Technical Support Document for the
Revisions to Definition of Cogeneration Unit in Clean Air Interstate Rule (CAIR), CAIR Federal
Implementation Plan, Clean Air Mercury Rule (CAMR), and CAMR Proposed Federal Plan;
Revision to National Emission Standards for Hazardous Air Pollutants for Industrial,
Commercial, and Institutional Boilers and Process Heaters; and Technical Corrections to CAIR

and Acid Rain Program Rules

Methodology for Thermal Efficiency and Energy Input Calculations and
Analysis of Biomass Cogeneration Unit Characteristics

EPA Docket number: EPA-HQ-OAR-2007-0012
April 2007

U.S. Environmental Protection Agency
Office of Air and Radiation


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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR

FIP, CAMR, and Proposed CAMR Federal Plan

This Technical Support Document (TSD) has several purposes. One purpose of the TSD is to set
forth the methodology for determining the thermal efficiency of a unit for purposes of applying
the definition of the term "cogeneration unit" under the existing CAIR, the CAIR model trading
rules, the CAIR FIP, CAMR, the CAMR Hg model trading rule, and the proposed CAMR
Federal Plan. Another purpose of the TSD is to present information relevant to the proposed
revisions, and other potential revisions for which EPA is requesting comment, concerning the
thermal efficiency standard. One of the critical values used in the determination of thermal
efficiency is the "total energy input" of the unit. Consequently, in connection with setting forth
the methodology for determining thermal efficiency, the TSD specifically addresses what
formula is to be used in calculating a unit's total energy input under the existing rules.

There are two major issues concerning the calculation of total energy input. The first issue is
whether, under the existing rules, total energy input is determined based on the higher or lower
heating value of the fuel or fuels combusted in the unit and how to calculate heating value. As
discussed below, EPA maintains that, under the existing rules, total energy input constitutes the
lower heating value of the fuel or fuels combusted by the unit, and EPA is requesting comment
on whether the existing rules should be revised to state explicitly the formula for calculating total
energy input using lower heating value. The second issue is whether and to what extent the
existing rules should be revised to exclude non-fossil fuel (such as biomass) from the calculation
of total energy input. As discussed below, EPA is requesting comment on the proposed revision,
and other potential revisions, concerning such exclusion. EPA is not requesting comment on any
other aspects of the thermal efficiency standard such as, for example, the adoption of a standard
as part of the definition of the term "cogeneration unit," the specific percentages of total energy
output that must be met, or the treatment of useful thermal energy in the thermal efficiency
standard.

Another purpose of the TSD is to address the information that EPA has developed concerning
the units potentially affected by the proposed change to the existing rules concerning the extent
to which non-fossil fuel should be excluded from the calculation of a unit's total energy input.
As discussed in the preamble of the proposed rule for which this TSD is provided, EPA has taken

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a number of steps to gather the most complete information we could about the number, size,
location, industry, fuel use, electricity sales, and environmental impacts of the units potentially
affected by the proposed change concerning the exclusion of non-fossil fuel from the calculation
of total energy input. The TSD provides more detailed information about the biomass
cogeneration unit inventory, data sources, and emissions calculations that EPA used in its
analysis for the proposed rule.

I. Thermal Efficiency and Total Energy Input

In this section of the TSD, EPA describes the methodology for calculating thermal efficiency of
a unit in order to help determine whether the unit qualifies for the cogeneration unit exemption.
In addition, EPA addresses the definition and calculation of "total energy input," which is used
in calculating thermal efficiency in order to determine whether the unit qualifies for the
cogeneration unit exemption.

A. Determining Thermal Efficiency

In CAIR, the CAIR model trading rules, the CAIR FIP, CAMR, the CAMR Hg model trading
rule, and the proposed CAMR Federal Plan, EPA included, as one criterion that a unit must meet
in order to potentially qualify for the cogeneration unit exemption, the requirement that the unit
meet a thermal efficiency standard. In adopting a thermal efficiency standard, EPA decided to
use the thermal efficiency standard adopted by the Federal Energy Regulatory Commission
(FERC) in determining whether a unit is a qualifying cogeneration unit under section (3)(18)(B)
of the Federal Power Act (as amended by the Public Utility Regulatory Policy Act (PURPA)).
However, EPA decided to make the thermal efficiency standard applicable to all fuels combusted
by a unit, while the FERC limited application of the standard to natural gas and oil. (See 18 CFR
292.205(a)(2) and (b)(1). See 70 FR 25277).

The methodology for determining thermal efficiency adopted by EPA in the existing rules can be
represented as the following:

Thermal Efficiency = (Net Electric Output + Net Thermal Output/2)/Fuel Heat Input (LHV)

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More background on the decision to use a thermal efficiency standard and how to perform the
thermal efficiency calculation can be found in the "Cogeneration Unit Efficiencies Calculation"
TSD for CAIR.1

B. Calculating Total Energy Input

1. Higher Heating Value vs. Lower Heating Value

A critical value used in applying the thermal efficiency standard is the "total energy input" for
the year for which thermal efficiency is being calculated. One of the first steps in determining
the total energy input for a unit is identifying the unit's fuel mix and the heat content or heating
value of the fuel or fuels combusted by the unit. Heating value, commonly expressed in Btu, can
be measured in several ways, but the most common are to use gross heat content (referred to as
"higher heating value" or "HHV") or to use net heat content (referred to as "lower heating value"
or "LHV"). According to the Energy Information Administration (EIA) of U.S. Department of
Energy, higher heating value includes, while low heating value excludes, "the energy used to
vaporize water (contained in the original energy form or created during the combustion
process)."2

As discussed above, EPA adopted in the existing rules the same thermal efficiency standard as
that adopted by FERC in determining whether a unit is a qualifying cogeneration unit, except
that EPA applied the thermal efficiency standard to all fuels and the FERC limited application of
the standard to natural gas and oil. FERC's regulations that included the thermal efficiency
standard stated that "energy input" in the form of natural gas and oil "is to be measured by the
lower heating value of the natural gas or oil." See 18 CFR 292.202(m). As explained by FERC
when it adopted these regulations in 1980 (45 FR 17959, 17962 (1980)):

Lower heating values were specified in the proposed rules in recognition of the fact that
practical cogeneration systems cannot recover and use the latent heat of water vapor
formed in the combustion of hydrocarbon fuels. By specifying that energy input to a

1	Cogeneration Unit Efficiencies Calculation, March 2005. OAR-2003-0053-2087
http://epa.gov/cair/pdfs/tsd_cogen.pdf

2	http://www.eia.doe.gov/glossary/glossary_h.htm

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facility excludes energy that could not be recovered, the commission hoped that the
proposed energy efficiency standards would be easier to understand and apply.

Because the thermal efficiency standard on which EPA's thermal efficiency standard was based
is premised on using LHV to determine total energy input, EPA believes that the thermal
efficiency standard in the existing CAIR, CAIR model trading rules, CAIR FIP, CAMR, CAMR
Hg model trading program, and the proposed CAMR Federal Plan should be interpreted as
similarly requiring the use of LHV of all fuels combusted at the unit in calculating a unit's total
energy input. EPA notes that, if a unit uses HHV for the calculations and meets the thermal
efficiency standard on that basis, the unit would necessarily meet the standard using LHV. See
45 FR 17962.

2. Definition of Lower Heating Value (LHV)

Although FERC regulations use lower heating value to measure a unit's energy input from
natural gas and oil, the regulations do not specify a formula for calculating lower heating value.
While there may be alternative definitions of, or formulas for calculating, LHV, EPA maintains
that the following formula is consistent with the FERC approach for calculating LHV of fuels by
excluding from the higher heating value of such fuels "the latent heat of water vapor formed in
the combustion of hydrocarbon fuels." See 45 FR 17962. Under this formula, the relationship
between the lower heating value of a fuel and the higher heating value of that fuel is:

LHV = HHV- 10.55(W + 9H)

Where:

LHV = lower heating value of fuel in Btu/lb,

HHV = higher heating value of fuel in Btu/lb,

W = Weight % of moisture in fuel, and
H = Weight % of hydrogen in fuel.

EPA believes that the existing CAIR, CAIR model trading rules, CAIR FIP, CAMR, CAMR Hg
model trading rule, and the proposed CAMR Federal Plan should be interpreted to require use of
this formula for calculating lower heating value for purposes of determining total energy input.

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This formula is consistent not only with the description of "lower heating value" by FERC, but
also with EIA's description of the term. Moreover, the formula reflects a standard approach to
calculating lower heating value. See the International Flame Research Foundation Combustion
Handbook, http://www.handbook.ifrf.net (IFRF 1999-2000) (discussing relationship between
higher and lower calorific value of a fuel).

EPA is requesting comment on the methodology described above for determining a unit's
thermal efficiency (i.e., on the use of lower heating value in the denominator of the equation for
thermal efficiency) and on the above-described formula for calculating LHV to determine a
unit's total energy input, under the existing regulations. In addition, EPA is considering adding
language to the existing regulations specifying this formula for calculating total energy input for
purposes of applying the thermal efficiency standard. In particular, EPA is considering revising
the definition of "total energy input" in the existing CAIR, CAIR model trading rules, CAIR FIP,
CAMR, CAMR Hg model trading rule, and proposed CAMR Federal Plan by adding the
following language to that definition:

The energy input of any form of energy shall be measured by the lower heating value of that
form of energy calculated as follows:

LHV = HHV- 10.55(W + 9H)

Where:

LHV = lower heating value of fuel in Btu/lb,

HHV = higher heating value of fuel in Btu/lb,

W = Weight % of moisture in fuel, and
H = Weight % of hydrogen in fuel.

As discussed in the preamble of the proposed rule for which this TSD is provided, EPA requests
comment on whether the formula for calculating lower heating value shown above should be
added to the existing regulations or whether some alternative formula for calculating total energy
input or lower heating value is appropriate and should be added to the existing regulations.

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3. Fuels to Include in Total Energy Input

In the rulemaking for which this TSD is provided, EPA is proposing to revise the thermal
efficiency standard, as applied to certain existing units, to include in "total energy input" only the
energy input from fossil fuel combusted by the units, rather than energy input from all fuels
combusted. This change would make it more likely that those existing units that burn biomass
and cogenerate electricity and useful thermal energy (referred to herein as "biomass cogeneration
units") could meet the thermal efficiency standard and qualify as exempt cogeneration units
under these rules. As discussed in the preamble of the rulemaking for which the TSD is
provided, EPA is requesting comment on the proposed revision and on an alternative under
which "total energy input" would instead be defined to include energy input from all fuels
combusted, except biomass.

II. Units Affected by the Proposed Rule Change

This section of the TSD discusses the approach EPA used to estimate the universe of
cogeneration units potentially affected by the proposed rule. As explained in more detail below,
we used several data sources and selection criteria to develop a list of units, estimate which units
would possibly be affected by a rule change, and what the environmental impacts might be.

These inventory lists of identified biomass cogeneration units represent EPA's best effort to
identify biomass cogeneration units that meet the specified criteria, but should not be assumed to
be all inclusive or a determination of rule applicability.

A. Inventory Criteria and Information

To start, EPA wanted to know more about the population of biomass cogeneration units currently
in use and their characteristics. We defined the appropriate criteria for the cogeneration units
and then applied the criteria to help identify units that would potentially be included in CAIR
and/or CAMR. The final inventory list of existing biomass cogeneration units was developed by
applying the following criteria:

•	Produced both electricity and useful thermal energy;

•	Associated with a cogeneration generator with capacity greater than 25MW;

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•	Reported some type of biomass fuel use (biomass and coal use for CAMR units) in the
2001-2004 period; and

•	Located in the CAIR or CAMR regions.

This exercise resulted in an inventory of 181 units in the CAIR region and 55 units in the CAMR
region. The list of CAIR units includes all known units in states that participate in the NOx
and/or S02 trading programs. These inventories are not to be used to determine applicability for
any biomass cogeneration units. Rather, they represent EPA's best attempt to identify units
potentially affected by the proposed rule. See Appendix A for List of Identified Biomass
Cogeneration Units in CAIR and CAMR Regions.

Once the units were identified, EPA collected more detailed information about the characteristics
of each unit. The inventory was populated with the following types of data from 2004, the most
recent baseline period year:

•	Plant location;

•	Industry category;

•	Unit size (generator nameplate);

•	Utilization

•	Unit fuel type(s) and amounts; and

•	Unit sales to the grid.

In addition, we had limited information about the emission controls installed on some units. The
information available was sufficient to allow EPA to estimate which units were most likely to be
affected by the proposed change to the CAIR and CAMR applicability provisions and
cogeneration unit definition to limit total energy input for some units to fossil fuels. Other units
were expected to either already be exempt from CAIR and CAMR or to remain covered by the
cap-and-trade programs regardless of the proposed change.

Emissions data at the unit level was not available and had to be estimated. The approach for
estimating emissions is covered later in this document.

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B. Data Sources

After researching several sources of data, EPA decided to use data reported by owners to the
Energy Information Administration (EIA). The EIA data is based on Electricity Survey Forms
860 and 767. We also considered data from EPA databases, the National Emission Inventory
(NEI), and Energy and Environmental Analysis, Inc (EEA) Industrial Boiler database, but found
that EIA had the most complete data for our needs at the individual unit level. The EIA database
contains the associated generator nameplate data that is an important applicability factor for
CAIR and CAMR. The associated generator nameplate is not available in the other databases.
EIA also identifies whether each generator is a cogenerator, and whether it meets FERC
qualifying facility requirements for cogeneration. In addition, there is an EIA data field that
identifies whether the generator delivers electricity to the grid (EGU/Non-EGU status).

However, the field only indicates those units that may deliver some amount of electricity to the
grid, but not how much they actually sold.

For the inventory, we used the EIA-860 and EIA-767 databases to identify all boilers associated
with a cogenerator with generator nameplate greater than 25 MW. The EIA-767 database has
fuel use and heat content by specific fuel type. This data can be used to identify units that burn
both biomass and any fossil fuel or any coal. We used this data for the inventory and identified
any unit burning any amount of a biomass fuel, and biomass fuel and coal, in the 2001 to 2004
period.

EIA, and the other databases, do not provide the data necessary to determine if an EGU
cogeneration unit is exempt -- percent of unit generating capacity or total amounts of electricity
sold to the grid, and overall thermal efficiency. Prior to 2001, EIA provided facility electricity
sales data and total facility nameplate in the non-utility version of EIA-860. This data can be
used to make an estimate of the percentage of plant capacity sold, but not unit capacity. In
addition, EIA does not collect unit emissions data from these sources, leaving a gap in the
inventory analysis.

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C. Developing Emissions Estimates

EIA does not collect measured emissions from the units of interest, but it does collect
information such as fuels burned, fuel heat and sulfur content, New Source Performance
Standards (NSPS) applicability, and control equipment information that can be used in
conjunction with emission factors to estimate annual NOx, SO2, and Hg emissions. The emission
calculations are based on 2004 fuel data and other emission-related information provided in the
EIA-767 boiler database, combined with emission factor information from other sources.
Estimation methods for each pollutant are outlined below.

1. NOx Emissions

Whenever possible, EIA annual controlled NOx rates (lb/mmBtu) and annual fuel heat input from
EIA-767 were used to calculate annual NOx emissions. The EIA annual controlled NOx rates are
in lbs/mmBtu and were found in the boiler table of the EIA-767 database. The EIA-767
instructions request that these rates be based on data from continuous emission monitors
(CEMs), if possible. If CEMS data are not available, these rates should be based on the method
used to report emissions data to environmental authorities. The controlled NOx rates are not fuel-
specific, so the same annual NOx rate was multiplied by each fuel's annual heat input in the
calculations.

However, not all units reported emission rate information on EIA-767, so we had to look to
additional sources for average emission factors. U.S. EPA AP-42 emission factors and National
Renewable Energy Lab (NREL) emission factors were used when EIA factors were not
available. AP-42 and NREL tables contain average emission factors for most unit type, NOx
control, and fuel type combinations. The NSPS status was the main driver used in determining
the most appropriate NOx emission factor since we did not have consistent boiler type
information from EIA-767. These emission factors were used in conjunction with the annual fuel
quantities and heat input for each boiler to calculate the annual NOx emission estimate for each
fuel burned by the unit. The NOx emission factors are reported in Table 1 below.

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Table 1

NOx Emission Factors (AP42 and NREL)

Unit Type

EIA Fuel

Emission
Factor

Factor Source

Non-NSPS Boiler
Non-NSPS Recovery
Furnace

Wood/Woodwaste Liquids
Other Biomass Liquids

1.66 lbs/1000
gals

NREL Table 12.6b

Non-NSPS Boiler
Non-NSPS Recovery
Furnace

Distillate Fuel Oil

24 lbs/1000 gals

AP42 Table 1.3-1

D Boiler

D Recovery Furnace

Residual Fuel Oil
Waste Oil (petroleum based
liquid waste)

40 lbs/1000 gals

AP42 Table 1.3-1

Non-NSPS Boiler
Non-NSPS Recovery
Furnace

Residual Fuel Oil
Waste Oil (petroleum based
liquid waste)

47 lbs/1000 gals

AP42 Table 1.3-1

Da Boiler
Db Boiler

Natural Gas

0.14 lb/mmBtu

AP42 Table 1.4-1

D Recovery Boiler

Natural Gas

0.19 lb/mmBtu

AP42 Table 1.4-1

Non-NSPS Boiler
Non-NSPS Recovery Boiler

Natural Gas

0.27 lb/mmBtu

AP42 Table 1.4-1

Non-NSPS Recovery Boiler

Propane Gas

0.27 lb/mmBtu

AP42 Table 1.5-1

Da Boiler
Db Boiler
Non-NSPS Boiler

Wood Waste Solids

0.22 lb/mmBtu

AP42 Table 1.6-2

D Recovery Furnace
Da Recovery Furnace
Non-NSPS Recovery
Furnace

Black Liquor

1.5 lbs/ton

NREL Table 12.6a

Non-NSPS Boiler

Other Biomass Solids

1.2 lbs/ton

NREL Table 12.6a

Non-NSPS Boiler

Sludge Waste

5 lbs/ton

NREL Table 12.6a

Non-NSPS Boiler

Tire Derived Fuel

22 lbs/ton

NREL Table 12.6a

D Boiler

Bituminous Coal

10 lbs/ton

AP42 Table 1.1-3

Non-NSPS Boiler

Bituminous Coal
Petroleum Coke
Waste Coal

15 lbs/ton

AP42 Table 1.1-3

Non-NSPS Boiler

Agricultural By-Products

1.2 lbs/ton

NREL Table 12.6a

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2. SO2 Emissions

The SO2 emissions were similarly calculated based on EIA fuel quantity, heat content, and fossil
fuel sulfur content from EIA-767, combined with SO2 emission factors from AP-42, NREL, 40
CFR Part 75, and NESCAUM. EIA fuel sulfur content was used in all of the fossil fuel emission
estimates except for natural gas, propane gas, and petroleum coke. The Part 75 default SO2
emission rate of 0.0006 lb/mmBtu was used for natural gas and propane gas. We assumed a
petroleum coke sulfur content of 4.5% since none of the facilities that burned petroleum coke
had reported the sulfur content to EIA.

SO2 emission factors for all of the non-fossil fuels, except for wood waste solids and black
liquor, were taken from the same NREL document used for the non-fossil fuel NOx emission
factors. The wood waste solids emission factor was taken from AP-42. The black liquor emission
factor was based on information from a NESCAUM document. The SO2 emission factors are
shown in Table 2 below.

Table 2

S02 Emission Factors (AP42, Part 75, NREL, NESCAUM)

EIA Fuel

Emission Factor

Factor Source

Wood/Wood Waste Liquids
Other Biomass Liquids

1.42 lbs/1000 gals

NREL Table 12.6a

Wood Waste Solids

0.025 lb/mmBtu

AP42 Table 1.6-2

Sludge Waste

2.8 lbs/ton

NREL Table 12.6a

Agricultural By-Products
Other Biomass Solids

0.08 lb/ton

NREL Table 12.6a

Black Liquor

1.5 lb/ton — 3 to 5% S, with
less than 1% of sulfur emitted.

NESCAUM BART

Distillate Fuel Oil
Residual Fuel Oil
Waste Oil

157 (%S) lbs/1000 gals

AP42 Table 1.3-1

Natural Gas

0.0006 lb/mmBtu

Part 75 Default Rate

Propane Gas

0.0006 lb/mmBtu

Part 75 Default Rate

Tire Derived Fuel

38 lbs/ton

NREL Table 12.6a

Bituminous Coal (CFB Boiler)

31 (%S) lbs/ton

AP42 Table 1.1-3

Bituminous Coal

38 (%S) lbs/ton

AP42 Table 1.1-3

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EIA Fuel

Emission Factor

Factor Source

Subbituminous Coal

38 (%S) lbs/ton

AP42 Table 1.1-3

Waste Coal (CFB Boiler)1

31 (%S) lbs/ton

AP42 Table 1.1-3

Petroleum Coke (CFB Boiler)1

31 (%S) lbs/ton - assumed S
content of 4.5%

AP42 Table 1.1-3

Petroleum Coke

38 (%S) lbs/ton - assumed S
content of 4.5%

AP42 Table 1.1-3

1 The EIA reported standard of 0.129 lb/mmBtu was used for one waste coal/petroleum coke fired CFB
unit in place of the petroleum coke sulfur content assumption used for other petroleum coke units.

EIA flue gas desulfurization (FGD) unit SO2 removal efficiencies for different types have been
included in the calculation. We are unsure how complete the FGD data are, so we also capped
NSPS unit SO2 emission rates at the emission limit in the applicable subpart. EIA-767
information on FGD units was used to identify units with SO2 control devices, and the FGD
control efficiency.

3. Hg Emissions

Although fuel Hg content is not reported by EIA, the annual Hg emissions had to be calculated
for coal burning units in CAMR. We decided to use the uncontrolled emission factors and
emission modification factors (from the Integrated Planning Model (IPM)) for the coal type and
control equipment that was reported to EIA. For the biomass cogeneration Hg estimate, we
calculated a median emission factor for bituminous coal and sub-bituminous coal from the EPA
emission factor clusters. The median emission factor for bituminous coal was 12.07 lbs/TBtu,
and 5.02 lbs/TBtu for sub-bituminous coal. The emission modification factors are based on
boiler type, coal type, and control equipment. The EIA data did not consistently identify boiler
type, so our assignment of emission modification factors was limited to coal type and control
equipment. The emission modification factors that we used for the biomass cogeneration
inventory are listed below in Table 3.

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Table 3

Emission Modification Factors Used in Biomass Unit Hg Estimates

Hg Emission
Modification
Factor

Unit
Type1

Coal
Type2

NOx
PostCombustion
Control

Particulate
Matter
Control

S02 Post
Combustion
Control

0.05

Fluidized
Bed

BIT

SNCR

Fabric Filter

Yes, Not Identified

0.05

Fluidized
Bed

BIT

None

Fabric Filter

None

0.64

Fluidized
Bed

BIT

None

Cold Side ESP

None

0.1

-

BIT

None

Fabric Filter

Dry FGD

0.11

-

BIT

None

Fabric Filter

None

0.34

-

BIT

None

Cold Side ESP

Wet FGD

0.64

-

BIT

None

Cold Side ESP

None

0.64

-

BIT

None

Cold Side ESP

Dry FGD

0.9

-

BIT

None

Wet Scrubber

None

0.97

-

SUB

None

Cold Side ESP

None

1.0

-

BIT

None

Hot Side ESP

None

1	Unit type was only identified for fluidized bed units.

2	Waste coal and synthetic coal were treated as bituminous.

D. Determining Affected Units

With an estimated universe of biomass cogeneration units and their attributes, the next step was
to try to estimate which ones were most likely to be affected by a change to the CAIR and
CAMR applicability provisions and cogeneration unit definition to limit total energy input to
fossil fuels for some units. This subset consists of units that are (1) below the threshold for
electricity sales and also (2) operating below the thermal efficiency standard. Because EPA does
not have either of these important pieces of information from EIA or the American Forest and
Paper Association (AF&PA), we had to use the information we did have to make a reasonable
assessment.

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Any units that reported to EIA that they did not have the ability to sell power to the grid were
eliminated first. There are 79 units in the inventory that reported they do not sell power to the
grid. Units at plants that sold more than the threshold (i.e., more than 1/3 potential electric
output capacity or 219,000 MWh) in 1999 or 2000 (the most recent years for which such data
exists) were also eliminated because they would still not qualify as exempt cogeneration units
from CAIR and CAMR, even with the proposed revisions to the applicability provisions and
cogeneration unit definition to limit total energy input to fossil fuels for some units. Using data
that EPA analyzed in developing the NOx NOD A Allocations, we identified 15 more units above
the electricity sales threshold.3 Since EPA did not have any evidence that any other units had
surpassed the threshold, it assumed that the rest had electricity sales below the threshold level to
be conservative in its estimates. EPA recognizes that some of these remaining units may have
sales above the threshold in unreported years and therefore also not qualify for the cogeneration
unit exemption. In addition, one unit in the inventory was found to have irreconcilable data
problems and not included in the results.

That left a total of 86 units that were selling power to the grid and assumed to be below the sales
threshold. EPA then analyzed the heat input of the remaining units to determine which ones
were likely to meet the thermal efficiency standard in the existing rules and therefore, already
qualify for the exemption from CAIR and CAMR for cogeneration units. The best indicator to
make this determination was the ratio of fossil heat input to total heat input. In general, the
higher the percentage of heat input from fossil fuels, the more likely a biomass cogeneration unit
is to meet the existing efficiency standard because there is less moisture in the fuel (moisture
lowers the thermal efficiency). To estimate which units were likely to meet the existing
efficiency standard in the cogeneration unit definition, EPA calculated the percentage of heat
input from biomass and the percentage of heat input from fossil fuel. We also performed
calculations on what percentage of fossil fuel was generally needed for a unit to be likely to meet
the existing efficiency standard based on the type of biomass and type of fossil fuel or fuels
burned. To do this, a number of assumptions about unit characteristics and performance

3 EPA published a Notice of Data Availability (NODA) with initial unit NOx allocations for the CAIR Federal
Implementation Plan trading programs, " Notice of Data Availability for EGU NOx Annual and NOx Ozone Season
Allocations for the Clean Air Interstate Rule Federal Implementation Plan Trading Programs," 71 FR 44283.

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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR

FIP, CAMR, and Proposed CAMR Federal Plan

attributes were required. These assumptions and calculations are EPA's best estimate, but are
not definitive measures of unit efficiency.

For units burning bituminous coal, EPA calculated that at least 40% of the heat input would have
to come from coal and the remainder from biomass. For other fossil fuels, the heat input
percentages were found to be at least 30% for heating oil and 10% for natural gas and the
remaining heat input from biomass. These are assumptions based on model unit characteristics
and may not apply to all units. Not all units with fossil fuel input above these levels are
guaranteed to meet the existing efficiency standard and not all units below these levels are
guaranteed not to meet the existing efficiency standard due to their particular boiler and turbine
characteristics. More information about the fuel and heat input assumptions and the thermal
efficiency calculation is available in the following sections.

Units with fossil heat input above the minimum are assumed to already meet the existing
efficiency standard and be eligible for the cogeneration unit exemption. We have assumed that
those units below the minimum are unlikely to meet the existing efficiency standard and will not
be eligible for the exemption, as currently written. These are the units that would be affected by
the proposed change in the efficiency standard to limit total energy input for some units to fossil
fuels. After calculating the heat input ratios for each unit, there were 55 units in this subset for
NOx emissions, 46 units for SO2 emissions, and 6 units for Hg emissions. The other units who
would not be affected by the change consist of 31 units for NOx emissions, 28 units for SO2
emissions, and 30 units for Hg emissions. The number of units for NOx and SO2 are not identical
because the state of Arkansas is only required to make NOx emissions reductions under CAIR,
not SO2 reductions. See Appendix B for the List of Biomass Cogeneration Units Potentially
Affected by the Proposal in CAIR and CAMR Regions.

E. Thermal Efficiency Estimates for Fossil Fuels

As discussed earlier in this TSD, the thermal efficiency standard is based on the ratio of energy
output to energy input determined by using the fuel's lower heating value (LHV). EPA
estimated the amounts of fossil fuels required to be co-fired with biomass to allow cogeneration

15


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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR

FIP, CAMR, and Proposed CAMR Federal Plan

units to meet the existing thermal efficiency standard of 42.5%. Units already meeting the
existing thermal efficiency standard would not be affected by the proposed action. The
following assumptions and methodologies were used to develop the estimates used to determine
which units were likely to be affected by the proposed rule:

1. Heat balance for a typical cogeneration unit firing biomass that does not meet the existing
EPA-specified thermal efficiency standard is shown in Table 4.4 This heat balance was
used as a basis for estimating the amounts of various fossil fuels required for co-firing
with biomass to improve the unit thermal efficiency to reach the 42.5% standard. The
cogeneration unit represented in Table 4 uses a backpressure turbine and provides process
steam at two different pressures. The boiler efficiency for this unit is only 69% and the
overall unit thermal efficiency based on the lower heating value of biomass is 39.6% —
below the thermal efficiency standard.

TABLE 4

Biomass-Fired Cogeneration Unit Heat Balance

Parameter

Unit

Value

Unit gross output

MW

6.6

Unit net output

MW

4.1

Unit net output

Btu/hr

13,993,300

Turbine inlet steam flow

lb/hr

200,000

Turbine inlet steam pressure

psig

900

Turbine inlet steam temperature

°F

800

Turbine inlet steam enthalpy

Btu/lb

1,411

Process steam #1 flow

lb/hr

65,000

Process steam #1 pressure

Psig

175

Process steam #1 temperature

°F

420

Process steam #1 enthalpy

Btu/lb

1,225

Process steam #2 flow

Lb/hr

135,000

Process steam #2 pressure

psig

50

4 AF&PA's Policy, Practical, and Legal Concerns about Inclusion of Biomass Fired Cogeneration Units in the Clean
Air Interstate Rule, Report Submitted by American Forest & Paper Association to EPA, September 18, 2006

16


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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR

FIP, CAMR, and Proposed CAMR Federal Plan

Parameter

Unit

Value

Process steam #2 temperature

°F

320

Process steam #2 enthalpy

Btu/lb

1,190

Makeup water enthalpy

Btu/lb

41

Process thermal output

Btu/hr

232,075,000

Power to heat ratio



0.06

Boiler efficiency

%

69

Boiler feedwater temperature

°F

250

Boiler feedwater enthalpy

Btu/lb

218

Fuel heat input (higher heating value)

Btu/hr

345,797,101

Fuel heat input (lower heating value)

Btu/hr

328,507,246

Thermal efficiency

%

71.2

Thermal efficiency (based on EPA
efficiency standard)

%

39.6

2. Table 5 shows typical biomass and fossil fuel ultimate analyses used in the estimates.
The fossil fuels include bituminous coal, sub-bituminous coal, lignite, natural gas, and
residual oil. The analysis for biomass was selected to match the 69% boiler efficiency
shown in Table 4.

TABLE 5
Fuel Ultimate Analyses

Fuel
Property

Biomass'l}

Bituminous

Coal(2)

Sub-
Bituminous

Coal(2)

Lignite(2)

Natural

Gas(1)

Residual
Oil(3)

Carbon, wt.

%

28.49

63.74

50.25

36.27

69.26

85.70

Hydrogen,
wt. %

3.14

4.5

3.41

2.42

22.68

10.50

Nitrogen, wt.

%

0.11

1.25

0.65

0.71

8.06

0.40

17


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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR

FIP, CAMR, and Proposed CAMR Federal Plan

Oxygen, wt.

%

21.12

6.89

13.55

10.76



0.52

Sulfur, wt. %

0.06

2.51

0.22

0.64

-

2.50

Moisture, wt.

%

45.00

11.12

27.40

31.24



0.30

Ash, wt. %

2.08

9.70

4.50

17.92

-

0.08

Higher
heating
value, Btu/lb

4,807

11,667

8,800

6,312

21,824

18,660

NOTES:

1. Source: Steam, Babcock & Wilcox, 40th Edition. The analysis of natural gas is based on the following

volumetric analysis: CH4: 90.0%; C2H6: 5.0%; and N2: 5.0%.

2.	Source: Environmental Footprints and Costs of Coal-Based Integrated Gasification Combined Cycle and
Pulverized Coal Technologies, EPA-430/R-06/006, July 2006.

3.	Source: Combustion, Combustion Engineering, 3rd Edition

3.	Compared to biomass, the analyses of all fossil fuels in Table 5 show lower moisture
contents, greater carbon contents, and greater heating values. If these fossil fuels are co-
fired with biomass, the boiler efficiency would improve, with the amount of improvement
depending on the amount of each fossil fuel in the fuel mix. A certain increase in the
boiler efficiency would be anticipated with the co-firing of each fossil fuel to improve the
overall thermal efficiency of the cogeneration plant to the required 42.5%. Therefore, the
main objective of these estimates was to determine the amount of each fossil fuel in the
fuel mix that would provide sufficient increase in the boiler efficiency to meet the
existing thermal efficiency standard.

4.	Boiler efficiencies and the lower and higher heating value ratios were estimated using
different proportions of biomass and fossil fuels in the fuel mix. These estimates were
based on well-established industry practices.5 The estimates were used in the
cogeneration unit heat balance (Table 4) to determine the boiler efficiency and the
amount of co-fired fossil fuel that would result in an overall unit thermal efficiency of
42.5%. Since the heating values of residual and distillate oils are close, the results of this
analysis for residual oil would also apply to distillate oil.

5 Steam, Babcock & Wilcox, 40th Edition.

18


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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR

FIP, CAMR, and Proposed CAMR Federal Plan

5. Table 6 presents the results of the analysis, showing the estimated percentage of each
fossil fuel (on a heat input basis) required to be co-fired with biomass in order to meet the
existing thermal efficiency standard. The corresponding ratio of lower to higher heating
value and boiler efficiency for each fossil fuel is also shown. The estimated amounts of
fossil fuels required to be co-fired with biomass on a heat input basis to meet the existing
thermal efficiency standard are as follows (rounded):

•	Lignite:	60%

•	Sub-bituminous coal: 50%

•	Bituminous coal:	40%

•	Residual oil:	30%

•	Natural gas:	10%

TABLE 6

Amounts of Fossil Fuels Required for Co-firing

Co-fired Fuel

Amount of Fuel

Co-fired,
% of heat input

Lower to Higher
Heating Value
Ratio

Boiler Efficiency,

%

Lignite

60

0.96

74.4

Sub-Bituminous
Coal

50

0.95

74

Bituminous Coal

40

0.95

74

Residual Oil

30

0.94

73.4

Natural Gas

10

0.94

73.3

6. The results of this analysis presented in Table 6 may vary due to differences in the

assumed fuel or cogeneration unit characteristics. For example, the boiler efficiency may
vary with a different biomass analysis, especially if the moisture content is significantly
different from what has been assumed and shown in Table 5. The overall thermal
efficiency of the cogeneration unit may also be different as a result of different design
parameters. However, it is expected that the results from different cogeneration unit and
fuel characteristics would not be significantly different from what is presented in the
estimates for this document.

19


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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

APPENDIX A

LIST OF IDENTIFIED BIOMASS COGENERATION UNITS IN THE CAIR REGION

PLANT NAME

STATE

COUNTY

PLANT
CODE

BOILER
ID

NAICS
CODE

Hours
Under
Load

Total HI
(mmBtu)

Biomass
HI (mmBtu)

Fossil HI
(mmBtu)

Est.
Annual
S02
Emissions
(tons)

Est.
Annual
NOx
Emissions
(tons)

Abitibi Consolidated Sheldon

TX

Harris

50253

1PB

322122

0











Alabama Pine Pulp

AL

Monroe

54429

RB2

322

8,621

13,734,572

13,541,792

192,780

944

824

Alabama Pine Pulp

AL

Monroe

54429

PB2

322

8,354

1,874,440

1,705,600

168,840

35

22

Alabama River Pulp

AL

Monroe

10216

PB1

322

8,473

3,495,210

3,264,000

231,210

60

122

Alabama River Pulp

AL

Monroe

10216

RB1

322

8,263

10,848,070

10,348,480

499,590

751

108

Ashdown

AR

Little River

54104

PB2

322122

8,532

7,117,398

2,174,400

4,942,998

1,253

1,174

Ashdown

AR

Little River

54104

RB3

322122

8,452

10,257,299

10,175,520

81,779

702

669

Ashdown

AR

Little River

54104

RB2

322122

8,441

6,672,803

6,573,720

99,083

453

438

Ashdown

AR

Little River

54104

PB3

322122

8,436

7,376,715

6,795,000

581,715

85

332

Ashdown

AR

Little River

54104

PB1

322122

8,543

3,816,794

3,468,600

348,194

192

115

Brunswick Cellulose

GA

Glynn

10605

6RB

322122

8,445

11,867,833

11,840,000

27,833

748

696

Brunswick Cellulose

GA

Glynn

10605

4PB

322122

8,356

5,341,232

3,996,125

1,317,207

1,980

656

Brunswick Cellulose

GA

Glynn

10605

5RB

322122

8,356

7,446,729

7,361,280

85,449

579

445

Cedar Bay Generating LP

FL

Duval

10672

CBC

22

7,560

7,549,458



7,549,458

468

642

Chester Operations

PA

Delaware

50410

10

322122

7,381

5,304,331

52,430

5,251,901

9,921

2,395

Cogentrix Roxboro

NC

Person

10379

1B

22

6,213

942,177

39,096

738,106

499

193

Cogentrix Roxboro

NC

Person

10379

1A

22

4,631

845,747

27,023

659,978

453

173

Cogentrix Roxboro

NC

Person

10379

1C

22

5,148

826,070

33,311

633,326

399

169

Covington Facility

VA

Covington

50900

7PB

32213

8,528

2,152,560

498,960

1,653,600

73

472

Covington Facility

VA

Covington

50900

8PB

32213

8,404

3,205,000

862,400

2,342,600

103

697

Covington Facility

VA

Covington

50900

2RB

32213

8,400

8,819,082

8,517,312

301,770

777

691

Covington Facility

VA

Covington

50900

1RB

32213

8,486

5,719,188

5,246,688

472,500

564

471

20


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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

LIST OF IDENTIFIED BIOMASS COGENERATION UNITS IN THE CAIR REGION

PLANT NAME

STATE

COUNTY

PLANT
CODE

BOILER
ID

NAICS
CODE

Hours
Under
Load

Total HI
(mmBtu)

Biomass
HI (mmBtu)

Fossil HI
(mmBtu)

Est.
Annual
S02
Emissions
(tons)

Est.
Annual
NOx
Emissions
(tons)

DeRidder Mill

LA

Beauregard

10488

PB1

322122

8,605

6,796,955

4,839,024

1,647,931

63

865

DeRidder Mill

LA

Beauregard

10488

PB2

322122

8,398

2,767,967

2,191,752

576,215

8

319

DeRidder Mill

LA

Beauregard

10488

REC

322122

8,171

7,754,583

7,139,571

615,013

522

572

Escanaba Paper Company

Ml

Delta

10208

11

322122

8,497

7,654,422

3,147,145

4,507,277

3,446

1,914

Escanaba Paper Company

Ml

Delta

10208

10

322122

8,486

7,842,134

7,521,423

320,711

531

500

Escanaba Paper Company

Ml

Delta

10208

9

322122

8,310

2,502,776

2,317,500

185,276

29

280

Finch Pruyn

NY

Warren

10511

9

322122

8,077

1,497,730

1,047,280

450,450

367

186

Finch Pruyn

NY

Warren

10511

8

322122

7,901

1,385,790

1,385,790



20

23

Finch Pruyn

NY

Warren

10511

10

322122

8,118

1,337,700

1,337,700



19

22

Flint River Operations

GA

Macon

50465

RB

322

8,254

8,770,620

8,727,108

43,512

689

965

Flint River Operations

GA

Macon

50465

PB

322

8,484

2,693,406

2,473,360

220,046

72

673

Gadsden

AL

Etowah

7

2

22

5,542

3,649,559

8,124

3,641,435

5,398

1,077

Gadsden

AL

Etowah

7

1

22

7,582

2,811,935

10,000

2,801,935

4,306

943

Gaylord Container Bogalusa

LA

Washington

54427

12

322122

8,568

6,360,750

6,017,400

343,350

345

716

Gaylord Container Bogalusa

LA

Washington

54427

10C

322122

8,568

3,611,452

3,449,700

161,752

43

401

Gaylord Container Bogalusa

LA

Washington

54427

21

322122

8,568

5,820,780

5,678,400

142,380

490

377

Gaylord Container Bogalusa

LA

Washington

54427

20

322122

8,568

3,719,610

3,639,600

80,010

305

240

Georgia Pacific Cedar Springs

GA

Early

54101

PB1

32213

8,280

5,552,354

1,909,200

3,643,154

7,799

1,284

Georgia Pacific Cedar Springs

GA

Early

54101

PB2

32213

8,240

5,552,354

1,909,200

3,643,154

7,799

1,284

Georgia Pacific Crossett

AR

Ashley

10606

10A

322122

8,479

5,228,500

4,360,458

868,042

55

1,281

Georgia Pacific Crossett

AR

Ashley

10606

9A

322122

8,040

3,804,691

3,193,502

611,189

40

304

Georgia Pacific Crossett

AR

Ashley

10606

8R

322122

8,437

11,061,260

10,980,900

80,360

757

719

Georgia Pacific Naheola Mill

AL

Choctaw

10699

4

322122

8,387

11,085,696

10,881,530

204,166

730

694

Georgia Pacific Palatka Operations

FL

Putnam

10611

4 COMB

322122

8,462

3,494,440

2,840,500

653,940

768

415

Georgia Pacific Palatka Operations

FL

Putnam

10611

4RB

322122

8,094

6,364,690

2,456,800

3,907,890

4,634

758

Georgia Pacific Port Hudson

LA

East Baton
Rouge

10612

PB1

322122

8,590

2,814,008

2,340,000

474,008

29

281

21


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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

LIST OF IDENTIFIED BIOMASS COGENERATION UNITS IN THE CAIR REGION

PLANT NAME

STATE

COUNTY

PLANT
CODE

BOILER
ID

NAICS
CODE

Hours
Under
Load

Total HI
(mmBtu)

Biomass
HI (mmBtu)

Fossil HI
(mmBtu)

Est.
Annual
S02
Emissions
(tons)

Est.
Annual
NOx
Emissions
(tons)

Georgia Pacific Port Hudson

LA

East Baton
Rouge

10612

RB2

322122

8,520

8,183,330

8,004,000

179,330

552

622

Georgia Pacific Port Hudson

LA

East Baton
Rouge

10612

RB1

322122

8,520

5,293,371

5,185,200

108,171

358

384

Green Power Kenansville

NC

Duplin

10381

1B

22

2,266

273,702

96,000

165,502

94

45

Green Power Kenansville

NC

Duplin

10381

1A

22

2,980

344,871

165,000

155,471

98

57

Inland Paperboard Packaging
Rome

GA

Floyd

10426

RF3

32213

1,599

316,052

10,880

305,172

67

48

Inland Paperboard Packaging
Rome

GA

Floyd

10426

RF4

32213

788

151,164

32,640

118,524

28

21

Inland Paperboard Packaging
Rome

GA

Floyd

10426

PB3

32213

8,599

2,997,150

2,482,004

485,116

445

427

Inland Paperboard Packaging
Rome

GA

Floyd

10426

PB1

32213

6,916

3,190,642

2,724,776

465,866

394

436

Inland Paperboard Packaging
Rome

GA

Floyd

10426

RF5

32213

8,175

8,130,490

8,087,272

43,218

624

583

International Paper Augusta Mill

GA

Richmond

54358

PB1

32213

8,347

5,126,835

2,860,011

2,266,824

1,287

935

International Paper Augusta Mill

GA

Richmond

54358

RB3

32213

8,438

11,453,163

11,406,957

46,206

735

688

International Paper Augusta Mill

GA

Richmond

54358

PB3

32213

8,426

4,973,896

4,821,606

152,290

60

551

International Paper Augusta Mill

GA

Richmond

54358

RB2

32213

8,359

2,974,331

2,716,595

257,736

471

216

International Paper Courtland Mill

AL

Lawrence

50245

PB3

322122

8,241

9,549,151

8,997,300

242,851

442

726

International Paper Courtland Mill

AL

Lawrence

50245

RB3

322122

8,363

8,054,211

8,041,050

13,161

611

1,301

International Paper Eastover
Facility

SC

Richland

52151

PB2

322122

8,664

3,022,823

2,502,600

45,923

331

451

International Paper Eastover
Facility

SC

Richland

52151

RF1

322122

8,480

4,629,895

4,569,600

60,295

372

295

International Paper Eastover
Facility

SC

Richland

52151

RF2

322122

8,458

10,593,852

10,534,800

59,052

768

53

International Paper Franklin Mill

VA

Isle of Wight

52152

7PB

322122

8,507

4,650,553

1,289,330

3,361,223

2,098

1,098

International Paper Franklin Mill

VA

Isle of Wight

52152

6PB

322122

8,364

3,194,246

1,437,660

1,756,586

819

482

International Paper Franklin Mill

VA

Isle of Wight

52152

6RB

322122

8,477

6,631,494

6,612,340

19,154

537

488

International Paper Franklin Mill

VA

Isle of Wight

52152

5RB

322122

8,324

2,723,140

2,340,380

382,760

555

231

22


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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

LIST OF IDENTIFIED BIOMASS COGENERATION UNITS IN THE CAIR REGION

PLANT NAME

STATE

COUNTY

PLANT
CODE

BOILER
ID

NAICS
CODE

Hours
Under
Load

Total HI
(mmBtu)

Biomass
HI (mmBtu)

Fossil HI
(mmBtu)

Est.
Annual
S02
Emissions
(tons)

Est.
Annual
NOx
Emissions
(tons)

International Paper Franklin Mill

VA

Isle of Wight

52152

4RB

322122

7,626

2,483,460

2,483,460



194

182

International Paper Georgetown
Mill

SC

Georgetown

54087

PB01

322122

8,587

4,257,583

2,419,217

1,119,166

1,249

766

International Paper Georgetown
Mill

SC

Georgetown

54087

PB02

322122

8,609

4,173,126

2,509,147

954,079

1,105

751

International Paper Georgetown
Mill

SC

Georgetown

54087

RB01

322122

8,308

5,673,035

5,505,938

167,097

556

387

International Paper Georgetown
Mill

SC

Georgetown

54087

RB02

322122

8,487

7,031,535

6,864,382

167,153

651

475

International Paper Louisiana Mill

LA

Morehouse

54090

3PB

322122

8,564

5,661,928

3,264,525

1,020,403

1,481

48

International Paper Louisiana Mill

LA

Morehouse

54090

5REC

322122

8,405

4,741,380

4,469,760

271,620

310

326

International Paper Louisiana Mill

LA

Morehouse

54090

6REC

322122

8,522

5,158,971

5,040,120

118,851

346

341

International Paper Pensacola

FL

Escambia

50250

4PB

322122

8,249

4,444,719

3,492,873

951,846

96

756

International Paper Pensacola

FL

Escambia

50250

2RB

322122

8,320

5,575,360

5,443,200

132,160

363

114

International Paper Pensacola

FL

Escambia

50250

1RB

322122

8,267

5,468,656

5,400,000

68,656

360

104

International Paper Pine Bluff Mill

AR

Jefferson

10627

RB4

32213

7,770

8,079,931

7,977,980

101,951

541

521

International Paper Pine Bluff Mill

AR

Jefferson

10627

BB1

32213

8,012

2,677,907

2,589,830

88,076

38

303

International Paper Pine Bluff Mill

AR

Jefferson

10627

RB2

32213

8,316

2,565,437

2,460,300

105,137

167

171

International Paper Pine Bluff Mill

AR

Jefferson

10627

RB3

32213

7,971

2,484,848

2,396,580

88,268

163

164

International Paper Prattville Mill

AL

Autauga

52140

PB1

32213

8,527

2,839,307

1,328,718

1,510,589

67

356

International Paper Prattville Mill

AL

Autauga

52140

PB2

32213

8,567

4,407,171

2,161,412

2,245,759

1,491

838

International Paper Prattville Mill

AL

Autauga

52140

RF1

32213

8,421

4,865,477

4,604,890

260,586

115

355

International Paper Prattville Mill

AL

Autauga

52140

RF2

32213

8,561

6,728,681

6,513,894

214,787

509

467

International Paper Quinnesec
Mich Mill

Ml

Dickinson

50251

WTB

322

8,468

2,980,069

2,812,320

167,749

123

447

International Paper Quinnesec
Mich Mill

Ml

Dickinson

50251

RB

322

8,490

7,406,214

7,367,160

39,054

508

704

International Paper Riegelwood
Mill

NC

Columbus

54656

PB2

32213

8,232

4,662,061

3,434,065

1,227,996

154

555

International Paper Riegelwood
Mill

NC

Columbus

54656

PB5

32213

8,304

5,206,612

4,265,518

941,094

121

606

23


-------
Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

LIST OF IDENTIFIED BIOMASS COGENERATION UNITS IN THE CAIR REGION

PLANT NAME

STATE

COUNTY

PLANT
CODE

BOILER
ID

NAICS
CODE

Hours
Under
Load

Total HI
(mmBtu)

Biomass
HI (mmBtu)

Fossil HI
(mmBtu)

Est.
Annual
S02
Emissions
(tons)

Est.
Annual
NOx
Emissions
(tons)

International Paper Rieaelwood
Mill

NC

Columbus

54656

RB3

32213

5,568

1,516,419

1,403,460

112,959

204

109

International Paper Rieaelwood
Mill

NC

Columbus

54656

RB4

32213

8,215

4,452,702

4,345,980

106,722

407

304

International Paper Rieaelwood
Mill

NC

Columbus

54656

RB5

32213

7,879

10,969,433

10,767,770

201,663

949

743

International Paper Riverdale Mill

AL

Dallas

54096

BLRB2

322122

8,532

4,257,388

3,936,072

321,316

80

639

International Paper Riverdale Mill

AL

Dallas

54096

BLRR2

322122

8,532

5,383,661

5,347,132

36,529

350

333

International Paper Savanna Mill

GA

Chatham

50398

13PB

32213

8,592

8,695,526

1,095,726

7,599,800

3,552

2,043

International Paper Savanna Mill

GA

Chatham

50398

15RB

32213

8,592

10,719,437

10,251,000

468,437

820

802

International Paper Texarkana Mill

TX

Cass

54097

PB2

32213

8,376

6,465,027

2,904,700

3,560,327

2,070

842

International Paper Vicksburg Mill

MS

Warren

54100

N1BABO

322122

8,480

1,482,201

127,750

1,354,451

508

234

International Paper Vicksburg Mill

MS

Warren

54100

N1REBO

322122

8,480

6,029,106

5,932,500

96,606

420

407

Jefferson Smurfit Fernandina
Beach

FL

Nassau

10202

5PWR

32213

8,520

4,337,240

2,849,180

1,488,060

1,982

547

Jefferson Smurfit Fernandina
Beach

FL

Nassau

10202

4REC

32213

8,605

5,044,840

5,044,840



348

326

Jefferson Smurfit Fernandina
Beach

FL

Nassau

10202

5REC

32213

8,452

5,034,400

5,034,400



347

326

Johnsonburg Mill

PA

Elk

54638

RB01

322122

8,426

5,133,165

5,051,402

81,762

361

357

Luke Mill

MD

Allegany

50282

2RB

322122

655

56,650



56,650

16

5

Luke Mill

MD

Allegany

50282

3RB

322122

8,592

7,661,949

7,566,803

95,146

609

516

M L Hibbard

MN

St Louis

1897

3

22

6,611

659,934

143,232

516,702

157

313

M L Hibbard

MN

St Louis

1897

4

22

6,616

641,438

143,232

498,206

158

316

Mansfield Mill

LA

De Soto

54091

PB2

32213

8,471

5,399,254

3,421,440

1,030,691

1,242

548

Mansfield Mill

LA

De Soto

54091

PB1

32213

8,508

6,101,037

4,263,600

893,175

1,362

397

Mansfield Mill

LA

De Soto

54091

RB1

32213

8,478

4,757,903

4,620,946

136,957

324

304

Mansfield Mill

LA

De Soto

54091

RB2

32213

8,516

4,912,941

4,812,786

100,155

329

312

Mead Coated Board

AL

Russell

54802

BB1

32213

7,717

2,253,982

2,001,650

252,332

29

254

Mead Coated Board

AL

Russell

54802

BB3

32213

7,765

5,002,328

4,897,991

104,337

61

546

24


-------
Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

LIST OF IDENTIFIED BIOMASS COGENERATION UNITS IN THE CAIR REGION

PLANT NAME

STATE

COUNTY

PLANT
CODE

BOILER
ID

NAICS
CODE

Hours
Under
Load

Total HI
(mmBtu)

Biomass
HI (mmBtu)

Fossil HI
(mmBtu)

Est.
Annual
S02
Emissions
(tons)

Est.
Annual
NOx
Emissions
(tons)

Mead Coated Board

AL

Russell

54802

BB2

32213

8,358

3,591,949

3,521,973

69,976

44

392

Mead Coated Board

AL

Russell

54802

REC1

32213

8,273

5,844,992

5,742,185

102,807

394

373

Mead Coated Board

AL

Russell

54802

REC2

32213

8,160

7,511,587

7,494,670

16,917

498

468

MeadWestvaco Evadale

TX

Jasper

50101

PB2

32213

8,442

4,979,311

2,766,400

2,212,911

35

603

MeadWestvaco Evadale

TX

Jasper

50101

PB6

32213

8,483

5,175,146

4,648,800

526,346

58

285

MeadWestvaco Evadale

TX

Jasper

50101

RB2

32213

8,167

2,887,374

2,842,000

45,374

196

190

MeadWestvaco Evadale

TX

Jasper

50101

RB3

32213

8,606

3,362,895

3,340,800

22,095

230

219

MeadWestvaco Evadale

TX

Jasper

50101

RB4

32213

8,712

6,055,062

6,043,600

11,462

417

392

Mobile Energy Services LLC

AL

Mobile

50407

7PB

22

8,472

5,924,678

3,223,894

2,700,784

1,788

908

MW Custom Papers

OH

Ross

10244

6

322122

8,443

2,323,216

2,293,569

29,648

34

255

MW Custom Papers

OH

Ross

10244

9

322122

8,756

4,643,845

4,586,326

57,519

445

413

Northhampton Generating LP

PA

Northampton

50888

BLR1

22

7,709

9,282,185

221,888

9,060,298

585

436

Okeelanta Cogeneration

FL

Palm Beach

54627

C

22

7,519

4,033,714

4,011,110

22,604

34

292

Okeelanta Cogeneration

FL

Palm Beach

54627

A

22

7,659

4,050,826

4,031,120

19,706

35

296

Okeelanta Cogeneration

FL

Palm Beach

54627

B

22

7,495

3,995,462

3,983,290

12,172

34

292

P H Glatfelter

PA

York

50397

5PB036

322122

8,496

4,795,518

1,230,394

3,565,124

3,950

647

P H Glatfelter

PA

York

50397

REC037

322122

8,280

7,129,373

7,111,380

17,993

429

356

Packaging Corp of America

TN

Hardin

50296

C1

32213

7,488

1,476,074

288,129

1,187,945

456

192

Packaging Corp of America

TN

Hardin

50296

C2

32213

8,585

6,566,343

4,425,874

2,140,469

1,093

1,083

Packaging Corp of America

TN

Hardin

50296

R3

32213

8,507

6,376,690

6,372,000

4,690

425

399

Packaging Corp of America

TN

Hardin

50296

R1

32213

8,210

2,868,389

2,868,000

389

191

179

Packaging Corp of America

TN

Hardin

50296

R2

32213

8,380

2,928,369

2,928,000

369

195

183

Port Wentworth Mill (Stone
Savanah)

GA

Chatham

50804

4

322

8,560

3,788,955

3,604,500

184,455

53

432

Port Wentworth Mill (Stone
Savanah)

GA

Chatham

50804

RE01

322

8,300

7,072,124

7,008,032

64,092

495

467

Rayonier Jesup Mill

GA

Wayne

10560

POWB

322

7,864

5,089,289

3,094,580

1,994,709

1,427

637

Rayonier Jesup Mill

GA

Wayne

10560

RB6

322

8,449

10,710,627

10,400,400

310,227

908

696

25


-------
Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

LIST OF IDENTIFIED BIOMASS COGENERATION UNITS IN THE CAIR REGION

PLANT NAME

STATE

COUNTY

PLANT
CODE

BOILER
ID

NAICS
CODE

Hours
Under
Load

Total HI
(mmBtu)

Biomass
HI (mmBtu)

Fossil HI
(mmBtu)

Est.
Annual
S02
Emissions
(tons)

Est.
Annual
NOx
Emissions
(tons)

Rayonier Jesup Mill

GA

Wayne

10560

RB5

322

8,484

7,092,217

6,960,000

132,217

557

455

S D Warren Muskegon

Ml

Muskegon

50438

4PB

322122

8,177

3,303,319

542,080

2,761,239

89

578

Sappi Cloquet Mill

MN

Carlton

50639

7PB

322122

7,950

1,486,311

1,097,220

389,091

16

102

Sappi Cloquet Mill

MN

Carlton

50639

9PB

322122

8,561

2,589,894

2,109,440

480,454

30

233

Sappi Cloquet Mill

MN

Carlton

50639

10RB

322122

8,525

8,682,091

8,569,288

112,803

620

451

Savannah River Mill

GA

Effingham

10361

5B

322122

8,454

3,462,113

21,980

3,440,133

9,623

927

Savannah River Mill

GA

Effingham

10361

3B

322122

8,533

3,196,370

21,980

3,174,390

8,601

863

SP Newsprint

GA

Laurens

54004

PB2

322122

8,520

3,742,462

780,494

1,527,746

2,377

150

Stone Container Florence Mill

SC

Florence

50806

PB4

322122

8,385

8,599,602

3,498,600

5,101,002

3,089

1,419

Stone Container Hodge

LA

Jackson

50810

CB

322122

8,516

7,108,390

2,961,000

4,147,390

38

886

Stone Container Hodge

LA

Jackson

50810

3RB

322122

8,459

3,521,448

3,192,000

329,448

224

254

Stone Container Hodge

LA

Jackson

50810

2RB

322122

8,309

6,458,318

6,372,600

85,718

447

431

Stone Container Hopewell Mill

VA

Hopewell City

50813

CB1

322122

8,568

4,316,175

2,556,000

1,760,175

1,031

1,081

Stone Container Hopewell Mill

VA

Hopewell City

50813

RB1

322122

8,401

5,010,480

4,976,050

34,430

359

330

TES Filer City Station

Ml

Manistee

50835

2

22

8,658

3,347,713

145,195

3,135,318

226

993

TES Filer City Station

Ml

Manistee

50835

1

22

8,098

3,154,695

145,195

2,942,299

212

934

Ticonderoga Mill

NY

Essex

54099

PB1

322122

8,400

4,688,267

949,381

3,738,886

428

488

Ticonderoga Mill

NY

Essex

54099

RB1

322122

8,400

3,062,078

2,906,400

155,678

395

283

West Point Mill (St Laurent Paper)

VA

King William

10017

RF04

322

8,263

5,542,140

5,142,720

399,420

695

355

West Point Mill (St Laurent Paper)

VA

King William

10017

PB10

322

8,424

4,615,480

4,320,640

294,840

337

521

West Point Mill (St Laurent Paper)

VA

King William

10017

RF05

322

8,068

5,456,026

5,322,550

133,476

381

439

Weyerhaeuser Columbus MS

MS

Lowndes

50184

COMB

322122

8,600

6,461,390

6,056,400

404,990

271

1,034

Weyerhaeuser Columbus MS

MS

Lowndes

50184

REC

322122

8,496

12,314,380

12,249,600

64,780

828

554

Weyerhaeuser Kentucky Mills

KY

Hancock

55429

BFB

322

8,439

3,290,933

2,950,500

340,433

75

247

Weyerhaeuser Kentucky Mills

KY

Hancock

55429

4REC

322

8,455

6,674,654

6,594,600

80,054

455

437

Weyerhaeuser Kentucky Mills

KY

Hancock

55429

3REC

322

8,228

4,261,330

4,247,920

13,410

293

276

Weyerhaeuser New Bern NC

NC

Craven

50188

RB

322

8,424

8,541,576

8,364,000

177,576

742

550

26


-------
Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

LIST OF IDENTIFIED BIOMASS COGENERATION UNITS IN THE CAIR REGION

PLANT NAME

STATE

COUNTY

PLANT
CODE

BOILER
ID

NAICS
CODE

Hours
Under
Load

Total HI
(mmBtu)

Biomass
HI (mmBtu)

Fossil HI
(mmBtu)

Est.
Annual
S02
Emissions
(tons)

Est.
Annual
NOx
Emissions
(tons)

Weyerhaeuser Pine Hill Operations

AL

Wilcox

54752

1PB

32213

8,549

4,118,160

2,304,050

1,814,110

48

499

Weyerhaeuser Pine Hill Operations

AL

Wilcox

54752

2PB

32213

8,506

5,372,115

3,681,550

1,690,565

576

772

Weyerhaeuser Pine Hill Operations

AL

Wilcox

54752

RECB

32213

8,270

7,303,421

6,916,617

386,804

765

553

Weyerhaeuser Plymouth NC

NC

Martin

50189

2HFB

322122

8,470

8,604,948

5,125,092

3,479,856

1,907

1,242

Weyerhaeuser Plymouth NC

NC

Martin

50189

5REC

322122

8,507

11,733,121

11,613,003

120,118

779

1,056

Weyerhaeuser Plymouth NC

NC

Martin

50189

1HFB

322122

8,262

6,751,997

6,242,418

509,579

468

770

Wisconsin Rapids Pulp Mill

Wl

Wood

10477

P1

322122

8,599

2,541,915

994,875

1,547,040

363

674

Wisconsin Rapids Pulp Mill

Wl

Wood

10477

P2

322122

8,538

2,541,915

994,875

1,547,040

363

686

Wisconsin Rapids Pulp Mill

Wl

Wood

10477

R1

322122

7,876

2,023,040

2,023,040



140

131

Wisconsin Rapids Pulp Mill

Wl

Wood

10477

R2

322122

8,234

2,023,040

2,023,040



140

131

Wisconsin Rapids Pulp Mill

Wl

Wood

10477

R3

322122

8,421

2,023,040

2,023,040



140

131

27


-------
Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

LIST OF IDENTIFIED BIOMASS COGENERATION UNITS IN THE CAMR REGION

PLANT NAME

STATE

COUNTY

PLANT
CODE

BOILER
ID

NAICS
CODE

Total HI
(mmBtu)

Biomass
HI (mmBtu)

Fossil HI
(mmBtu)

Est. Annual

Hg
Emissions
(lbs)

Ashdown

AR

Little River

54104

PB2

322122

7,117,398

2,174,400

4,942,998

53.44

Bucksport Mill

ME

Hancock

50243

8

322122

2,768,668

1,601,490

829,228



Cedar Bay Generating LP

FL

Duval

10672

CBC

22

7,549,458



7,549,458

4.54

Chester Operations

PA

Delaware

50410

10

322122

5,304,331

52,430

5,251,901

1.49

Cogentrix Roxboro

NC

Person

10379

1B

22

942,177

39,096

738,106

0.98

Cogentrix Roxboro

NC

Person

10379

1A

22

845,747

27,023

659,978

0.88

Cogentrix Roxboro

NC

Person

10379

1C

22

826,070

33,311

633,326

0.84

Covington Facility

VA

Covington

50900

7PB

32213

2,152,560

498,960

1,653,600

6.79

Covington Facility

VA

Covington

50900

8PB

32213

3,205,000

862,400

2,342,600

9.61

Escanaba Paper Company

Ml

Delta

10208

11

322122

7,654,422

3,147,145

4,507,277

53.07

Gadsden

AL

Etowah

7

2

22

3,649,559

8,124

3,641,435

27.52

Gadsden

AL

Etowah

7

1

22

2,811,935

10,000

2,801,935

21.32

Georgia Pacific Cedar Springs

GA

Early

54101

PB1

32213

5,552,354

1,909,200

3,643,154

38.32

Georgia Pacific Cedar Springs

GA

Early

54101

PB2

32213

5,552,354

1,909,200

3,643,154

38.32

Green Power Kenansville

NC

Duplin

10381

1B

22

273,702

96,000

165,502

0.22

Green Power Kenansville

NC

Duplin

10381

1A

22

344,871

165,000

155,471

0.21

Inland Paperboard Packaging Rome

GA

Floyd

10426

PB3

32213

2,997,150

2,482,004

485,116

5.86

Inland Paperboard Packaging Rome

GA

Floyd

10426

PB1

32213

3,190,642

2,724,776

465,866

5.55

International Paper Augusta Mill

GA

Richmond

54358

PB1

32213

5,126,835

2,860,011

2,266,824

22.18

International Paper Franklin Mill

VA

Isle of Wight

52152

7PB

322122

4,650,553

1,289,330

3,361,223

25.03

International Paper Franklin Mill

VA

Isle of Wight

52152

6PB

322122

3,194,246

1,437,660

1,756,586

13.57

International Paper Georgetown Mill

SC

Georgetown

54087

PB01

322122

4,257,583

2,419,217

1,119,166

10.02

International Paper Georgetown Mill

SC

Georgetown

54087

PB02

322122

4,173,126

2,509,147

954,079

8.03

International Paper Louisiana Mill

LA

Morehouse

54090

3PB

322122

5,661,928

3,264,525

1,020,403

5.60

International Paper Pensacola

FL

Escambia

50250

4PB

322122

4,444,719

3,492,873

951,846

10.61

International Paper Prattville Mill

AL

Autauga

52140

PB2

32213

4,407,171

2,161,412

2,245,759

13.86

International Paper Quinnesec Mich Mill

Ml

Dickinson

50251

WTB

322

2,980,069

2,812,320

167,749

1.33

International Paper Riegelwood Mill

NC

Columbus

54656

PB2

32213

4,662,061

3,434,065

1,227,996



International Paper Riegelwood Mill

NC

Columbus

54656

PB5

32213

5,206,612

4,265,518

941,094



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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

LIST OF IDENTIFIED BIOMASS COGENERATION UNITS IN THE CAMR REGION

PLANT NAME

STATE

COUNTY

PLANT
CODE

BOILER
ID

NAICS
CODE

Total HI
(mmBtu)

Biomass
HI (mmBtu)

Fossil HI
(mmBtu)

Est. Annual

Hg
Emissions
(lbs)

International Paper Savanna Mill

GA

Chatham

50398

13PB

32213

8,695,526

1,095,726

7,599,800

91.73

M L Hibbard

MN

St Louis

1897

3

22

659,934

143,232

516,702

2.51

M L Hibbard

MN

St Louis

1897

4

22

641,438

143,232

498,206

2.42

Mansfield Mill

LA

De Soto

54091

PB2

32213

5,399,254

3,421,440

1,030,691

5.76

Mansfield Mill

LA

De Soto

54091

PB1

32213

6,101,037

4,263,600

893,175

8.57

Mobile Energy Services LLC

AL

Mobile

50407

7PB

22

5,924,678

3,223,894

2,700,784

30.23

Northhampton Generating LP

PA

Northampton

50888

BLR1

22

9,282,185

221,888

9,060,298

3.23

P H Glatfelter

PA

York

50397

5PB036

322122

4,795,518

1,230,394

3,565,124

42.90

Packaging Corp of America

TN

Hardin

50296

C2

32213

6,566,343

4,425,874

2,140,469

24.85

Rumford Cogeneration

ME

Oxford

10495

6

22

4,486,241

1,358,300

2,340,541

28.25

Rumford Cogeneration

ME

Oxford

10495

7

22

3,796,003

1,156,000

1,964,203

23.71

S D Warren Muskegon

Ml

Muskegon

50438

4PB

322122

3,303,319

542,080

2,761,239

20.63

Savannah River Mill

GA

Effingham

10361

5B

322122

3,462,113

21,980

3,440,133

0.50

Savannah River Mill

GA

Effingham

10361

3B

322122

3,196,370

21,980

3,174,390

0.66

SP Newsprint

GA

Laurens

54004

PB2

322122

3,742,462

780,494

1,527,746

11.80

Stone Container Florence Mill

SC

Florence

50806

PB4

322122

8,599,602

3,498,600

5,101,002

60.93

Stone Container Hopewell Mill

VA

Hopewell City

50813

CB1

322122

4,316,175

2,556,000

1,760,175

13.20

TES Filer City Station

Ml

Manistee

50835

2

22

3,347,713

145,195

3,135,318

3.78

TES Filer City Station

Ml

Manistee

50835

1

22

3,154,695

145,195

2,942,299

3.55

Weyerhaeuser Columbus MS

MS

Lowndes

50184

COMB

322122

6,461,390

6,056,400

404,990

2.84

Weyerhaeuser Longview WA

WA

Cowlitz

50187

11B

322122

5,529,500

4,192,700

1,336,800

16.14

Weyerhaeuser Pine Hill Operations

AL

Wilcox

54752

2PB

32213

5,372,115

3,681,550

1,690,565

11.29

Weyerhaeuser Plymouth NC

NC

Martin

50189

2HFB

322122

8,604,948

5,125,092

3,479,856

4.57

Weyerhaeuser Plymouth NC

NC

Martin

50189

1HFB

322122

6,751,997

6,242,418

509,579

0.33

Wisconsin Rapids Pulp Mill

Wl

Wood

10477

P1

322122

2,541,915

994,875

1,547,040

7.53

Wisconsin Rapids Pulp Mill

Wl

Wood

10477

P2

322122

2,541,915

994,875

1,547,040

7.53

29


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Technical Support Document for Proposed Revisions to Cogeneration Definition in CAIR, CAIR FIP, CAMR, and Proposed CAMR

Federal Plan

APPENDIX B

The List of Identified Biomass Cogeneration Units Potentially Affected by the Proposal in CAIR and CAMR Regions is available on
the CAIR and CAMR websites on the Technical Information pages:

http://www.epa.gov/CAIR/technical.html
http://www.epa.gov/ttn/atw/utilitv/utiltoxpg.html

The TSD and Appendix B are also available in the public docket for the proposed rule (EPA-HQ-OAR-2007-0012):
http://www.regulations.gov

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