Control Strategy Tool (CoST)
Control Measures Database (CMDB)

Documentation

Office of Air Quality Planning and Standards
U.S. Environmental Protection Agency
Research Triangle Park, NC 27711

Contacts: David Misenheimer, Larry Sorrels, Darryl Weatherhead

Last Updated
June 9, 2010


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Control Strategy Tool (CoST) Control Measures Database (CMDB) Documentation

Contents

Tables	iv

Figures	iv

Acronyms	v

1	Introduction	1

2	Control Measures	2

2.1	Origins and Status of the Control Measures Database	2

2.2	Costs Associated with Control Measures	4

2.3	Developing New Control Measure Information	4

3	Control Measures Database Data Elements	5

3.1	Summary Table	6

3.2	Efficiency Records Table	7

3.3	SCCs Table	10

3.4	Equations Table	10

3.5	References Table	11

3.6	Examples of Control Measure Data Tables	12

4	Using the CMDB to Develop Control Strategies	19

4.1	Summary of the Strategy Development Process	19

4.2	Strategy Inputs Relevant to Control Measures	21

4.3	Control Measure Filtering and Custom Overrides	22

5	References	23

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Tables

Table 1. Summary Information Table Format	6

Table 2. Efficiency Records Table Format	7

Table 3. Excerpt from the gdplev Table Used to Convert Data between Cost Years	9

Table 4. SCCs Table Format	10

Table 5. Equations Table Format	11

Table 6. References Table Format	12

Table 7. Summary Table Example*	13

Table 8. Efficiency Records Table Example*	14

Table 9. SCCs Table Example	15

Table 10. Cost Equations Table Example	16

Table 11. References Table Example	17

Figures

Figure 1. Basic Steps for Running a Control Strategy Using CoST	20

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Acronyms

CAP	criteria air pollutant

CE	control efficiency

CAMD	Clean Air Markets Division (EPA)

CARB	California Air Resources Board

CMAQ	Community Multiscale Air Quality modeling system

CMAS	Community Modeling and Analysis System

CMDB	Control Measures Database

CoST	Control Strategy Tool

CRF	capital recovery factor

CSV	comma-separated values

EC	elemental carbon

EMF	Emissions Modeling Framework

EPA	U.S. Environmental Protection Agency

FGD	flue gas desulfurization

FGR	flue gas recirculation

FIPS	Federal Information Processing Standards

GDP	Gross Domestic Product

GHG	greenhouse gas

GIS	geographic information system

GUI	graphical user interface

HAP	hazardous air pollutant

HEID	Health and Environmental Impacts Division (EPA)

IE	Institute for the Environment (UNC)

IPM	Integrated Planning Model

LNB	low NOx burner

MOVES	MOtor Vehicle Emission Simulator

NAICS	North American Industry Classification System

NEI	National Emissions inventory

NSCR	non-selective catalytic reduction

OC	organic carbon

O&M	operating and maintenance

ORL	one record per line

OTAQ	Office of Transportation and Air Quality (EPA)

OTC	Ozone Transport Commission

PM	particulate matter

PR	percent reduction

RE	rule effectiveness

RP	rule penetration

RPO	regional planning organization

SCC	Source Classification Code

SIC	Standard Industrial Classification

SNCR	selective non-catalytic reduction

SQL	Structured Query Language

SMOKE	Sparse Matrix Operator Kernel Emissions modeling system

tpy	tons per year

UNC	University of North Carolina

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VOC	volatile organic compound(s)

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1 Introduction

The U.S. Environmental Protection Agency (EPA) Health and Environmental Impacts Division
(HEID) is developing the Control Strategy Tool (CoST) to support national- and regional-scale
multipollutant air quality modeling analyses. CoST allows users to estimate the emission
reductions and costs associated with future-year emission control strategies, and then to generate
emission inventories that reflect the effects of applying the control strategies [Misenheimer,
2007; Eyth, 2008], The emissions reductions achieved by control strategies are due to the
application of control measures to emission sources. Control measures are devices, techniques,
or practices that reduce emissions for at least one pollutant of interest for a particular group of
emission sources. CoST tracks information about control measures, their costs, and the types of
emission sources to which they apply. This tool helps users develop control strategies that match
control measures to emission sources using the available algorithms such as "Maximum
Emissions Reduction", "Least Cost", and "Apply Measures in Series" (these terms are explained
in Section 4.1)

CoST is a component of the Emissions Modeling Framework (EMF), which is currently being
used by EPA to solve many of the long-standing complexities of emissions modeling [Houyoux,
2008], Emissions modeling is the process by which emissions inventories and other related
information are converted to hourly, gridded, chemically speciated emissions estimates suitable
for input to an air quality model such as EPA's Community Multiscale Air Quality (CMAQ)
modeling system (Byun, 2006). The EMF supports the management and quality assurance of
emissions inventories and emissions modeling related data, and also the running of the Sparse
Matrix Operator Kernel Emissions (SMOKE) modeling system to develop CMAQ inputs.
Providing CoST as a tool integrated within the EMF facilitates a level of collaboration between
control strategy developers and emissions inventory modelers that was not previously possible.
CoST supports multipollutant analyses and data transparency, and provides a wide array of
options for developing control strategies. CoST has been developed to replace the older
AirControlNET software (discussed in Section 2.1).

CoST has been developed to provide an extensible software system for developing control
strategies. The tool uses EPA HEID's Control Measures Database (CMDB) to develop control
strategies, and provides a user interface to that database. The CMDB is a relational database that
contains information on an extensive set of control measures for point sources (ptipm and
ptnonipm sectors), non-point (nonpt), and mobile sources (onroad and nonroad). Information
contained in the database includes descriptions of the measures, control efficiencies for the
pollutants affected, costs of control, and the types of sources or processes to which the control
measures can be applied. The CMDB currently resides in the EMF as a set of tables in
PostgresSQL (http://www.postgresql.org).

The information in the CMDB can be imported into and exported from CoST. For many of the
control measures in the CMDB, a simple cost factor in terms of dollars per ton of pollutant
reduced is used to calculate the cost of the control measure when applied to a specific source.
However, a few control measures use more robust cost equations to determine engineering costs
that take into account several variables for the source, when values for those variables are
available. These equations are described in "Documentation of Cost Equations in EPA's Control
Strategy Tool" (http://www.epa.gov/ttn/ecas/cost.htm).

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Analyses have been performed by EPA HEID to compare the results of CoST to results of
independently developed strategies for criteria air pollutants (CAPs) for point, nonpoint, and
mobile sources. It was determined that CoST could reproduce these strategies if the inputs to the
independently developed strategies were consistent with those given to CoST. The tool has not
yet been used for hazardous air pollutants (HAPs), but it has been used in some limited analyses
for greenhouse gases (GHGs). The main limiting factors in using CoST for greenhouse gas
analyses are the availability of GHG emissions inventories at an appropriate level of detail, and
the availability of control measure data in the CMDB for greenhouse gases.

This document describes the history and contents of the CMDB. For additional information on
other aspects of CoST, see the following independent documents:

•	"Control Strategy Tool (CoST) Training Manual and User's Guide"

•	"Control Strategy Tool (CoST) Development Document"

•	"Control Strategy Tool (CoST) Glossary of Terms"

•	"Documentation of Cost Equations in EPA's Control Strategy Tool"

These documents, and additional information about CoST, can be found at: http://www.epa.gov/
ttn/ecas/cost.htm. If you are unsure of the meaning of terms used in this document, consult the
"Control Strategy Tool (CoST) Glossary of Terms".

2 Control Measures

2.1 Origins and Status of the Control Measures Database

The CMDB began as a collection of point- and nonpoint-source control measures extracted from
AirControlNET (for more information on AirControlNET, see
http://www.epa.gov/ttn/ecas/AirControlNET.htm). The control measures used by
AirControlNET were primarily targeted at single-pollutant analyses for studies related to
particulate matter (PM) and ozone. Information was included in the database for PMi0, PM2.5,
N0X, volatile organic compounds (VOC), NH3, SO2, and Hg. Data were extracted from
AirControlNET into a set of files in comma separated value (CSV) format that were readable by
standard spreadsheet software and could be imported into CoST.

The data in the CMDB are separated into six tables for each control measure:

1)	summary information about the control measure;

2)	efficiency records describing the reductions achieved by, and the costs required to apply,
the measure for each affected pollutant;

3)	a list of Source Classification Codes (SCCs) to which the measure applies;

4)	cost equation information (parameters used to compute the results of cost equations), for
measures to which this is applicable;

5)	references providing additional information on the control measure and how its control
efficiency and cost information were derived; and

6)	additional information that does not fit well within one of the five previous categories,
especially parameters that are unique to a single control measure or a subset of control
measures.

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These tables operate as a relational database and are currently housed within the EMF database
as a set of tables within the EMFPostgresSQL database. The tables are described in detail in
Section 3.

Control measures are available in the CMDB for point sources, nonpoint sources, and mobile
sources (onroad and nonroad). Control measure data in the database are taken from EPA reports
and databases, and reflect data from EPA regulatory development and control studies, regional
planning organizations (RPOs) such as the Ozone Transport Commission (OTC), and individual
State agencies such as the California Air Resources Board (CARB).

•	Point and nonpoint sources: Most of the control measures in the database for point and
nonpoint sources are derived from national average data. This means that the actual
results of applying the measures will vary when the devices are applied to specific
sources. It is particularly important to keep this in mind if the data are applied to local-
scale analyses. The control efficiency records of the CMDB support storing information
at several levels of geographic specificity, including national, state, or county level. For
example, some data for nonpoint sources are state specific and reflect the varying levels
of cost and control for each state. Note that although control measures are available for
electricity utility point sources in the CMDB, most analyses involving these are
performed using the Integrated Planning Model (IPM), a model employed by EPA's
Clean Air Markets Division (CAMD).

•	Mobile sources: Mobile-source measures are typically derived from data made available
by EPA's Office of Transportation and Air Quality (OTAQ) as a result of analyses
undertaken using emissions models such as MOBILE6, NONROAD, and MOVES. For
example, some mobile-source control measure information in the CMDB was generated
by running MOBILE and NONROAD with and without controls. The results were then
used to calculate control efficiencies for each pollutant affected, specific to each county.
For controls not currently covered in these models, information was obtained from recent
studies conducted by OTAQ to identify appropriate control efficiencies, costs, and
affected SCCs. Note that the mobile-source measure information currently in the CMDB
was derived for particular analyses and is not sharable with external partners (such as
State organizations) because it is not broadly applicable. State air agencies and other
organizations needing mobile-source control measure information should run the
appropriate mobile-source models and consult with OTAQ to obtain control measure
information for their particular applications.

There have been several efforts to review and enhance the data in the CMDB. Organizations that
have been involved in these efforts include Alpine Geophysics, Research Triangle Institute
(RTI), the University of North Carolina at Chapel Hill (UNC), E.H. Pechan & Associates, and
various offices within EPA. In its current form, the database primarily supports CAP control
strategy analyses and has extensive coverage for NOx controls for industrial sources. In early
2009, E.H. Pechan & Associates began work for EPA to quality assure, enhance and expand the
CMDB, which included the following tasks:

•	Resolve inconsistencies with AirControlNET "At-A-Glance" documentation

•	Re-evaluate SCCs applicable for each control measure

•	Update the control and cost information for several key industries

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•	Add control measure information for HAPs

•	Fill in missing control measure descriptions

2.2	Costs Associated with Control Measures

For many of the control measures in the CMDB, a simple cost factor in terms of "dollars per ton
of pollutant reduced" is used to calculate the cost of the control measure when applied to a
specific source. These cost-per-ton factors are estimates of the cost of control measures in
circumstances where there is limited information on how the engineering control costs vary with
respect to variables specific to the source, such as unit size, capacity, and inlet flow rate. These
cost-per-ton factors are the primary method of estimating costs for nonpoint-source control
measures. They are generated by taking the annualized control costs for a source or set of
sources and dividing by the measured or estimated emission reductions for the source(s). It
should be noted that these simple cost-per-ton factors may produce results with a high level of
uncertainty when applied to a small number of sources in a local-scale analysis.

For a few control measures, a different approach is used: cost equations. These equations
calculate engineering costs that take into account several variables specific to the source, when
data for those variables are available. Cost equations are most commonly available for point-
source control measures. These additional data can sometimes be found in the emissions
inventory, but often need to be obtained from other sources. See "Documentation of Cost
Equations in EPA's Control Strategy Tool" (available at http://www.epa.gov/ttn/ecas/cost.htm)
for more information on cost equations and their inputs.

Note that due to the methods used to obtain the cost data, there are limitations and uncertainties
inherent in both the cost-per-ton factors and the cost equation parameters, so caution must be
used when applying these approaches for estimating cost, especially for local-scale analyses.

2.3	Developing New Control Measure Information

There is an ongoing need for new and expanded control measure information in the CMDB, for
several reasons:

•	New control measures'. New measures are constantly being developed to address various
air quality and health-related issues and to achieve greater efficiencies in industrial
processes and mobile-source equipment.

•	Co-impacts: More data are needed on impact of established control measures on
pollutants other than the major targeted pollutant, such as the co-impacts of the measure
on HAPs and GHGs.

•	Improved characterization: Some existing control measure data are highly uncertain and
need to be improved to reflect latest practices.

Regarding the first bullet above, the general steps for developing new control measure
information for the CMDB are as follows:

1)	Identify and describe the control measure, including other control measures that this
measure might replace or be combined with.

2)	Collect information on the pollutants affected.

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3)	Collect information on the reductions to or increases in emissions of other pollutants as a
result of the measure application, either by itself or in addition to other measures. (For
example, a measure targeted at NOx may result in an increase in ammonia emissions.)
Identify ranges of reduction that can be achieved and calculate a single value of most
likely reduction.

4)	If possible, generate a cost equation that takes into account the variables that have the
greatest impact on cost, in terms of both capital costs and operating and maintenance
costs. If it is not possible to generate a cost equation, then calculate a cost-per-ton
reduction factor.

3 Control Measures Database Data Elements

As discussed in Section 2.1, the data in the CMDB are separated into five different tables for
each control measure:

1)	summary information about the control measure;

2)	efficiency records describing the reductions achieved by, and the costs required to apply,
the measure for each affected pollutant;

3)	a list of SCCs to which the measure applies;

4)	cost equation information (parameters used to compute the results of cost equations), for
measures to which this is applicable;

5)	references providing additional information on the control measure; and

6)	additional information that does not fit well within one of the five previous categories,
especially parameters that are unique to a single control measure or a subset of control
measures. The table in which this additional information is managed is called the
properties table.

These tables are described in Sections 3.1 through 3.5. In the tabular descriptions in these
sections, a data type is designated for each data field. The data types are:

•	"Char": Characters or text strings, with the assigned length of the data field shown in
parentheses (e.g., Char(128)).

•	"Real": Number fields that use a floating-point representation, which can handle numbers
with a fractional part as well as whole numbers.

•	"int": Whole numbers, with the assigned length of the integer field appended to "int"
(e.g., int4).

•	"Date": Date in the format mm/dd/yyyy.

Each table has one or more columns that comprise a primary key. A primary key is a column or
set of columns whose contents uniquely identify each row in a table. No two distinct rows in the
table can have the same value (or combination of values) for the primary key. Section 3.6 then
gives an example of each table type.

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3.1 Summary Table

The summary table in the CMDB provides high-level information about each control measure.
The fields in the summary table of the CMDB import-export format are shown in Table 1. Data
provided in the import-export format can be easily read into the database, and conversely subsets
of data in the database can be written into files in this format. The primary keys to this table are
the CMName and the CMAbbreviation (i.e., each measure must have its own unique name and
unique abbreviation); these keys are indicated in bold.

An example of a summary table is shown in Table 7 in Section 3.6.

Table 1. Summary Information Table Format

Column Label*

Data Type

Field Description

CMName

Char(255)

A unique name for the control measure that is described in a given row of the
summary table. Typically, the name consists of the combined fields
"ControlTechnology" and "SourceGroup" (describe in rows 3 and 4 below),
separated by a semicolon (e.g., SNCR; Ammonia - Oil-Fired Reformers). This is
a unique name that summarizes the control technology and the sources to which
it applies.

CMAbbreviation

Char(10)

An acronym-style unique abbreviation for the control measure. The abbreviation
is specific to an industry or source category. The first letter typically refers to the
major pollutant (i.e., pollutant that the control measure is primarily meant to
reduce): A=NH3, N=NOx, P=PM, S=S02, V=VOC. The next letters refer to the
Control Measure, followed by letters that refer to Source Group or Industry,
followed by letters that refer to Fuel Type or additional Industry information.

MajorPoll

Char(128)

Major pollutant: the pollutant most reduced by the control measure. Current
pollutant abbreviations include NH3, NOx, PM10, PM2_5, S02, VOC, etc. This
is used only to group related measures, and has no impact on how the measure
is assigned to sources in CoST.

ControlTechnology

Char(128)

The method used to reduce emissions (this can represent a device, practice, or
process). Note that when editing data for a control measure using the CoST
Graphical User Interface (GUI), you can type in a new entry for control
technology and this entry then becomes available when making future selections
from the control technology pull-down menu.

SourceGroup

Char(128)

The source group or industry sector to which the control measure applies. Note
that when editing data for a control measure using the CoST Graphical User
Interface (GUI), you can type a new entry for source group and this entry then
becomes available when making future selections from the source group pull
down menu.

Sector

Char(128)

The emission inventory sector or group of sectors to which the measure applies:
PTNONIPM (stationary point sources not covered by IPM), PTIPM (stationary
point source covered by IPM, generally some type of utility boiler), NONPT
(previously referred to as "area sources"), ONROAD (mobile highway vehicles),
NONROAD (mobile nonhighway sources such as construction equipment, and
lawn & garden equipment), ALM (airplanes, locomotives, and marine vessels),
PTFIRE (fires identified as point sources), AFDUST (area fugitive dust sources),
or AG (agricultural).

Class

Char(64)

Characterizes the status of the control measure. Current options are: Known
(i.e., already in use), Emerging (i.e., expected to be used in the future),
Hypothetical (i.e., the specified data are hypothetical), or Obsolete (i.e., no
longer in use).

EquipLife

Real

The expected life of the control measure equipment, in years.

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Column Label*

Data Type

Field Description

NEIDeviceCode

int4

The numeric code used in the National Emission Inventory (NEI) to indicate that
the measure has been applied to a source. In the NEI, this may be referred to
as APCJD. NEI Control Device Codes are available at:
ftD://ftD.eDa.aov/Emislnventorv/2002finalnei/documentation/Doint/auamentation

Doint/02nei IkuD states 011907.ziD

DateReviewed

Date

Date on which the control measure data were last reviewed (mm/dd/yyyy)

DataSource

Char(128)

A list of numeric codes separated by '|' (pipes) that refer to items in the
references table (see Section 3.5)

Description

Char(un-
limited)

Expanded description of the control measure, its applicability, and any other
relevant information.

* Unique keys are indicated in bold.

3.2 Efficiency Records Table

The efficiency records in the CMDB provide information about the control efficiency achieved
by the control measure, and the cost of applying the measure for each pollutant. The fields in the
efficiency records table of the CMDB import-export format are shown in Table 2. The
CMAbbreviation field is a "foreign key" that refers to a record in the summary table with the
same value for CMAbbreviation. Thus, the control measure name and other summary
information associated with the efficiency records can be looked up by finding the entry in the
summary table that has the same value as the CMAbbreviation field in the efficiency records
table. The fields with the column label in bold are used to compose the primary key for the
efficiency record. In other words, each unique record in the table must have a unique
combination of CMAbbreviation, Pollutant, Locale, Effective Date, ExistingMeasureAbbr,
MinEmissions, and MaxEmissions. This also means that you can specify different values for the
control efficiency and cost per ton for different pollutants, locales (i.e., states or counties), and
source sizes (the latter is done using the MinEmissions and MaxEmissions columns).

An example of an efficiency records table is shown in Table 8 in Section 3.6.

Table 2. Efficiency Records Table Format

Column Label*

Data Type

Description

CMAbbreviation

Char(10)

Acronym-style unique abbreviation for the control measure. See Table 1 for
more information. For the efficiency record to be valid, the value of
CMAbbreviation used for the efficiency record must be found in the
CMAbbreviation column of the summary table.

Pollutant

Char(128)

The pollutant impacted by the control measure (i.e., emissions of the
pollutant are either decreased or increased): PM10, PM2_5, PM_METALS,
EC, OC, S02, VOC, NOx, etc. This can be the major pollutant (see Table
1) or any other pollutant impacted by the measure. New pollutants (e.g.,
HAPs) may be added as necessary. Eventually, CoST will be updated to
support groups of related pollutants that behave similarly, such as 'Organic
HAPs', and individual GHGs.

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Column Label*

Data Type

Description

Locale

Char(6)

Particular areas of the country for which this record applies. This field can
be populated with a two-digit State FIPS code, or a five-digit State/County
FIPS code. If this field is empty, then it is assumed that the control measure
information applies nationwide. Locale might be included for sources such
as Onroad Mobile sources for which the MOBILE model calculates
individual control efficiencies for each county in the nation.

Effective Date

Date

Date (mm/dd/yyyy) when a particular efficiency record becomes effective
nationwide or in a specific locale (e.g., some measures are phased in over
time). The system will find the record with the closest effective date that is
less than or equal to the specified target year for the analysis (which is
usually the same as the year for which the inventory was constructed). If
this field is empty, then the record is assumed to apply to any date.

Existing MeasureAbbr

Char(10)

This field should be populated when the data for the record are provided,
assuming that a control measure has already been applied to the source.
The contents of the field should be the control measure abbreviation that
corresponds to the existing measure. The reason for this field is that the
efficiency of, and cost of applying, the measure may vary when there is
already a control measure installed on a source. (This field is not currently
used when assigning sources to measures)

NEIExistingDevCode

int4

This field applies only when the specified measure (per its NEI device code
abbreviation) is already applied to the source. (This field is not currently
used.)

MinEmissions

Real

This record applies only when the uncontrolled emissions for the inventory
source record exceed the specified amount.

MaxEmissions

Real

This record applies only when the uncontrolled emissions for the inventory
source record are less than or equal to the specified amount.

ControlEfficiency

Real

The [median] control efficiency (in units of percent reduction, e.g., 99.9% for
a 99.9% reduction in emissions) that is achieved when the measure is
applied to the source, exclusive of rule effectiveness and rule penetration.
Note that there are sometimes disbenefits for certain pollutants as a result
of the control measure, so control efficiency can be negative to indicate that
the amount of a pollutant actually increased.

CostYear

int4

The year that is the basis for the capital and annual cost estimate.

CostPerTon

Real

The cost to reduce each ton of the specified pollutant.

RuleEff

Real

The rule effectiveness of the measure, which may vary by locale. Rule
effectiveness is defined as "the ability of a regulatory program to achieve all
the emissions reductions that could have been achieved by full compliance
with the applicable regulations at all sources at all times". A rule
effectiveness of 100% means that all sources are fully complying at all
times.

RulePen

Real

The rule penetration of the measure, which may vary by locale. Rule
penetration is the percent of sources that are required to implement the
control measure. Rule penetration might vary over time as a new rule is
"phased in" gradually. RulePen is typically 100 for measures applied to
point sources.

EquationType

Char(128)

"cpton" for Cost per Ton, or give equation type (Type 1, Type 2, etc.).
Currently only cpton is used here and other equations are stored separately
in the Equations table.

CapRecFactor

Real

The capital recovery factor, based on the interest rate and the equipment
life in years.

DiscountRate

Real

The discount/interest rate used to compute annualized capital costs.

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Column Label*

Data Type

Description

CapAnnRatio

Real

Ratio of the total capital investment to the total annual costs.

IncrementalCPT

Real

Incremental cost per ton if another control has already been applied. (This
is not currently used in computations.)

Details

Char(255)

Text that specifies information about the source of data for this record; or
the reason the data for the record was changed.

* Unique keys are indicated in bold.

Regarding the use of CMDB cost data: Cost data obtained by EPA for the CMDB are in terms of
a particular year, and that year varies from one control measure to another. To compute the cost
results for a control strategy, it is necessary to escalate or de-escalate the costs to a consistent
year in order to adjust for inflation and create consistency when adding up costs and comparing
costs. This cost escalation is done using the following formula:

Cost ($) for a year of interest = Cost for original cost year x Chained GDP for cost year

Chained GDP for year of interest

where the chained GDP is the chained Gross Domestic Product available from the United States
Department of Commerce Bureau of Economic Analysis spreadsheet at

http://www.bea.gov/national/xls/gdplev.xls. The current chained GDP table used in the CMDB is
dated January 30, 2009. An excerpt of this table is shown in Table 3.

Table 3. Excerpt from the gdplev Table
Used to Convert Data between Cost Years

Year

Current_GDP

Chained_GDP

1996

7816.9

8328.9

1997

8304.3

8703.5

1998

8747

9066.9

1999

9268.4

9470.3

2000

9817

9817

2001

10128

9890.7

2002

10469.6

10048.8

2003

10960.8

10301

2004

11712.5

10675.8

2005

12455.8

10989.5

2006

13246.6

11294.8

2007

13807.5

11523.9

To facilitate comparing the costs of control measures with one another, a normalized version of
the control measure cost per ton is actually stored within the CMDB and is called the "Reference
year cost per ton". These costs have all been converted to a consistent "Reference Year" using
the above formula, so that the cost of any measure can be compared with any other even if their

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cost years differ. Currently, the reference year is 2006. In addition, during the course of a CoST
run for a given strategy, the costs are converted (using the above formula) from the reference
year to the cost year that is specified by the CoST user as an input to the strategy, and the results
of the strategy are therefore presented in terms of the specified cost year.

3.3 SCCs Table

The SCCs table identifies the specific SCCs to which each control measure applies. The
CMAbbreviation field is a foreign key that refers to a record in the summary table with the same
value for CMAbbreviation. Thus, the control measure name and other summary information
associated with the efficiency records can be looked up by finding the entry in the summary table
that has the same value as the CMAbbreviation field in the SCCs table. The fields with the
column label in bold are used to compose the primary key for the SCC record. In other words,
each unique record in the table must have a unique combination of CMAbbreviation and SCC.

When CoST runs a control strategy, the control measure is considered for application for any
inventory sources that have one of the SCCs specified for the measure. Thus, if the measure can
apply to sources with more than one SCC, there should be multiple rows listed in this table with
the same value for the CMAbbreviation. Note that CoST requires an explicit list of SCCs to be
listed for each measure, and will not expand a general SCC ending in zeros to specific SCCs
(e.g., 2310000000 will not expand to 2311011000). However, if it is anticipated that a general
SCC (ending in zeros) might appear in the inventory and if the measure should be applied to the
source, that SCC should be included in the CMDB.

An example of an SCCs table is shown in Table 9 in Section 3.6.

Table 4. SCCs Table Format

Column Label*

Data Type

Description

CMAbbreviation

Char(10)

Acronym-style unique abbreviation for the control measure. See Table 1 for
more information. For the SCC record to be valid, its CMAbbreviation must be
found in the summary table.

SCC

Char(10)

Source Classification Code to which the control measure applies: there are
11,000+ SCCs. The SCC is emissions unit specific and often industry specific,
but may be applied generically to industries for certain sources, such as
Industrial Boilers.

Status

Char(128)

Whether the SCC is Current, Non-existent, or Inactive. (This field is informational
and is not considered during any computations.)

* Unique keys are indicated in bold.

3.4 Equations Table

The equations table contains parameters used to compute the results of cost equations. The
CMAbbreviation field is a foreign key that refers to a record in the summary table with the same
value for CMAbbreviation. Thus, the control measure name and other summary information
associated with the cost equations can be looked up by finding the entry in the summary table
that has the same value as the CMAbbreviation field in the cost equations table. Currently, at
most a single entry should appear in this table for each CMAbbreviation. If there is no

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applicable equation for the measure, no rows should appear for that CMAbbreviation. There are
several types of cost equations, and the variables specified in the Varl through VarlO data fields
differ for each type. More information on these variables and the available cost equations can be
found in "Documentation of Cost Equations in EPA's Control Strategy Tool (CoST)" at
http://www.epa.gov/ttn/ecas/models/documentation control strategy tool cost equations%20.p
df.

An example of an equations table is shown in Table 10 in Section 3.6.

Table 5. Equations Table Format

Column Label*

Data Type

Description

CMAbbreviation

Char(10)

Acronym-style unique abbreviation for the control measure. See Table 1 for
more information. For the equation record to be valid, its CMAbbreviation must
be found in the summary table.

CMEqnType

Char(128)

Cost equation "type": Type 1, Type 2, Type 3, Type 4, Type 5, Type 6, Type 7,
Type 8 equations as specified in "Documentation of Cost Equations in EPA's
Control Strategy Tool (CoST)". Each type uses multiple variables to estimate the
costs.

Pollutant

Char(128)

The pollutant being reduced for which the equation is computing costs (i.e.,
emissions of the pollutant are either decreased or increased): PM10, PM2_5,
PM_METALS, EC, OC, S02, VOC, NOx, etc. Typically this is the major pollutant
impacted by the measure.

CostYear

int4

The year that is the basis for the capital and annual cost estimate.

Vaii

Real

Value for 1 st variable in cost equation.

Var2

Real

Value for 2nd variable in cost equation.

Var3

Real

Value for 3rd variable in cost equation.

Var4

Real

Value for 4th variable in cost equation.

Var5

Real

Value for 5th variable in cost equation.

Var6

Real

Value for 6th variable in cost equation.

Var7

Real

Value for 7th variable in cost equation.

Var8

Real

Value for 8th variable in cost equation.

Var9

Real

Value for 9th variable in cost equation.

Var10

Real

Value for 10th variable in cost equation.

* Unique keys are indicated in bold.

3.5 References Table

The references table provides a list of references that are referred to in the DataSource field in
the summary tables for all control measures. In the references table, the DataSource column is
the key, and multiple control measures may refer to the same data source. The DataSource
numeric code in this table relates to the codes list in the DataSource field in the summary table

An example of a references table is shown in Table 11 in Section 3.6.

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Table 6. References Table Format

Column Label*

Data Type

Description

DataSource

Char(128)

Numeric code of the reference or data source for the control information
(numbered 1 through xx).

Description

Char(512)

Expanded description of the control measure, its applicability, and any other
relevant information.

* Unique keys are indicated in bold.

3.6	Properties Table

The properties table includes fields that are unique to a single or small number of control
measures, or that do not fit easily within the previously described tables. Unlike the other
CMDB tables, this table does not contain a fixed set of pre-defined fields but instead allows the
user to add any number of new fields. This format allows greater flexibility for adding new
information to the CMDB that does not readily fit within the existing fields of the previous
tables.

3.7	Examples of Control Measure Data Tables

Tables 7 through 12 provide examples of data contained in the CMDB.

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Table 7. Summary Table Example*

CMName

CMAbbreviation

Major
Poll

Control
Technology

SourceGroup

Sector

Class

Equip
Life

Date

Reviewed

Data
Source

Description

AF + IR; Internal

NAFRIICGS

NOx

AF + IR

Internal

PTNONIPM

Known

15

2006

1135

N0227

Combustion Engines -







Combustion













Gas







Engines - Gas













Amine Scrubbing; Sulfur
Recovery Plants -
Elemental Sulfur (Claus:

SAMSCSRP95

S02

Amine Scrubbing

Sulfur Recovery
Plants - Elemental
Sulfur

PTNONIPM

Known

15

2006

1

S0601

2 Stage w/o control (92-
95% removal))





















Amine Scrubbing; Sulfur
Recovery Plants -
Elemental Sulfur (Claus:

SAMSCSRP96

S02

Amine Scrubbing

Sulfur Recovery
Plants - Elemental
Sulfur

PTNONIPM

Known

15

2006

1

S0701

3 Stage w/o control (95-
96% removal))





















Biosolid Injection

NBINTCEMK

NOx

Biosolid Injection

Cement Kilns

PTNONIPM

Known

15

2006

1

NCEMK

Technology; Cement
Kilns





Technology















Biosolid Injection;
Cement Manufacturing

NDBIOCM

NOx

Biosolid Injection

Cement
Manufacturing

PTNONIPM

Emerging

15



40



Catalyst

Additive;Petroleum

SCATPETCRK

S02

Catalyst Additive

Petroleum Refinery
Catalytic and

PTNONIPM

Known



2006

28|29



Refinery Catalytic and
Thermal Cracking Units







Thermal Cracking
Units













CEM Upgrade and

PCUIMASMN

PM10

CEM Upgrade and

Asphalt

PTNONIPM

Known



2006

1



Increased Monitoring of





Increased

Manufacture













PM Controls;(PM10)
Asphalt Manufacture





Monitoring
Frequency of PM
Controls















* The column NEIDeviceCode has been excluded to make the table fit on the page and because there were no data in that column.

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Table 8. Efficiency Records Table Example*

CMAbbreviation

Pollutant

Locale

Effective
Date

Min

Emis

sions

Max

Emis

sions

Control
Efficiency

Cost
Year

Cost
PerTon

RuleEff

Rule
Pen

Equation
Type

Cap
Rec
Factor

Cap
Ann
Ratio

In ere

mental

CPT

NAFRICGS

NOx





365



20.00%

1990

380

100

100

cpton

0.1098

1.5

380

NAFRICGS

NOx





0

365

20.00%

1990

1570

100

100

cpton

0.1098

2.8

1570

SAMSCSRP95

S02









98.4%

1990



100

100

5

.1098





SAMSCSRP96

S02









97.8%

1990



100

100

5

.1098





NBINTCEMK

NOx









23.0%

1997

310

100

100

cpton

.1098

7.3



NDBIOCM

NOx









40.0%

1999

336.7

100

100









NWTINGTJF

NOx





365



68.00%

1990

650

100

100

cpton

0.1098

1.6

650

SCATPETCRK

S02









43.00%

2004

1493

100

100

cpton







NWTINGTNG

NOx





365



76.00%

1990

730

100

100

cpton

0.1098

1.6

730

NWTINGTNG

NOx





0

365

76.00%

1990

1510

100

100

cpton

0.1098

3.1

1510

NWTINGTOL

NOx





0

365

68.00%

1990

1290

100

100

cpton

0.1098

2.9

1290

NWTINGTOL

NOx





365



68.00%

1990

650

100

100

cpton

0.1098

1.6

650

PCUIMASMN

PM10









7.70%

2003

5200

100

100

cpton







PCUIMASMN

PM10

37

1/1/2010





10.0%

2003

5200

100

100

cpton







PCUIMASMN

PM2_5









7.70%





100

100









PCUIMCHMN

PM10









7.70%

2003

5200

100

100

cpton







PCUIMCHMN

PM2_5









7.70%





100

100









PCUIMCHMN

PM_METALS









7.70%





100

100









PCUIMCIBCL

PM2_5









7.70%





100

100









PCUIMCIBCL

PM10









7.70%

2003

5200

100

100

cpton







PCUIMCIBLP

PM10









7.70%

2003

5200

100

100

cpton







* The columns ExistingMeasureAbbr, NEIExistingDevCode, DiscountRate, and Details have been excluded to make the table fit on the page and because there were no data in
these columns.

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Table 9. SCCs Table Example

CMAbbreviation

see

Status

NAFRICGS

20100202

Current

NAFRICGS

20100205

Current

NAFRICGS

20100206

Current

NAFRICGS

20100207

Current

NAFRICGS

20100208

Current

NAFRICGS

20100209

Current

NAFRICGS

20200202

Current

NAFRICGS

20200204

Current

NAFRICGS

20200205

Current

NAFRICGS

20200206

Current

NAFRICGS

20200207

Current

SAMSCSRP95

30103201

Current

SAMSCSRP96

30103202

Current

SAMSCSRP97

30103203

Current

SCATPETCRK

30600201

Current

SCATPETCRK

30600202

Current

SCATPETCRK

30600301

Current

NWTINGTNG

20100201

Current

NWTINGTNG

20100205

Current

NWTINGTNG

20100206

Current

NWTINGTNG

20100207

Current

NWTINGTNG

20100208

Current

NWTINGTNG

20100209

Current

NWTINGTNG

20200201

Current

PCUIMASMN

30500100

Inactive

PCUIMASMN

30500101

Current

PCUIMASMN

30500102

Current

PCUIMASMN

30500103

Current

PCUIMASMN

30500104

Current

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Table 10. Cost Equations Table Example

CMAbbreviation

CMEqn
Type

Pollut
ant

Cost
Year

Var1

Var2

Var3

Var4

Var5

Var6

Var7

Var8

Var9

Var10

NLNBOUBCW

Type 1

NOx

1999

23.4

0.36

0.07

300

0.36

0.85









NLNBOUBCW2

Type 1

NOx

1999

23.4

0.36

0.07

300

0.36

0.85









SFGDWUBVHS

Type 1

S02

1990

174

6.3

1.8

500

0.6

0.65









SRPNGUBCF

Type 1

S02

1998

1566

25.44

2.42

500

0.6

0.65









NLNBUGTNG

Type 2

NOx

1990

71281.1

0.51

7826.3

0.51

71281.1

0.51

7826.3

0.51

0.11



NLNBUIBCW

Type 2

NOx

1990

53868.7

0.6

11861.1

0.6

53868.7

0.6

11861.1

0.6

0.14



SFGDSPPSP

Type 3

S02

1990





















SFGDSSGCO

Type 3

S02

1990





















SSADPPRMTL

Type 3

S02

1990





















SDLABPLSS

Type 4

S02

1990





















SDLABPZSS

Type 4

S02

1990





















SNS93SACA

Type 4

S02

1990





















SAMSCSRP95

Type 5

S02

1990





















SAMSCSRP96

Type 5

S02

1990





















SAMSCSRP97

Type 5

S02

1990





















SFGDSCMOC

Type 6

S02

1990





















SFGDSECMP

Type 6

S02

1990





















PDESPCIBCL

Type 8

PM10

1995

27

16

710

41

110











PDESPCIBOL

Type 8

PM10

1995

27

16

710

41

110











PFFMSASMN

Type 8

PM10

1998

29

11

412

62

126











PFFMSMICC

Type 8

PM10

1998

29

11

412

62

126











PWESPMPOR

Type 8

PM10

1995

40

19

923

135

220











PWESPMPZC

Type 8

PM10

1995

40

19

923

135

220











PWESPWDPP

Type 8

PM10

1995

40

19

923

135

220











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Table 11. References Table Example

Data
Source

Description

1

"AirControlNET Database, May 2006" Prepared for US EPA, OAQPS, RTP, NC 27711. Prepared by Pechan & Associates, Inc., 5528-B Hempstead Way, Springfield,
VA 22151. May 2006.

2

"AirControlNET v.4.1 Documentation Report." Prepared for US EPA, OAQPS, RTP, NC 27711. Prepared by Pechan & Associates, Inc., 5528-B Hempstead Way,
Springfield, VA 22151. Pechan Report No. 05.09.009/9010.463. September 2005. www.epa.gov/ttnecas1/models/DocumenationReport.pdf

3

Pechan, 1995: E.H. Pechan & Associates, Inc., "Regional Particulate Strategies - Draft Report," prepared for U.S. Environmental Protection Agency, Office of Policy
Planning and Evaluation, Washington, DC, September 1995.

4

Pechan, 1998: E.H. Pechan & Associates, Inc., "Clean Air Act Section 812 Prospective Cost Analysis - Draft Report," prepared for Industrial Economics, Inc., Cambridge,
MA, September 1998.

5

Pechan, 1997: E.H. Pechan & Associates, "Additional Control Measure Evaluation forthe Integrated Implementation of the Ozone and Particulate Matter National
Ambient Air Quality Standards, and Regional Haze Program," prepared for U.S. Environmental Protection Agency, July 1997.

6

SCAQMD, 1996: South Coast Air Quality Management District, "1997 Air Quality Management Plan, Appendix IV-A: Stationary and Mobile Source Control Measures."
August 1996.

7

EPA, 1986: U.S. Environmental Protection Agency, Air and Engineering Research Laboratory, Identification, Assessment, and Control of Fugitive Particulate Emissions,
EPA/600/8-86/023, prepared by Midwest Research Institute, August 1986.

9

SCAQMD, 1994: South Coast Air Quality Management District, "1994 Air Quality Management Plan, Appendix l-D: Best Available Control Measures PM-10 SIP for the
South Coast Air Basin," April 1994.

10

Clapper, 1999: W. Clapper, Sunline Transit Services, personal communication with J. Reisman, E.H. Pechan & Associates, Inc., August 18, 1999.

11

Harrison, 1999: J. Harrison, GCS Western Power, personal communication with J. Reisman, E.H. Pechan & Associates, Inc., August 18, 1999.

12

Pechan, 1999: E.H. Pechan & Associates, Inc., "Control Measure Evaluations: The Control Measure Data Base forthe National Emissions Trends Inventory (Control
NET)," prepared for U.S. Environmental Protection Agency, Office of Air Quality Planning and Standards, Innovative Strategies and Economics Group, Research
Triangle Park, NC, September 1999

13

Pechan, 1998: E.H. Pechan & Associates, Inc., "Clean Air Act Section 812 Prospective Cost Analysis - Draft Report," prepared for Industrial Economics, Inc., Cambridge,
MA, September 1998.

14

Peters, 1977: J.A. Peters, and T. R. Blackwood, Monsanto Research Corporation, "Source Assessment: Beef Cattle Feedlots," prepared for U.S. Environmental Agency,
Office of Research and Development, Research Triangle Park, NC, June 1977.

15

EPA, 1974: U.S. Environmental Protection Agency, "Investigation of Fugitive Dust, Volume I Sources, Emissions, and Control," EPA-450/3-74-036a. June 1974.

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Table 12. Properties Table Example

CMAbbreviation

Name

Category

Units

Data Type

DB FieldName

Value

SDLABPLSS

ADMIN PCT

No category

%

double precision

ADMIN PCT

0

NLNBNPHDO

APPLICATION

No category



text

APPLICATION

This control is the use of low NOx
burner (LNB) technology and
selective non catalytic reduction
(SNCR) to reduce NOx emissions.
LNBs reduce the amount of NOx
created from reaction between fuel
nitrogen and oxygen by lowering the
temperature of one combustion zone
and reducing the amount of oxygen
available in another. SNCR controls
are post-combustion control
technologies based on the chemical
reduction of nitrogen oxides (NOx)
into molecular nitrogen (N2) and
water vapor (H20).

This control is applicable to small (40
to 174 MMBtu/hr) distillate oil-fired
process heaters with uncontrolled
NOx emissions greater than 10 tons
per year.

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4 Using the CMDB to Develop Control Strategies

This section provides an overview of how the control measure data are used in developing
control strategies, to provide some context regarding how the fields in the database are used.

4.1 Summary of the Strategy Development Process

A control strategy applies a set of control measures to emissions inventory sources in a specified
geographic region (in addition to any controls that are already in place) to accomplish an
emissions reduction goal. Such goals are usually set to improve air quality and/or to reduce risks
to human health. CoST automates the key steps for preparing and running control strategies
designed to estimate emissions reductions and their associated costs.

The inputs to a control strategy consist of:

•	a set of parameters that control how the strategy is run,

•	one or more emissions inventory datasets,

•	filters to limit the sources included from those datasets;

•	filters to limit which control measures are to be included in the analysis, and

•	constraints that limit the application of measures to specific sources based on the
resulting costs and/or emissions reduction achieved.

A diagram of the basic steps for running a control strategy is shown in Figure 1.

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Figure 1. Basic Steps for Running a Control Strategy Using CoST

1) Input Basic Parameters (e.g.):

•	Type of Analysis

•	Cost Year

•	Target Pollutant



2) Select Strategy Algorithm (e.g.):

•	Max Emissions Reduction

•	Least Cost

•	Least Cost Curve

~~I

3) Select Inventory Dataset(s):

•	Sectors (e.g., ptipm, ptnonipm,
nonpt, onroad, nonroad)

•	Projection year (e.g., 2020, 2030)

•	Filters for specific SCCs,
geographic areas, etc.

4) Select Control Measures:

•	Default is to include known
measures

•	Can select certain technologies

5) Select Constraints (e.g.):

•	Max cost/ton controls (e.g.,
$20K/ton)

•	Min emissions size (e.g., 10 tpy)

6) Run
Strategy
Query

Outputs:

Detailed
Pairing of
Measures to
Sources

Various
Summary
Files

Control
Case
Emissions
inventory

At this time, six algorithms are available in CoST to control how measures are assigned to
sources:

1.	Annotate Inventory: Assigns control measures to the inventory based on the specified
control efficiency for each source. This algorithm can also be used to fill in control
measure information for inventory sources that are missing details on the actual control
measures used, but have a control efficiency assigned. (It could be applied to either a
base- or future-year inventory.)

2.	Apply Measures in Series: Assigns all control measures that can be used for a source to
that source in the specified order. This is often used for mobile sources, for which the
control measures are typically independent of one another.

3.	Least Cost: Each source is assigned a single measure to achieve a specified percentage
or absolute reduction in a region with the minimum possible annualized cost.

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4.	Least Cost Curve: Performs least-cost runs iteratively at multiple percent reductions so
that a cost curve can be developed that shows how the annualized cost increases as the
level of desired reduction increases.

5.	Maximum Emissions Reduction: Assigns to each source the single measure that
provides the maximum reduction for the target pollutant, regardless of cost.

6.	Project Future-Year Inventory: Applies control programs and growth factors to
sources, as would be needed to project a base-year inventory to a future-year inventory.

The main CoST output for each control strategy is a table called the "Strategy Detailed Result".
This table consists of emission source-control measure pairings, each of which contains
information about the cost and emission reduction that would be achieved if the measure were
applied to the source. Some columns available in the Strategy Detailed Result are:

CM_Abbrev, POLL, SCC, FIPS, PlantJD, Annual_cost, Ann_cost_per_ton, control_efficiency,
final_emissions, emis_reduction, inv_emissions, SIC, NAICS, equation_type, ...

For examples of Strategy Detailed Result tables, please see the "CoST Development Document"
or the "CoST Training Manual and User's Guide". The Strategy Detailed Result table can be
combined, in an automated manner, with the original input inventory to produce a controlled
emissions inventory that reflects implementation of the strategy; this inventory includes
information about the measures that have been applied to the controlled sources. The controlled
inventory can then be directly input to the SMOKE modeling system to prepare air quality
model-ready emissions data. In addition, comments are placed at the top of the inventory file to
indicate the strategy that produced it and the settings of the high-level parameters that were used
to run the strategy.

4.2 Strategy Inputs Relevant to Control Measures

All types of control strategies have fields for which the user can specify values prior to running
the strategy. For a complete listing of the fields, see the "CoST Development Document"
(http://www.epa.gov/ ttn/ecas/cost.htm). The following fields are particularly relevant to how
control measure efficiency records are selected and applied to emissions inventory sources:

•	Target Year: This is the target year for the strategy run. Typically, this is the year
represented by the input inventory(ies). For the "Project Future-Year Inventory" analysis
type, the target year represents the future year to which you are projecting the inventory.
For control measure efficiency records to be considered for a strategy, the specified
effective date for the record must be equal to or earlier than the target year, or the
effective date may be unspecified to indicate that it is relevant to any year.

•	Target Pollutant: The pollutant that is targeted as the primary interest for reduction in this
control strategy. The 'Least Cost' and 'Maximum Emissions Reduction' algorithms will
consider reductions of this pollutant when performing their computations. Note that
reductions of pollutants other than the selected target pollutant (e.g., PMi0, PM2.5, EC,
OC) will be included in strategy results if (1) they appear in the inventories that are input
to the strategy and (2) they are reduced by measures applied as part of the strategy. These
pollutants are sometimes referred to as "co-impact pollutants.", and the impact on the
emissions can either be a reduction (i.e., a benefit) or an increase (i.e., a disbenefit).

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The following settings for the strategy are known as "constraints". If the constraint values are
not satisfied for a particular control measure and source combination, the measure under
consideration will not be applied to the source, and CoST will look for another measure that
satisfies all of the constraints.

•	Minimum Emissions Reduction (tons): If specified, requires each control measure to
reduce the target pollutant by the specified minimum tonnage for a particular source
(down to the plant+point+stack+segment level of specification). If the minimum tonnage
reduction is not attained when applying a measure to the source, that measure will not be
applied and another that meets the constraint will be selected, if possible.

•	Minimum Control Efficiency (%): If specified, requires each control measure used in the
strategy to have a control efficiency greater than the specified control efficiency for a
particular source and target pollutant.

•	Maximum Cost per Ton ($/ton): If specified, each control measure must have an
annualized cost per ton less than the specified maximum annualized cost per ton for the
target pollutant for each source. If the maximum cost per ton is exceeded when applying
a measure to the source, that measure will not be applied and another that meets the
constraint will be selected, if possible. This cost is based on 2006 dollars.

•	Maximum Annualized Cost ($/vr): If specified, each control measure must have an
annualized cost less than the specified annualized cost for the target pollutant for each
source. If the maximum annualized cost is exceeded when applying a measure to the
source, that measure will not be applied and another that meets the constraint will be
selected, if possible. This cost is based on 2006 dollars.

•	Minimum Percent Reduction Difference for Replacement Control (%): If specified, each
control measure must cause a percent reduction in emissions greater than the specified
value in order for the old control measure to be "replaced by" the new control measure,
according to the formula:

(original emissions-new emissions) * 100 / original emissions > min. percent red. diff

By expressing the requirement in this way, it would allow a control with 99.9%
efficiency to replace one with 99% efficiency, for example. Note that incremental
controls that add an additional device onto a previously controlled source are not yet
supported by CoST, except for the Apply Measures in Series strategy type, for which all
controls are assumed to be independently applicable. In the event that a combination of
two control devices is listed as a control measure (e.g., low NOx burner [LNB] + flue gas
recirculation [FGR]) and provides an appropriate level of emissions reduction, that
combination control measure can serve as a replacement control for the original measure.

4.3 Control Measure Filtering and Custom Overrides

For all strategy types except "Project Future-Year Inventory", the measures used during an
analysis can be filtered either by measure class (see field 7 in Table 1) or by specifying specific
measures to consider for the strategy run.

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Control Strategy Tool (CoST) Control Measures Database (CMDB) Documentation

•	Measure class: By default, only measures with the class set to "Known" are included in a
strategy run. Measures with other classes — Emerging, Hypothetical, or Obsolete —
may be selected for inclusion in a strategy. Note that only the measures with the classes
selected by the user will be included in the strategy run.

•	Specific measures: As an alternative to selecting the classes of measures to include, users
can select specific measures to include in the strategy. Values for rule penetration and
rule effectiveness can be overridden for the specified measures. Note that in the CMDB
the geographic extent for individual measures can be limited to certain sets of counties by
specifying a region dataset for the measure from one of the available datasets with the
"List of Counties (CSV)" dataset type. For algorithms that support the application of
multiple measures to sources, such as "Apply Measures in Series", an order of application
can be specified for the selected measures and they will be applied in ascending order.
For example, a mobile-source strategy may have the following specified for each
measure: an order of application, a geographic region, and a rule penetration override.

Control measure filtering and custom overrides are not available for the "Project Future Year

Inventory" strategy type. Instead, the user may select from a list of available control programs.

Control programs are described in more detail in the "Control Strategy Tool (CoST) Training

Manual and User's Guide".

5 References

Byun, D.W., K.L, Schere. "Review of the Governing Equations, Computational Algorithms, and
Other Components of the Models-3 Community Multiscale Air Quality (CMAQ) Modeling
System". Appl. Mech. Rev. 2006, 59, pp. 51-77.

Eyth, A.M., D. del Vecchio, D. Yang, D. Misenheimer, D. Weatherhead, L. Sorrels, "Recent
Applications of the Control Strategy Tool (CoST) within the Emissions Modeling
Framework", 17th Annual Emissions inventory Conference, Portland, OR, 2008.
(http://www.epa.gov/ttn/chief/conference/eil7/session8/evth.pdf)

Houyoux, M.R., M. Strum, R. Mason, A. Eyth, A. Zubrow, C. Allen, "Using SMOKE from the
Emissions Modeling Framework", 17th Annual Emissions inventory Conference, Portland,
OR, 2008. (http://www.epa.gov/ttn/chief/conference/eil7/session6/houvoux pres.pdf)

Misenheimer, D.C., "A New Tool for Integrated Emissions and Controls Strategies Analysis",
16th Annual Emissions inventory Conference, Raleigh, NC, 2007.
(http://www.epa.gov/ttn/chief/conference/eil6/sessionl/misenheimer.pdf)

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