&EPA
                                                                                     United Slates
                                                                                     Environmental Protection
                                                                                     Agwrevr
Fluorinated Gas Production
Final Rule: Subpart L, Mandatory Reporting of Greenhouse Gases
What Must Be Monitored by Each Producer of Fluorinated Gases?

                   Conduct the Following Monitoring Activities...

All Fluorinated Gas Production Facilities:
 D  For processes that have at least one
    process vent with annual uncontrolled
    fluorinated GHG emissions of one ton or
    more, conduct an initial scoping
    speciation to identify all fluorinated
    GHGs that may be generated

 D  Measure GHG emissions that occur as a
    result of startups, shutdowns, and
    malfunctions, either recording
    fluorinated GHG emissions during these
    events, or documenting that these events
    do not result in significant fluorinated
    GHG emissions

 If using the Mass Balance Approach
D   Describe the analytical methods used in the
    site GHG Monitoring Plan, including the
    description of the method, a description of
    the analytical measurement equipment and
    procedures, quantitative estimates of the
    method's accuracy and precision for the
    analytes of interest at the concentrations of
    interest, as well as a description of how
    these accuracies and precisions were
    estimated, including the validation protocol
    used
 Measure the following masses on a monthly or more frequent basis using flowmeters, weigh scales, or a
 combination of volumetric and density measurements with accuracies and precisions that allow the
 facility to meet the error criteria:
 D  Total mass of each fluorine-containing
    product produced
 D  Total mass of each fluorine-containing
    reactant fed into the process
D   The mass removed from the process in each
    stream fed into the destruction device

D   The mass removed from the process in each
    recaptured stream
 Measure the following concentrations at least once each calendar month during which the process is
 operating to be representative of the full range of process conditions using equipment and methods with
 an accuracy and precision that allow the facility to meet the error criteria:
 D  The concentration (mass fraction) of
    each fluorine-containing reactant,
    product, and by-product in each stream
    that is fed into the destruction device,
    OR the concentration of total fluorine in
    each stream that is fed into the
    destruction device
D   The concentration (mass fraction) of each
    fluorine-containing by-product in each
    stream that is recaptured OR the
    concentration of total fluorine in  each
    stream that is recaptured

D   Characterize emissions from process vents
    at frequency specified in rule
Fluorinated Greenhouse Gas Production Monitoring Checklist
Mandatory Reporting of Greenhouse Gases
                            November 2010
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 If using the Process-Vent-Specific Emission Factor Approach
Conduct an emissions test to develop the process-vent-specific emission factor every 10 years, when a
change to the operating scenario is calculated to result in a 15 percent or greater change in the emission
factor, or when a continuous process vent with less than 10,000 mtCO2e is later found to have emissions
of 10,000 mtCO2e or greater.  Measure process activity during the year.
 D  Conduct the emissions test during
    representative performance of the
    process or operating scenario(s) of the
    process, as applicable. For continuous
    processes, sample the process vent for a
    minimum of 3 runs of 1 hour each. If
    the relative standard deviation among
    the emission factors based on each run is
    greater than 15%, sample for an
    additional 3 runs.

 D  Both during the test and throughout each
    year, measure the process activity (e.g.,
    process feed or process production)
    using flow meters, weigh scales, or other
    measurement devices or instruments
    with an accuracy and precision of ±1
    percent of full scale or better.
D   If process vents from separate processes are
    manifolded together, sample emissions
    from each process in the ducts before the
    emissions are combined or sample in the
    common duct when only one process is
    operating.  Alternatively, sample the
    combined emissions and use engineering
    calculations or engineering assessments to
    allocate the emissions to each process vent,
    provided the sum of calculated emissions
    across the process vents is within 20% of
    the total measured emissions.

D   Produce an emissions test report that
    contains all information and data used to
    derive the process-vent-specific emission
    factor, as well as key process conditions
    during the test.
 If using the Process-Vent-Specific Emission Calculation Factor Approach	
Conduct an emissions calculation for each operating scenario for each batch and continuous process vent
every 10 years, or when a change to the operating scenario is expected to change the process-vent-specific
emissions calculation factor. Measure process activity during the year.
 D  For continuous process vents, determine
    the emissions based on the process
    activity for representative performance
    of the operating scenario; for batch
    process vents, determine emissions
    based on the process activity for each
    typical batch operating scenario.

 D  Throughout each year, measure the
    process activity (e.g., process feed or
    process production) using flow meters,
    weigh scales, or other measurement
    devices or instruments with an accuracy
    and precision of ±1 percent of full scale
    or better.
D   The emission calculation must be
    documented by identifying the process, the
    operating scenario, and the process vents.
    The documentation must contain the
    information and data used to calculate the
    process-vent-specific emission calculation
    factor.
Fluorinated Greenhouse Gas Production Monitoring Checklist
Mandatory Reporting of Greenhouse Gases
                             November 20 fO
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 If the Facility conducts a site-specific leak detection method or monitoring approach for pieces of
 equipment:	
 D  If you determine that EPA Method 21 is
    appropriate for monitoring leaks from
    your process, conduct screening value
    concentration measurements using
    Method 21.

 D  Conduct monitoring on at least 1/3 of
    equipment annually, ensuring this 1/3 is
    representative of equipment in the
    process.
 If the Facility Destroys Fluorinated GHGs:
OR
D   Develop a site-specific leak monitoring
    approach.

D   Validate the leak monitoring method and
    describe the method and the validation in
    the GHG Monitoring Plan.

D   Conduct monitoring on at least 1/3 of
    equipment annually if emissions are
    estimated based on monitoring of
    individual pieces of equipment. Ensure this
    1/3 is representative of equipment in the
    process.
Conduct an emissions test to determine the destruction efficiency. If CF4, SF6, or a saturated PFC other
than CF4 is vented to the destruction device in more than trace concentrations, develop a destruction
efficiency specifically for that compound or for a more difficult-to-destroy surrogate that is specified in the
rule to take credit for the emissions reduction.
 D  Sample the inlet and outlet of the
    destruction device for a minimum of
    three runs of 1 hour each to determine
    the destruction efficiency.
      D   Conduct the test when operating at high loads
          reasonably expected to occur and when
          destroying the most-difficult-to-destroy
          fluorinated GHG (or a more difficult to
          destroy surrogate) that is fed into the device
          or that belongs to the group of fluorinated
          GHGs for which you wish to establish a DE.
Track emissions from destruction device malfunctions and measure previously produced fluorinated
GHGs fed into destruction device:
 D  Account for any temporary reductions
    in the destruction efficiency that result
    from any malfunctions of the
    destruction device.

 D  Measure the mass of each fluorinated
    GHG that is fed into the destruction
    device and that was previously
    produced using flow meters, weigh
    scales, or a combination of volumetric
    and density measurements  with an
    accuracy and precision of ±1 percent
    of full scale or better.
      D   Measure the concentration of the fluorinated
          GHG being destroyed (if the measured mass
          includes more than trace concentrations of
          materials other than the fluorinated GHG
          being destroyed).
Fluorinated Greenhouse Gas Production Monitoring Checklist
Mandatory Reporting of Greenhouse Gases
                                     November 2010
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 If the Facility vents residual fluorinated GHGs from containers:
 D  Measure residual fluorinated GHGs in              D  Develop a heel factor (based on
    containers received by the facility using      OR        representative samples) for each
    either scales or pressure and temperature                combination of fluorinated GHG, container
    measurements with an accuracy and                    size, and container type, and apply this
    precision of ± 1 percent                                factor to the number of containers vented.
See also the information sheet for Fluorinated Greenhouse Gas Production available at:
htto://epa.gov/climatechange/emissions/ghg infosheets.html.
Fluorinated Greenhouse Gas Production Monitoring Checklist                                November 2010
Mandatory Reporting of Greenhouse Gases

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