q
    2
    ,
    Hg,
    or flow
    rate)
    at
    each
    unit
    or
    stack,
    a
    regular
    non-redundant
    backup
    CEMS
    may
    not
    be
    used
    to
    report
    data
    at that
    affected
    unit
    or
    common
    stack
    for
    more
    than
    720
    hours
    in
    any
    one
    calendar
    year
    (in
    accordance
    with
    40
    CFR
    75.74(c),
    incorporated
    by
    reference
    in
    Section
    225.140),
    unless
    the
    CEMS
    passes
    a RATA
    at that
    unit
    or stack.
    For
    each
    parameter
    monitored
    at each
    unit
    or
    stack,
    the use
    of
    a
    like-kind
    replacement
    non-redundant
    backup
    analyzer
    (or
    analyzers)
    is
    restricted
    to 720
    cumulative hours
    per
    calendar
    year,
    unless
    the
    owner
    or
    operator
    redesignates
    the like-kind
    replacement
    analyzer(s) as
    component(s)
    of regular
    non-redundant
    backup
    CEMS
    and
    each
    redesignated
    CEMS
    passes
    a
    RATA
    at
    that
    unit
    or
    stack.
    E)
    For
    each
    regular
    non-redundant
    backup
    CEMS,
    no
    more
    than
    eight
    successive
    calendar
    quarters
    must
    elapse
    following
    the
    quarter
    in which
    the
    last
    RATA
    of
    the CEMS
    was
    done
    at
    a
    particular
    unit
    or
    stack,
    without
    performing
    a
    subsequent
    RATA.
    Otherwise,
    the
    CEMS
    may
    not be
    used
    to
    19

    report
    datafrorn
    thattmitórstacfr
    uiitilthe
    hour
    of
    completiônof
    a
    passing
    RATA at
    that
    location.
    F)
    Each
    regularnon-redundant
    backup
    CEMS
    must
    be
    represented
    in
    the
    monitoring
    plan
    required
    under
    Section 1.10
    of
    this
    Appendix
    as
    a
    separate
    monitoring
    system,
    with
    unique
    system
    and
    component
    identification
    numbers.
    When like-kind
    replacement
    non-redundant
    backup
    analyzers
    are
    used,
    the
    owner
    or
    operator
    must
    represent
    each
    like-
    kind
    replacement
    analyzer
    used
    during
    a particular
    calendar
    quarter
    in
    the
    monitoring
    plan
    required
    under
    Section
    1.10
    of
    this
    Appendix
    as
    a
    component
    of
    a
    primary monitoring
    system.
    The
    owner
    or
    operator
    must
    also
    assign
    a
    unique
    component
    identification
    number
    to
    each
    like-kind
    replacement
    analyzer,
    beginning
    with
    the
    letters
    “LK”
    (e.g.,
    “LKl,”
    “LK2,”
    etc.)
    and
    must
    specify
    the
    manufacturer,
    model
    and
    serial
    number
    of
    the
    like-kind
    replacement
    analyzer.
    This
    information
    may
    be added,
    deleted
    or
    updated
    as
    necessary,
    from
    quarter
    to quarter.
    The
    owner
    or
    operator
    must
    also
    report
    data
    from
    the
    like-kind
    replacement
    analyzer
    using
    the
    system
    identification
    number
    of
    the
    primary
    monitoring
    system
    and
    the
    assigned
    component
    identification
    number
    of the
    like-kind
    replacement
    analyzer.
    For
    the
    purposes
    of
    the
    electronic
    quarterly
    report
    required
    under
    40
    CFR
    75.64,
    incorporated
    by
    reference
    in
    Section
    225.140,
    the
    owner
    or
    operator
    may
    manually
    enter
    the
    appropriate
    component
    identification
    number(s)
    of
    any
    like-kind
    replacement
    analyzer(s)
    used
    for
    data
    reporting
    during
    the
    quarter.
    G)
    When
    reporting data
    from
    a
    certified
    regular
    non-redundant
    backup
    CEMS,
    use
    a
    method
    of
    determination
    (MODC) code
    of”02.”
    When
    reporting
    data
    from
    a
    like-kind
    replacement
    non-redundant
    backup
    analyzer,
    use
    a
    MODC
    of”17” (see
    Table
    4a
    under
    Section
    1.11
    of
    this
    Appendix).
    For
    the
    purposes
    of
    the
    electronic
    quarterly
    report
    required
    under
    40
    CFR
    75.64,
    incorporated
    by
    reference
    in
    Section
    225.140,
    the
    owner
    or
    operator
    may
    manually
    enter
    the
    required
    MODC
    of
    “17”
    for
    a
    like-kind
    replacement
    analyzer.
    H)
    For
    non-redundant
    backup
    mercury
    CEMS
    and
    sorbent
    trap
    monitoring
    systems,
    and
    for
    like-kind
    replacement
    mercury
    analyzers,
    the
    following
    provisions
    apply
    in
    addition
    to,
    or,
    in
    some
    cases,
    in
    lieu
    of,
    the
    general
    requirements
    in
    paragraphs
    (d)(2)(A)
    through
    (d)(2)(H)
    of
    this
    Section:
    i)
    When
    a
    certified
    sorbent
    trap
    monitoring
    system is
    brought
    into
    service
    as
    a regular non-redundant
    backup monitoring
    system,
    the
    20

    system
    must
    be
    operated
    according
    to
    the
    procedures
    in
    Section
    1.3
    of
    this
    Appendixand
    Exhibit.D
    to
    this
    Appendix;
    ii)
    When
    a regular
    non-redundant
    backup
    mercury
    CEMS
    or
    a like-
    kind
    replacement
    mercury
    analyzer
    is brought
    into
    service,
    a
    linearity
    check
    with elemental
    mercury
    standards,
    as
    described
    in
    paragraph
    (c)(1)(B)
    of this
    Section
    and
    Section
    6.2
    of Exhibit
    A
    to
    this Appendix,
    and
    a
    single-point
    system
    integrity
    check,
    as
    described
    in
    Section
    2.6 of
    Exhibit
    B
    to this
    Appendix,
    must
    be
    performed.
    Alternatively,
    a 3-level
    system
    integrity
    check,
    as
    described
    in
    paragraph
    (c)(1)(E)
    of
    this
    Section
    and
    paragraph
    (g)
    of
    Section
    6.2
    in Exhibit
    A to
    this Appendix,
    may
    be
    performed
    in
    lieu
    of
    these
    two tests.
    iii)
    The
    weekly
    single-point
    system
    integrity
    checks
    described
    in
    Section
    2.6 of
    Exhibit
    B
    to
    this
    Appendix
    are required
    as long
    as
    a
    non-redundant
    backup
    merëury
    CEMS
    or like-kind
    replacment
    mercury
    analyzer
    remains
    in service,
    unless
    the
    daily
    calibrations
    of
    the mercury
    analyzer
    are
    done
    using
    a
    NEST-traceable
    source
    or
    other
    approved
    source
    of
    oxidized
    mercury.
    3)
    Reference
    method
    backups.
    A monitoring
    system
    that is
    operated
    as
    a
    reference
    method
    backup
    system
    pursuant
    to the
    reference
    method
    requirements
    of
    Methods
    2,
    3A,
    30A,
    30B in
    appendix
    A of
    40
    CFR 60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    need
    not
    perform
    arid
    pass the
    certification
    tests
    required
    by
    paragraph
    (c)
    of
    this
    Section
    prior, to
    its use
    pursuant
    to
    this paragraph.
    e)
    Certification/recertification
    procedures
    for
    either
    peaking
    unit
    or by-pass
    stack/duct
    continuous
    emission
    monitoring
    systems.
    The
    owner
    or
    operator
    of
    either
    a peaking
    unit
    or
    by-pass
    stack/duct
    continuous
    emission
    monitoring
    system
    must
    comply
    with
    all
    the
    requirements
    for certification
    or recertification
    according
    to the
    procedures
    specified
    in
    paragraphs
    (a). (b),
    and
    (c)
    of this
    Section,
    except
    as follows:
    the
    owner
    or
    operator
    need
    only
    perform
    one Nine-run
    relative
    accuracy
    test
    audit
    for
    certification
    or
    recertification
    of
    a
    flow
    monitor
    installed
    on the
    by-pass
    stack/duct
    or on
    the
    stack/duct
    used only
    by
    affected
    peaking
    unit(s).
    The relative
    accuracy
    test
    audit
    must be
    performed
    during
    normal
    operation
    of
    the peaking
    unit(s)
    or the
    by-pass
    stack/duct.
    f)
    Certification/recertification
    procedures
    for
    alternative
    monitoring
    systems.
    The
    designated
    representative
    representing
    the
    owner
    or operator
    of
    each
    alternative
    monitoring
    system
    approved
    by
    the Agency
    as
    equivalent
    to or
    better
    than
    a
    continuous
    emission
    monitoring
    system
    according
    to
    the
    criteriain
    subpart
    E
    of 40
    CFR
    7.5,
    .
    incorporated
    by
    reference
    in Section
    225.
    140
    must
    apply
    for
    certification
    to the
    Agency
    21

    apply
    for
    recertification
    to
    the.
    Agency
    following
    a replacement,
    modification,
    or
    change
    according
    to the
    procedures
    in
    paraaph
    (c)
    of
    this
    Section.
    The
    owneror
    operator
    of
    an
    alternative
    monitoring
    system
    must
    comply
    with
    thenotification
    andapplication
    requirements
    fOr
    certification
    or
    recertification
    according
    to
    the
    procedures
    specified
    in
    paragraphs
    (a)
    and
    (b)
    of
    this
    Section.
    Section
    1.5
    Quality
    assurance
    and
    quality
    control
    requirements
    a)
    Continuous emission
    monitoring
    systems.
    Theowner or
    operator
    of
    an affected
    unit
    must
    operate
    calibrate
    and
    maintain
    each
    continuous mercury
    emission
    monitoring
    system
    used
    to
    report
    mercury
    emission
    data
    as
    follows:
    1)
    The
    owner
    or
    operator
    must
    operate,
    calibrate
    and
    maintain
    each
    primary
    and
    redundant
    backup
    continuous
    emission
    monitoring
    system
    according
    to
    the
    ciuajjy
    assurance
    and
    quality
    control
    procedures
    in
    Exhibit
    B
    to this
    Appendix.
    2)
    The
    owner
    or
    operator
    must
    ensure
    that
    each
    non-redundant
    backup
    CEMS
    meets
    the
    quality
    assurance
    requirements
    of
    Section
    1.4(d)
    of
    this
    Appendix
    for
    each
    day
    and
    quarter
    that
    the
    system
    is
    used
    to
    report
    data.
    31
    The
    owner
    or
    operator
    must
    perform
    quality
    assurance
    upon
    a
    reference
    method
    backup
    monitoring
    system
    according
    to
    the requirements
    of method
    2
    or
    3A
    in
    appendix
    A
    of 40
    CFR
    60,
    incorporated
    by
    reference
    in
    Section
    225.140
    (supplemented,
    as
    necessary,
    by
    guidance
    from
    the
    Administrator
    or
    the
    Agency),
    or
    one
    of
    the
    mercury
    reference
    methods
    in
    Section
    1.6
    of
    this
    Appendix,
    as
    applicable,
    instead
    of the
    procedures
    specified
    in Exhibit
    B
    of
    this
    Appendix.
    b)
    Calibration gases.
    The
    owner
    or
    operator
    must
    ensure
    that
    all
    calibration
    gases
    used
    to quality assure
    the
    operation
    of
    the
    instrumentation
    required
    by
    this
    Appendix
    must
    meet
    the
    definition
    in
    40 CFR
    72.2,
    incorporated
    by
    reference
    in Section
    225.140.
    Section 1.6
    Reference
    test
    methods
    a)
    The
    owner
    or operator
    must
    use the
    following
    methods,
    which
    are
    found
    in
    appendix
    A-4
    to
    40
    CFR
    60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    or
    have
    been
    published
    by
    ASTM,
    to
    conduct
    the
    following tests:
    monitoring
    system
    tests
    for
    certification
    or
    recertification
    of
    continuous
    mercury
    emission
    monitoring
    systems
    the
    emission
    tests
    required under
    Section
    1.15(c)
    and
    (d)
    of
    this
    Appendix;
    and
    required
    quality
    assurance
    and
    quality
    control
    tests:
    22

    1)
    Mëthóds
    1-or
    l,A’are’
    the
    referen&
    nethdsf&selectibn
    of sampling
    site
    and
    sample
    traverses.
    2)
    Method
    2
    or
    its
    allowable
    alternatives,
    as
    provided
    in
    appendix
    A
    to
    40
    CFR
    60.
    incorporated
    by
    reference
    in
    Section
    225.140,
    except
    for
    Methods
    2B
    and
    2E,
    are
    the
    reference
    methods
    for
    determination
    of
    volumetric
    flow.
    3)
    Methods
    3,
    3A,
    or 3B
    are
    the
    reference
    methods
    for
    the
    determination
    of the
    dry
    molecular
    weight
    02
    and
    CO
    2
    concentrations
    in
    the
    emissions.
    4)
    Method.4
    (either
    the
    standard
    procedure
    described
    inSection
    8.1
    of
    the
    method
    or
    the
    moisture
    approximation
    procedure
    described in
    Section
    8.2
    of
    the
    method)
    must
    be used
    to
    correct
    pollutant
    concentrations
    from
    a
    dry
    basis
    to
    a wet
    basis
    (or
    from
    a
    wet
    basis
    to
    a
    dry
    basis)
    and
    must
    be
    used
    when
    relative
    accuracy
    test
    audits
    of
    continuous
    moisture
    monitoring
    systems
    are
    conducted.
    For
    the
    purpose
    of
    determining
    the
    stack
    gas
    molecular
    weight,
    however,
    the
    alternative
    wet
    bulb
    drybuibtechnigue
    for
    approximating
    the
    stackgas
    moisture
    content
    ‘described
    in
    Section 2.2
    of
    Method 4
    may
    be
    used
    in
    lieu
    of
    the
    procedures
    in
    Sections
    8.1
    and
    8.2
    of
    the
    method.
    5)
    ASTM
    D6784-02,
    Standard
    Test
    Method
    for
    Elemental,
    Oxidized,
    Particle-Boirn
    and
    Total
    Mercury
    in
    Flue
    Gas
    Generated
    from
    Coal-FiredStationary
    Sources
    (Ontario
    Hydro
    Method)
    (incorporated
    by
    reference
    under
    Section
    225.140)
    is the
    reference
    method
    for
    determining
    mercury
    concentration.
    A)
    A1ternatively
    Method
    29
    in appendix
    A-8
    to
    40
    CFR
    60,
    incorporated
    by’
    reference
    in
    Section 225.140,
    may
    be
    used,
    with
    these
    caveats:
    The
    procedures
    for
    preparation
    of
    mercury
    standards
    and
    sample
    analysis
    in
    Sections
    13.4.1.1
    through
    13.4.1.3
    ASTM
    D6784-02
    (incorporated
    by
    reference
    under
    Section
    225.140)
    must
    be
    followed
    instead
    of
    the
    procedures
    in
    Sections
    7.5.33
    and
    11.1.3 of
    Method
    29
    in
    appendix
    A-8
    to
    40
    CFR
    60,
    and
    the
    QAJOC
    procedures
    in Section
    13.4.2
    of
    ASTM
    D6784-02
    (incorporated
    by
    reference
    under
    Section
    225.140)
    must
    be
    performed
    instead
    of
    the
    procedures
    in Section
    9.2.3
    of
    Method
    29
    in
    appendix
    A-8
    to
    40
    CFR
    60.
    The
    tester
    may
    also
    opt
    to
    use
    the
    sample
    recovery
    and
    preparation
    procedures
    in
    ASTM
    D6784-02
    (incorporated
    by
    reference
    under
    Section
    225.140)
    instead
    of
    the
    Method
    29
    in
    appendix
    A
    8 to
    40
    CFR
    60
    procedures,
    as follows:
    Sections
    8.2.8
    and
    8.2.9.1
    of
    Method 29
    in
    appendix
    A-8
    to 40
    CFR
    60
    may
    be
    replaced
    with
    Sections
    13.2.9.1
    through
    13.2.9.3
    of
    ASTM
    D6784-02
    (incorporated
    by
    reference
    under
    Section
    225.140):
    Sections
    82.9.2
    and
    8.2.9.3
    of
    Method
    29in
    appendix
    A-8
    to
    40
    CFR
    60
    may
    be
    replaced
    with
    Sections
    13.2.10.1
    23

    under
    Section
    225.140);
    Section
    8.3.4 of
    Method 29
    in
    appendix
    A-8
    to
    40
    CFR
    60may
    be
    replacedwith
    Section 13.3.4
    or
    13.3.6
    of
    ASTMD6784-02’(as
    appropriate)
    (incorporated
    byreference
    under
    Section
    225.140);
    and;
    Section
    8.3.5
    of
    Method
    29 in
    appendix
    A-8
    to
    40
    CFR
    60
    may
    be
    replaced
    with
    SectiOn
    13.3.5.
    or
    13.3.6
    of
    ASTM
    D6784-02
    (as
    appropriate)
    (incorporated
    by
    reference
    under
    Section
    225.140).
    B)
    Whenever
    ASTM
    D6784-02
    (incorporated
    by
    reference
    under
    Section
    225.140)
    or
    Method
    29
    inappendixA-8 to
    40
    CFR
    60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    is
    used,
    paired
    sampling
    trains
    are
    required.
    To
    validate
    a
    RATA
    run
    or
    an
    emission
    test
    run,
    the
    relative
    deviation
    (RD),
    calculated
    according
    to
    Section
    11.6
    of
    Exhibit
    D
    to this
    Appendix,
    must
    not
    exceed
    10
    percent, when
    the
    average
    concentration
    is
    greater
    than
    1.0
    .tg/m
    3
    .
    If
    the
    average
    concentration
    is
    less
    than
    or
    equal
    to
    1.0
    .tg/m
    3
    ,
    the
    RD
    must
    not
    exceed
    20
    percent.
    The
    RD
    results
    are
    also
    acceptable
    if
    theabsolute
    difference
    betWeen
    the
    mercuryconcentrations
    measured
    by
    the
    paired
    trains
    does
    not
    exceed
    0.03 .tg/m
    3
    .
    If
    the
    RD
    criterion
    is met,
    the
    run
    is
    valid.
    For
    each
    valid
    run,
    average
    the
    mercury
    concentrations
    measured
    by
    the
    two
    trains
    (vapor
    phase,
    only).
    C)
    Two
    additional
    reference
    methods
    that
    may
    be
    used
    to measure
    mercui’
    concentration
    are:
    Method
    30A,
    “Determination
    of
    Total
    Vapor
    Phase
    Mercury
    Emissions
    from
    Stationary
    Sources
    (Instrumental
    Analyzer
    Procedure)”
    and
    Method
    30B,
    “Determination
    of
    Total
    Vapor
    Phase
    Mercury
    Emissions
    from
    Coal-Fired
    Combustion
    Sources
    Using
    Carbon
    Sorbent Traps”.
    D)
    When
    Method
    29
    in
    appendix•A-8
    to 40
    CFR
    60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    or
    ASTM
    D6784-
    02
    (incorporated
    by
    reference
    under
    Section
    225.140)
    is used
    for
    the
    mercury
    emission
    testing
    required
    under
    Section
    1.15(c)
    and
    (d)
    of
    this
    Appendix,
    locate
    the
    reference
    method
    test
    points
    according
    to Section 8.1
    of
    Method
    30A,
    and
    if
    mercury
    stratification
    testing
    is
    part
    of
    the
    test
    protocol,
    follow
    the
    procedures
    in
    Sections
    8.L3
    through
    8.1.3.5
    of
    Method
    30A.
    b)
    The
    owner
    or
    operator
    may
    use
    any
    of
    the
    following
    methods,
    which
    are
    found
    in
    appendix
    A
    to
    40
    CFR
    60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    or
    have
    been
    published
    by
    ASTM,
    as a
    reference
    method
    backup
    monitoring
    system
    to
    provide
    quality
    assured monitor
    data:
    1)
    Method
    3A
    for
    determining
    02
    or
    CO
    2
    concentration;
    24

    2)
    Method
    2,.or
    its. allowable
    alternatives,
    as
    provided
    in
    appendix
    A
    to
    .40
    CFR60,
    incorporatedby
    reference
    in Section
    225.140,
    except
    for
    Methods
    2B
    and
    2E,
    for
    determining
    volumetric
    flow
    The sample
    point(s)
    for
    reference
    methods
    must
    be
    located
    according
    to
    the provisions
    of
    Section
    6.5.4
    of
    Exhibit
    A
    to
    this
    Appendix.
    3)
    ASTM
    D6784-02,
    Standard
    Test Method
    for
    Elemental,
    Oxidized,
    Particle-Bound
    and
    Total
    Mercury
    in
    Flue
    Gas
    Generated
    from
    Coal-Fired Stationary
    Sources
    (Ontario
    Hydro
    Method)
    (incorporated
    by
    reference
    under
    Section
    225.140)
    for
    deterrpining
    mercury
    concentratiom..
    4)
    Method
    29 in
    appendix
    A-8
    to 40
    CFR
    60,
    incorporated
    by
    reference
    in Section
    225.140,
    for
    determining
    mercury
    concentration;
    5)
    Method
    30A
    for
    determining
    mercury
    concentration;
    and
    6’)
    Method
    30B
    for
    determining
    mercury
    concentration.
    c)
    Instrumental
    EPA
    Reference
    Method
    3A
    in
    appendices
    A-2
    and
    A-4
    of
    40
    CFR
    60,
    incorporated
    by
    reference
    in Section
    225.140,
    must
    be
    conducted
    using
    calibration
    gases
    as
    defined
    in Section
    5 of Exhibit
    A to
    this
    Appendix.
    Otherwise,
    pcrformance
    tests
    must
    be conducted and
    data reduced
    in
    accordance
    with
    the
    test methods
    and
    procedures
    of
    this
    part
    unless
    the
    Agency:
    1)
    Specifies
    or
    approves,
    in
    specific
    cases,
    the use
    of
    a reference
    method
    with
    minor
    changes
    in
    methodology;
    2)
    Approves
    the
    use of
    an
    equivalent
    method;
    or
    3)
    Approves
    shorter
    sampling
    times
    and
    smaller
    sample
    volumes
    when
    nencitct1
    by
    process
    variables
    or other
    factors.
    Section 1.7
    Out-of-control
    veriods and
    system
    bias
    testin2
    a)
    If an
    out-of-control
    period
    occurs
    to
    a
    monitor
    or
    continuous
    emission
    monitoring
    system,
    the
    owner
    or
    operator
    must
    take
    corrective
    action
    and
    repeat
    the tests
    applicable
    to
    the
    “out-of-control
    parameter”
    as described
    in Exhibit
    B of
    this
    Appendix.
    1)
    For
    daily
    calibration
    error
    tests,
    an
    out-of-control
    period
    occurs
    when
    the
    calibration
    error
    of
    a
    pollutant
    concentration
    monitor
    exceeds
    the
    applicable
    specification
    in
    Section
    2.1.4
    of Exhibit
    B to
    this Appendix.
    25

    2)
    the
    error
    in
    linearity
    at
    any
    of
    three
    gas
    concentrations
    (low,
    mid-range,
    and high)
    exceeds
    the
    applicable
    specification
    in
    Exhibit
    A to this
    Appendix.
    3)
    For relative
    accuracy
    test
    audits,
    an
    out-of-control period
    occurs
    when
    the
    relative
    accuracy
    exceeds
    the
    applicable
    specification
    in
    Exhibit
    A
    tO this
    Appendix.
    b)
    When
    a monitor
    or
    continuous
    emission
    monitoring
    system
    is
    out-of-control,
    any
    data
    recorded
    by
    the
    monitor
    or monitoring
    system
    are
    not quality-assured
    and must
    not
    be
    used
    in
    calculating
    monitor
    data
    availabilities
    pursuant
    to
    Section
    1.8 of
    this
    Appendix.
    c)
    When
    a monitor
    or
    continuous
    emission
    monitoring
    system
    is
    out-Of-control,
    the
    owner
    or
    operator
    must take
    one
    of the
    following
    actions
    until
    the monitor
    or monitoring
    system
    has
    successfully
    met
    the
    relevant
    criteria
    in
    Exhibits
    A
    and
    B of
    this
    Appendix
    as
    demonstrated
    by
    subsequent
    tests:
    1)
    Use
    a certified
    ‘backup
    monitoring
    system
    or
    a
    reference
    method
    for
    measuring
    and
    recording
    emissions
    from
    the
    affected
    unit(s);
    or
    2)
    Adjust
    the gas
    discharge
    paths
    from
    the affected
    unit(s)
    with
    emissions
    normally
    observed
    by the
    out-of-control
    monitor
    or
    monitoring
    system
    so
    that all
    exhaust
    gases
    are monitored
    by
    a
    certified
    monitor
    or
    monitoring
    system
    meeting
    the
    requirements
    of
    Exhibits
    A
    and B
    of this
    Appendix.
    d)
    When
    the bias
    test
    indicates
    that
    a flow
    monitor,
    a diluent
    monitoring
    system,
    a
    mercury
    concentration
    monitoring
    system
    or asorbent
    trap
    monitoring
    system
    is biased
    low
    (i.e.,
    the
    arithmetic
    mean of
    the differences
    between
    the reference
    method
    value and
    the
    monitor
    or
    monitoring
    system
    measurements
    in a
    relative
    accuracy
    test
    audit
    exceed
    the
    bias
    statistic
    in
    Section
    7 of
    Exhibit
    A
    to
    this
    Appendix),
    the
    owner
    or
    operator
    must
    adjust
    the
    monitor
    or
    continuous
    emission
    monitoring
    system
    to eliminate
    the
    cause
    of
    bias
    such that
    it
    passes
    the
    bias
    test.
    Section
    1.8
    Determination
    of
    monitor
    data
    availability
    a)
    Following
    initial
    certification
    of
    the required
    CO,Q
    2
    ,
    flow
    monitoring
    system(s),
    Hg
    concentration,
    or moisture
    monitoring
    system(s)
    at a
    particular
    unit
    or
    stack
    location
    (i.e.,
    the
    date
    and
    time at
    which
    quality-assured
    data
    begins
    to be
    recorded
    by CEMS(s)
    at
    that
    location),
    the
    owner
    or
    operator
    must
    begin
    calculating
    the
    percent
    monitor
    data
    availability
    as described
    in
    paragraph
    (a)(1)
    of
    this
    Section.
    by means
    of
    the
    automated
    data
    acquisition
    and
    handling
    system,
    and
    the
    percent
    monitor
    data
    availability
    for
    each
    monitored
    parameter.
    26

    I)
    Föliöng
    initialcertificàtión,
    the
    owneror
    operatormust
    use
    Equation
    8
    to
    caláulate,
    hourly,
    percent monitor-
    data
    availability
    for
    each
    calendar
    quarter.
    TOtal
    unit
    operating
    hours
    for
    which
    quality-assured
    data
    Percent
    was
    recorded
    for
    the
    calendar
    quarter
    monitor
    data
    =
    X
    100
    (Eq.
    8)
    availability
    Total
    unit
    operatinghours
    for
    the-calendar
    quarter
    2)
    When
    calculating
    percent
    monitor
    data
    availability
    using
    Equation
    8.
    the
    owner
    or
    operator
    must include
    all
    unit
    operating
    hours,
    and
    all
    monitor
    operating
    hours
    for
    which
    quality-assured
    data
    were
    recorded
    by
    a
    certified
    primary
    monitor;
    a
    certified
    redundantor
    non-redundant
    backup
    monitor
    or
    a
    reference
    method
    for
    that
    unit.
    Section
    1.9 - Determination
    of
    sorbent
    trap
    monitoring
    systems
    data
    availability
    a)
    -
    If
    a
    primary
    sorbenttrap
    monitoring
    system
    has
    not
    been
    certified
    by
    the
    applicable
    compliance
    date
    specified
    under
    35
    Ill
    Admin.
    Code
    Part
    225,
    Subpart
    B,
    and
    if
    quality-
    assured
    mercury
    concentration
    data
    from
    a certified
    backup
    mercury
    monitoring
    system,
    reference
    method,
    or
    approved
    alternative
    monitoring
    system
    are
    unavailable,
    the
    owner
    or
    operator must-perform
    quarterly
    emissions
    testing
    in
    accordance
    with
    Section
    225.239
    until
    such time
    the
    primary
    sorbent
    trap
    monitoring
    system
    has
    been
    certified.
    b)
    For
    a
    certified
    sorbent
    trap
    system,
    a missing
    data
    period
    will
    occur
    in
    the
    following
    circumstances,
    unless quality-assured
    mercury
    concentration
    data
    from
    a
    certified
    backup
    mercury
    CEMS,
    sorbent
    trap
    system,
    reference
    method,
    or
    approved
    alternative
    monitoring
    system
    are
    available:
    1)
    A
    gas sample
    is
    not
    extracted
    from
    the
    stack
    during
    unit
    operation
    (e.g;,
    during_a
    monitoring
    system
    malfunction
    or
    when
    the
    system
    undergoes
    maintenance);
    or
    2)
    The
    results
    of
    the
    mercury
    analysis
    for
    the
    paired
    sorbent
    traps
    are
    missing
    or
    invalid
    (as
    determined
    using
    the
    quality
    assurance
    procedures
    in
    Exhibit
    D
    to
    this
    Appendix).
    The
    missing
    data
    period
    begins
    with
    the
    hour
    in
    which
    the
    paired
    sorbent
    traps
    for
    which
    the
    mercury
    analysis
    is
    missing
    or
    invalid
    were
    put
    into
    service.
    The.-missingdata-period.ends
    -at-
    the
    first
    hour in-
    which
    valid
    mercury
    concentration
    data
    are
    obtained
    with
    another
    pair
    of
    sorbent
    traps (i.e.,
    the
    hour
    at
    27

    whichthis
    pair’oftràps
    wasp1acedin
    servie}
    orwith
    acertified
    backup
    mercury
    CEMS,
    reference
    method, or
    approved
    alternative
    monitoring
    systeim
    c)
    Following
    initial
    certification
    of
    thesorbent
    trapmonitoringsystem,
    begin
    reporting
    the
    percent
    monitor
    data
    availability
    in
    accordance
    with
    Section 1.8
    of
    this
    Appendix.
    Section 1.10
    Monitoring
    plan
    a)
    The
    owner
    or
    operator
    of an
    affected
    unit
    must
    prepare and
    maintain
    a
    mercury
    emissions
    monitoring
    plan.
    b)
    Whenever
    the
    owner
    or
    operator
    makes
    a
    replacement,
    modification,
    or
    change
    in
    the
    certified
    CEMS.
    including
    a
    change
    in
    the
    automated data
    acquisition
    and
    handling
    system
    or
    in
    the
    flue
    gas
    handling
    system,
    that
    affects
    information
    reported
    in
    the
    monitoring
    plan
    (e.g.,
    a
    change
    to a
    serial
    number
    for
    a
    component
    of
    a monitoring
    system),
    then
    the
    owner
    or
    operator must
    update
    the
    monitoring
    plan,
    by
    the
    applicable
    deadline
    specified
    in
    40
    CFR
    75.62,
    incorporated
    by
    reference
    in
    Section
    225.140,
    or
    elsewhere
    in
    this
    Appendix.
    c)
    Contents
    of
    monitoring
    plan
    for
    specific
    situations.
    The
    following
    additional
    information
    must
    be
    included
    in the
    monitoring
    plan
    for
    the
    specific
    situations
    described.
    For
    each
    monitoring
    system
    recertification,
    maintenance,
    or
    other
    event,
    the
    designated
    representative
    must
    include
    the
    following
    additional
    information
    in
    electronic
    format
    in
    the
    monitoring
    plan:
    1)
    Component/system
    identification
    code;
    2)
    Event
    code
    or
    code
    for
    required
    test;
    3)
    Event begin
    date
    and
    hour;
    4)
    Conditionally
    valid
    data
    period
    begin
    date
    and
    hour
    (if
    applicable);
    5)
    Date
    and
    hour
    that
    last
    test
    is
    successfully
    completed:
    and
    6)
    Indicator
    of
    whether
    conditionally
    valid
    data
    were
    reported
    at
    the
    end
    of
    the
    quarter.
    d)
    Contents of
    the
    mercury
    monitoring
    plan.
    The
    requirements
    of
    paragraph
    (d)
    of
    this
    Section must
    be
    met
    on
    and
    after
    July
    1,
    2009.
    Each
    monitoring
    plan
    must
    contain
    the
    information
    in
    paragraph
    (d)(1)
    of
    this
    Section
    in
    electronic
    format
    and
    the
    information
    in
    paragraph
    (d)(2)
    of
    this
    Section
    in
    hardcopy
    format.
    Electronic
    storage
    of
    all
    monitoring
    28

    plan
    i
    permissible
    prOvided
    that’
    a
    paper
    copy
    of
    the
    information
    can
    be
    furnished
    upon
    request
    for
    audit
    vurposes.
    1)
    Electronic::
    A)
    The
    fäcilityORISPL number
    developed
    by
    the
    Department
    of
    Energy
    and
    used
    in
    the
    National
    Allowance
    Data
    Base
    (or
    equivalent
    facility
    ID
    number
    assigned
    by
    USEPA,
    if
    the
    facility
    does
    not
    have
    an
    ORISPL
    number).
    Also
    provide
    the
    following
    information
    for
    each
    unit
    and
    (as
    applicable)
    for
    each
    common
    stack;
    and/or
    pipe,
    and
    each
    multiple
    stack
    and/or
    pipe
    involve4
    in the
    monitoring
    plan:
    i)
    A
    representation
    of
    the
    exhaust
    configuration
    for
    the
    units
    in
    the
    monitoring
    plan.
    Provide
    the
    ID
    number
    of
    each
    unit
    and
    assign
    a
    unique
    ID
    number
    to
    each
    common
    stack, common
    pipe,
    multiple
    stack,
    and/or
    multiple
    pipe
    associated
    with
    the
    unit(s)
    represented
    inthe
    monitoring
    plan:
    For
    common
    and
    multiple
    stacks
    and/or
    pipes,
    provide
    the
    activation
    date
    and
    deactivation
    date
    (if
    applicable)
    of
    each
    stack
    and/or
    pipe
    ii)
    Identification
    of
    the
    monitoring
    system
    location(s)
    (e.g.,
    at
    the
    unit-
    level
    4
    on
    the
    common
    stack,
    at
    each
    multiple
    stack,
    etc.).
    Provide
    an
    indicator
    (“flag”)
    if
    the
    monitoring
    location
    is
    at a
    bypass stack
    or
    in
    the
    ductwork
    (breeching);
    iii)
    The
    stack
    exit
    height
    (ft)
    above
    ground level
    and
    ground
    level
    elevation
    above
    sea
    level,
    and
    the
    inside
    cross-sectional
    area
    (ft
    2
    )
    at
    the
    flue
    exit
    and
    at the
    flow
    monitoring
    location
    (for
    units
    with
    flow
    monitors,
    only).
    Also
    use
    appropriate
    codes
    to
    indicate
    the
    material(s)
    of
    construction
    and
    the
    shape(s)
    of
    the
    stack
    or
    duct
    cross-section(s)
    at
    the
    flue
    exit
    and
    (if
    applicable)
    at
    the
    flow
    monitor
    location;
    iv)
    The
    type(s)
    of
    fuel(s)
    fired
    by
    each
    unit.
    Indicate
    the
    start
    and
    (if
    applicable)
    end
    date
    of
    combustion
    for
    each
    type
    of
    fuel,
    and
    whether
    the
    fuel
    is
    the
    primary,
    secondary,
    emergency,
    or
    startup
    v)
    The
    type(s)
    of
    emission
    controls
    that
    are
    used
    to
    reduce
    mercury
    emissions
    from
    each
    unit.
    Also
    provide
    the
    installation
    date,
    optimization.
    date,
    and
    retirement
    date
    (if
    applicable)
    of
    the
    emission
    controls,
    and
    indicate
    whether the
    controls
    are
    an
    original
    29

    installätibm
    and
    vi)
    Maximum
    hourly
    heat
    input
    capacity
    of eachunit.
    B)
    For
    each
    monitored
    parameter
    (i.e.,
    mercury
    concentration,
    diluent
    concentration,
    or
    flow)
    at
    each
    monitoring
    location,
    specify
    the
    monitoring
    methodology
    for
    the
    parameter.
    If the
    unmonitored
    bypass
    stack
    approach
    is
    used
    for
    a particular
    parameter,
    indicate
    this
    by
    means
    of
    an appropriate
    code.
    Provide
    the
    activation
    date/hour, and
    deactivation
    date/hour
    (if
    applicable)
    for
    each
    monitoring
    methodology.
    C)
    For
    each
    required
    continuous emission
    monitoring
    system,
    and
    each
    sorbent
    trap
    monitoring
    system
    (as
    defined
    in Section
    225.130),
    identify
    and
    describe
    the
    major
    monitoring
    components
    in
    the
    monitoring
    system
    (e.g.,
    gas
    analyzer,
    flow
    monitor,
    moisture
    sensor,
    DAHS
    software,
    etc.).
    Other
    important
    components
    in
    the
    system
    (e.g.,
    sample
    probe,
    PLC.
    data
    logger,
    etc.)
    may
    also
    be
    represented
    in
    the
    monitoring
    plan,
    if
    necessary.
    Provide
    the
    following
    specific
    information
    about
    each
    component
    and
    monitoring
    system:
    i)
    For
    each
    required
    monitoring
    system,
    assign
    a
    unique,
    3-
    character
    alphanumeric
    identification
    code
    to
    the
    system;
    indicate
    the
    parameter
    monitored
    by
    the
    system;
    designate
    the
    system
    as a
    primary,
    redundant
    backup,
    non-redundant
    backup,
    data
    backup,
    or
    reference
    method
    backup
    system,
    as
    provided
    in
    Section
    1 .2(cflf
    this
    Appendix:
    and
    indicate
    the
    system
    activation
    date/hour
    and
    deactivation
    date/hour
    (as
    applicable).
    ii)
    For
    each
    component
    of each
    monitoring
    system
    represented
    in
    the
    monitoring
    plan,
    assign
    a unique,
    3-character
    alphanumeric
    identification
    code
    to
    the
    component;
    indicate
    the
    manufacturer,
    model
    and
    serial
    number;
    designate
    the
    component
    type;
    for
    gas
    analyzers,
    indicate
    the
    moisture
    basis
    of measurement;
    indicate
    the
    method
    of
    sample
    acquisition
    or operation,
    (e.g.,
    extractive
    pollutant
    concentration
    monitor
    or thermal
    flow
    monitor):
    and
    indicate
    the
    component
    activation
    date/hour
    and
    deactivation
    date/hour (as
    applicable).
    D)
    Explicit
    formulas,
    using
    the
    component
    and
    system
    identification
    codes
    for
    the
    primary
    monitoring
    system,
    and
    containing
    all constants
    and
    factors
    required
    to
    derive
    the
    required
    emission
    rates,
    heat
    input
    rates,
    etc.
    from
    the
    hourly
    data
    recorded
    by
    the
    monitoring
    systems.
    Formulas
    using
    the
    30

    systenT
    andcompoflentDcödës
    for
    backup’
    monitoring
    systems
    are
    required
    only
    if different
    formulas
    for.the
    same
    parameter
    are
    used
    for
    the
    primary and
    backup
    monitoring systems
    (e.g.,
    if
    the primary
    system
    measures
    pollutant
    concentration
    on.a
    differentmoisture
    basis
    from
    the
    backup
    system).
    Provide
    the
    equation number
    or
    other
    appropriate
    code
    for
    each
    emissions
    formula
    (e.g.,
    use
    code
    F-i
    if
    Equation
    F-i
    in
    Exhibit
    C
    to
    this
    Appendix
    is
    used
    to calculate
    SO,
    mass
    emissions).
    Also
    identify
    each
    emissions
    formula
    with
    a
    unique
    three
    character
    alphanumeric
    code.
    The
    formula
    effective
    start
    date/hour
    and
    inactivation
    date/hour
    (as
    applicable)
    must
    be
    included
    for
    each
    formula
    E)
    For
    each
    parameter
    monitored
    with
    CEMS, provide
    the
    following
    information:
    i)
    Measurement
    scale;
    ii)
    Maximum
    potential
    value
    (and
    method
    of
    calculation);
    iii)
    Maximum
    expected
    value
    (if
    applicable)
    and
    method
    of
    calculation;
    iv)
    Span
    value(s)
    and
    ff11-scale
    measurement
    range(s);
    v)
    Daily
    calibration
    units
    of
    measure;
    vi)
    Effective
    date/hour,
    and
    (if
    applicable)
    inactivation
    date/hour
    of
    each
    span
    value;
    vii)
    The
    default
    high
    range
    value
    (if
    applicable)
    and
    the
    maximum
    allowable
    low-range
    value
    for
    this
    option.
    F)
    If
    the monitoring
    system
    or
    excepted
    methodology
    provides
    for
    the
    use
    of
    a constant,
    assumed,
    or
    default
    value
    for
    a
    parameter
    under
    specific
    circumstances,
    then
    include
    the
    following
    information
    for
    each
    such
    value
    for
    each
    parameter:
    i)
    Identification
    of the
    parameter;
    ii)
    Default,
    maximum,
    minimum,
    or
    constant
    value,
    and
    units
    of
    measure
    for
    the
    value;
    iii)
    Purpose
    of
    the
    value:
    31

    iv)
    Indicator
    of use,
    i.e.,
    during
    controlled
    hours,
    uncontrolled
    hours,
    or all
    operating hours;
    v)
    Type
    of
    fuel;
    vi)
    Source
    of
    the
    value:
    vii)
    Value
    effective
    date and
    hour:
    viii)
    Date
    and
    hour
    value
    is no
    longer
    effective.
    (if
    applicable):
    and
    G)
    Unless
    otherwise
    specified
    in Section
    6.5.2.1
    of
    Exhibit
    A
    to
    this
    Appendix,
    for
    each
    unit
    or common
    stack
    on which
    hardware
    CEMS
    are
    installed:
    i)
    Maximum
    hourly
    gross
    load
    (in
    MW,
    rounded
    to the
    nearest
    MW,
    or steam
    load
    in 1000
    lb/hr
    (i.e.,
    klb/br),
    rounded
    to
    the
    nearest
    klb/hr,
    or thermal
    output
    in
    mmBtulhr,
    rounded
    to
    the
    nearest
    mmBtulhr), for units
    that
    produce
    electrical
    or
    thermal
    output;
    ii)
    The
    upper
    and lower
    boundaries
    of the.
    range
    of
    operation
    (as
    defined
    in
    Section
    6.5.2.1
    of Exhibit
    A to this
    Appendix),
    expressed
    in
    megawatts,
    thousands
    of lb/hr
    of
    steam,
    nimBtuJhr
    of
    thermal
    output,
    or
    fl/sec
    (as
    applicable);
    iii)
    Except
    for
    peaking
    units,
    identify
    the most
    frequently
    and
    second
    most
    frequently
    used
    load
    (or
    operating)
    levels
    (i.e.,
    low,
    mid,
    or
    high)
    in
    accordance
    with
    Section
    6.5.2.1
    of Exhibit
    A
    to
    this
    Appendix,
    expressed
    in
    megawatts,
    thousands
    of
    lb/hrof
    steam,
    mmBtulhr
    of
    thermal
    output,
    or fl/sec
    (as
    applicable);
    iv)
    An
    indicator
    of whether
    the
    second
    most
    frequently
    used
    load
    (or
    operating)
    level
    is
    designated
    as
    normal
    in Section
    6.5.2.1
    of
    Exhibit
    A
    to this
    Appendix;
    v)
    The date
    of
    the
    data
    analysis
    used
    to determine
    the
    normal
    load
    (or
    operating
    level(s)
    and
    the
    two
    most
    frequently-used
    load(or
    operating)
    levels
    (as
    applicable);
    and
    Activation and
    frfii
    dates
    and hours,
    when
    the
    maximum
    hourly
    gross
    load,
    boundaries
    of
    the
    range
    of
    operation,.normal
    vi)
    32

    load
    (or
    operatirig
    ievel()ór
    two
    most frëguenth’-used’lôad(br
    operating)
    levels
    change and
    are
    updated.
    H)
    For
    each
    unit
    for
    which
    .CEMS
    árenot
    installed,
    the
    maximum
    hourly
    gross
    load
    (in
    MW,
    rounded
    to
    the:
    nearest
    MW,
    or
    steam
    load
    in klblhr,
    rounded
    to the
    nearest
    klblhr,
    or
    steam
    load
    in
    mmBtu/hr,
    rounded
    to
    the
    nearest
    nmiBtu!hr):
    I)
    For
    each
    unit
    with
    a flow
    monitor
    installed
    on
    a
    rectangular
    stack
    or
    duct,
    if a
    wall
    effects
    ad
    justment
    factor
    (WAF)
    is
    determined
    and
    applied to
    the
    hourly
    flow
    rate
    data:
    i)
    Stack
    or
    duct
    width
    at
    the
    test
    location,
    fi;
    ii)
    Stack
    or
    duct
    depth
    at
    the
    test
    location,
    ft;
    iii)
    Wall
    effects
    adjustment
    factor
    (WAF),to
    the
    nearest
    0.0001:
    iv)
    Method
    of
    determining
    the
    WAF:
    v)
    WAF
    Effective
    date
    and
    hour:
    vi)
    WAF
    no
    longer
    effective
    date
    and
    hour
    (if
    applicable):
    vii)
    WAF
    determination
    date:
    viii)
    Number
    of
    WAF
    test
    runs:
    ix)
    Number
    of Method
    1
    traverse
    points
    in
    the
    WAF
    test:
    x)
    Number
    of
    test
    ports
    in the
    WAF
    test:
    and
    xi)
    Number
    of
    Method
    1 traverse
    points
    in
    the
    reference
    flow
    RATA.
    2)
    Hardcopy
    A)
    Information,
    including
    (as
    applicable):
    Identification
    of
    the
    test
    strategyj
    protocol
    for
    the
    relative
    accuracy
    test
    audit:
    other
    relevant
    test
    information:
    calibration
    gas
    levels
    (percent
    of
    span)
    for
    the
    calibration
    error
    test
    and
    linearity
    check
    and
    span:
    and
    apportionment
    strategies
    under
    Sections
    1.2
    and
    1.3
    of
    this
    Appendix.
    33

    B)
    Description
    of
    site
    locations
    for
    each
    monitoring
    component
    in
    the
    continuous
    emission
    monitoring
    systems,
    including
    sQhematic
    diagrams
    and
    ngineering
    drawings
    specified
    in 40
    CFR
    75.53(e)(2)(iv)
    and
    (e)(2)(v),
    incorporated
    by
    reference
    in Section
    225.140,
    and
    any
    other
    documentation
    that
    demonstrates
    each
    monitor
    location
    meets
    the
    appropriate
    siting
    criteria.
    C)
    A
    data
    flow
    diagram
    denoting
    the
    complete
    information
    handling
    path
    from
    output
    signals
    of
    CEMS
    components
    to
    final
    reports.
    D)
    For
    upits
    monitored
    by
    a
    continuous
    emission
    monitoring
    system,
    a
    schematic
    diagram
    identifying
    entire
    gas
    handling
    system
    from
    boiler
    to
    stack
    for
    all
    affected
    units,
    using
    identification
    numbers
    for
    units,
    monitoring
    systems
    and
    components,
    and
    stacks corresponding
    to
    the
    identification
    numbers
    provided
    in paragraphs
    (d)(1)(A)
    and
    (d)(l)(C)
    of
    this
    Section. The
    schematic
    diagram
    must
    depict
    stack
    height
    and
    the
    height
    of any
    monitor
    locations.
    Comprehensive
    and/or
    separate
    schematic
    diagrams
    must
    be
    used
    to
    describe
    groups
    of
    units
    using
    a
    common
    stack.
    E)
    For
    units
    monitored
    by
    a continuous
    emission
    monitoring
    system,
    stack
    and
    duct
    engineering
    diagrams
    showing
    the
    dimensions
    and
    location
    of
    fans,
    turning
    vanes,
    air
    preheaters,
    monitor
    components,
    probes,.
    reference
    method
    sampling
    ports,
    and
    other
    equipment
    that
    affects
    the
    monitoring
    system
    location,
    performance,
    or
    quality
    control
    checks.
    Section 1.11
    General
    recordkeeping
    provisions
    The
    owner
    or
    operator
    must
    meet all
    of
    the
    applicable
    recordkeeping
    requirements
    of
    Section
    225.290 and
    of
    this
    Section.
    a)
    Recordkeeping
    requirements
    for
    affected
    sources.
    The
    owner
    or
    operator
    of
    any
    affected
    source
    subject
    to
    the
    requirements
    of
    this
    Appendix
    must
    maintain
    for
    each
    affected
    unit
    a
    file
    of
    all
    measurements,
    data,
    reports,
    and
    other information
    required
    by
    Part
    225,
    Subpart
    B
    at
    the
    source
    in
    a
    form
    suitable
    for
    inspection
    for
    at
    least
    three
    (3)
    years
    from
    the
    date
    of each
    record.
    The
    file
    must
    contain
    the
    following
    information:
    1)
    The
    data
    and
    information
    required
    in
    paragraphs
    (b)through
    (h)
    of
    this
    Section,
    beginning
    with
    the
    earlier
    ofthedate
    of provisional
    certification
    or
    July
    1,
    2009;
    2)
    The
    supporting
    data
    and
    information
    used
    to
    calculate
    values required
    in
    paragraphs
    (b)
    through
    (g)
    of this
    Section.
    excluding
    the
    subhourly
    data
    points
    used
    to
    compute
    hourly
    averages
    under
    Section
    1.2(c)
    of
    this
    Appendix,
    beginning
    34

    with
    the
    earin’r’offfiëdàteof’mvjsibnaf
    certification
    or
    July
    1, 2009;
    3)
    the
    data
    and information
    required
    in
    Section
    1.12
    of this
    Appendix.
    for
    spëci&
    situations,
    beginning
    with
    the
    earlierof
    thedate
    ofprovisional
    certification
    or
    July
    1.2009;
    4)
    The
    certification
    test
    data
    and
    information
    required
    in
    Section
    1.13
    of
    this
    Appendix
    for tests
    required
    under
    Section
    1.4
    of
    this
    Appendix,
    beginning
    with
    the
    date
    of the
    first
    certification
    test
    performed,
    the quality
    assurance
    and
    quality
    control
    data
    and
    informationrequired
    in
    Section
    1.13
    of
    this
    Appendix
    for
    tests,
    and
    the
    quality
    assurance/quality
    control
    plan
    required
    under
    Section
    1.5
    of
    this
    Appendix
    and
    Exhibit
    B
    to
    this Appendix,
    beginning
    with
    the
    date
    of
    provisional
    certification;
    5)
    The
    current
    monitoring
    plan
    as
    specified
    in Section
    1.10
    of
    this
    Appendix,
    beginning
    with
    the
    initial
    submission
    required
    by
    40 CFR
    75.62,
    incorporated
    by
    reference
    in Section
    225.140;
    and
    6)
    The
    quality
    control
    plan
    as
    described
    in Section
    1 of Exhibit
    B
    to
    this
    Appendix,
    beginning with
    the
    date
    of provisional
    certification.
    b)
    Operating
    parameter
    record
    provisions.
    The
    owner
    or operator
    must
    record
    for
    each
    hour
    the
    following
    information
    on
    unit operating
    time,
    heat
    input
    rate,
    and
    load,
    separately,
    for
    each
    affected
    unit
    and
    also
    for
    each
    group
    of
    units
    utilizing
    a common
    stack
    and
    a
    common
    monitoring
    system:
    1)
    Date
    and
    hour;
    2)
    Unit
    operating
    time
    (rounded
    up
    to the
    nearest
    fraction
    of
    an hour
    (in
    equal
    increments
    that
    can
    range
    from
    one
    hundredth
    to
    one quarter
    of an
    hour,
    at the
    option
    of
    the
    owner
    or
    operator));
    3)
    Hourly
    gross
    unit
    load
    (rounded to
    nearest
    MWge)
    4)
    Steam
    load
    in 1000
    lbs/hr
    at stated
    temperatures
    and
    pressures,
    rounded
    to the
    nearest 1000
    lbs/hr.
    5)
    Operating load
    range
    corresponding
    to hourly
    gross
    loadof
    1 to 10,
    except
    for
    units
    using
    a common
    stack,
    which
    may
    use up
    to 20
    load
    ranges
    for
    stack
    or
    fuel
    flow,
    as
    specified
    in the
    monitoring
    plan;
    6’
    Hourly
    heat
    inrmt
    rate
    (mmBtu/hr
    rounded
    to
    the nearest
    tenth’r
    35

    7):
    Identification code
    for
    formula
    used
    for heat
    input,
    as
    provided
    imSection
    1 10
    of
    this
    Appendix;
    and
    8)
    For
    Mercury
    CEMS
    units
    only,
    F-factor
    for
    heat
    input
    calculation
    and
    indication
    of
    whether
    the
    diluent
    cap
    was
    used
    for
    heat
    input
    calàulations
    for
    the
    hour.
    c)
    Diluent
    record
    provisions.
    The
    owner
    or
    operator
    of
    a unit
    using
    a
    flow
    monitor
    and
    an
    Q2
    diluent
    monitor
    to determine
    heat
    input,
    in
    accordance
    with
    EguationF-
    17 or
    F-I
    8
    of
    Exhibit
    C
    to
    this
    Appendix,
    or
    a
    unit
    that
    accounts
    for heat
    input
    using
    a
    flow
    monitor
    and
    a
    CO
    2
    diluent
    monitor
    (which
    is
    used
    only
    for
    heat
    input
    determination
    and
    is
    not
    used
    as
    a
    CO
    2
    pollutant
    concentration
    monitor)
    must
    keep
    the
    following
    records
    for
    the
    Q2
    or
    CO
    2
    diluent
    monitor:
    1)
    Component-system
    identification
    code,
    as
    provided
    in
    Section
    1.10
    of
    this
    Appendix;
    2)
    Date
    and
    hour;
    3)
    Hourly
    average
    diluent
    gas
    (O
    or
    C0
    2
    )
    concentration
    (in
    percent,
    rounded
    to
    the
    nearest
    tenth);
    4)
    Percent
    monitor
    data
    availability
    for the
    diluent
    monitor
    (recorded to
    the
    nearest
    tenth
    of
    a percent),
    calculated
    pursuant
    to
    Section
    1.8 of
    this
    Appendix;
    and
    5)
    Method
    of
    determination
    code
    for
    diiuent
    gas
    (02
    or
    GO,)
    concentration
    data
    using
    Codes
    1-55,
    in
    Table
    4a
    of
    this
    Section.
    d)
    Missing
    data
    records.
    The
    owner
    or
    operatormust
    record
    the
    causes
    of
    any
    missing
    data
    periods
    and
    the
    actions
    taken
    by
    the
    owner
    or
    operator
    to correct
    such
    causes.
    e)
    Mercury emission
    record
    provisions
    (CEMS).
    The
    owner
    or operator
    must
    record
    for
    each
    hour
    the
    information
    required
    by
    this
    paragraph
    for
    each
    affected
    unit
    using
    mercury
    CEMS
    in
    combination
    with
    flow
    rate,
    and
    (in
    certain
    cases)
    moisture,
    and
    diluent
    g
    monitors,
    to
    determine
    mercury
    concentration
    and
    (if
    applicable)
    unit
    heat
    input
    under
    Part
    225,
    Subpart
    B.
    1)
    For mercury
    concentration
    during
    unit
    operation,
    as
    measured
    and
    reported
    from
    each
    certified
    primary
    monitor,
    certified
    back-up
    monitor,
    or
    other
    approved
    method
    of
    emissions
    determination:
    A)
    Component-system
    identification
    code,
    as
    provided
    in
    Section
    1.10
    of this
    36

    Appendix;
    B)
    Date
    and
    hour
    C)
    Hourly
    mercury
    concentration
    Uig/scm,
    rounded
    to
    the
    nearest
    tenth).
    For.
    a
    particular
    pair
    of
    sorbent
    traps,
    this
    will be
    the
    flow-proportional
    average
    concentration
    for
    the
    data
    collection
    period;
    D)
    Method
    ofdetermination
    for hourly
    mercury
    concentration
    using
    Codes
    1-
    55
    in Table
    4a
    of this
    Section;
    and
    E)
    The
    percent
    monitor
    data availability
    (to
    the
    nearest
    tenth
    of
    a
    percent),
    calculated
    pursuant
    to
    Section
    1.8
    of this
    Appendix.
    2)
    For flue
    gas
    moisture
    content
    during
    unit
    operation
    (if
    required),
    as
    measured
    and
    reported
    from
    each
    certified
    primary
    monitor,
    certified
    back-up
    monitor,
    or
    other
    approved
    method
    of
    emissions
    deterniination
    (except
    where
    a
    default
    moisture
    value
    is
    approved
    under
    40
    CFR
    75.66.
    incorporated
    by
    reference
    in
    Section
    225.140):
    A).
    Component-system
    identification
    code,
    as provided
    in
    Section
    1.10
    of
    this
    Appendix;
    B)
    Date
    and
    hour;
    C)
    Hourly
    average
    moisture
    content
    of
    flue.
    gas
    percent, rounded
    to
    the
    nearest
    tenth).
    If
    the
    continuous
    moisture
    monitoring
    system
    consists
    of
    wet-and
    dry-basis
    oxygen
    analyzers,
    also
    record
    both
    the
    wet-
    and
    dry-
    basis
    oxygen
    hourly
    averages
    (in
    percent
    02,
    rounded
    to the
    nearest
    tenth);
    D)
    Percent
    monitor
    data
    availability
    (recorded
    to
    the nearest
    tenth
    of
    a
    percent)
    for
    the
    moisture
    monitoring
    system,
    calculated
    pursuant to
    Section
    1.8
    of this
    Appendix;
    and
    E)
    Method
    of determination
    for hourly
    average
    moisture
    percentage,
    using
    Codes
    1-55
    in
    Table
    4a
    of
    this
    Section.
    3)
    For
    diluent
    gas
    (02
    or
    Q)
    concentration
    during
    unit
    operation
    (if
    required),
    as
    measured
    and
    reported
    from
    each
    certified
    primary
    monitor,
    certified
    back-up
    monitor,
    or
    other
    approved
    method
    of emissions
    determination:
    A)
    Component-system
    identification
    code,
    as provided
    in Section
    1.10
    of
    this
    37

    Appendix;
    Dtc
    and
    hour;
    C)
    Hourly
    average
    diluent
    gas
    (02
    or
    CO,)
    concentration
    (in
    percent.
    rounded
    to
    the
    nearest
    tenth);
    D)
    Method
    of
    determination
    code
    for
    diluent
    gas
    (02
    or
    C0
    2
    )
    concentration
    data
    using
    Codes
    1-55,
    in
    Table
    4a
    of this
    Section;
    and
    The.
    percent
    mnnitnr
    v1hi1ity
    (to
    the
    nearest
    tenth
    of
    a
    percent)
    for
    the
    02
    or
    CO,
    monitoring
    system
    (if
    a
    separate
    02
    or
    CO
    2
    monitoring
    system
    is used
    for
    heat
    input
    determination),
    calculated
    pursuant
    to
    Section
    1.8
    of
    this
    Appendix.
    4)
    For
    stack
    gas
    volumetric
    flow
    rate
    during
    unit
    operation,
    as measured
    and
    reported
    from
    each
    certified primary
    monitor,
    certified
    back-up
    monitor,
    or
    other
    approved
    method
    of
    emissions
    determination,
    record
    the
    information
    required
    under
    40
    CFR
    75.57(c)(2)(i)
    through
    (c)(2)(vi),
    incorporated
    by
    reference
    in
    Section
    225.140.
    5)
    For
    mercury
    mass
    emissions
    during
    unit
    operation,
    as
    measured
    and
    reported
    from
    the
    certified
    primary
    monitoring
    system(s),
    certified redundant
    or
    non-redundant
    back-up
    monitoring
    system(s),
    or
    other
    approved
    method(s) of
    emissions
    determination:
    A)
    Date
    and
    hour;
    B)
    Hourly
    mercury
    mass
    emissions
    (ounces,
    rounded
    to
    three
    decimal
    places);
    Tthrntifirtinn
    cofor
    miccicrn
    ftwmu1
    used
    to
    derive
    hourly
    mercury
    mass
    emissions
    from
    mercury
    concentration,
    flow
    rate
    and
    moisture
    data,
    as
    provided
    in
    Section 1.10
    of
    this
    Appendix.
    1)
    Mercury emission
    record
    provisions
    (sorbent
    trap
    systems).
    The
    owner
    or
    operator
    must
    record
    for
    each
    hour
    the
    information
    required
    by
    this
    paragraph,
    for
    each
    affected
    unit
    using
    sorbent
    trap
    monitoring
    systems
    in
    combination
    with
    flow
    rate,
    moisture,
    anji
    certain
    cases)
    diluent
    gas
    monitors,
    to
    determine
    mercury
    mass
    emissions
    and
    (if
    required)
    unit
    heat
    input
    under
    Part
    225.
    1)
    For
    mercury
    concentration
    during
    unit
    operation,
    as
    measured
    and
    reported
    from
    each
    certified
    primary
    monitor,
    certified
    back-up
    monitor,
    or
    other
    approved
    E.)
    C)
    38

    method
    of emissions
    determination:
    A)
    Component-system
    identification
    code, as
    provided
    in
    SectiOn
    l.1Oof
    this
    Appendix;
    B)
    Date
    and
    hour;
    C)
    Hourly
    mercury
    concentration
    (g/dscm,
    rounded
    to the
    nearest
    tenth).
    For
    a particular
    pair
    of sorbent
    traps,
    this will
    be
    the
    flow-proportional
    average
    concentration
    for the
    data
    collection
    period;
    D)
    Method
    of determination
    for
    hourly
    average
    mercury
    concentration
    using
    Codes
    1-
    55 in Table
    4a
    of
    this
    Section;
    and
    B)
    Percent
    monitor
    data availability
    (recorded
    to
    the
    nearest
    tenth
    of
    a
    percent),
    calculated
    pursuant
    to
    Section
    1.8
    of this
    Appendix;
    2)
    For
    flue
    gas
    moisture
    content
    during
    unit
    operation,
    as measured
    and
    reported
    from
    each
    certified
    primary
    monitor,
    certified
    back-up
    monitor,
    or
    other
    approved
    method
    of emissions
    determination
    (except
    where
    a
    default
    moisture
    value
    is
    approved
    under
    40 CFR
    75.66,
    incorporated
    by reference
    in Section
    225.140),
    record
    the
    information
    required
    under
    paragraphs
    (e)(2)(A)
    through
    (e)(2)(E)
    of
    this
    Section;
    3)
    For diluent
    gas
    (02
    or
    C02)
    concentration
    during
    unit operation
    (if
    required
    for
    heat
    input
    determination),
    record
    the
    information
    required
    under
    paraaphs
    (e)(3)(A)
    through
    (e)(3)(E)
    of this
    Section.
    4)
    For
    stack
    gas
    volumetric
    flow
    rate
    during
    unit
    operation,
    as
    measured
    and
    reported
    from
    each
    certifiedprimary
    monitor,
    certifiedback-up
    monitor,
    or
    other
    approved
    method
    of
    emissions
    determination,
    record
    the
    information
    required
    under
    40
    CFR
    75.57(c)(2)(i)
    through
    (c)(2)(vi),
    incorporated
    by
    reference
    in
    Section
    225.140.
    5)
    6)
    Record
    the
    average
    flow
    rate
    of
    stack
    gas
    through.
    each
    sorbent
    trap.(in
    appropriate
    units,
    e.g.,
    liters/mm,
    cc/mm,
    dscmlmin).
    For
    mercury
    mass
    emissions
    during
    unit
    operation,
    as measured
    and
    reported
    from
    the certified
    primary
    monitoring
    system(s),
    certified
    redundant
    or
    non-redundant
    back-up
    monitoring
    system(s),
    or
    other approved
    method(s)
    of
    emissions
    determination,
    record
    the
    information
    required
    under
    paragraph
    (e)(5)
    of this
    Section.
    39

    7)
    Record
    the
    gas
    flow
    meter
    reading
    (in
    dscm,
    roundedtQ
    the.nearest
    hundredth)
    at
    the
    beginning
    and
    end
    of the
    collection
    period
    and at
    least once
    in
    each
    unit
    operating
    hour
    during
    the
    collection
    period.
    -
    8)
    Calculate
    and
    record
    the
    ratio
    of the bias-adjusted
    stack
    gas flow
    rate
    to
    the
    sample
    flow rate,
    as
    described
    in
    Section
    11.2
    of
    Exhibit
    D
    to
    this
    Appendix.
    Table
    4a.--Codes
    for Method
    of Emissions
    and Flow
    Determination
    Code
    Hourly
    emissions/flow
    measurement
    or
    estimation
    method
    1
    Certified
    primary
    emission/flow
    monitoring
    system.
    2
    Certified
    backup
    emission/flow
    monitoring
    system.
    3
    Approved
    alternative
    monitoring
    system.
    4
    Reference
    method:
    17 ....
    Like-kind
    replacement
    non-redundant
    backup
    analyzer.
    32
    .... Hourly
    Hg
    concentration
    determined
    from
    analysis
    of
    a single
    trap
    multiplied
    by a
    factor of
    1.111
    when
    one
    of the
    paired
    traps
    is
    invalidated
    or damaged
    (See
    Appendix
    K, section
    8).
    33
    ....
    Hourly
    Hg concentration
    determined
    from
    the
    trap resulting
    in the
    higher
    Hg
    concentration
    when
    the
    relative
    deviation
    criterion
    for the
    paired
    traps
    is not
    met
    (See
    Appendix
    K, section
    8).
    40
    ....
    Fuel specific
    default
    value
    (or
    prorated
    default
    value)
    used
    for
    the
    hour.
    54
    .... Other
    quality
    assured
    methodologies
    approved
    through
    petition.
    These
    hours
    are included
    in
    missing
    data
    lookback
    and
    are treated
    as
    unavailable
    hours for
    percent
    monitor
    availability
    calculations.
    55
    ....
    Other substitute
    data approved
    through
    petition.
    These
    hours
    are
    not
    included
    in
    missing
    data
    lookback
    and
    are treated
    as unavailable
    hours
    for percent
    monitor
    availability
    calculations.
    Section
    1.12
    General
    recordkeepin
    provisions
    for specific
    situations
    The
    owner
    or
    operator
    must
    meet
    all of
    the applicable
    recordkeeping
    requirements
    of this
    Section.
    Tn
    accordance
    with
    40
    CFR
    75.34,
    incorporated
    by
    reference
    in
    Section
    225.140,
    the owner
    or
    operator
    of
    an
    affected
    unit
    with
    add-on
    emission
    controls
    must record
    the
    applicable
    information
    in this
    Section
    for
    each
    hour
    of
    missing
    mercury
    concentration
    data.
    Except
    as
    otherwise
    provided
    in 40
    CFR
    75
    .
    3
    4fçfl
    1
    incorporated
    by
    reference.in
    Section225.140,
    for
    units
    with
    add-on
    mercury
    emission
    controls,
    the
    owner
    or
    operator
    must
    record:
    40

    a)
    Parametric
    data
    which
    demonstrate,
    for
    each
    hour
    of
    missing
    mercury
    emission
    data,
    the..
    proper
    operation
    of the
    add-on
    emission
    controls,
    as
    described
    in
    the quality
    assurance/quality
    control
    program
    for
    the
    unit.
    The
    parametric
    data
    must
    be
    maintained
    on
    site
    and
    must.
    be
    submitted,.
    upon
    request,
    to the
    Agency.
    Alternatively,
    for
    units
    equipped
    with
    flue
    gas desulfurization (FGD)
    systems,
    the
    owner
    or
    operator
    may
    use
    quality-assured
    data
    from a
    certified
    SO
    2
    monitor
    to demonstrate
    proper
    operation
    of
    the
    emission
    controls
    during
    periods
    of
    missing
    mercury
    data;
    b)
    A
    flag indicating,
    for each
    hour
    of
    missing
    mercury
    emission
    data,
    either
    that the
    add-on
    emission
    controls
    are operating
    properly,
    as evidenced
    by
    all
    parameters
    being within
    the
    ranges
    specified
    in the
    quality
    assurance/quality
    control
    program,
    or
    that
    the
    add-on
    emission
    controls
    are not
    operating
    properly.
    Section
    1.13
    Certification,
    quality
    assurance,
    and
    quality
    control
    record
    provisions
    The
    owner
    or
    operator
    mustmeet
    all
    of the
    pplicable
    recordkeepingrequirements
    of this
    Section.
    a)
    Continuous emission
    monitoring
    systems.
    The owner
    or
    operator
    must
    record
    the
    applicable
    information
    in this
    Section
    for
    each
    certified
    monitor
    or certified
    monitoring
    system
    (including
    certified
    backup
    monitors)
    measuring
    and
    recording
    emissions
    or
    flow
    from
    an
    affected
    unit.
    1)
    For each
    flow
    monitor,
    mercury
    monitor,
    or
    diluent
    gas monitor
    (including
    wet-
    and
    dry-basis
    0,
    monitors
    used
    to
    determine
    percent
    moisture),
    the
    owner
    or
    operator
    must
    record
    the
    following
    for
    all daily
    and
    7-day
    calibration
    error
    tests,
    all daily
    system
    integrity
    checks,
    and
    all off-line
    calibration
    demonstrations,
    including
    any follow-up
    tests
    after corrective
    action:
    A)
    Component-system
    identification
    code
    (on
    and
    after
    January
    1,
    2009,
    only
    the
    component
    identification
    code
    is
    required);
    B)
    Instrument
    span
    and
    span
    scale;
    C)
    Date
    and
    hour;
    D)
    Reference
    value
    (i.e.,
    calibration
    gas
    concentration
    or
    reference
    signal
    value,
    in
    ppm or
    other appropriate
    units);
    E)
    Observed
    value
    (monitor
    response
    during
    calibration,
    in
    ppm
    or
    other
    appropriate
    units);..
    41

    F)
    Percent calibration
    error
    (rounded
    to the nearest
    tenth of a
    percent)
    (flag
    if
    using
    alternative
    performance specification
    for
    low
    emitters or
    differential
    pressure
    flowmànitors);
    G)
    Reference signal or calibration
    gas
    level;
    H)
    For
    7-day
    calibration
    error
    tests, a test number
    and
    reason
    for test;
    I)
    For
    7-day calibration
    tests for certification
    or recertification,
    a
    certification
    from
    the
    cylinder
    gas vendor
    or
    CEMS
    vendor
    that calibration
    gas,
    as
    defined
    in 40.
    CFR 72.2, incoiorated
    by reference
    in Section
    225.140,
    and
    Exhibit
    A to this Appendix,
    was
    used
    to conduct calibration
    error
    testing;
    J)
    Description
    of any
    adjustments, corrective
    actions,
    or
    maintenance
    prior
    to
    a passed test
    or
    following
    a failed test; and
    K)
    Indication
    of
    whether
    the unit is off-line
    or on-line.
    2)
    For
    each flow monitor, the
    owner
    or operator
    must record
    the following
    for
    all
    daily interference
    checks,
    including any follow-up
    tests after
    corrective
    action.
    A)
    Component-system
    identification
    code
    (after
    January
    1, 2009,
    only
    the
    component
    identification
    code is
    required);
    B)
    Date
    and
    hour;
    C)
    Code indicating whether
    monitor
    passes
    or fails the
    interference
    check;
    and
    D)
    Description
    of
    any
    adjustments,
    corrective
    actions,
    or
    maintenance
    prior
    to
    a
    passed
    test or following
    a failed test.
    3)
    For
    each mercury concentration
    monitor,
    or diluent gas
    monitor (including
    wet-
    and
    dry-basis
    O2monitors
    used to determine percent
    moisture),
    the
    owner
    or
    operator must
    record the following
    for the initial
    and all subsequent
    linearity
    check(s)
    and
    3-level
    system integrity
    checks
    (mercury
    monitors with
    converters,
    only),
    including any
    follow-up tests after corrective
    action:
    A)
    Component-system
    identification
    code
    (on
    and after
    July 1, 2009,
    only
    the
    component
    identification
    code is required);
    42

    B)
    Jnstrument
    span
    and span
    scale
    (only
    span
    scale is required
    on
    and
    after
    July
    1,
    2009);
    C)
    Calibration
    gas level;
    D)
    Date
    and time
    (hour
    and
    minute)
    of each
    gas
    injection
    at
    each
    calibration
    gas level;
    E)
    Reference
    value•
    (i.e.,
    reference
    gas concentration
    for each
    gas
    injecticn
    at
    each
    calibration
    gas
    level,
    in
    ppm
    or other
    appropriate
    units);
    F)
    Observed
    value
    (monitor
    response
    to each
    reference
    gas
    injection
    at
    each
    calibration
    gas level,
    in ppm
    or
    other
    appropriate
    units);
    G)
    Mean
    of reference
    values
    and mean
    of
    measured
    values
    at
    each
    calibration
    gas
    level;
    H)
    Linearity
    error at
    each of the
    reference
    gas concentrations
    (rounded
    to
    nearest tenth
    of a
    percent)
    (flag
    if using
    alternative
    performance
    specification);
    I)
    Test number
    and
    reason
    for
    test (flag
    if aborted
    test);
    and
    J)
    Description
    of any adjustments,
    corrective
    action, or
    maintenance
    prior
    to
    a p.assed
    test
    or
    following
    a failed
    test.
    4)
    For each
    differential
    pressure
    type flow
    monitor,
    the owner
    or
    operator
    must
    record
    items
    in
    paragraphs
    (a)(4)(A)
    through
    (E)
    of
    this Section,
    for
    all
    quarterly
    leak
    checks, including
    any
    follow-up
    tests after
    corrective
    action.
    For
    each
    flow
    monitor,
    the owner
    or operator
    must
    record
    items
    in
    paragraphs
    (a)(4)(F)
    and
    (G)
    of
    this Section
    for
    all flow-to-load
    ratio
    and
    gross
    heat
    rate tests:
    A)
    Component-system
    identification
    code
    (on
    and after
    July 1,
    2009,
    only
    the
    system
    identification
    code
    is required).
    B)
    Date and
    hour.
    C)
    Reason
    for
    test.
    D)
    Code indicating
    whether
    monitor
    passes
    or fails
    the
    quarterly
    leak
    check.
    43

    B)
    Description
    of any
    adjustments,
    corrective
    actions, or
    maintenance
    prior
    to
    a
    passed
    test.
    or
    following a
    failed
    test.
    F)
    Test
    data from the
    flow-to-load
    ratio or gross heat rate
    (GHR) evaluation,
    including:
    i)
    Monitoring
    system
    identification
    code:
    ii)
    Calendar
    year
    and
    quarter:
    iii)
    Indication
    of whether the
    test is a flow-to-load
    ratio or
    gross
    heat
    rate evaluation;
    iv)
    Indication
    of
    whether
    bias
    adjusted flow rates were
    used;
    v)
    Average absolute
    percent
    difference
    between
    reference
    ratio
    (or
    GHR)
    andhourly
    ratios (or GHR
    values);
    vi)
    Test
    rejj
    vii)
    Number
    of hours
    used in final quarterly
    average;
    viii)
    Number of
    hours
    exempted
    for use
    of a different fuel
    type:
    ix)
    Number of hours exempted
    for
    load ramping
    up
    or down;
    x)
    Number
    of hours exempted
    for scrubber
    bypass;
    xi)
    Number
    of hours exempted
    for hours
    preceding
    a
    normal-load
    flow
    RATA;
    xii)
    Number
    of hours exempted
    for hours preceding
    a
    successful
    diagnostic
    test, following a
    documented
    monitor repair
    or
    major
    component
    replacement;
    xiii)
    Number
    of hours excluded
    for
    flue gases
    discharging
    simultaneously
    thorough
    a main
    stack
    and a bypass
    stack;
    and
    xiv)
    Test number.
    G)
    Reference
    data
    for
    the flow-to-loadratio
    or gross.heat
    rate
    evaluation,
    including
    (as applicable):
    44

    i)
    Reference
    flow
    RATA
    end
    date.
    and
    time.;.
    ii)
    Test
    number
    of the
    reference
    RATA;
    iii)
    Reference
    RATA
    load
    and load
    level;
    iv)
    Average
    reference
    method
    flow rate
    during
    reference
    flow
    RATA;
    v)
    Reference.
    flow/load
    ratio;
    vi)
    Average
    reference
    method
    diluent
    gas
    concentration
    during
    flow
    RATA
    and diluent
    gas
    units
    of
    measure;
    vii)
    Fuel specific
    Fd-or
    Fe—factor
    during
    flow RATA
    and F-factor
    units
    of
    measure;
    viii)
    Reference
    gross
    heat
    rate
    value;
    ix)
    Monitoring
    system
    identification
    code;
    x)
    Average
    hourly
    heat input
    rate
    during
    RATA;
    xi)
    Average
    gross
    unit
    load;
    xii)
    Operating
    load
    level;
    and
    An indicator
    (“flw”
    -,
    if senarnte
    reference
    ratios
    are
    calculated
    for
    each
    multiple
    stack.
    5)
    For each
    flow monitor,
    each diluent
    gas
    (02
    or
    C0
    2
    )
    monitor
    used to
    determine
    heat
    input,
    each
    moisture
    monitoring
    system,
    mercury
    concentration
    monitoring
    system,
    each
    sorbent
    trap
    monitoring
    system,
    and
    each
    approved
    alternative
    monitoring
    system,
    theowner
    or operator
    must
    record
    the following
    information
    for the
    initial
    and
    all subsequent
    relative
    accuracy
    test audits:
    A)
    Reference
    method(s)
    used.
    B)
    Individual
    test
    run data
    from
    the
    relative
    accuracy
    test
    audit
    for
    the
    flow
    monitor,
    CO
    2
    emissions
    concentration
    monitor-diluent
    continuous
    emission
    monitoring
    system,
    diluent
    gas
    (02
    or
    C0
    2
    )
    monitor
    used
    to
    determine
    heat input,
    moisture
    monitoring
    system,
    mercury
    concentration
    xiii)
    45

    monitoring
    system,
    sorbenttrap
    monitoring
    system,
    or
    approved
    alternative
    monitoring
    system,
    including:
    i)
    Date,
    hour,
    and
    minute
    of
    beginning
    of
    test
    run;
    ii)
    Date,
    hour,
    and
    minute
    of
    end
    of
    test
    run;
    iii)
    Monitoring
    system
    identification
    code;
    iv)
    Test
    number
    and
    reason
    for
    test;
    v)
    Operating
    level
    (low,
    mid,
    high,
    or normal,
    as
    appropriate)
    and
    number
    of
    operating
    levels
    comprising
    test;
    vi)
    Normal
    load
    (or
    operating
    level)
    indicator
    for
    flow
    RATAs
    (except
    for
    peaking
    units);
    vii)
    Units
    of
    measure;
    viii)
    Run
    number:
    ix)
    Run
    value
    from
    CEMS
    beiun tested,
    in the
    anpronriate
    units
    of
    measure;
    x)
    Run
    value
    from
    reference
    method,
    in
    the
    appropriate
    units
    of
    measure;
    xi)
    Flag
    value
    (0.
    1, or
    9,
    as
    appropriate)
    indicating
    whether
    run
    has
    been
    used
    in
    calculating
    relative
    accuracy
    and
    bias
    values
    or
    whether
    the
    test
    was
    aborted
    prior
    to
    completion;
    xii)
    Average
    gross
    unit
    load,
    expressed
    as
    a
    total
    gross
    unit
    load,
    rounded
    to
    the
    nearest
    MWe,
    or
    as
    steam
    load,
    rounded
    to
    the
    nearest
    thousand
    lb/hr),
    except
    for
    units
    that
    do not
    produce
    electrical
    or
    thermal
    output;
    and
    xiii)
    Flag
    to
    indicate
    whether
    an
    alternative
    nerformance
    has
    been
    used.
    C)
    Calculations
    and
    tabulated
    results,
    as
    follows:
    46

    i)
    Arithmetic
    mean of
    the monitoring
    system
    measurement
    values,
    of
    the reference
    method
    values,
    and
    of
    their
    differences,
    as
    specified
    in Equation
    A—7
    in Exhibit
    A
    to
    this
    Appendix;
    ii)
    Standard
    deviation,
    as
    specified
    in
    Equation
    A—8 in
    Exhibit
    A to
    this Appendix;
    iii)
    Confidence
    coefficient,
    as
    specified
    in
    Equation
    A—9
    in
    Exhibit
    A
    to
    this
    Appendix;
    iv)
    Statistical
    “t” value
    used
    in calculations;
    v)
    Relative
    accuracy
    test results,
    as
    specified
    in Equation
    A—i
    0
    in
    Exhibit
    A to
    this
    Appendix.
    For multi-level
    flow
    monitor
    tests
    the
    relative
    accuracy
    test
    results
    must
    be
    recorded
    at
    each load
    (or
    operating)
    level tested.
    Each
    load
    (or
    operating)
    level
    must
    be
    expressed
    as
    a total
    gross
    unit
    load,
    rounded
    to
    the nearest
    MWe,
    or
    as steam
    load,
    rounded
    to
    the nearest
    thousand
    lb/hr,
    or as
    otherwise
    specified
    by
    the
    Agency,
    for
    units that
    do
    not
    produce
    electrical
    or
    thermal
    output;
    vi)
    Bias
    test
    results
    as specified
    in
    Section
    7.4.4.in
    Exhibit
    A
    to
    this
    Appendix;
    and
    D)
    Description
    of any
    adjustment,
    corrective
    action,
    or
    maintenance
    prior
    to
    a
    passed
    testor
    following
    a failed
    or aborted
    test.
    E)
    For
    flow
    monitors,
    the
    equation
    used
    to
    linearize
    the flow
    monitor
    and
    the
    numerical
    values
    of
    the polynomial
    coefficients
    or K
    factor(s)
    of
    that
    equation.
    F)
    For moisture
    monitoring
    systems,
    the coefficient
    or “K”
    factor
    or
    other
    mathematical
    algorithm
    used
    to adjust
    the
    monitoring
    system
    with
    respect
    to
    the
    reference
    method.
    6)
    For each
    mercury
    concentration
    monitor,
    and
    each
    CO
    2
    or
    02
    monitor
    used
    to
    determine
    heat
    input,
    the
    owner
    or
    operator
    must
    record
    the following
    information
    for
    the
    cycle
    time
    test:
    A)
    Component-system
    identification
    code
    (on
    and
    after
    July
    1, 2009,
    only
    the
    component
    identificationcode
    is req
    uired):
    47

    B)
    Date;
    C)
    Start
    and
    end
    times:
    D)
    Upscale
    and downscale
    cycle
    times for each component;
    E)
    Stable start monitor value;
    F)
    Stable end
    monitor
    value;
    G)
    Reference
    value of calibration
    as(es):
    H)
    Calibration
    gas
    level;
    I)
    Total cycle time;
    J)
    Reason fortest;
    and
    K)
    Test number.
    7)
    In
    addition
    to
    the
    information in paragraph
    (a)(5)
    of this Section,
    the
    owner
    or
    ppcrator must record, for each
    relative accuracy test
    audit, supporting
    information
    sufficient
    to
    substantiate
    compliance
    with
    all
    applicable
    sections
    and appendices
    in thispart. Unless otherwise
    specified
    in this part or in an
    applicable
    test
    method,
    the
    information in paragraphs
    (a)(7)(A)
    through
    (a)(7)(H)
    of this
    Section
    may
    be
    recorded
    either
    in.
    hard
    copy format,
    electronic format or. a
    combination
    of
    the
    two, and the owner or operator
    must maintain this information
    in a
    format
    suitable
    for inspection and audit purposes.
    This RATA supporting
    information
    must
    include, but must not
    be limited to. the following
    data elements:
    A)
    For each RATA
    using
    Reference Method 2
    (or
    its allowable
    alternatives)
    in
    appendix
    A to 40 CFR
    60,
    incorporated
    by reference
    in Section
    225.140,
    to determine volumetric
    flow rate:
    i)
    Information
    indicating whether
    or not the location
    meets
    requirements
    of Method 1 in appendix
    A to 40 CFR
    60,
    incorporated
    by reference
    in Section
    225.140;
    and
    ii)
    Information
    indicating whether
    or not the equipment
    passed
    the
    required leak checks.
    48

    B)
    For
    each run
    ofeach
    RATA
    using
    Reference
    Method
    2
    (or
    its
    allowable
    alternatives
    in
    appendix
    A to 40 CFR.60,
    incooratedby
    reference
    in
    Section
    225.
    140)to
    deterniine
    volumetric
    flow
    rate,
    record the
    following
    data
    elements
    (as
    applicable
    to the
    measurement
    method
    used):
    i)
    Operating
    level
    (low,
    mid, high,
    or normal,
    as
    appropriate)
    ii)
    Number
    of reference
    method
    traverse
    points;
    iii)
    Average
    stack gas
    temperature
    (°F);
    iv)
    Barometric
    pressure
    at test port
    (inches
    of
    mercury);
    v)
    Stack static
    pressure
    (inches
    of H
    2
    Q)j
    vi)
    Absolute
    stack gas pressure
    (inches
    of
    mercury);
    vii)
    Percent
    CO
    2
    and
    O2in
    the
    stack gas,
    dry basis;
    viii)
    CO, and Oreference
    method
    used;
    ix)
    Moisture
    content
    of stack
    gas
    (percent
    H2
    Q)j
    x)
    Molecular
    weight
    of
    stack gas,
    dry basis (lb/lb-mole);
    xi).
    Molecular
    weight
    of stack
    gas, wet
    basis
    (lb/lb-mole);
    xii)
    Stack
    diameter
    (or
    equivalent
    diameter)
    at the test
    port
    (ft);
    xiii)
    Average
    square root
    of velocity
    head
    of
    stack
    gas
    (inches
    of
    H
    2)
    forthe
    run;
    xiv)
    Stack
    or
    duct
    cross-sectional
    area at
    test
    port
    (ft
    2
    );
    xv)
    Average
    velocity
    (ft/see):
    xvi)
    Average
    stack flow
    rate,
    adjusted,
    if applicable,
    for wall
    effects
    (seth,
    wet
    basis);
    xvii)
    Flow rate
    reference
    method
    used;
    xviii)
    Average
    velocity,
    adjusted
    for
    wall effects
    49

    xix)
    Calculated
    site-specifi’c)
    wall
    éffêcts
    adjustment
    factor
    determined
    during
    the
    run, and, if
    different, the
    wall
    effects
    adjustment
    factor
    used
    in the calculations;
    and
    xx)
    Default wall
    effects
    adiustment
    factor
    used.
    C)
    For
    each traverse
    point
    of each
    run of
    each RATA
    using
    Reference
    Method
    2
    (or
    its allowable
    alternatives
    in appendix
    A
    to 40
    CFR
    60,
    incorporated
    by
    reference
    in
    Section
    225.140)
    to
    determine
    volumetric
    flow
    rate,
    record the
    following
    data
    elements
    (as applicable
    to
    the
    measurement
    method
    used):
    i)
    Reference
    method
    probe
    type;
    ii)
    Pressure
    measurement
    device
    type;
    iii)
    Traverse
    point ID;
    iv)
    Probe or
    pitot
    tube
    calibration
    coefficient;
    v)
    Date
    of latest
    probe or
    pitot
    tube
    calibration;.
    vi)
    Average
    velocity
    differential
    pressure
    at
    traverse
    point
    (inches
    of
    O)
    or
    the
    average
    of the
    square roots
    of the
    velocity
    differential
    pressures
    at the traverse
    point
    ((inches
    of
    H
    2
    0)”
    2
    );
    vii)
    Ts,
    stack
    temperature
    at
    the traverse
    point
    (°F);
    viii)
    Composite
    (wall
    effects)
    traverse
    point
    identifier;
    ix)
    Number of
    points included
    in
    composite
    traverse
    point;
    x)
    Yaw angle
    of
    flow
    at
    traverse
    point
    (degrees);
    xi)
    Pitch
    angle
    of
    flow at traverse
    point
    (degrees);
    xii)
    Calculated
    velocity
    at traverse
    point
    both
    accounting
    and
    not
    accounting
    for wall
    effects
    (ftJsec);
    and
    xiii)
    Probe
    identification
    number.
    50

    D)
    For
    each
    RATA’
    using
    Or 3A
    in
    appendix
    A
    to
    40 CFR
    60,
    incoorated
    by
    reference
    in
    Section
    225..
    140,
    to
    determine,
    C0
    2
    ,
    orQconcentration:.
    i)
    Pollutant
    or
    diluent
    gas
    being
    measured;
    ii
    Soan
    of reference
    method
    analyzer:
    iii)
    Type
    of
    reference
    method
    system
    (e.g.,
    extractive
    or
    dilution
    type):
    iv)
    Reference
    method
    dilution
    factor
    (dilution
    type
    systems,
    only);
    v)
    Reference
    gas
    concentrations
    (zero,
    mid,
    and
    high
    gas
    levels)
    used
    for
    the 3-point
    pre-test
    analyzer
    calibration
    error
    test
    (or,
    for
    dilution
    type
    reference
    method
    systems,
    for
    the 3-point
    pre-test
    system
    calibration
    error
    test)
    and for
    any
    subsequent
    recalibrations:
    vi)
    Analyzer
    responses
    to
    the zero-,
    mid-,
    and high-level
    calibration
    gases
    during
    the
    3-point
    pre-test
    analyzer
    (or
    system)
    calibration
    error
    test
    and
    during
    any
    subsequent
    recalibration(s);
    vii)
    Analyzer
    calibration
    error
    at
    each
    gas,
    level
    (zero,
    mid,
    and
    high)
    for
    the
    3-point
    pre-test
    analyzer
    (or
    system)
    calibration
    error
    test
    and
    for any
    subsequent
    recalibration(s)
    (percent
    of
    span
    value);
    viii)
    Upscale
    gas
    concentration
    (mid
    or
    high
    gas
    level)
    used
    for
    each
    pre-run
    or postrun
    system
    bias
    check
    or.(fordilution
    type
    reference
    method
    systems)
    for each
    pre-run
    or post-run
    system
    calibration
    error
    check;
    ix)
    Analyzer
    response
    to
    the
    calibration
    gas
    for
    each
    pre-run
    or
    post-
    run
    system
    bias
    (or
    system
    calibration
    error)
    check;
    x)
    The arithmetic
    average
    of
    the
    analyzer
    responses
    to the
    zero-level
    gas,
    for
    each
    pair
    of
    pre-
    and
    post-run
    system
    bias
    (or
    system
    calibration
    error)
    checks;
    xi)
    The
    arithmetic
    average
    of the
    analyzer
    responses
    to
    the
    upscale
    calibration
    gas,
    for
    each
    pair
    of
    pre-
    and
    post-run
    system
    bias
    (or
    system
    calibration
    error)
    checks;
    51

    xii)
    The
    results
    of each
    pre-run’and
    each
    post-run
    system
    bias
    (or
    system
    calibratign
    error)
    check
    using
    the
    zero-level
    gas
    (percentage
    of span
    value);
    xiii)
    The
    results
    of
    each prerun
    and each
    post-runsystem
    bias
    (or
    system
    calibration
    error)
    check
    using
    the
    upscale
    calibration
    gas
    (percentage
    of span
    value):
    xiv)
    Calibration
    drift
    and zero
    drift
    of analyzer
    during
    each
    RATA
    run
    (percentage
    of
    span
    value);
    xv)
    Moisture
    basis
    of
    the reference
    method
    analysis:
    xvi)
    Moisture
    content
    of stack
    gas,
    in percent,
    during
    each
    test
    run
    (if
    needed
    to convert
    to moisture
    basis
    of
    CEMS
    being
    tested’);
    xvii)
    Unadjusted
    (raw)
    average
    pollutant
    or diluent
    gas
    concentration
    for
    each run;
    xviii)
    Average
    pollutant
    or diluent
    gas concentration
    for
    each
    run,
    corrected
    for
    calibration
    bias
    (or
    calibration
    error)
    and, if
    applicable,
    corrected
    for moisture;
    xix)
    The
    F-factor
    used
    to convert
    reference
    method
    data
    to units
    of
    lb/mniBtu
    (if
    applicable);
    xx)
    Date(s)
    of the
    latest
    analyzer
    interference
    test(s);
    xxi)
    Results
    of the
    latest
    analyzer
    interference
    test(s);
    xxii)
    For
    each
    calibration
    gas
    cylinder
    used
    during
    each
    RATA.
    record
    the
    cylinder
    gas
    vendor,
    cylinder
    number,
    expiration
    date,
    pollutant(s)
    in
    the
    cylinder,
    and certified
    gas
    concentration(s).
    E)
    For each
    test
    run of
    each
    moisture
    determination
    using
    Method
    4
    in
    appendix
    A to 40
    CFR
    60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    (or
    its
    allowable
    alternatives),
    whether
    the
    determination
    is
    made
    to
    support
    a
    gas
    RATA,
    to
    support
    a flow
    RATA,
    or
    to
    quality
    assure
    the
    data
    from
    a continuous
    moisture
    monitoring
    system,
    record
    the
    following
    data
    elements
    (as
    applicable
    to
    the moisture
    measurement
    method
    uçç
    i)
    Test
    number:
    52

    ii).
    Run
    number;
    iii)
    The
    beginning
    date, hour.
    and
    minute
    of
    the
    run;
    iv)
    The
    ending
    date,
    hour,
    and
    minute
    of
    the
    run;
    v)
    Unit
    operating
    level
    (low,
    mid,
    high,
    or
    normal,
    as
    appropriatç)j
    vi)
    Moisture
    measurement
    method;
    vii)
    Volume
    of
    H
    2
    O
    collected
    in
    the
    impingers
    (ml);
    viii)
    Mass
    of
    H,O collected
    in
    the
    silica
    gel
    (g);
    ix)
    Dry
    gas
    meter calibration
    factor;
    x)
    Average
    dry
    gas
    meter
    temperature
    (°F);
    xi)
    Barometric
    pressure
    (inches
    of
    mercury);
    xii)
    Differential
    pressure
    across
    the
    orifice
    meter
    (inches
    of
    H
    2
    Q)j
    xiii)
    Initial
    and
    final
    dry
    gas
    meter
    readings
    (ft
    3
    );
    xiv)
    Total
    sample
    gas
    volume,
    corrected
    to
    standard
    conditions
    (dscf);
    and
    xv)
    Percentage
    of
    moisture
    in
    the
    stack
    gas
    (percent
    HQ)
    F)
    The
    raw
    data
    and
    calculated
    results
    for
    any
    stratification
    tests
    performed
    in
    accordance
    with
    Sections
    6.5.5.1
    through
    6.5.5.3
    of
    Exhibit
    A
    to
    this
    Appendix.
    G)
    For
    each
    RATA
    run
    using
    the
    Ontario
    Hydro
    Method
    to
    determine
    mercury
    concentration:
    i)
    Percent
    CO,
    and
    O2in the
    stack
    gas,
    dry
    basis;
    ii)
    Moisture
    content
    of
    the
    stack
    gas
    (percent
    H
    2
    Q)j
    iii)
    Average
    stack
    temperature
    (°F);
    53

    iv)
    Dry
    gas
    volume
    metered
    (dscm);
    v)
    Percent
    isokinetic;.
    vi)
    Particle-bound
    mercury
    collected
    by the
    filter,
    blank,
    and
    probe
    rinse
    (j.tgm);
    vii)
    Oxidized
    mercury
    collected
    by
    the KC1
    impingers
    (tgm);
    viii)
    Elemental
    mercury
    collected
    in
    the
    HNO
    3
    Q
    2
    impinger
    and
    in
    the
    KMnOdSQ
    4
    impingers
    U.igm);
    ix)
    Total
    mercury,
    including
    particle-bound
    mercury
    (gm);
    and
    x)
    Total
    mercury,
    excluding
    particle-bound
    mercury
    fligm)
    H)
    All appropriate
    data
    elements
    for
    Methods
    30A
    and 30B.
    I)
    For
    a unit
    with
    a
    flow monitor
    installed
    on
    a
    rectangular
    stack
    or
    duct,
    if
    a
    site-specific
    default
    or
    measured
    wall
    effects
    adjustment
    factor
    (WAFjJ
    used
    to correct
    thestack
    gas
    volumetric
    flow
    rate
    data
    to
    account
    for
    velocity
    decay
    near
    the
    stack
    or duct
    wall,
    the
    owner
    or
    operator
    must
    keep
    records
    of
    the following
    for
    each
    flow
    RATA
    performed
    with
    EPA
    Method
    2 in
    appendices
    A—i
    and A—2
    to
    40
    CFR
    60,
    incorporated
    by
    reference
    in Section 225.140,
    subsequent
    to
    the
    WAP
    determination:
    i)
    Monitorjpgsystem
    lD
    ii)
    Test
    number;
    iii)
    Operating
    level;
    iv)
    RATA
    end
    date
    and
    time;
    v)
    Number
    of Method
    1
    traverse
    points;
    and
    vi)
    Wall
    effects
    adjustment
    factor
    (WAF),
    to
    the
    nearest
    0.0001.
    J)
    For each
    RATA
    run
    using
    Method
    29 in
    appendix
    A—8
    to 40
    CFR
    60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    to.
    determine
    mercury
    concentration:
    54

    i).
    Percent
    CO
    2
    and
    Q
    2
    in
    the
    stack
    ga
    dry
    basis;.
    ii)
    Moisture
    content
    of
    the stack
    gas
    (percent
    H,Q)j
    iii)
    Average
    stack
    gas
    temperature
    (°F);
    iv)
    Dry
    gas
    volume
    metered
    (dscm);
    v)
    Percent
    isokinetic;.
    vi)
    Particulate
    mercury
    collected
    in the
    front
    half
    of the
    sampling
    train,
    corrected
    for
    the
    front-half
    blank
    value
    (iig);
    and
    vii)
    Total
    vapor
    phase
    mercury
    collected
    in
    the back
    half
    of
    the
    sampling
    train,
    corrected
    for
    the back-half
    blank
    value
    (jig).
    8)
    For
    each
    certified
    continuous
    emission
    monitoring
    system,
    excepted
    monitoring
    system,
    or
    alternative
    monitoring
    system,
    the date
    and
    description
    of
    each
    event
    which
    requires
    certification,
    recertification,
    or
    certain
    diagnostic
    testing
    of
    the
    system
    and
    the
    date
    and
    type
    of each
    test
    performed.
    If
    the conditional
    data
    validation procedures
    of
    Section
    1
    .4(b)(3)
    of this
    Appendix
    are
    to
    be used
    to
    validate
    and
    report
    data
    prior
    to
    the completion
    of
    the
    required
    certification,
    recertification,
    or
    diagnostic
    testing,
    the
    date
    and
    hour
    of the
    probationary
    calibration error
    test
    must
    be
    reported
    to
    mark
    the beginning
    of
    conditional
    data
    validation.
    9)
    Hardcopy
    relative
    accuracy
    test
    reports,
    certification
    reports,
    recertification
    reports, or
    semiannual
    or annual
    reports
    for
    gas
    or flow
    rate
    GEMS,
    mercury
    CEMS,
    or
    sorbent
    trap
    monitoring
    systems
    are required
    or
    requested
    under
    40
    CFR
    75.60(b)(6)
    or
    75.63,
    incorporated
    by
    reference
    in Section
    225.140,
    the
    reports
    must
    include,
    at
    a
    minimum,
    the
    following
    elements
    (as
    applicable
    to the
    type(s)
    of
    test(s)
    performed:
    A)
    Summarized
    test
    results.
    B)
    DAHS
    printouts
    of the
    CEMS
    data
    generated
    during
    the
    calibration
    error,
    linearity,
    cycle
    time,
    and
    relative
    accuracy
    tests.
    C)
    For
    pollutant
    concentration
    monitor
    or diluent
    monitor
    relative
    accuracy
    tests
    at
    normal
    operating
    load:
    55

    i)
    The
    rawrefèrence’inetho&dàta
    from
    each
    run,
    i.e.,
    the
    dataunder
    paragraph
    (a)(7)(D,)(xvii)
    of this
    Section
    (usually
    in
    the
    form
    of a
    computerized
    printout, showing
    a
    series
    of
    one-minute
    readings
    and
    the
    run
    average):
    ii)
    The
    raw
    data
    and
    results
    for
    all
    required
    pre-test,
    post-test,
    ore-run
    and
    post-run
    quality
    assurance
    checks
    (i.e.,
    calibration
    gas
    injections)
    of
    the reference
    method
    analyzers,
    i.e.,
    the
    data
    under
    paragraphs
    (a)(7)(D)(v)
    through
    (a)(7)(D)(xiv)
    of
    this
    Section:
    iii)
    The
    raw
    data
    and
    results
    for
    any
    moisture measurements
    made
    during
    the
    relative
    accuracy
    testing,
    i.e.,
    the
    data
    under
    paragraphs
    (a(7)(E)(i)
    through
    (a)(7)(E)(xv)
    of
    this
    Section;
    and
    iv)
    Tabulated,
    final,
    corrected
    reference
    method
    run
    data
    (i.e.,
    the
    actual
    values
    used
    in
    the
    relative
    accuracy
    calculations),
    along
    with
    the
    equations used
    to
    convert
    the
    raw
    data
    to the
    final
    values
    and
    example
    calculations
    to demonstrate
    how
    the
    test
    data
    were
    reduced.
    D)
    For
    relative
    accuracy
    tests
    for
    flow
    monitors:
    i)
    The
    raw
    flow
    rate
    reference
    method
    data,,
    from
    Reference
    Method
    2
    (or
    its
    allowable
    alternatives)
    under
    appendix
    A
    to 40
    CFR
    60,
    incorporated
    by
    reference
    in Section
    225.140,
    including
    auxiliary
    moisture
    data
    (ofienin
    the
    form
    of
    handwritten
    data
    sheets),
    i.e.,
    the
    data
    under
    paragraphs
    (a)(7)(B)(i)
    through
    (a)(7)(B)(xx),
    paragraphs
    (a)(7)(C)(i)
    through
    (a)(7)(C)(xiii),
    and,
    if
    applicable,
    paragraphs
    (a)(7)(E)(i)
    through
    (a)(7)(E)(xv)
    of
    this
    Section;
    and
    ii)
    The
    tabulated,
    final
    volumetric
    flow
    rate
    values
    used
    in
    the
    relative
    accuracy
    calculations
    (determined
    ‘from
    the
    flow
    rate
    reference
    method
    data
    and
    other
    necessary
    measurements,
    such
    as
    moisture,
    stack
    temperature
    and
    pressure),
    along
    with
    the
    equations
    used
    to
    convert
    the
    raw
    data
    to the
    final
    values
    and
    example
    calculations
    to
    demonstrate
    how
    the
    test
    data
    were
    reduced.
    B)
    Calibration
    gas
    certificates
    forthe
    gases
    used
    in
    the
    linearity, calibration
    error,
    and
    cycle
    time
    tests
    and
    for
    the
    calibration gases
    used
    to
    quality
    assure
    the
    gas
    monitor
    reference
    method
    data
    during
    the
    relative
    accuracy
    test
    audit.
    56

    F)
    Laboratory
    calibrationsof
    the
    söurcesampling
    equipment.For
    sorbent
    trap
    monitoring
    systems,
    the
    laboratory
    analyses
    of
    all
    sorb
    ent
    traps,
    and
    inforrnaion
    documenting
    the
    results
    of
    aIlleak
    checks
    and
    other
    applicable
    quality
    control
    procedures
    G)
    A
    copy
    of the
    testprotocol
    used
    for
    the
    CEMS
    certifications
    or
    recertifications,
    including
    narrative
    that
    explains
    any
    testing
    abnormalities,
    problematic
    sampling,
    and
    analytical
    conditions
    that
    required
    a change
    to
    the
    test
    protocol,
    and/or
    solutions
    to
    technical
    problems
    encountered
    during the
    testing
    program:
    H)
    Diagrams
    illustrating
    test
    locations
    and
    sample point
    locations
    (to
    verify
    that
    locations
    are
    consistent
    with
    information
    in
    the
    monitoring
    plan).
    Include
    a discussion
    of
    any
    special
    traversing
    or
    measurement
    scheme.
    The
    discussion
    must
    also
    confirm
    that
    sample
    points
    satisfy
    applicable
    acceptance
    criteria.
    I)
    Names of
    key
    personnel
    involved
    in
    the
    test
    program,
    including
    test
    team
    members,
    plant
    contacts,
    agency
    representatives
    and
    test
    observers
    on
    site.
    10)
    Whenever,
    reference
    methods
    are.
    used
    as backup monitoring
    systems
    pursuant to
    Section
    1 .4(d)(3)
    of
    this
    Appendix,
    the
    owner
    or
    operator
    must
    record
    the
    following
    infonnation:
    A)
    For
    each
    test
    run
    using
    Reference
    Method
    2
    (or
    its
    allowable
    alternatives
    in appendix
    A
    to
    40 CFR
    60.
    incorporated
    by
    reference
    in
    Section
    225.140)
    to
    determine
    volumetric
    flow
    rate,
    record
    the
    following
    data
    elements
    (as’
    applicable
    to the
    measurement
    method
    used):
    i)
    Unit
    or stack
    identification
    number;
    ii)
    Reference
    method
    system
    and
    component
    identification
    numbers;
    iii)
    Run
    date
    and
    hour;
    iv)
    The
    data
    in
    paragraph
    (a)(7)(B)
    of
    this
    Section,
    except
    for
    paragraphs
    (a)(7)(B)(i),
    (vi),
    (viii),
    (xii),
    and
    (xvii)
    through
    (xx);
    and
    v)
    The
    data
    in
    paragraph
    (a)(7)(C).
    except on a
    run
    basis.
    57

    B’)’
    Fär’each
    eférenc’e’method’
    test
    runusing
    Method’6C,
    7E
    or’3A
    in
    appendix
    A
    to
    40.
    CFR
    60.
    incorporated
    by
    reference
    in Section
    225.
    14Q
    to
    determine
    SQ2,
    NON,
    CO
    2
    .
    0IZQ2
    concentration:
    i)
    Unit
    or
    stack
    identification
    number;
    ii)
    The
    reference
    method
    system
    and
    component
    identification
    numbers;
    iii)
    Run
    number:
    iv)
    Run
    start
    date
    and
    hour;
    v)
    Run
    end
    date
    and
    hour;
    vi)
    The
    data
    in
    paragraphs
    (a)(7)(D)(ii)
    through
    (ix)
    and
    (xii)
    through
    (xv);
    and
    (vii)’
    Stack
    gas
    density
    adjustment
    factor
    (if
    applicable).
    C)
    For
    each
    hour
    of
    each
    reference
    method
    test
    run
    using
    Method
    6C,
    7E,
    or
    3A
    in
    appendix
    A to
    40
    CFR
    60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    to
    determine
    SO,,
    NON,
    CO,.
    oQ,
    concentration:
    i)
    Unit
    or
    stack
    identification
    number;
    The
    reference
    method
    system
    and
    comoonent
    identification
    numbers;
    iii)
    Run
    number;
    iv)
    Run
    date
    and
    hour;
    v)
    Pollutant
    or
    diluent
    gas
    being
    measured;
    vi)
    Unadjusted
    (raw)
    average
    pollutant
    or
    diluent
    gas
    concentration
    for
    the
    hour;
    and
    vii)
    Average
    pollutant
    or
    diluent
    gas
    concentration
    for
    the
    hour,
    adjusted
    as
    appropriate
    for
    moisture,
    calibration
    bias
    (or
    calibration
    error)
    and
    stack
    gas
    density.
    11)
    Foreach
    other
    quality-assurance
    test
    or
    other
    quality
    assurance
    activity, the
    owner
    or
    operator
    must
    record
    the
    following
    (as
    applicable):
    ii)
    58

    A)
    B)
    C)
    D
    )
    E)
    Test
    result;
    F)
    Reason
    for
    test:
    and
    G)
    Test
    code.
    12)
    For
    each
    request
    for
    a
    quality
    assurance
    test
    extension
    or
    exemption,
    for
    any
    loss
    of
    exempt
    status,
    and
    for each
    single-load
    flow
    RATA
    claim
    pursuant
    to
    Section
    2.3.1
    .3(c)(3)
    of
    Exhibit
    B to
    this
    Appendix,
    the
    owner
    or
    operator
    must
    record
    the
    following
    (as
    applicable):
    A)
    For
    a RATA
    deadline
    extension
    or exemption
    request:
    i)
    ii)
    iii)
    iv)
    v,
    Monitoring
    system
    ntifi-finn
    r-i1
    Date
    of last
    RATA.
    RATA
    iniration
    date
    without
    PYtA1iflrv
    RATA
    expiration
    date
    with
    extension;
    Type
    of RATA
    extension
    of
    exemption
    claimed
    or
    lost;
    vi)
    Year
    to
    date
    hours
    of
    usage
    of fuel
    other
    than very
    low
    sulfur
    fuel;
    vii)
    Year
    to date
    hours
    of
    non-redundant
    back-up
    CEMS
    usage
    at
    the
    unit/stack;
    and
    viii)
    Ouarter
    and
    year.
    B)
    For
    a
    linearity
    test
    or flow-to-load
    ratio
    test
    quarterly
    exemption:
    i)
    Component-system
    identification
    code;
    Component/system
    identification
    code;
    Parameter;
    Test
    or
    activity
    completion
    date
    and
    hour;
    Test
    or
    activity
    descrintion:
    59

    ii)
    Type
    of
    test;.
    iii)
    Basis
    for
    exemption;:.
    iv)
    Ouarter
    and
    year;
    and
    v)
    Span
    scale.
    C)
    For
    a
    fuel
    flowmeter
    accuracy
    test
    extensn:
    i)
    Component-system
    identification
    code;
    ii)
    Date
    of
    last
    accuracy
    test;
    iii)
    Accuracy
    test expiration
    date
    without
    extension:
    iv)
    Accuracy
    test
    expiration
    date
    with
    extension;
    v)
    Type
    of
    extension;
    and
    vi)
    Quarter
    atid
    year.
    D)
    For
    a
    single-load (or
    single-level)
    flow
    RATA
    claim:
    i)
    Monitoring
    system
    identification
    code;
    ii)
    Ending
    date
    of
    last
    annual
    flow
    RATA;
    iii)
    The
    relative
    frequency
    (percentage)
    of unit
    or
    stack
    operation
    at
    each
    load
    (or
    operating)
    level
    (low,
    mid,
    and
    high)
    since
    the
    previous
    annual
    flow
    RATA,
    to
    the
    nearest
    0.1
    percent;
    iv)
    End
    date
    of
    the
    historical
    load
    (or
    operating
    level)
    data
    collection
    period;
    and
    v)
    Indication
    of the
    load
    (or
    operating)
    level
    (low,
    mid
    or high)
    claimed
    for
    the
    single-load
    flow
    RATA.
    13)
    For
    the
    sorbent
    traps
    used
    in
    sorbent
    trap
    monitoring
    systems
    to
    quantify
    mercury
    concentration
    .under
    Sections 1.14
    through
    1.18
    of
    this
    Appendix
    (including
    60

    sorbent
    traps
    usedforrefative’
    accuracy’testiPg)
    theowner
    or
    operator must
    keep
    records
    of
    the following:
    A)
    The
    ID
    number
    of
    the
    monitoring
    system
    in
    which
    each
    sorb
    ent
    trap
    was
    usedto
    collect
    mercury;
    B)
    The
    unique
    identification
    number
    of
    each
    sorbent
    trap;
    C)
    The
    beginning
    and
    ending
    dates
    and
    hours
    of
    the data
    collection
    period
    for
    each
    sorbent
    trap;
    D)
    The
    average
    mercury
    concentration
    (in
    igm1dscm)
    for the
    data
    collection
    period;
    E)
    Information
    documenting
    the
    results
    of
    the
    required
    leak
    checks;
    F)
    The
    analysis
    of
    the
    mercury
    collected
    by
    each
    sorbent
    trap;
    and
    G)
    Tnfcrmtini,
    ilnr.llrrlenting
    the
    results
    of the
    other
    applicable
    quality
    control
    procedures
    in
    Section
    1.3
    of this
    Appendix
    and
    in Exhibits
    B and
    0
    to this
    Appendix.
    b)
    Except
    as
    otherwise
    provided
    in
    Section
    1.12(a)
    of this
    Appendix,
    for
    units
    with
    add-on
    mercury
    emission
    controls,
    the
    owner
    or operator
    must
    keep
    the
    following
    records
    on-site
    in
    the
    quality
    assurance/quality
    control
    plan
    required
    by
    Section
    1
    of
    Exhibit
    B
    to
    this
    Appendix:
    1)
    A
    list
    of operating
    parameters
    for
    the
    add-on
    emission
    controls,
    including
    parameters
    in Section
    1.12
    of
    this
    Appendix,
    appropriate
    to the
    particular
    installation
    of
    add-onemission
    controls;
    and
    2)
    The
    range
    of
    each
    operating
    parameter
    in
    the
    list
    that
    indicates
    the
    add-on
    emission
    controls
    are properly
    operating.
    c)
    Excepted
    monitoring
    for
    mercury
    low
    mass
    emission
    units
    under
    Section
    1.15(b)
    of
    this
    Appendix.
    For
    qualifying
    coal-fired
    units
    using
    the
    alternative
    low
    mass
    emission
    methodology
    under
    Section
    1.15(b),
    the
    owner
    or
    operator
    must
    record
    the
    data
    elements
    described
    in
    Section
    1.13(a)(7)(G),
    Section
    1.13(a)(7)(H),
    or Section
    1.13(a)(7)(J)
    of
    this
    Appendix,
    as
    applicable,
    for
    each
    run
    of
    each
    mercury
    emission
    test
    and
    re-test
    required
    under
    Section 1.1
    5(c)(1)
    or
    Section
    1.1
    5(d)(4)(C)
    of
    this
    Appendix.
    61

    d)
    DAHS
    Veriflcätian For eachDAHS(thissing
    data and
    formula)
    verification
    that
    i
    required
    for
    initiai
    certification,
    recertification,
    or for
    certain
    diagnostic
    testing
    of a
    monitoring
    system,
    record
    the
    date
    and hour
    that
    the DAHS
    verification
    is
    successfully
    completed.
    (This
    requirement
    only applies
    to units
    thatreport
    monitoring
    plan
    data
    in
    accordance
    with
    Section
    1.10(d)
    of
    this
    Appendix.)
    Section
    1.14
    General
    provisions
    a)
    Applicability.
    The
    owner
    or
    operator
    of a unit
    must
    comply
    with
    therequirements
    of
    this
    Appendix
    to
    the extent
    that
    compliance
    is
    required
    by
    Part
    225.
    For
    purposes
    of
    this
    Appendix,
    the
    term “affected
    unit”
    means
    any coal-fired
    unit
    (as
    defined
    in
    40
    CFR72.2,
    incorporated
    by
    reference)
    that
    is subject
    to
    Part 225.
    The
    term “non-affected
    unit”
    means
    any unit
    that is
    not subject
    to
    such
    a
    program,
    the
    term
    “permitting
    authority”
    means
    the
    Agency,
    and the
    term
    “designated
    representative”
    means
    the responsible
    party
    under
    Part
    225.
    b)
    Compliance dates.
    The
    owner
    or operator
    of anaffectéd
    unitmust
    ineet
    the comn1inr
    deadlines
    established
    by
    Part 225,
    Subpart
    B.
    c)
    Prohibitions.
    1)
    No owner
    or
    operator
    of an
    affected
    unit Or
    a non-affected
    unit
    under
    Section
    1.l6(b)(2)(B) of
    this
    Appendix
    will
    use any
    alternative
    monitoring
    system.
    alternative
    reference
    method,
    or
    any
    other
    alternative
    for
    the required
    continuous
    emission
    monitoring
    system
    without
    having
    obtained
    prior
    written
    approval
    in
    accordance
    with
    paragraph
    (f)
    of
    this Section.
    2)
    No
    owner
    or operator
    of
    an
    affected
    unit
    or
    a
    non-affected
    unit under
    Section
    1.1
    6(b)(2)(B)
    of
    this
    Appendix
    will
    operate
    the
    unit so
    as to
    discharge,
    or
    allow
    to
    be
    discharged
    emissions
    of
    mercury
    to
    the
    atmosphere
    without
    accounting
    for
    all••
    such
    emissions
    in
    accordance
    with
    the
    applicable
    provisions
    of
    this
    Appendix.
    3)
    No owner
    or operator
    of an affected
    unit or
    a non-affected
    unit
    under
    Section
    1.1
    6(b)(2)(B)
    of
    this
    Appendix
    will disrupt
    the
    continuous
    emission
    monitoring
    system,
    any
    portion
    thereof,
    or any
    other
    approved
    emission
    monitoring
    method.
    and
    thereby
    avoid
    monitoring
    and
    recording
    mercury
    mass
    emissions
    discharged
    into
    the atmosphere,
    except
    for
    periods
    of
    recertification
    or
    periods
    when
    calibration,
    quality
    assurance
    testing,
    or
    maintenance
    is performed
    in
    accordance
    with
    the provisions
    of
    this
    Appendix
    applicable
    to
    monitoring
    systems
    under
    Section
    1.15
    of this
    Appendix.
    4)
    No
    owner
    or
    operator
    of
    an affected
    unit
    or
    a non-affected
    unit
    under
    Section
    62

    1.
    I6(b)(2’kB)
    wiWrètire
    or
    permanently
    dIsëontihuêuse
    of
    the
    continuOus
    emission
    monitoring
    system,
    any
    component
    thereof,
    or
    any
    other
    approved
    emission
    monitoring
    system
    under
    this
    Appendix,
    except
    under
    any
    one
    of
    the
    foIlàwig
    circumstances
    A)
    During
    the
    periodthatthe
    unit
    is
    covered
    by
    a retired
    unit
    exemption
    that
    is
    in
    effect
    under
    Part
    225;
    or
    B)
    The
    owner
    or
    operator
    is monitoring
    mercury
    mass
    emissions
    from
    the
    affectedunitwithanother.
    certified
    monitoring
    system
    approved,
    in
    accordance
    with
    the
    provisions
    of Section
    225.250;
    or
    C)
    The
    designated
    representative
    submits
    notification
    of
    the
    date
    of
    certification
    testing
    of
    a
    replacement
    monitoring
    system
    in
    accordance
    with
    Part
    225.240(d).
    d)
    Quality
    assurance
    and
    quality
    control
    requirements.
    For
    units
    that
    use
    continuous
    emission
    monitoring
    systems
    to
    account
    for
    mercury
    mass
    emissions,
    the
    owner
    or
    operator
    must
    meet
    the
    applicable
    quality
    assurance
    and quality
    control
    requirements
    in
    Section
    1.5
    and
    Exhibit
    B to
    this
    Appendix
    for the
    flow
    monitoring
    systems,
    mercury
    concentration
    monitoring
    systems,
    moisture
    monitoring.
    systems,
    and diluent
    monitors
    required
    under
    Section
    1.15
    of
    thisAppendix.
    Units
    using
    sorbent
    trap
    monitoring
    systems
    must.meet
    the
    applicable
    quality
    assurance
    requirements
    in
    Section
    1.3
    of this
    Appendix,
    Exhibit
    D to
    this
    Appendix,
    and Sections
    1.3
    and 2.3
    of Exhibit
    B to
    this
    Appendix.
    e)
    Reporting
    data
    prior
    to
    initial
    certification.
    If,
    by
    the applicable
    compliance
    date
    under
    Part
    225,
    the
    owner
    or operator
    of an
    affected
    unit
    has
    not
    successfully
    completed
    all
    required
    certification
    tests
    for
    any
    monitoring
    system(s),
    he
    or
    she must
    determine,
    record,
    and report
    dataprior
    to
    initial
    certification
    in
    accordance
    with
    Section
    225.239
    of
    this
    Part.
    f)
    Petitions.
    1)
    The
    designated
    representative
    of
    an
    affected
    unit
    that
    is
    also
    subject
    to
    the
    Acid
    Rain
    Program
    may
    submit
    a petition
    to
    the
    Agency
    requesting
    an
    alternative
    to
    any requirement
    of
    Sections
    L
    14
    through
    1.18
    of
    this
    Appendix.
    Such
    a
    petition
    must
    meet
    the
    requirements
    of 4D
    CFR
    75.66,
    incorporated
    by
    reference
    in
    Section
    225.140,
    and
    any
    additional
    requirements
    established
    by
    Part
    225,
    Subp
    B. Use
    of
    an alternative
    to
    any
    requirement
    of
    Sections
    1.14
    through
    1.18
    of this
    Appendix
    is
    inaccordancewithSections
    1.14
    through
    1.18
    of
    this
    Appendix
    and
    with
    Part
    225,
    Subpart
    B only
    to the
    extent
    that
    the
    petition
    is approved
    in
    writing
    63

    by
    the Agency;
    2)
    Noithstanding
    pargraph(fl(fl
    of this Section,
    petitions
    requesting.an
    alternative
    to
    a
    requirement concerning
    any additional
    CEMS
    required
    solely
    to
    meet
    the common stack
    provisions
    of
    Section
    1.16 of this
    Appendix
    must
    be
    submitted
    to the
    Agency
    and
    will
    be
    governed
    by paragraph
    (f)(3)
    of this
    Section.
    Such a petition
    must
    meet the
    requirements
    of 40 CFR
    75.66,
    incorporated
    by
    reference
    in Section
    225.140,
    and
    any additional
    requirements
    established
    by Part
    225,
    Subpart
    B.
    3)
    The
    designated
    representative
    of an affected
    unit
    that is not
    subject
    to
    the
    Acid
    Rain Program
    may submit
    a
    petition
    to the
    Agency
    requesting an
    alternative
    to
    any requirement
    of Sections
    1.14
    through
    1.18
    of this Appendix.
    Such
    a
    netition
    must
    meet the
    requirements
    of 40
    CFR 75.66, incorporated
    by reference
    in
    Section 225.140.
    and any
    additional
    requirements
    established
    by Part
    225,
    Subpart
    B. Use of an
    alternative to any requirement
    of
    Sections 1.14
    through
    1.18
    of
    this
    Appendix
    is in
    aecordatice
    with Sections
    1.14
    through 1.18 of this
    Appendix
    only
    to the extent
    that
    it is
    approved in writing
    by
    the Agency.
    Section 1.15 Monitoring
    of mercury
    mass emissions
    and
    heat
    input
    at the
    unit level
    The
    owner or
    operator of the affected
    coal-fired
    unit must:
    a)
    Meet the
    general operating
    requirements
    in
    Section 1.2
    of this
    Appendix
    for
    the
    following
    continuous emission
    monitors
    (except
    as
    provided
    in accordance
    with subpart
    E
    of 40
    CFR
    75,
    incorporated
    by reference in
    Section.225.140):
    1)
    A mercury
    concentration
    monitoring
    system (consisting
    of a mercury
    pollutant
    concentration
    monitor and
    an automated
    DAHS,
    which
    provides
    a
    permanent,
    continuous
    record
    of mercury
    emissions in units
    of micrograms
    per
    standardcubic
    meter
    (jig/scm))
    or
    a
    sorbent trap
    monitoring
    system,
    to measure
    the
    mass
    concentration
    of total vapor
    phase mercury
    in
    the flue
    gas,
    includingthe
    elemental
    and oxidized forms
    of
    mercury,
    in micrograms
    per standard
    cubic
    meter
    (jig/scm);
    and
    2)
    A flow monitoring
    system;
    and
    3)
    A continuous
    moisture monitoring
    system
    (if
    correction
    of
    mercury “‘-°“
    for
    moisture is required),
    as described
    in 40
    CFR
    75.11(b),
    incorporated
    by
    reference
    in Section 225.140.
    Alternatively,
    the owner
    or
    operator
    may
    use
    the
    appropriate
    fuel-specific
    default
    moisture value
    provided
    in 40
    CFR
    75.11.
    incorporated
    by
    reference
    in
    Section
    225.140,
    or
    a site-specific
    moisture
    value
    64

    approved-bypetitiön under
    40CFR”75’6
    iricorporated
    by
    reference
    in
    Section
    225.140;
    and
    4)-
    If
    heat
    input
    is
    quired*to
    be
    reported-under
    Part-225,
    the
    owner
    or
    operator
    must
    meet
    the
    general
    operating.
    requirements
    for a
    flow
    monitoring
    system
    and
    an
    02
    or
    CO
    2
    monitoring
    system
    to
    measure
    heat
    input
    rate.
    b)
    For
    an affected
    unit
    that
    emits
    464
    ounces
    (29
    ib)
    of
    mercury
    per
    year
    or less,
    use
    the
    following
    excepted
    monitoring
    methodology.
    To
    implement
    this
    methodology
    for
    a
    gua1ifying-
    unit,
    the
    owner
    or
    operator
    must
    meet
    the
    general
    operating
    requirements
    in
    Section
    1.2
    of
    this
    Appendix
    for
    the
    continuous
    emission
    monitors
    described
    in
    paragraphs
    (a)(2)
    and
    (a)(4)
    of this
    Section,
    and
    perform
    mercury
    emission
    testing
    for
    initial
    certification
    and
    on-going
    quality-assurance,
    as
    described
    in
    paragraphs
    (c)
    through
    (e)
    of
    this
    Section.
    c)
    To
    determine whether
    an affected unit
    is
    eligible
    to use
    the
    monitoring
    provisions
    in
    paragraph
    (b)
    of
    this
    Section:
    1)
    The
    owner
    or
    operator
    must
    perform
    mercury
    emission
    testing
    within
    18
    months
    before
    the
    compliance
    date
    in
    Section
    1.14(b)
    of
    this
    Appendix,
    to determine
    the
    mercury
    concentration
    (i.e.,
    total
    vapor
    phase,
    mercury) in
    the
    effluent.
    A)
    The
    testing
    must
    be performed
    using
    one
    of
    the
    mercury
    reference
    methods
    listed
    in Section
    1
    .6(a)(5)
    of this
    Appendix,
    and
    must
    consist
    of a
    minimum
    of
    3
    runs
    at the
    normal
    unit
    operating
    load,
    while
    combusting
    coal.
    The
    coal
    combusted
    during
    the
    testing
    must
    be
    representative
    of
    the
    coal
    that
    will
    be combusted
    at
    the start
    of
    the
    mercury
    mass
    emissions
    reduction
    program
    (preferably
    from
    the
    same
    source(s)
    of
    supply).
    The
    minimum
    time
    per
    run
    must
    be
    1 hour
    if
    Method
    30A’is
    used.
    Ifither
    Method
    29
    in appendix
    A-8
    to
    40
    CFR
    60,
    incorporated
    by
    reference,
    ASTM
    D6784-02
    (the
    Ontario
    Hydro
    method)
    (incorporated
    by
    reference
    under
    Section
    225.140),
    or
    Method
    30B
    is
    used,
    paired
    samples
    are
    required
    for
    each
    test-run
    and
    the
    runs
    must
    be
    long
    enough
    to
    ensure
    that
    sufficient
    mercury
    is
    collected
    to analyze.
    When
    Method
    29
    in
    appendix
    A-8
    to
    40
    CFR
    60,
    incorporated
    by
    reference,
    or
    the
    Ontario
    Hydro
    method
    is
    used,
    the
    test
    results
    must
    be based
    on
    the
    vapor
    phase
    mercury
    collected in
    the
    back-half
    ofthe
    sampling
    trains
    (i.e.,
    the
    non-filterable
    impinger
    catches).
    For
    each
    Method
    29
    in
    appendix
    A-8
    to
    40
    CFR
    60.
    incorporated
    by
    reference,
    Method
    30B,
    or Ontario
    Hydro
    method
    test
    run,
    the
    paired trains
    must
    meet
    the
    relative
    deviation
    (RD)
    requirement
    specified
    in
    Section’
    l.6(a)(5) of
    this
    Appendix
    or
    Method30B,
    as
    B)
    65

    applicable.
    If the RD
    specification
    is met,
    the results
    of the two
    samples
    must
    be averaged
    arithmetically.
    C)
    If the
    unit is equipped
    with
    flue
    gas
    desulfurization
    or add-on
    mercury
    emission
    controls,
    the controls
    must
    be operating
    normally
    during
    the
    testing,
    and, for
    the
    purpose
    of establishing
    proper
    operation
    of
    the
    controls,
    the owner
    or
    operator
    must record
    parametric
    data or
    SO
    2
    concentration
    data
    in
    accordance
    with Section
    1.12(a)
    of
    this
    Appendix.
    D)
    If two
    or
    more
    of
    units
    of
    the
    same type
    qualify
    as
    a
    group
    of
    identical
    units
    in
    accordance
    with
    40
    CFR
    75.19(c)(1)(iv)(B),
    incorporated
    by
    reference
    in Section
    225.140,
    the owner
    or
    operator
    may
    test
    a
    subset
    of
    these
    units in
    lieu
    of
    testing
    each
    unit
    individually.
    If this
    option
    is
    selected,
    the number
    of units
    required
    to be
    tested
    must be
    determined
    from
    Table
    LM-4
    in
    40 CFR 75.19,
    incorporated
    by reference
    in
    Section
    225.140.
    For the
    purposes
    of the required
    retests
    under
    paragraph
    (d)(4)
    of
    this
    Section,
    it
    is
    strongly
    recommended
    that
    (to
    the
    extent
    practicable)
    the
    same
    subset
    of the
    units
    not
    be
    tested in
    two successive
    retests,
    and
    that
    every
    effort
    be
    made to
    ensure that
    each unit
    in the group
    of
    identical
    units
    is
    tested
    in a timely
    manner.
    2)
    A)
    Based
    on
    the results
    of the emission
    testing,
    Equation
    1 of this
    Section
    must
    be used
    to
    provide a
    conservative
    estimate
    of the annual
    mercury
    mass emissions
    from
    the unit:
    E
    = N
    x
    K
    x
    C’Hg
    x
    Qmax
    (Equation
    1)
    Where:
    E
    =
    Estimated
    annual
    mercury
    mass
    emissions
    from
    the affecte1
    unit.
    (ounces/year)
    K
    =
    Units conversion
    constant,
    9.978
    x l0 oz-scmljig-scf
    N
    = Either
    8,760
    (the
    number
    of hours in
    a
    year)
    or
    the maximum
    number
    of
    operating
    hours per
    year
    (if
    less
    than
    8,760)
    allowed
    by the
    unit’s
    Federally-enforceable
    operating
    permit.
    CHg
    = The
    highest
    mercury
    concentration
    (jig/scm)
    from any
    of
    the
    test
    runs
    or 0.50
    FIg/scm, whichever
    isgreater
    66

    =
    Ma5cimum
    pOtentiálflowrate,
    determined
    according
    to
    Section
    2.1.2.1
    of
    ExhibitA to
    thisAppendix,
    (scfli
    B)
    Equation
    1
    of
    this
    Section
    assumes
    that
    the
    unit
    operates
    at its
    maximum
    potential flow
    rate,
    either
    year-round
    or
    for
    the
    maximum
    number
    of
    hours
    allowed
    by the
    operating
    permit
    (if
    unit
    operation
    is
    restricted
    to
    less
    than
    8,760
    hours
    per
    year).
    If the
    permit
    restricts
    the
    annual
    unit
    heat
    input
    but
    not
    the
    number
    of
    annual
    unit
    operating
    hours,
    the
    owner
    or
    operator
    may
    divide
    the
    allowable
    annual
    heat
    input
    (mmBtu)
    by
    the design
    rated
    heat
    input
    capacity
    of
    the
    unit
    (mmBtu/hr)
    to
    determine
    the
    value
    of
    “N”
    in
    Equation
    1.
    Also,
    note
    that
    if
    the
    highest
    mercury
    concentration
    measured
    in
    any
    test
    run
    is
    less
    than
    0.50
    JIg/scm,
    a default
    value
    of
    0.50
    rig/scm
    must
    be
    used
    in
    the
    calculations.
    3)
    If the
    estimated
    annual
    mercury
    mass
    emissions
    from
    paragraph
    (c)(2)
    of
    this
    Section are
    464
    ounces
    per
    year
    or
    less,
    then
    the unit
    is
    eligible
    to use
    the
    monitoring
    provisions
    in
    paragraph
    (b)
    of
    this
    Section,
    and continuous
    monitoring
    of
    the
    mercury
    concentration
    is
    not
    required
    (except
    as otherwise
    provided
    in
    paragraphs
    (e)
    and
    (f)
    of this
    Section).
    d)
    If
    theowner
    or operator
    of
    an:
    eligible-unit
    under
    paragraph
    (c)(3)
    of
    this
    Section
    elects
    not
    to
    continuously
    monitor
    mercury
    concentration,
    then
    the following
    requirements
    must
    be
    met:
    1)
    The
    results
    of
    the
    mercury
    emission
    testing
    performed
    under
    paragraph
    (c)
    of this
    Section
    must
    be
    submitted
    as a
    certification
    application
    to
    the
    permitting
    authority,
    no
    later
    than
    45
    days
    afler
    the
    testing
    is
    completed.
    The
    calculations
    demonstrating
    that
    the
    unit
    emits
    464
    ounces
    (or
    less)
    per
    year
    of
    mercury
    must
    also,
    be
    provided,, and
    the
    default
    mercury
    concentration
    that
    will
    be used
    fbr
    reporting
    under
    Section
    1.18
    of
    this
    Appendix
    must
    be
    specified
    in
    both
    the
    electronic
    and
    hard
    copy
    portions
    of
    the
    monitoring
    plan
    for
    the
    unit.
    The:
    methodology
    is
    considered
    to
    be
    provisionally
    certified
    as
    of
    the
    date
    and
    hour
    of
    completion
    of the
    mercury
    emission
    testing.
    2)
    Following
    initial
    certification,
    the
    same
    default
    mercury
    concentration
    value
    that
    was
    used
    to
    estimate
    the
    unit’s
    annual
    mercury
    mass
    emissions
    under
    paragraph
    (c)
    of
    this
    Section
    must
    be
    reported
    for
    each
    unit
    operating
    hour,
    except
    as
    otherwise
    provided
    in
    paragraph
    (d)(4WD)
    or
    (d)(6)
    of this
    Section.
    The
    default
    mercury
    concentration
    value
    must
    be
    updated
    as
    appropriate,
    according
    to
    paragraph
    (d)(5)
    of this
    Section.
    67

    4)
    The mercury
    emission
    testing
    described
    in paragraph
    (c)
    of
    this Section
    must he
    repeated
    periodically,
    for
    the
    purposes
    of
    quality-assurance,
    as
    follows:
    A)
    If
    the
    results
    of the
    certification
    testing
    under
    paragraph
    (c)
    of this
    Section
    show
    that the
    unit emits
    144
    ounces
    (9 ib)
    of mercury
    per
    year
    or
    less,
    the
    first
    retest
    is required
    by
    the
    end
    of the
    fourth
    QA
    operating
    quarter
    (as
    defined
    in 40
    CFR
    72.2, incorporated
    by
    reference)
    following
    the
    calendar
    quarter
    of the
    certification
    testing;
    or
    B)
    If the
    results
    of the
    certification
    testing
    under
    paragraph
    (c)
    of this
    Section
    show
    that
    the unit
    emits
    more
    than
    144
    ounces
    of mercury
    per
    year.
    but
    less
    than or
    equal to
    464 ounces
    per
    year,
    the first
    retest
    is required
    by
    the
    end of
    the second
    QA
    operating
    quarter
    (as
    defined
    in 40
    CFR 72.2,
    incorporated
    by
    reference)
    following
    the
    calendar
    quarter
    of
    the•
    certification
    testing;
    and
    C)
    Thereafter,
    retesting
    must
    be required
    either
    semiannually
    or
    annually
    (i.e.,
    by the
    end of
    the second
    or
    fourth
    QA
    operating
    quarter
    following
    the
    quarter
    of the previous
    test),
    depending
    on
    the
    results
    of
    the
    previous
    test.
    To determine
    whether
    the next
    retest
    is due
    within
    two or
    four
    QA
    operating
    quarters,
    substitute
    the
    highest
    mercury
    concentration
    from
    the
    current
    test
    or 0.50
    ig/scm
    (whichever
    is
    greater)
    into
    the equation
    in
    paragraph
    (c)(2)
    of this
    Section:
    If
    the estimated
    annual
    mercury
    mass
    emissions
    exceeds
    144
    ounces,
    the next
    test
    is
    due within
    two
    OA
    operating
    quarters.
    If the
    estimated
    annual
    mercury
    mass
    emissions
    is 144
    ounces
    or
    less,
    the
    next test
    is
    due
    within
    four
    OA
    operating
    quarters.
    D)
    An
    additional
    retest
    is required
    when
    there
    is a
    change
    in
    the
    coal
    rank
    of
    the primary
    fuel
    (e.g.,
    when
    the primary
    fuel
    is switched
    from
    bituminous
    coal
    to
    lignite).
    Use
    ASTM
    D388-99
    (incorporated
    by
    reference
    under
    Section
    225.140)
    to
    determine
    the coal
    rank.
    The
    four
    principal
    coal
    ranks
    are anthracitic,
    bituminous,
    subbituminous,
    and
    lignitic.
    The ranks
    of
    anthracite
    coal
    refuse
    (culm)
    and bituminous
    coal
    refuse
    (gob)
    must
    be
    anthracitic
    and
    bituminous,
    respectively.
    The
    retest
    must be
    perfonned
    within
    720
    unit
    operating
    hours
    of the
    change.
    5)
    The
    default
    mercury
    concentration
    used
    for
    reporting
    under
    Section
    1.18
    of this
    Appendix
    mustbe
    updated
    after
    each
    reguiredretest. Thisincludes
    retests
    thatare
    required
    prior
    to
    the
    compliance
    date
    in
    Section
    1.14(b)
    of this
    Appendix.
    The
    3)
    The
    hourly
    mercury
    mass
    emissions
    must
    be calculated
    according
    to Section
    4.1.3
    inExhibitCto
    this
    Appendix.
    68

    updated
    value
    must either
    be the highest
    mercury
    concentration
    measured
    in any
    of
    the test
    runs.
    or
    0.50
    .i.g/scm,
    whichever
    is greater.
    The
    updated
    value
    must
    he
    applied
    begirming
    with
    the first
    unit
    operating
    hour
    in
    whih
    mercury
    emissions
    data
    are
    required
    to be reported
    after
    completion
    of
    the retest,
    except
    as
    provided
    in
    paragraph
    (d)(4)(D)
    of
    this
    Section,
    where
    the
    need
    to
    retest
    is
    triggered
    by a..
    change
    in the
    coal rank
    of
    the primary
    fuel.
    In
    that case,
    apply
    the updated
    default
    mercury
    concentration
    beginning
    with
    the
    first
    unit
    operating
    hour in
    which
    mercury
    emissions
    are required
    to
    be reported
    after
    the
    date
    and
    hour of
    the
    fuel
    switch.
    6)
    If the.
    unit
    is equipped
    with
    a
    flue
    gas
    .desulfurization
    system
    or add-on
    mercury
    controls,
    the
    owner
    or
    operator
    must
    record
    the
    information
    required
    under
    Section
    1.12
    of
    this
    Appendix
    for
    each
    unit
    operating
    hour,
    to document
    proper
    operation
    of
    the
    emission
    controls.
    e)
    For
    units
    with
    common
    stack
    and
    multiple
    stack
    exhaust
    configurations,
    the
    use
    of the
    monitoring
    methodology
    described’
    inparagraphs
    (b)
    through
    (d)
    bfthis
    Section
    is
    restricted
    as follows:
    1)
    The
    methodology
    may
    not
    be used
    for reporting
    mercury
    mass
    emissions
    at
    a
    common
    stack
    unless
    all of the
    units
    using the
    common
    stack
    are
    affected,
    units
    and
    the units’
    combined
    potential
    to emit
    does
    not
    exceed
    464
    ounces
    of
    mercury
    per year
    times
    the number
    of units
    sharing
    the stack,
    in
    accordance
    with
    paragraphs
    (c)
    and (d)
    of this
    Section.
    If the
    test
    results
    demonstrate
    that
    the
    units
    sharing
    the
    common
    stack
    qualify
    as
    low mass
    emitters,
    the
    default
    mercury
    concentration
    used
    for.
    reporting
    mercury
    mass
    emiss.ions
    at
    the common
    stack
    must
    either be
    the
    highest
    value
    obtained
    in
    any
    test run
    or
    0.50
    gig/scm,
    whichever
    is greater.
    A)
    The initial
    emission
    testing
    required
    under
    paragraph
    (c)
    of this
    Section
    may
    be
    perfonned
    at the
    common
    stack
    if
    the following
    conditions
    are
    met.
    Otherwise,
    testing
    of
    the individual
    units
    (or
    a subset
    of
    the
    units,
    if
    identical,
    as described
    in paragraph
    (c)(
    1 )(D)
    of
    this Section)
    is
    required:
    i)
    The
    testing
    must
    be
    done
    at a
    combined
    load
    corresponding
    to
    the•
    designated
    normal
    load level
    (low,
    mid,
    or high)
    for
    the
    units
    sharing
    the
    common
    stack, in
    accordance
    with
    Section
    6.5.2.1
    of
    Exhibit
    A to this
    Appendix;
    All of
    the units
    that
    share
    the
    stack
    must
    be operating
    in
    a
    normal.
    stable
    manner
    and
    at tyical
    load
    levels during
    the
    emission
    testing.
    The
    coal
    combusted
    in
    each
    unit during
    the
    testing
    must
    be
    ii)
    69

    representative
    of
    the
    coal
    that
    will
    be combusted
    in
    that
    unit
    at the
    start
    of
    the
    mercury
    mass
    emission
    reduction
    program
    (preferably.
    from
    the
    same
    source(s)
    of
    supply):
    iii)
    If flue
    gas
    desulfurization
    and/or
    add-on
    mercury
    emission
    controls
    are
    used
    to reduce
    level
    the
    emissions
    exiting
    from
    the
    common
    stack,
    these
    emission
    controls
    must
    be
    operating
    normally
    during
    the
    emission
    testing
    and,
    for
    the
    purpose
    of
    establishing
    proper
    operation
    of
    the
    controls,
    the
    owner
    or operator
    must
    record
    parametric
    data
    or
    SO
    1
    concentration
    data
    in accordance
    with
    Section
    L12(a)
    of
    this
    Appendix:
    iv)
    When
    calculating
    E,
    the estimated
    maximum
    potential
    annual
    mercury
    mass
    emissions
    from
    the
    stack,
    substitute
    the
    maximum
    potential
    flow
    rate
    through
    the
    common
    stack
    (as
    defined
    in
    the
    monitoring
    plan)
    and
    the
    highest
    concentration
    from
    any
    test
    run
    (or
    0.50
    J.tg/scm,
    if
    greater)
    into
    Equation
    1;
    v)
    The
    calculated
    value
    of
    B must
    be divided
    by
    the
    number
    of units
    sharing
    the
    stack.
    If
    the result,
    when
    rounded
    to the
    nearest
    ounce,
    does
    not
    exceed
    464
    ounces,
    the
    units
    qualify
    to
    use
    the
    low
    mass
    emission
    methodology;
    and
    vi)
    If
    the
    units
    qualify
    to
    use
    the
    methodology,
    the
    default
    mercury
    concentration
    used
    for
    reporting
    at
    the
    common
    stack
    must
    be
    the
    highest
    value
    obtained
    in
    any
    test
    runor
    0.50
    J.Lg/scm, whichever
    is
    greater:
    or
    B)
    The
    retests
    reciuired
    under
    paragraph
    (d)(4)
    of
    this
    Section
    may
    also
    be
    done
    at the
    common
    stack.
    If
    this
    testing
    option
    iS chosen,
    the
    testing
    must
    be
    done
    at
    a
    combined
    load
    corresponding
    to
    the
    designated
    normal
    load
    level
    (low,
    mid,
    or
    high)
    for
    the units
    sharing
    the
    common
    stack,
    in
    accordance
    with
    Section
    6.5.2.1
    of
    Exhibit
    A to
    this
    Appendix.
    Provided
    that
    the
    required
    load
    level
    is
    attained
    and
    that
    all
    of
    the units
    sharing
    the
    stack
    are
    fed
    from
    the
    same
    on-site
    coal
    supply
    during
    normal
    operation,
    it
    is
    not
    necessary
    for
    all
    of
    the units
    sharing
    the
    stack
    to
    be in
    operation
    during
    a retest.
    However,
    if two
    or
    more
    of
    the
    units
    that
    share
    the
    stack
    are
    fed
    from
    different
    on-site
    coal
    supplies
    (e.g.,
    one
    unit
    burns
    low-sulfur
    coal
    for
    compliance
    and
    the
    other
    combusts
    higher-sulfur
    coal),
    then
    either:
    i)
    Perform
    the
    retest
    with
    all
    units
    in normal
    operation:
    or
    70

    ii)
    If this
    is
    not
    possible,
    dueto
    circumstances
    beyond
    the
    control
    of
    the owner
    or
    operator
    (e.g.,
    a
    forced
    unit
    outage),
    perform
    the
    retest
    with
    the
    available
    units
    operating
    and
    assess
    the
    test
    results
    as
    follows.
    Use
    the
    mercury
    concentration
    obtained
    in
    the
    retest
    for
    reporting
    purposes
    under
    this
    part
    if
    the
    concentration
    is
    greater
    than
    or
    equal
    to
    the
    value
    obtained
    in
    the
    most
    recent
    test.
    If
    the
    retested
    value
    is
    lower
    than
    the
    mercury
    concentration
    from
    the
    previous
    test,
    continue
    using
    the
    higher
    value
    from
    the
    previous
    test
    for reporting
    purposes
    and
    use
    that
    same
    higher
    mercury
    concentration
    value
    in
    Equation
    1 to
    determine
    the
    due
    date
    for
    the
    next
    retest,
    as described
    in paragraph
    (e)(1)(C)
    of
    this
    Section.
    C)
    If
    testing
    is
    done
    at
    the
    common
    stack,
    the
    due
    date
    for
    the
    next
    scheduled
    retest
    must
    be
    determined
    as
    follows:
    i)
    Substitute
    the
    maximum
    potential
    flow
    rate
    for
    the
    common
    stack
    (as
    defined
    in
    the
    monitoring
    plan)
    and
    the
    highest
    mercury
    concentration
    from
    any
    test
    run
    (or
    0.50
    rig/scm,
    if greater)
    into
    Equation
    1;
    ii)
    If
    the
    value
    of
    E obtained
    from
    Equation
    1,
    rounded
    to
    the
    nearest
    ounce.
    is greater
    than
    144
    times
    the
    number
    of
    units
    sharing
    the
    common
    stack,
    but
    less
    than
    or equal
    to 464
    times
    the
    number
    of
    units
    sharing
    the
    stack,
    the
    next
    retest
    is
    due
    in
    two
    QA
    operating
    quarters;
    iii)
    If
    the
    value
    of
    E
    obtained
    from
    Equation
    1,
    rounded
    to
    the
    nearest
    ounce,
    is
    less
    than
    or equal
    to
    144
    times
    the
    number
    of
    units
    sharing
    the
    common
    stack,
    the
    next
    retest
    is due
    in
    four
    QA
    operating
    quarters.
    2)
    For
    units
    with
    multiple
    stack
    or
    duct
    configurations,
    mercury emission
    testjpg
    must
    be
    performed
    separately
    on
    each
    stack
    or
    duct,
    and
    the
    sum
    of
    the
    estimated•
    annual
    mercury
    mass
    emissions
    from
    the
    stacks
    or
    ducts
    must
    not
    exceed
    464
    ounces
    of
    mercury
    per
    year.
    For
    reporting
    purposes,
    the
    default
    mercury
    concentration
    used
    for
    each
    stack
    or
    duct
    must
    either
    be
    the highest
    value
    obtained
    in
    any
    test
    run
    for
    that
    stack
    or 0.50
    jig/scm,
    whichever
    is
    greater.
    3)
    For
    units
    with
    a
    main
    stack
    and
    bypass
    stack
    configuration,
    mercury
    emission
    testing must
    be
    performed
    only
    on the
    main
    stack.
    For
    reporting
    purposes,
    the
    -
    default
    mercury
    concentration
    used
    for
    the
    main
    stack
    must
    either
    be
    the
    highest
    71

    value
    obtained
    in
    any
    test
    run
    for
    that
    stack
    or
    0.50
    pglscm,
    whichever
    is
    greater.
    Whenever
    the
    main
    stack
    is
    bypassed,
    the
    maximum potential
    mercury
    concentration,
    as
    defined
    in
    Section
    2.1.3
    of Exhibit
    A
    to
    this
    Appendix,
    must-be
    reported.
    f)
    At
    the
    end
    of
    each
    calendar
    year,
    if
    the
    cumulative
    annual
    mercury
    mass
    emissions
    from
    an
    affected
    unit
    have
    exceeded
    464
    ounces,
    then
    the owner
    must
    install,
    certify,
    operate,
    and
    maintain
    a mercury
    concentration
    monitoring
    system
    or a
    sorbent
    trap
    monitoring
    system
    no
    later-than
    180
    days
    after
    the
    end
    of
    the calendar
    year
    in
    which
    the
    annual
    mercury
    mass
    emissions
    exceeded
    464
    ounces.
    For
    common
    stack
    and
    multiple
    stack
    configurations,
    installation
    and
    certification
    of
    a mercury
    concentration
    or
    sorbent
    trap
    monitoring
    system
    on
    each
    stack
    (except
    for
    bypass
    stacks)
    is
    likewise
    required
    within
    180
    days
    after
    the
    end
    of the
    calendar
    year,
    if:
    1)
    The
    annual
    mercury
    mass
    emissions
    at
    the
    common
    stack
    have
    exceeded
    464
    ounces
    times
    the
    number
    of
    affected
    units
    using
    the
    common
    stack;
    or
    2)
    The
    sum
    of the
    annual
    mercury
    mass
    emissions
    from
    all
    of
    the
    multiple
    stacks
    or
    ducts
    has
    exceeded
    464
    ounces;
    or
    3)
    The
    sum
    of
    the annual
    mercury
    mass
    ‘-----.-.‘.-‘fl-L,
    - -,
    pmicdnn’
    from
    the
    main
    and
    hvnass
    stacks
    has
    exceeded
    464
    ounces.
    g)
    For
    an
    affected
    unit
    that
    is using
    a
    mercury
    concentration
    CEMS or
    a sorbent
    trap
    system
    -
    under
    Section
    1.15(a)
    of
    this
    Appendix
    to
    continuously
    monitor
    the
    mercury
    mass
    emissions, the
    owner
    or
    operator
    may
    switch
    to the
    methodology
    in
    Section
    1.15(b)
    of
    this
    Appendix,
    provided
    that
    the
    applicable
    conditions
    in
    paragraphs
    (c)
    through
    (f)
    of
    this
    Section
    are
    met.
    Section
    1.16
    stacks
    Monitorini
    of
    mercury
    mass
    emissions
    and
    heat
    innut
    at
    cOmmon
    and
    multinle
    a)
    Unit
    utilizing
    common
    stack
    with
    other
    affected
    unit(s).
    When
    an
    affected
    unit
    utilizes
    a
    common
    stack
    with
    one
    or more
    affected
    units,
    but
    no non-affected
    units,
    the
    owner
    or
    operator
    must
    either:
    1)
    Install,
    certify,
    operate,
    and
    maintain
    the
    monitoring
    systems
    described
    in
    Section
    1.15(a)
    of this
    Appendix
    at
    the
    common
    stack,
    record
    the
    combined
    mercury
    mass
    emissions
    for
    the
    units
    exhausting
    to
    the
    common
    stack.
    Alternatively,
    if,
    in
    accordance
    with
    Section
    1.15(e)
    of
    this
    Appendix,
    each
    of
    the
    units
    using
    the
    common
    stack
    is
    demonstrated
    to emit
    less
    than
    464
    ounces
    of
    mercury-per
    year,
    the
    owner
    or
    operator
    may
    install,
    certify,
    operate
    and
    maintain
    the
    monitoring
    72

    systems
    and
    perform
    the
    mercury
    emission
    testing
    described
    under
    Section
    1.15(b)
    of
    this
    Appendix.
    If
    reporting
    of
    the
    unit
    heat
    input,
    rate
    is
    required,
    determine
    the
    hourly
    unit
    heat
    input
    rates
    either
    by:
    A)
    Apportioning
    the
    common
    stack
    heat
    input
    rate
    to
    the
    individual
    units
    according
    to
    the
    procedures
    in
    40
    CFR
    75.1
    6(e)(3).
    incorporated
    by
    reference
    in
    Section 225.140;
    or
    B)
    Installing,
    certifyirtg,
    operating,
    and
    maintaining
    a
    flow
    monitoring
    system
    and
    diluent monitor
    in
    the
    duct
    to the
    common
    stack
    from
    each
    unit;
    or
    2)
    Install,
    certify,
    operate,
    and
    maintain
    the
    monitoring
    systems
    and
    (if
    applicable)
    perform
    the
    mercury
    emission
    testing described
    in
    Section
    1.15(a)
    or
    Section
    1.15(b)
    of
    this
    Appendix
    in
    the
    duct
    to
    the
    common
    stack
    from
    each
    unit.
    b)
    Unit
    utilizing
    common
    stack with
    nonaffected
    unit(s).
    When
    one
    or
    more
    affected
    units
    utilizes
    a
    common
    stack
    with
    one
    or
    more
    nonaffectedünits,
    the
    owner
    or
    operator
    must
    either:
    1)
    Install,
    certify, operate,
    and
    maintain
    the
    monitoring
    systems
    and
    (if
    applicable)
    perform
    the
    mercury
    emission
    testing
    described
    in
    Section
    1.15(a) or
    Section
    1.15(b)
    of
    this
    Appendix
    in
    the
    duct
    to
    the
    common
    stack
    from
    each
    affected
    unit;
    or
    2)
    Install,
    certify,
    operate,
    and
    maintain
    the
    monitoring
    systems
    described
    in
    Section
    1.15(a)
    of
    this
    Appendix
    in
    the
    common
    stack;
    and
    A)
    Install,
    certify,
    operate,
    and
    maintain
    the
    monitoring
    systems
    and
    (if
    applicable)
    perform
    the
    mercury
    emission
    testing
    described
    in
    Section
    1.15(a)
    or
    Section
    1.15(b) of
    this
    Appendix
    in
    the
    duct
    to
    the
    common
    stack
    from
    each
    non-affected
    unit.
    The
    designated
    representative
    must
    submit
    a
    petition
    to
    the
    Agency
    to
    allow
    a method
    of
    calculating
    and
    reporting
    the
    mercury
    mass
    emissions
    from
    the
    affected
    units
    as
    the
    difference
    between
    mercury
    mass
    emissions
    measured
    in
    the
    common
    stack
    and
    mercury
    mass
    emissions
    measured
    in
    the
    ducts
    of the
    non-
    affected
    units,
    not
    to
    be
    reported
    as
    an
    hourly
    value
    less
    than
    zero.
    The
    Agency
    may
    approve
    such
    a
    method
    whenever
    the
    designated
    representative
    demonstrates,
    to
    the
    satisfaction
    of
    the
    Agency,
    that
    the
    method
    ensures
    that
    the
    mercury
    mass
    emissions
    from
    the
    affected
    units
    are
    not
    underestimated;
    or
    B)
    Count
    the
    combined
    emissions
    measured
    at
    the
    common
    stack
    as
    the
    73

    mercury
    mass
    emissions
    for the
    affected
    units,
    for recordkeeping
    and
    compliance
    purposes,
    in accordance
    with
    paragraph
    (a)
    of
    this
    Section;
    or
    C)
    Submit
    a
    petition
    to the Agency
    to allow
    use of
    a method
    for
    apportioning
    mercury
    mass
    emissions
    measured
    in the
    common
    stack
    to
    each
    of the
    units
    using
    the
    common
    stack
    and for
    reporting
    the
    mercury
    mass
    emissions.
    The Agency
    may approve
    such
    a method
    whenever
    the
    designated
    representative
    demonstrates,
    to the
    satisfaction
    of the
    Agency,
    that
    the
    method
    ensures
    that
    the mercury
    mass emissions
    from
    the
    affected
    units
    are
    not
    underestimated.
    3)
    If the
    monitoring
    option
    in paragraph
    (b)(2)
    of this
    Section
    is
    selected,
    and
    if
    heat
    input
    is
    reciuired
    to
    be reported
    under Part
    225,
    the owner
    or
    operator
    must
    either:
    A)
    Apportion
    the
    common
    stack
    heat input
    rate
    to the individual
    units
    according
    to
    the
    procedures
    in 40
    CFR
    75.16(e)(3), incorporated
    by
    reference
    in
    Section
    225A40;
    or:
    B)
    Install
    a
    flow
    monitoring
    system
    and a
    diluent
    gas
    (02
    or
    C02Lmonitoriun
    system
    in
    the
    duct leading
    from
    each
    affected
    unit
    to
    the common
    stack,
    and
    measure
    the
    heat input
    rate
    in
    each
    duct,
    according
    to
    Section
    2.2
    of
    Exhibit
    C
    to
    this Appendix.
    c)
    Unit
    with
    a main
    stack
    and a
    bypass
    stack.
    Whenever.any
    portion
    of the
    flue
    gases
    from
    an
    affected
    unit
    can be
    routed
    through
    a bypass
    stack
    to avoid
    the
    mercury
    monitoring
    system(s)
    installed
    on the
    main
    stack, the
    owner
    and
    operator
    must
    either:
    1)
    Install,
    certify,
    operate,
    and maintain
    the monitoring
    systems
    described
    in
    Section
    1.15(a)
    of
    this
    Appendix
    on both
    the
    main
    stack
    and
    the
    bypass
    stack
    and
    calculate
    mercury
    mass
    emissions
    for the
    unit
    as
    the sum
    of
    the mercury
    mass
    emissions
    measured
    at
    the two
    stacks;
    2)
    Install,
    certify,
    operate,
    and
    maintain
    the
    monitoring
    systems
    described
    in
    Section
    1.15(a)
    of this
    Appendix
    at
    the
    main
    stack
    and measure
    mercury
    mass
    emissions
    at
    the
    bypass
    stack
    using
    the appropriate
    reference
    methods
    in Section
    1.6(b)
    of
    this Appendix.
    Calculate
    mercury
    mass
    emissions
    for
    the
    unit as
    the sum
    of
    the
    emissions
    recorded
    by
    the
    installed
    monitoring
    systems
    on the
    main
    stack
    and
    the
    emissions
    measured
    by
    the reference
    method
    monitoring
    systems;
    3)
    Install,
    certify,
    operate,
    and
    maintain
    the
    monitoring
    systems
    and
    (if
    applicable)
    perfo
    the
    mercury-
    emission
    testing
    described
    in
    Section
    1.15(a)
    or Section
    1.15(b)
    of this
    Appendix
    only
    on
    the
    main
    stack.
    If
    this
    option
    is chosen,
    it is
    not
    74

    necessary
    to
    designate
    the
    exhaust
    configuration
    as
    a
    multiple
    stack
    configuration
    in
    the
    monitoring
    plan
    required
    under
    Section
    1.10
    of
    this
    Appendix,
    since
    only:
    the
    mainstack
    is
    monitored;
    or
    4)
    If
    the
    monitoring
    option
    in
    paragraph
    (c)(1)
    or
    (c)(2)
    of
    this
    Section
    is
    selected,
    and
    if
    heat
    input
    is
    required
    to
    be
    reported
    under
    Part
    225,
    the
    owner
    or
    operator
    must:
    A)
    Use the
    installed
    flow
    and
    diluent
    monitors
    to
    determine
    the
    hourly
    heat
    input
    rate
    at
    each
    stack
    (mmBtu/hr), according
    to
    Section
    2.2
    of
    Exhibit
    C
    to
    this
    Appendix;
    and
    B)
    Calculate
    the
    hourly
    heat
    input
    at
    each
    stack
    (in
    mmBtu)
    by
    multiplying
    the
    measured
    stack
    heat
    input
    rate
    by
    the
    corresponding
    stack
    operating
    time;
    and
    C)
    Determine
    the
    hourly
    unit
    heat
    input
    by
    summing
    the
    hourly
    stack
    heat
    input
    values.
    d)
    Unit with
    multiple
    stack
    or
    duct
    configuration.
    When
    the
    flue
    gases
    from
    an
    affected
    unit
    discharge
    to
    the
    atmosphere
    through
    more
    than
    one
    stack,
    or
    when
    the
    flue
    gases
    from
    an
    affected
    unit
    utilize
    two
    or
    more
    ducts
    feeding
    into
    a
    single
    stack
    and
    the
    owner
    or
    operator chooses
    to
    monitor
    in
    the.
    ducts
    rather
    than
    in
    the
    stack,
    the.
    owner
    or
    operator
    must
    either:
    1)
    Install,
    certify,
    operate,
    and
    maintain
    the
    monitoring
    systems
    and
    (if
    applicable)
    perform
    the
    mercury
    emission
    testing
    described
    in
    Section
    1.15(a)
    or
    Section
    1.15(b)
    of
    this
    Appendix
    in
    each
    of
    the
    multiple
    stacks
    and
    determine
    mercury
    mass
    emissions
    from
    the
    affected
    unit
    as
    the
    sum
    of
    the
    mercury
    mass
    emissions
    recorded
    for
    each
    stack.
    If another
    unit
    also
    exhausts flue
    gases
    into
    one
    of
    the
    monitored
    stacks,
    the
    owner
    or
    operator
    must
    comply
    with
    the
    applicable
    requirements
    of
    paragraphs
    (a)
    and
    (b)of
    this
    Section.
    in
    order
    to
    properly
    determine
    the
    mercury
    mass
    emissions
    from
    the
    units
    using
    that
    stack;
    2)
    Install,
    certify, operate,
    and
    maintain
    the
    monitoring
    systems
    and
    (if
    applicable)
    perform
    the
    mercury
    emission
    testing
    described
    in
    Section
    1.15(a)
    or
    Section
    1.15(b)
    of
    this
    Appendix
    in
    each
    of
    the
    ducts
    that
    feed
    into
    the
    stack,
    and
    determine
    mercury
    mass
    emissions
    from
    the
    affected
    unit
    using
    the
    sum
    of
    the
    mercury
    mass
    emissions
    measured
    at
    each
    duct,
    except
    that
    where
    another
    unit
    also
    exhausts
    flue
    gases
    to
    one
    or
    more
    of
    the
    stacks, the
    owner
    or
    operator
    must
    also
    comply
    with
    the
    applicable
    75

    requirements
    of
    paragraphs
    (a)
    and
    (b)
    of
    this
    Section to
    determine
    and
    record
    mercury
    mass
    emissions
    fiom
    the
    units
    using that
    stack;
    or.
    3)
    If
    the
    monitoring
    option in paragraph
    (d)(1) or
    (d)(2)
    of
    this
    Section
    is
    selected,
    and
    if
    heat
    input
    is
    required
    to
    be
    reported
    under
    Part
    225,
    the
    owner
    or
    operator
    must:
    A)
    Use the
    installed
    flow
    and
    diluent
    monitors
    to
    determine
    the
    hourly
    heat
    input
    rate
    at
    each
    stack
    or
    duct
    (mmBtu/hr),
    according
    to
    Section
    2.2
    of
    Exhibit
    C
    to
    this
    Appendix;
    and
    B)
    Calculate
    the
    hourly
    heat
    input at
    each
    stack
    or
    duct
    (in
    mmBtu)
    by
    multiplying
    the
    measured
    stack
    (or
    duct)
    heat
    input
    rate
    by
    the
    corresponding
    stack
    (or
    duct)
    operating
    time;
    and
    Determine
    the
    hourly
    unit
    heat
    input
    by
    summing
    the
    hourly
    stack
    (or
    duct)
    heat
    input
    values.
    Section
    1.17
    Calculation
    of
    mercury
    mass
    emissions
    and
    heat
    input
    rate
    The
    owner
    or
    operator
    must
    calculate
    mercury
    mass
    emissions
    and
    heat
    input rate
    in
    accordance
    with
    the
    procedures
    in
    Sections
    4.1
    through
    4.3
    of
    Exhibit
    F
    to
    this
    Appendix.
    Section
    1.18
    Recordkeepg
    and
    reporting
    a)
    General
    recordkeeping
    provisions.
    The
    owner
    or
    operator
    of
    any
    affected
    unit
    must
    maintain
    for
    each
    affected
    unit
    and
    each
    non-affected
    unit
    under
    Section
    1.1
    6(b)(2)(B)
    of
    this
    Appendix
    a
    file
    of
    all
    measurements,
    data,
    reports,
    and
    other
    information
    required
    by
    this
    part
    at
    the
    source
    in
    a
    form
    suitable
    for
    inspection
    for
    at
    least
    3
    years
    from
    the
    date
    of
    each
    record.
    Except
    for
    the
    certification
    data
    required
    in
    Section
    1.11
    (a)(4) of
    this
    Appendix
    and
    the
    initial
    submission
    of
    the
    monitoring
    plan
    required
    in
    Section
    1.11
    (a)(5)
    of
    this
    Appendix,
    the
    data
    must
    be
    collected
    beginning
    with
    the
    earlier
    of
    the
    date
    of
    provisional
    certification
    or
    the
    compliance
    deadline
    in
    Section
    1.14(b)
    of
    this
    Appendix.
    The
    certification
    data
    required
    in
    Section
    1.11
    (a)(4) of
    this
    Appendix
    mustbe
    collected
    beginning
    with
    the
    date
    of
    the
    first
    certification
    test
    performed.
    The
    file
    must
    contain
    the
    following
    information:
    1)
    The
    information
    required
    in
    Sections
    1.11
    (a)(2),
    (a)(4),
    (a)(5),
    (a)(6),
    (b),
    (c)
    (if
    applicable),
    (d).
    and
    (e)
    or
    (f)
    of
    this
    Appendix
    (as
    applicable);
    2)
    Theinformation
    required
    in
    Section
    1.12
    of
    this
    Appendix,
    for
    units
    with
    fluegas
    desulihrization
    systems
    or
    add-on
    mercury
    emission
    controls;
    C)
    76

    3)
    For
    affected
    units,
    using
    mercury
    CEMS
    or
    sorbent
    trap
    monitoring,
    systems,
    for
    each
    hour when
    the ‘unit
    is
    operating,
    record
    the
    mercury
    mass
    emissions,
    ‘ calculated
    in
    accordance
    with
    Section
    4 of Exhibit
    C
    to this
    Appendix.
    4)
    Heat
    input
    and
    mercury
    methodologies
    for
    the
    hour;
    and
    5)
    Formulas from
    itrrrnn1an
    for
    total mercury
    mass
    arni
    heat
    input
    rate
    (if
    applicable);
    b)
    Certification,
    quali-
    assurance
    and
    quality
    control
    recordprovisions.
    The
    owner
    or
    operator
    of
    any
    affected
    unit
    must
    record
    the
    applicable
    information
    in Section
    1.13
    of
    this
    Appendix
    for
    each
    affected
    unit
    or
    group
    of units
    monitored
    at a common
    stack
    and
    each non-affected
    unit
    under
    Section
    1.16(b)(2)(B) of
    this
    Appendix.
    c)
    Monitoring
    plan
    recordkeeping
    provisions.
    1)
    General
    provisions.
    The
    owner
    or operator
    of
    an
    affected
    unit
    must
    prepare
    and
    maintain
    a monitoring
    plan
    for
    each
    affected
    unit
    or
    group
    of
    units
    monitored
    at
    a
    conmion
    stack
    and each
    non-affected
    unit
    under
    Section
    1.16(b)(2)(B)
    of
    this
    Appendix.
    The monitoring
    plan
    must
    contain
    sufficient
    information
    on the
    continuous
    monitoring
    systems
    and
    the
    use
    of
    data
    derived
    from
    these
    systems to
    demonstrate
    that
    all
    the
    unit’s
    mercury
    emissions
    are monitored
    and
    reported.
    2)
    Updates.
    Whenever
    the
    owner
    or
    operator
    makes
    a
    replacement,
    modification,
    or
    change
    in
    a certified
    continuous
    monitoring
    system
    or
    alternative
    monitoring
    system
    under
    40
    CFR
    75,
    subpart
    B. incorporated
    by
    reference
    in
    Section
    225.140,
    including
    a
    change
    in
    the
    automated
    data
    acquisition
    and
    handling
    system
    or
    in
    the
    flue
    gas
    handling
    system,
    that
    affects
    information
    reported
    in the
    monitoring
    plan
    (e.g..
    a
    change
    to a
    serial.number
    for
    a component-of
    a
    monitoring
    system),
    then
    the owner
    or
    operator
    must
    update
    the
    monitoring
    plan.
    3)
    Contents
    of the
    monitoring
    plan.
    Each
    monitoring
    plan
    must
    contain
    the
    information
    in
    Section
    1.1
    0(d)(
    1)
    of
    this
    Appendix
    in
    electronic
    format
    and
    the’
    information
    in Section
    1.10(d)(2)
    in hardcopy
    format.
    d)
    General
    reporting
    provisions.
    1)
    The
    designated
    representative
    for
    an
    affected
    unit
    must
    comply
    with
    all
    reporting
    requirements
    in this
    Section
    and
    with
    any
    additional
    requirements
    set
    forth
    in
    35
    Ill. Adm
    Code
    Part
    225.-
    aA,,aAAb..,,,.
    ,ALfr,
    - --
    ‘AAAA)bJSJL1tJ
    77

    2)
    The:
    designated
    representative”
    foan
    àffêctedmit
    must
    submit
    the
    following
    for
    each
    affected
    unit
    or
    group.
    of
    units
    monitoredat
    a
    common
    stack
    and
    each
    non
    affected
    unit
    under
    Section
    1.1
    6(b)(2)(B)
    of
    this
    Appendix:
    A)
    Monitoring
    plans
    in
    accordance
    with
    paragraph
    (e)
    of this
    Section;
    and
    B)
    Ouarterlv
    reports
    in
    accordance
    with
    paragraph
    (f)
    of
    this
    Section.
    3)
    Other
    petitions
    and
    communications.
    The
    designated
    representative
    for
    an
    affected
    unit
    must
    submit
    petitions,
    correspondence,
    application
    forms,
    and
    petition-related
    test
    results,
    in
    accordance
    with
    the provisions
    in
    Section
    1.14(f)
    of
    this
    Appendix.
    4)
    Quality
    assurance
    RATA
    reports.
    If
    requested
    by
    the
    Agency,
    the
    designated
    representative
    of
    an
    affected
    unit
    must
    submit
    the
    quality
    assurance
    RATA
    report
    for
    each
    affected
    unit
    or
    group
    of
    units
    monitored
    at
    a
    common
    stack
    and
    each
    non-affected
    unit
    under
    Section
    1.1
    6(b)(2)(B)
    of
    this
    Appendix
    by
    the
    later
    of
    45
    days
    after
    completing
    a
    quality
    assurance
    RATA
    according’to
    Section
    2.3
    ‘of
    Exhibit
    B
    to
    this
    Appendix
    or
    15
    days
    of receiving
    the
    request.
    The
    designated
    representative
    must
    report
    the
    hardcopy
    information
    required
    by
    Section
    1.13
    (a)(9)
    of this
    Appendix
    to the
    Agency.
    5)
    Notifications.
    The
    designated
    representative
    for
    an affected
    unit
    must
    submit
    written
    notice
    to
    the
    Agency
    according
    to
    the
    provisions
    in
    40
    CFR
    75.61,
    incorporated
    by
    reference
    in
    Section 225.140,
    for each
    affected
    unit
    or
    group
    of
    units
    monitored
    at a
    common
    stack
    and
    each
    non-affected
    unit
    under
    Section
    1.1
    6(b)(2)(B)
    of this
    Appendix.
    e)
    Monitoring
    plan
    reporting.
    1)
    Electronic
    submission.
    Thern
    designated representative
    for
    an affected
    ‘unit
    ‘must
    submit to the
    Agency
    and
    US
    EPA,
    or
    an
    alternate
    Agency
    designee
    if
    one is
    specified,
    a
    complete,
    electronic,
    up-to-date
    monitoring
    plan
    file
    in
    a format
    specified
    by
    the
    Agency
    for
    each
    affected
    unit
    or
    group
    of
    units
    monitored
    at
    a
    common
    stack
    and
    each
    non-affected unit
    under
    Section
    1.
    16(b)(2)(B)
    of
    this
    Appendix,
    as
    follows:
    No
    later
    than
    21
    days
    prior
    to
    the
    commencement
    of
    initial
    certification
    testing;
    at the
    time
    of
    a
    certification
    or
    recertification
    application
    submission;
    and
    whenever
    an update
    of
    the electronic
    monitoring
    plan
    is
    required,
    either
    under
    Section
    1.10
    of
    this
    Appendix
    or
    elsewhere
    in this
    Appendix.
    2)
    Hardcopy submission.
    The
    designated
    representative
    of
    an
    affected
    unit
    must
    submit
    all
    of
    the hardcopy
    information required
    under
    Section
    1.10
    of
    this
    Appendix,
    for
    each
    affected
    unit
    or group
    of units
    monitored
    at
    a
    common
    stack
    78

    and
    each
    non-affected
    unit
    under
    Section
    L16(b)(2)(B)
    of
    this
    Appendix,
    to
    the
    Agency
    prior
    to
    initial
    certification. Thereafter,
    the
    designated
    representative
    must
    submit
    hardcopy
    infOrmation
    only
    if that
    portion
    of the
    monitoring
    plan
    is revised.
    The
    designated
    representative must
    submit
    the required
    hardcopy
    information
    as
    follows:
    no
    later
    than
    21
    days
    prior
    to the
    commencement
    of
    initial
    certification
    testing;
    with
    any
    certification
    or
    recertification
    application,
    if
    a
    hardcopy
    monitoring
    plan
    change
    is
    associated
    with
    the recertification
    event;
    and
    within
    30
    days
    of
    any
    other
    event
    with
    which
    a hardcopy
    monitoring
    plan
    change
    is
    associated,
    pursuant
    to Section
    1.10(b)
    of
    this
    Appendix.
    Electronic
    submittal
    of
    all
    monitoring
    plan
    information,.
    includinghardcopy
    portions,
    is
    permissible
    provided
    that
    a paper
    copy
    of
    the hardcopy
    portions
    can
    be
    furnished
    upon
    request.
    f)
    Quarterly
    reports.
    1)
    Electronic
    submission.
    Electronic
    quarterly
    reports
    must
    be submitted,
    beginning
    with
    the
    calendar
    quarter
    containing
    the compliance
    date in
    Section
    1.14(b)
    of this
    Appendix,
    unless
    otherwise
    specified
    in
    35 Ill.
    Admin.
    Code
    Part
    225.
    The
    designated
    representative
    for
    an
    affected
    unit
    must
    report
    the
    data
    and
    information
    in this
    paragraph
    (f)(1.)
    and
    the
    applicable
    compliance
    certification
    information
    in
    paragraph
    (fl(2)
    of this
    Section
    to
    the
    Agency
    and
    USEPA,
    or
    an
    alternate
    Agency
    designee
    if one
    is
    specified,
    quarterly
    in
    a format
    specified
    by
    the
    Agency,
    except
    as
    otherwise
    provided
    in 40
    CFR
    75.64(a),
    incorporated
    by reference
    in
    Section
    225.140,
    for units
    in
    long-term
    cold
    storage.
    Each
    electronic
    report
    must
    be
    submitted
    to
    the Agency
    within
    45
    days
    following
    the
    end
    of
    each
    calendar
    quarter.
    Except
    as
    otherwise
    provided
    in
    40
    CFR
    75.64(a)(4)
    and
    (a)(5),
    incorporated by
    reference
    in Section
    225.140,
    each
    electronic
    report
    must
    include
    the date
    of
    report
    generation
    and
    the following
    information
    for
    each
    affected
    unit
    or
    group
    of units
    monitored
    at
    a common
    stack:
    A)
    The
    facility
    information
    in
    40 CFR
    75.64(a)(3),
    incorporated
    by
    reference
    in
    Section
    225.140;
    and
    B)
    The
    information
    and
    hourly
    data
    required
    in paragraphs
    (a)
    and(b)
    of
    this
    Section,
    except
    for:
    i)
    Descriptions
    of
    adjustments,
    corrective
    action,
    and
    maintenance;
    ii)
    Information
    which
    is incompatible
    with
    electronic
    reporting
    (e.g.,
    field
    data
    sheets,
    lab
    analyses,
    quality
    control
    plan);
    iii)
    For
    units
    with
    flue
    gas
    desulfurization
    systems
    or
    with
    add-on
    79

    mercury
    emission
    controls the
    paramethc
    information
    in
    Section
    1.12
    of
    this
    Appendix:
    iv)
    Information
    required
    by
    Section
    1.
    11(d)
    of
    this
    Appendix
    concerning
    the
    causes
    of
    any
    missing
    data
    periods
    and
    the
    actions
    taken
    to
    cure
    such
    causes;
    v)
    Hardcopy
    monitoring
    plan
    information
    required
    by
    Section
    1.10
    of
    this
    Appendix
    and
    hardcopy
    test
    data
    and
    results
    required
    by
    Section
    1.13
    of
    this
    Appendix:
    vi)
    Records
    of
    flow
    polynomial
    equations
    and
    numerical
    values
    required
    by
    Section
    1.13(a)(5)(E)
    of
    this
    Appendix:
    vii)
    Stratification
    test
    results
    required
    as
    part
    of
    the
    RATA
    supplementary
    records
    under
    Section
    1.
    13(a)(7) of
    this
    Appendix;
    Data
    and
    results
    of
    RATAs
    that
    are
    aborted
    or
    nvJ
    1ctt1
    due
    to
    problems
    with
    the
    reference
    method
    or operational
    problems with
    the
    unit
    and
    data
    and
    results
    of
    linearity
    checks
    that
    are
    aborted
    or
    invalidated
    due
    to
    operational
    problems
    with
    the
    unit;
    ix)
    Supplementary
    RATA
    information
    required
    under
    Section
    1.13(a)(7)
    of
    this
    Appendix,
    except
    that:
    the
    applicable
    data
    elements
    under
    Section
    1.1
    3(a)(7)(B)(i)
    through
    (xx)
    of
    this
    Appendix
    and
    under
    Section
    1 1
    3(a)(7)(C)(i)
    through
    (xiii)
    of
    this
    Appendix
    must be reported
    for
    flow
    RATAs
    at
    circular
    or
    rectangular
    stacks
    (or
    ducts)
    in
    which
    angular
    compensation
    for
    yaw
    and/or
    pitch
    angles
    is used
    (i.e.,
    Method
    2F or
    2G
    in
    appendices
    A-i
    and
    A-2
    to
    40
    CFR
    60,
    incorporated
    by
    reference
    in Section
    225.140),
    with
    or
    without
    wall
    effects
    adjustments;
    the
    applicable
    data
    elements
    under
    Section
    1.13(a)(7)(B)(i)
    through
    (xx)
    of
    this
    Appendix
    and
    under
    Section
    l.13(a)(7)(C)(i)
    throug
    (xiii)
    of this
    Appendix
    must
    be
    reported
    for
    any
    flow
    RATA
    run
    at
    a circular
    stack
    in
    which
    Method
    2
    in appendices
    A-i
    and
    A-2
    to
    40
    CFR
    60,
    incorporated
    by
    reference
    in
    Section
    225.140,
    is
    used
    and
    a
    wall
    effects
    adjustment
    factor
    is
    determined
    by
    direct
    measurement:
    the
    data
    under
    Section
    1.1
    3(a)(7)(B)(xx)
    of
    this
    Appendix
    must
    be
    reported
    for
    all
    flow
    RATAs
    at
    circular
    stacks
    in
    which
    Method
    2
    in
    appendices
    A-i
    and
    A-2
    to
    40
    CFR
    60,
    incorporatedby
    reference
    in
    Section
    225.140,
    is
    used
    and
    a
    default
    wall
    effects
    adjustment
    factor
    is applied;
    and
    the
    data
    under
    viii)
    80

    Section
    i.
    I3(7)rn(i)
    though
    (vi)
    must
    be
    reported for
    all
    flow
    RATAs
    at
    rectangular
    stacks
    or
    ducts
    in
    which.
    Method
    2
    in
    appendices
    A-1
    and
    A-2
    to
    40 CFR
    60,
    incorporated
    by
    reference
    in Section
    225.140,
    is
    used
    anda
    wall
    effects
    adjustment factor
    is
    applied.
    x)
    For
    units
    using
    sorbent
    trap
    monitoring systems,
    the
    hourly
    gas
    flow
    meter
    readings
    taken
    between
    the
    initial
    and
    final
    meter
    readings
    for
    the data
    collection
    period;
    and
    C)
    Ounces
    of
    mercury
    emitted
    during
    quarter
    and
    cumulative
    ounces
    of
    mercury
    emitted
    in the
    year-to-date
    (rounded
    to
    the
    nearest
    thousandth);
    and
    D)
    Unit
    or
    stack
    operating
    hours
    for
    quarter,
    cumulative
    unit
    or
    stack
    operating
    hours
    for
    year-to-date;
    and
    E)
    Reporting
    period
    heat
    input
    (if
    applicable)
    and
    cumulative,
    year-to-date
    heat
    input.
    2)
    Compliance
    certification.
    A)
    The
    designated
    representative
    must
    certify
    that
    the
    monitoring
    plan
    information
    in
    each
    quarterly electronic
    report
    (i.e.,
    component
    and
    system
    identification
    codes,
    formulas,
    etc.)
    represent
    current
    operating
    conditions
    for
    the
    affected
    unit(s)
    B)
    The
    designated
    representative
    must
    submit
    and
    sign
    a
    compliance
    certification
    in
    support
    of
    each
    quarterly
    emissions
    monitoring
    report
    based
    on
    reasonable
    inquiry
    of
    those
    persons
    with
    primary
    responsibility
    for
    ensuring
    that
    all
    of the
    unit’s
    emissions
    are
    correctly
    and
    fully
    monitored.
    The
    certification
    must
    state
    that:
    i)
    The
    monitoring
    data
    submitted were
    recorded
    in
    accordance
    with
    the
    applicable
    requirements
    of
    this
    Appendix,
    including
    the
    quality
    assurance
    procedures
    and
    specifications;
    and
    ii)
    With
    regard
    to
    a
    unit
    with
    an
    FGD
    system
    or with
    add-on
    mercury
    emission
    controls,
    that
    for
    all
    hours
    where
    mercury
    data
    is
    missing
    in
    accordance
    with
    Section
    1.13(b)
    of this
    Appendix,
    the
    add-on
    emission
    controls
    were
    operating
    within
    the
    range
    of
    parameters
    listed
    in
    the
    quality-assurance
    plan
    for
    the
    unit
    (or
    that
    quality-
    81

    assure&SO
    CEMSdatawereavailábleto
    document
    proper
    operation
    of
    the
    emission
    controls).
    3)
    Additional
    reporting-reguirements
    The
    designated
    representative
    must
    also
    comply
    with
    all
    of the
    quarterly
    reporting requirements
    in 40 CFR
    75.64(d),
    (f),
    and (g),
    incorporated
    by
    reference
    in
    Section
    225.140.
    82

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