DSHW-2012-002300 - 0901a068802bc947

u'lvision of
Solid and Hazardous Waste
23 March 2012
8200-FY12-077
Mr. Scott T. Anderson, Executive Secretary
State of Utah Department of Environmental Quality
Division of Solid and Hazardous Waste
195 N.1950 W.
P.O. Box 144880
Salt Lake City, Utah 84114-4880
Re: ATK Launch Systems-Promontory EPA ID number UTD009081357
Revised Preliminary Air Dispersion Modeling Assessment Draft Report for Open
Bum and Open Detonation Treatment Units at ATK Launch Systems for Use in
the Human Health and Ecological Risk Assessments
Dear Mr. Anderson:
Enclosed is the Revised Preliminary Air Dispersion Modeling Assessment Draft Report
for the Open Burn and the Open Detonation Treatment Units at ATK Launch Systems
Promontory facility. This information is necessary to conduct the Human Health and
Ecological Risk Assessments for our OB/OD operations.
Please contact me if you have any questions conceming this report. My telephone
number is [phone] or you can contact Blair Palmer at [phone].
/ certify under penalty of law that this document and all attachments were prepared under my
direction or supervision in accordance with a system designed to assure that qualified personnel
properly gather and evaluate the informalion submitted. Based on my inquiry of the person or
persons who manage the system, or those persons direcdy responsible for gathering ihe
information, the information is, to the best of my knowledge and belief, true, accurate, and
complete. I am aware that there are significant penalties for submitting false information,
including the possibility of fine and imprisonment for knowing violations.
Sincerely
George E.'Gooch, Manager
Environmental Compliance
cc: JeffVandel
Division of
Solid and Hazardous Waste
MAR 2 3 2012
Z(XZ.-0D2SW
REVISED PRELIMINARY
AIR DISPERSION MODELING
ASSESSMENT DRAFT REPORT
FOR
OPEN BURN AND OPEN DETONATION
TREATMENT UNITS
AT
ATK LAUNCH SYSTEMS
BRIGHAM CITY, UTAH
MARCH 2012
TABLE OF CONTENTS
MARCH 2012
Division of Solid and Hazardous Waste
MAR 2 3 2012
SECTION PAGE NO.
1.0 INTRODUCTION 1-1
2.0 AIR DISPERSION MODELING PROTOCOL 2-1
2.1 TERRAIN AND SITE DESCRIPTION 2-1
2.2 TREATMENT LOCATIONS 2-1
2.2.1 M-136 Treatment Unit Description 2-2
2.2.2 M-225 Treatment Unit Description 2-2
2.3 AIR QUALITY DISPERSION MODEL SELECTION 2-3
2.3.1 Fiat and Complex Terrain Modeling 7 2-3
2.4 LAND USE ANALYSIS 2-4
2.5 SURFACE ROUGHNESS HEIGHT 2-5
2.6 OB/OD SOURCE SCENARIOS 2-5
2.7 M-136 TREATMENT QUANTITY SCENARIOS 2-7
2.8 M-225 TREATMENT QUANTITY SCENARIOS 2-7
2.9 SOURCE PARAMETERS 2-7
2.9.1 ODOBi Emissions Testing and Emission Factors 2-7
2.10 MODELING ASSUMPTIONS FOR M-136 AND M-225 2-10
2.11 DEPOSITION MODELING 2-12
2.12 RECEPTOR NETWORKS 2-14
2.12.1 General Receptor Networks 2-14
2.12.2 Discrete Receptor Network 2-15
2.13 METEOROLOGICAL DATA 2-16
2.13.1 Surface Data 2-16
2.13.2 Upper Air Observations (Mixing Height Data) 2-17
2.13.3 Meteorological Preprocessor 2-18
2.14 OBODM MODELING METHODOLOGY 2-18
2.14.1 Discrete Receptors :.2-19
2.14.2 General Grid Receptors 2-20
3.0 AIR DISPERSION MODELING RESULTS 3-1
3.1 PRESENTATION OF RESULTS 3-1
3.2 DISCRETE RECEPTORS 3-2
3.2.1 Compliance with NAAQS 3-3
3.2.2 Compliance with Utah 1-Hour Acute Gas TSLs 3-6
3.2.3 Compliance with Utah 24-Hour Chronic Gas TSLs 3-8
3.2.4 Compliance with Utah 24-Hour Chronic Particulate TSLs 3-10
3.3 GENERAL GRID MAXIMUM IMPACT RECEPTORS.. 3-12
3.3.1 Compliance with NAAQS 3-12
3.3.2 Compliance with Utah 1-Hour Acute Gas TSLs 3-12
3.3.3 Compliance with Utah 24-Hour Chronic Gas TSLs 3-12
3.3.4 Compliance with Utah 24-Hour Chronic Particulate TSLs 3-13
3.3.5 Compliance with OSHA 8-Hour TWA Criteria 3-13
3.4 UNCERTAINTY ANALYSIS 3-13
3.4.1 Uncertainties Due To Emissions Parameters 3-13
3.4.2 Uncertainties Due To Source Parameters 3-13
3.4.3 Uncertainties Due To Meteorological Parameters 3-14
3.4.4 Uncertainties Due To Particle Size 3-14
3.4.5 Uncertainty Due To OBODM 3-15
3.5 SUMMARY AND RECOMMENDATIONS 3-16
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MARCH 2012
TABLE OF CONTENTS (Continued)
SECTION
REFERENCES.
PAGE NO.
R-1
APPENDICES
A
B
C
D
E
G
H
J
L
ATK DISPERSION MODELING LAND USE ANALYSES FOR M-136 AND M-225
M-245 METEOROLOGICAL DATA AND DATA RECOVERY STATISTICS
ANNUAL WIND ROSE PLOTS ATK M-245 METEOROLOGICAL STATION FOR
1997, 1998, 1999, 2000, AND 2001
GAS MODELING RESULTS
PARTICULATE MODELING RESULTS
GAS DISPERSION FACTORS
PARTICULATE DISPERSION FACTORS
DISCRETE RECEPTOR MODELING
HOURLY AND ANNUAL EMISSION FACTORS AND EMISSION RATES
TABLES
NUMBER
2-1 M-136 Treatment Unit Sources, Wastes Treated, Modeled Treatment Quantities per Event,
Treatment Schedule and Applicable Emission Factors
2-2 M-225 Treatment Unit Sources, Wastes Treated, Modeled Treatment Quantities per Event,
Treatment Schedule and Applicable Emission Factors
2-3 M-136 Source Parameters
2-4 M-225 Source Parameters
2-5 1.3 Class Waste Material "Conservative" Maximum Emission Factors (lbs/lb)
2-6 1.3 Class Waste Material "Corrected" Emission Factors (lbs/lb)
2-7 Summary of Deposition Modeling Parameters
2-8 ATK Modeling Analysis Discrete Receptors
2-9 M-136 Maximum General Grid Onsite/Offsite Receptors and Associated Grid Sectors
2- 10 M-225 Maximum General Grid Onsite/Offsite Receptors and Associated Grid Sectors
3- 1 Summary of Adams Ranch Receptor Concentrations in Comparison to NAAQS from M-136 and
M-225 Using Conservative and Corrected Emission Factors
3-2 Summary of ATK Ranch Receptor Concentrations in Comparison to NAAQS from M-136 and M-
225 Using Conservative and Corrected Emission Factors
3-3 Summary of Autoliv Receptor Concentrations in Comparison to NAAQS from M-136 and M-225
Using Conservative and Corrected Emission Factors
3-4 Summary of Bear River Bird Refuge Receptor Concentrations in Comparison to NAAQS from
M-136 and M-225 Using Conservative and Corrected Emission Factors
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MARCH 2012
TABLES (Continued)
NUMBER
3-5 Summary of Blue Creek Receptor Concentrations in Comparison to NAAQS from M-136 and
M-225 Using Conservative and Corrected Emission Factors
3-6 Summary of Boundary 1 Receptor Concentrations in Comparison to NAAQS from M-136 and
M-225 Using Conservative and Corrected Emission Factors
3-7 Summary of Boundary 2 Receptor Concentrations in Comparison to NAAQS from M-136 and
M-225 Using Conservative and Corrected Emission Factors
3-8 Summary of Boundary 3 Receptor Concentrations in Comparison to NAAQS from M-136 and
M-225 Using Conservative and Corrected Emission Factors
3-9 Summary of Boundary 4 Receptor Concentrations in Comparison to NAAQS from M-136 and
M-225 Using Conservative and Corrected Emission Factors
3-10 Summary of Christensen Ranch Receptor Concentrations in Comparison to NAAQS from M-136
and M-225 Using Conservative and Corrected Emission Factors
3-11 Summary of Holmgren Ranch Pond Receptor Concentrations in Comparison to NAAQS from
M-136 and M-225 Using Conservative and Corrected Emission Factors
3-12 Summary of Howell Dairy Receptor Concentrations in Comparison to NAAQS from M-136 and
M-225 Using Conservative and Corrected Emission Factors
3-13 Summary of North Plant Main Area Receptor Concentrations in Comparison to NAAQS from
M-136 and M-225 Using Conservative and Corrected Emission Factors
3-14 Summary of Penrose Receptor Concentrations in Comparison to NAAQS from M-136 and M-225
Using Conservative and Corrected Emission Factors
3-15 Summary of Salt Creek Waterfowl Management Receptor Concentrations in Comparison to
NAAQS from M-136 andM-225 Using Conservative and Corrected Emission Factors
3-16 Summary of South Plant Main Area Receptor Concentrations in Comparison to NAAQS from
M-136 and M-225 Using Conservative and Corrected Emission Factors
3-17 Summary of Thatcher Receptor Concentrations in Comparison to NAAQS from M-136 and M-225
Using Conservative and Corrected Emission Factors
3-18 Summary of Adams Ranch 1-Hour Gas Concentrations from Ml 36 and M225 in Comparison to
Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-19 Summary of ATK Ranch 1-Hour Gas Concentrations from Ml 36 and M225 in Comparison to
Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-20 Summary of Autoliv 1-Hour Gas Concentrations from M136 and M225 in Comparison to Utah
Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-21 Summary of Bear River Bird Refuge 1-Hour Gas Concentrations from M136 and M225 in
Comparison to Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-22 Summary of Blue Creek 1-Hour Gas Concentrations from M136 and M225 in Comparison to Utah
Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-23 Summary of Boundary 1 1-Hour Gas Concentrations from Ml36 and M225 in Comparison to
Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-24 Summary of Boundary 2 1-Hour Gas Concentrations from Ml36 and M225 in Comparison to
Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-25 Summary of Boundary 3 1-Hour Gas Concentrations from Ml36 and M225 in Comparison to
Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-26 Summary of Boundary 4 1-Hour Gas Concentrations from Ml36 and M225 in Comparison to
Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-27 Summary of Christian Ranch 1-Hour Gas Concentrations from M136 and M225 in Comparison to
Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-28 Summary of Howell Dairy 1-Hour Gas Concentrations from M136 and M225 in Comparison to
Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-29 Summary of Holmgren Ranch Pond 1-Hour Gas Concentrations from M136 and M225 in
Comparison to Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
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TABLES (Continued)
NUMBER
3-30 Summary of North Plant 1-Hour Gas Concentrations from Ml 36 and M225 in Comparison to Utah
Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-31 Summary of Penrosel-Hour Gas Concentrations from M136 and M225 in Comparison to Utah
Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-32 Summary of Salt Creek Waterfowl Mgmt 1-Hour Gas Concentrations from M136 and M225 in
Comparison to Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-33 Summary of South Plant 1-Hour Gas Concentrations from Ml 36 and M225 in Comparison to
Utah Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-34 Summary of Thatcher 1-Hour Gas Concentrations from Ml 36 and M225 in Comparison to Utah
Acute 1-Hour TSLs Using Conservative and Corrected Emission Factors
3-35 Summary of Adams Ranch 24-Hour Gas Concentrations fronn M136 and M225 in Comparison to
Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-36 Summary of AT Ranch 24-Hour Gas Concentrations from Ml 36 and M225 in Comparison to Utah
24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-37 Summary of Autoliv 24-Hour Gas Concentrations from Ml 36 and M225 in Comparison to Utah
24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-38 Summary of Bear River Bird Refuge 24-Hour Gas Concentrations from Ml36 and M225 in
Comparison to Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-39 Summary of Blue Creek 24-Hour Gas Concentrations from Ml 36 and M225 in Comparison to
Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-40 Summary of Boundary 1 24-Hour Gas Concentrations from Ml36 and M225 in Comparison to
Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-41 Summary of Boundary 2 24-Hour Gas Concentrations from Ml 36 and M225 in Comparison to
Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-42 Summary of Boundary 3 24-Hour Gas Concentrations from Ml 36 and M225 in Comparison to
Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-43 Summary of Boundary 4 24-Hour Gas Concentrations from Ml36 and M225 in Comparison to
Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-44 Summary of Christensen Ranch 24-Hour Gas Concentrations from Ml 36 and M225 in
Comparison to Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-45 Summary of Holmgren Ranch Pond 24-Hour Gas Concentrations from Ml 36 and M225 in
Comparison to Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-46 Summary of Howell Dairy 24-Hour Gas Concentrations from Ml36 and M225 in Comparison to
Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-47 Summary of North Plant 24-Hour Gas Concentrations from Ml36 and M225 in Comparison to
Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-48 Summary of Penrose 24-Hour Gas Concentrations from Ml 36 and M225 in Comparison to Utah
24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-49 Summary of Salt Creek Waterfowl Mgmt 24-Hour Gas Concentrations from Ml36 and M225 in
Comparison to Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-50 Summary of South Plant 24-Hour Gas Concentrations from Ml36 and M225 in Comparison to
Utah 24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-51 Summary of Thatcher 24-Hour Gas Concentrations from Ml 36 and M225 in Comparison to Utah
24-Hour Chronic TSLs Using Conservative and Corrected Emission Factors
3-52 Summary of Adams Ranch 24-Hour Particulate Concentrations from Ml 36 and M225 in'
Comparison to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-53 Summary of ATK Ranch 24-Hour Particulate Concentrations from M136 and M225 in Comparison
to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-54 Summary of Bear River Bird Refuge 24-Hour Particulate Concentrations from Ml36 and M225 in
Comparison to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
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MARCH 2012
TABLES (Continued)
NUMBER
3-55 Summary of Blue Creek 24-Hour Particulate Concentrations from Ml36 and M225 in Comparison
to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-56 Summary of Boundary 2 24-Hour Particulate Concentrations from Ml36 and M225 in Comparison
to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-57 Summary of Boundary 3 24-Hour Particulate Concentrations from Ml 36 and M225 in Comparison
to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-58 Summary of Boundary 4 24-Hour Particulate Concentrations from M136 and M225 in Comparison
to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-59 Summary of Christensen Ranch 24-Hour Particulate Concentrations from M136 and M225 in
Comparison to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-60 Summary of Holmgren Ranch Pond 24-Hour Particulate Concentrations from M136 and M225 in'
Comparison to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-61 Summary of Howell Dairy 24-Hour Particulate Concentrations from M136 and M225 in
Comparison to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-62 Summary of North Plant Main Area 24-Hour Particulate Concentrations from M136 and M225 in
Comparison to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-63 Summary of Penrose 24-Hour Particulate Concentrations from M136 and M225 in Comparison to
Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-64 Summary of Salt Creek Waterfowl Management 24-Hour Particulate Concentrations from Ml 36
and M225 in Comparison to Utah Chronic 24-Hour TSLs Using Conservative and Corrected
Emission Factors
3-65 Summary'of South Plant Main Area 24-Hour Particulate Concentrations from Ml36 and M225 in
Comparison to Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
3-66 Summary of Thatcher 24-Hour Particulate Concentrations from Ml 36 and M225 in Comparison to
Utah Chronic 24-Hour TSLs Using Conservative and Corrected Emission Factors
FIGURES
NUMBER
2-1 Site Location Map
2-2 M-135 Treatment Unit, 3 kilometer General Receptor Grid and Ghd Sectors, 100 Meter Increment
2-3 M-136 Treatment Unit, 3 km to 10 km General Receptor Grid and Grid Sectors, 500 Meter
Increment
2-4 M-225 Treatment Unit, 3 kilometer General Receptor Grid and Grid Sector, 100 Meter Increment
2-5 M-225 Treatment Unit, 3 km to 10 km General Receptor Grid and Grid Sectors, 500 Meter
Increment
2-6 Location of ATK Promontory M-136 and M-225 Treatment Units and Discrete Receptors
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1.0 INTRODUCTION
ATK Launch Systems (ATK) Inc., located 28 miles west of Brigham City, Utah currently operates open
buming (OB) and open detonation (OD) units for the treatment of hazardous waste propellants and
propellant contaminated materials. These treatment units are identified as M-136 and M-225 and are
subject to RCRA 40 CFR Subpart X permitting requirements for miscellaneous treatment units. These
units are currently operating as interim status facilities.
The Utah Department of Environmental Quality Division of Solid and Hazardous Waste (UDSHW) is
requiring ATK to conduct new air dispersion modeling, human health, and ecological risk assessments in
support of a new Subpart X permit application. In accordance with the Human Health Risk Assessment
Protocol (HHRAP) for Hazardous Waste Combustion Facilities (U.S. EPA, 2005) guidance, before the risk
assessments can be conducted, an air dispersion modeling analysis must be performed to evaluate the
air quality impact of the M-136 and M-225 treatment units. The results of the air dispersion modeling
analysis will be input into human health and ecological risk assessment models to determine the potential
risk and hazard from the OB/OD treatment units.
At the request of ATK, Tetra Tech, Inc. (Tetra Tech) conducted a preliminary full scale modeling analysis
(Tetra Tech, 2011b) and submitted it to UDSHW for review and comment in October 2011. This
preliminary modeling analysis has been conducted using a UDSHW approved air dispersion modeling
protocol (Tetra Tech, 2011a). Technical review of the modeling analysis was conducted by Tech Law
and comments were issued in January 2012. Based on Tech Law comments, it was necessary to revise
several sections of the original air dispersion modeling protocol relative to M-136 and M-225 proposed
treatment quantities and treatment schedule, emission factor tables, and modeling methodology to
address impacts to discrete receptors and the general receptor grid, which focused on worst case
meteorological events. The revised modeling protocol sections were issued as an addendum (Tetra
Tech, 2012) and a new modeling analysis was conducted using the new protocol procedures.
The revised preliminary modeling analysis is designed to support human health and ecological risk
assessments, and incorporates guidance provided in the Human Health Risk Assessment Protocol for
Hazardous Waste Combustion Facilities (U.S.EPA, 2005). Air dispersion modeling and risk assessment
for this type of facility typically starts with conservative (health protective) assumptions that are designed
to incorporate highly conservative, and often unrealistic modeling and exposure parameters. There are
many reasons for this, both historical and practical, and if the risks are acceptable additional refinements
may not be required. However, the risk assessment process is designed to be an iterative process, as
described in Chapter 1 of the HHRAP guidance (U.S. EPA, 2005), which notes that "you can view risk
assessments as an iterative process with a number of available options once risk estimates are
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produced". This iterative process, showing the various options, is graphically represented in Figure 1-1 of
the guidance. Further refinements to this process are often undertaken as a matter of course.
The 2005 HHRAP references Guidelines for Ensuring and Maximizing the Quality, Objectivity, Utility, and
Integrity, of Information Disseminated by the Environmental Protection Agency (U.S. EPA 2002) that
emphasizes that "risk assessments may be performed iteratively, with the first iteration employing
protective (conservative) assumptions to identify possible risks" The analysis does not terminate after the
first screening, and it is possible that "a more refined, data-intensive risk assessment" is necessary "if
potential risks are identified in a screening level assessment" (Page 1-11). It is, therefore, common for
additional information to be added to the initial risk assessment "e.g. site-specific information that's more
representative of the actual exposure settings" (Page 1-12). Furthermore, the iterative process "enables
you to determine if the risks identified in the earlier assessment accurately represent the situation at a
given combustion facility" (Page 1-12). Consequently, the initial air dispersion modeling analysis may not
be fully representative of the current conditions at ATK's OB/OD treatment areas.
This revised preliminary modeling report shows the results of a conservative type of modeling exercise
and is based on a number of protective conservative assumptions designed to overestimate the
environmental impact of the M-136 and M-225 treatment units, and each step compounds these
conservative assumptions into subsequent steps of the assessment process. The modeling process
incorporates conservative assumptions about the types of waste being processed; the energy released
during treatment and associated plume rise, modeling protocols, worst case meteorological conditions,
averaging period concentrations, and plume dispersion and deposition phenomena.
In reality, this approach may not actually reflect operating conditions or meteorological conditions at the
facility in the future and represents a worst-case analysis. It is ATK's intention to utilize the results in this
report to identify in discussions with UDSHW, the areas where conservative, health protective, but facility-
related realistic assumptions may be developed to refine the work presented in this dispersion modeling
report. The outcome will result in a more realistic evaluation of plume dispersion and risk assessment for
a facility that operates within acceptable regulatory limits.
ATK typically treats three different waste type packages; one hundred percent pure propellant; 85 percent
pure propellant with 15 percent waste materials, and 65 percent pure propellant with 35 percent waste
materials. Historically, most the material treated at ATK is either pure propellant or the 85%/15% waste
mixture. In this modeling analysis, it was conservatively assumed that the lower level of propellant
(65 percent) and higher waste levels (35 percent) were burned, which would overestimate the potential
impacts because these trash burns would have lower plume temperature and result in higher air
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MARCH 2012
dispersion factors, and this mixture would potentially contain more of the by-products than 100 percent
pure propellant.
Other areas of potential overestimation that might significantly affect the results in this modeling report
are background chemicals, and the method detection limits. For example, ATK's wastes are low in sulfur,
but the initiation system used during the burn testing in the ODOBi test chamber uses sulfur containing
materials that were not subtracted from the original test results. The test burn results showed sulfur
dioxide (SO2) that was too low to be reliably measured, but this report assumes; a) that sulfur is present
at reliably measurable levels; b) that it is due to the waste and not the burn initiator; and c) that if it was
not detected it was actually present at its method detection limit -
In addition, the modeling analysis has assumed that all discrete receptors and maximum impact onsite
and offsite receptors impacts come as a result of only worst case meteorological conditions, which may
not necessarily be the case during actual treatment events in the future. This assumption will most likely
result in an over prediction of the annual average impacts to all receptors. Screening methodology was
also utilized to extrapolated 1-hour worst case modeling results to longer averaging periods (3-hour,
8-hour, and 24-hours) for assessing compliance with National Ambient Air Quality Standards (NAAQS), to
Utah acute and chronic toxic screening levels, and OSHA 8-hour exposure criteria.
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MARCH 2012
2.0 AIR DISPERSION MODELING PROTOCOL
The modeling methodology used in this modeling analysis is based on information provided by ATK,
technical experts, discussions with comments received from UDSHW, new emissions test data, guidance
defined in the HHRAP (U.S.EPA, 2005), and technical review comments provided by Tech Law on the
initial preliminary model analysis (Tetra Tech, 2011). Tetra Tech conducted the initial preliminary
modeling analysis in 2011 (Tetra Tech, 2011b), using a UDSHW approved air dispersion modeling
protocol (Tetra Tech, 2011a). Technical review of the modeling analysis was conducted by Tech Law
and comments were issued in January 2012. Based on the review comments, it was necessary to revise
the original air dispersion modeling protocol relative to M-136 and M-225 proposed treatment quantities
and treatment schedule, emission factor tables, and modeling methodology to address impacts to
discrete receptors and the general receptor grid, and .utilized worst case meteorological events to
accommodate the proposed new treatment schedule.. The revised modeling protocol was issued as an
addendum (Tetra Tech, 2012) and all protocol revisions have been used in the analysis and are
incorporated in Section 2.0 ofthis report.
2.1 TERRAIN AND SITE DESCRIPTION
The ATK facility is located in the Blue Spring Valley, which is bounded on the east and west by Blue
Spring Hills, and the Engineer, and Promontory Mountain Ranges, respectively. Within the Blue Spring
Valley, the terrain is characterized by gentle topography that slopes down from the mountain crest at an
elevation of approximately 6,060 feet above mean sea level (AMSL) toward the center of the Blue Creek
Valley at an elevation of 4,250 feet AMSL. As a result, the surrounding environment extending out to
10 kilometers (km) from each treatment unit can be characterized as complex terrain.
For air modeling purposes, terrain is referred to as "complex" if the elevation of the surrounding land,
within the assessment area, is above the top of the emission release point Because ATK conducts OB
and OD treatment essentially at ground level in burn pans and uncovered pits, all receptors having an
elevation greater than the treatment unit base elevation are considered complex terrain receptors. All
receptors at or below the treatment unit base elevation are considered to be flat terrain receptors.
2.2 TREATMENT LOCATIONS
OB and OD treatment of reactive wastes is conducted at two treatment facilities. The main treatment
facility is M-136, which is located centrally to the two main manufacturing sites. A second OB treatment
facility is M-225, which is located in a remote development called Plant III. The M-225 unit is located
about 9 km southeast of the M-136 unit. The location of both treatment units are shown in Figure 2-1. A
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MARCH 2012
description of the treatment unit activities that are conducted at each unit are descnbed in Sections 2.2.1
and 2.2.2.
2.2.1 M-136 Treatment Unit Description
M-136 is the primary treatment unit for conducting open burning at ATK. The total annual quantity of
waste treated at the M-136 treatment unit is approximately 100 times the annual quantity treated at
M-225. The materials treated at M-136 include primary bulk waste propellant, 1.1 and 1.3, contaminated
waste, laboratory waste and obsolete rocket motors.
The M-136 treatment unit consists of 14 burn stations. OB is conducted at 14 burn stations in unlined or
lined (with clay soil) trays seven days a week (Monday through Sunday). OB of obsolete rocket motors is
conducted at Burn Station 14. OD of.waste materials is conducted at either Burn Station 13 or 14.
Detonation pits are prepared using augers, and then the reactive wastes are placed in the pit uncovered
and detonated.
A description of M-136 sources, treatment quantities, and treatment schedule assumed in this modeling
analysis are present in Table 2-1.
2.2.2 M-225 Treatment Unit Description
M-225 receives small amounts of the reactive waste materials from the Plant III propellant development
area. These reactive wastes are treated via open burning or open detonation. Reactive wastes are
treated in burn pans and include pure double base (1.1) propellants and composite propellants (1.3), as
well as, reactive contaminated trash materials such as cloth and paper wipes, metal containers, plastics,
and propellant ingredients.
The treatment activity at M-225 involves small quantities of waste material. Open detonation treatment of
1.1 pure propellants is conducted at one location within the M-225 fenced area. Detonation pits are
usually prepared using augers, and then the reactive wastes are placed in the pit uncovered and
detonated.
A description of M-225 sources and treatment quantities and treatment schedule assumed in this
modeling analysis are present in Table 2-2
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2.3 AIR QUALITY DISPERSION MODEL SELECTION
The HHRAP guidance recommends the use of the Industrial Source Complex Short Term 3 (ISCST3)
dispersion model (U.S.EPA, 1995a) for risk assessment evaluations. However, ISCST3 is designed for
sources associated with industrial facilities, rather than OB/OD treatment operations. In the case of
waste treatment activities at ATK, a special dispersion model is needed to simulate the quasi-continuous
and instantaneous plume release cloud rise, and dispersion of OB and OD sources. OB treatment is
typically considered as a quasi-continuous source, whereas OD is considered to be an instantaneous
source.
The United States Environmental Protection Agency (U.S: EPA) maintains a Support Center for
Regulatory Air Models called SCRAMS. The only SCRAM model that is specific to OB and OD treatment
operations is the Open Burn/Open Detonation Dispersion Model (OBODM) (Kramer, 1997). This model
has also been identified by UDSHW as the model of choice .for conducting the ATK air dispersion
modeling analysis in support of the human health and ecological risk assessments. OBODM is the
preferred model for OB/OD sources and the latest version of the model (1.3.24) was used in this analysis
to calculate the air quality impact of emissions from M-136 and M-225. However, OBODM is limited in the
number of receptors (100) it can address in a single model run, which necessitates numerous model runs
and significantly more post-processing time, particularly in the case of large receptor networks requiring
analysis with multiple years of meteorological data.
OBDOM is specifically designed to predict air quality impacts (particulate and gas concentrations and
particle deposition) from OB and OD treatment; however cannot predict particulate concentrations and
deposition in complex terrain. However, an alternate procedure has been develop to estimate particulate
concentrations and particle deposition and is discussed in Section 2.11. Because OBODM is specifically
designed for OB and OD treatment, it can accommodate source-specific input data regarding treatment
operations. This allows OBODM to provide greater detail regarding the spatial and temporal variation of
emissions and meteorological conditions, and enhances the model's ability to evaluate individual source
impacts. OBODM does not address particle bound modeling. As a result,'this modeling protocol
assumes that the calculated particulate concentrations are equal to particle-bound concentrations and
modeled particulate gravitational deposition is equal to particle-bound gravitational deposition.
2.3.1 Flat and Complex Terrain Modeling
Within a 10 kilometer radius of the ATK facility, the terrain is characterized by topography that slopes
down from peak mountain elevations of approximately 6,900 feet above mean sea level (amsl) to flat
terrain elevations of approximately 4,200 feet amsl. The M-136 and M-225 treatment units are located at
elevations of approximately 4,587 feet amsl and 4,597 feet amsl respectively.
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OBODM will be used to assess the impact from ATK treatment operation to receptor locations in both flat
and complex terrain. A receptor location is defined as a flat terrain receptor if the receptor elevation is
equal to or less than the source elevation. A receptor location is defined as complex if the receptor
elevation is greater than the source elevation. As a result the surrounding environment extending out to
10 kilometers from the ATK facility can be characterized by a combination of flat and complex terrain
relative to the elevation of the M-136 and M-225 treatment units.
OBODM has the capability to calculate downwind concentrations for both flat and complex terrain
receptors. However, in complex terrain mode, the model cannot be used when calculating concentration
with gravitational deposition occurring or gravitational deposition for particulates with appreciable settling
velocities. In this assessment, a particle size distribution has been assumed for the particulate and
deposition calculations. Further discussion of an alternate methodology for addressing particulate
impacts to complex terrain receptors is discussed in Section 2.11.
2.4 LAND USE ANALYSIS
Land use information is necessary for the selection of certain air dispersion modeling variables
(dispersion coefficients and surface roughness). The land use characteristics surrounding a source of air
emission can be determined from the United States Geological Survey (USGS) 7.5-minute topographic
maps, aerial photographs, or visual surveys of the area. The land use classification for the area
surrounding the M-136 and M-225 treatment units was determined from the Thatcher Mountain
7.5-minute (1:24,000 scale) quadrangle using the Auer method (Auer, 1978), as described in
Section 3.3.2.1 of the HHRAP guidance (U.S.EPA, 2005). Using this method, areas are defined as either
"rural" or "urban."
A radius of 3 km beyond each treatment unit source was given a general inspection to determine whether
the area within 3 km is rural or urban according to Auer's (Auer, 1978) definitions. This inspection
resulted in a rural classification for both treatment units. The 3 km radius area was broken down into
smaller areas (100 meters by 100 meters) for a more detailed inspection. Each small area was then
either classified as rural or urban.
The total count of rural areas was greater than 50 percent surrounding each treatment unit. As a result,
the land use classification is rural for both M-136 and M-225. The results of the land use analysis for both
treatment units is presented in Appendix A.
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MARCH 2012
2.5 SURFACE ROUGHNESS HEIGHT
The surface roughness height used in this modeling analysis is based on the methodology given in
Section 3.3.2.2 of the HHRAP guidance (U.S.EPA, 2005). The results of the land use classification
described in Section 2.4 and the five-years of meteorological data for the ATK M-245 on-site
meteorological monitoring station were used to calculate site-specific surface roughness heights for both
treatment units. Based on the HHRAP guidance methodology, all wind sectors were classified as desert
shrub land. In this case, the annual site-specific surface roughness height for both treatment units was
calculated to be approximately 0.26 meters.
2.6 OB/OD SOURCE SCENARIOS
In order to calculate the air quality impact of OB and OD treatment operations, OBODM requires specific
information regarding the characteristics of the treatment source. For example, OBODM requires input
data indicating the type and amount of material being treated, how it is being treated (OB or OD), the heat
content, burn rate of the material, the amount of matenal being treated, the source dimensions, and the
plume release height
The following OB/OD treatment source scenarios were evaluated in this air dispersion modeling analysis
for ATK treatment operations:
• OB treatment of pure propellant and energetic-contaminated materials at M-136 and M-225.
• OD treatment of energetic waste at M-136 and M-225.
The source scenarios assumed for M-136 and M-225 are discussed below.
M-136 Treatment Unit Source Scenario
The M-136 Unit is the primary treatment location and includes 14 burn stations. All treatment is
conducted in pans with the exception of Burn Station 14 obsolete rocket motor treatment, which consists
of a bermed area used for the OB of obsolete rocket motors and wastes that are treated in uncovered pits
by OD at Stations 13 or 14. Detonation pits are usually prepared using augers, and then the reactive
wastes are placed in the pit uncovered and detonated. Although the OBODM model has the capability to
model multiple source scenarios and. individual locations in the same model run, computer resources
(both computational and memory/output file size) preclude modeling all individual M-136 treatment
stations. As a result, certain M-136 treatment stations were consolidated into a single source, where
deemed applicable, and as recommended in modeling guidance, in order to accommodate computer
resources.
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MARCH 2012
U.S. EPA modeling guidance (U.S.EPA, 2000) allows the merging of multiple emission points that are
located within close proximity to one another and if the emission points have similar release parameters.
In the case of M-136, the 14 burn stations were consolidated into three separate sources with discrete
coordinates due to the separation distance between the burn station areas. For example, in the case of
M-136 Burn Stations 1-12, all stations are located in one general treatment area that measures
approximately 160 x 220 meters.
The approximate separation distance from the Burn Station 1-12 area to Burn Station 13 is approximately
200 - 250 meters. The estimated separation distance from Burn Station 13 to Burn Station 14 is about
500 meters. As a result, these two treatment Ideations (Station 13 and 14) were treated as two separate
OB sources due to their respective treatment areas and separation distances. OD was assumed to take
place at Station 13. The UTM coordinates selected for each of these treatment sources represent the
center of the respective treatment operational areas.
The four M-136 source areas used in this modeling analysis include the following Burn Stations:
Source 1 - representing Burn Stations 1-12 (OB of 1.1, 1.3, and contaminated trash)
Source 2 - representing Burn Station 13 (OB of 1.1, 1.3, and contaminated trash)
Source 3 - representing Burn Station 14 (OB of 1.1, 1.3, and contaminated trash)
Source 4 - representing Burn Station 13 (OD of waste energetics)
Source 5 - representing Burn Station 14 treatment of large rocket motors < 26,000 pounds
The modeling analysis assumed that M-136 treatment will be conducted in accordance with the treatment
schedule shown in Table 2-1. Each source was modeled at a unit emission rate.
M-225 Treatment Unit Source Scenario
The M-225 Unit is a small area consisting of five burn stations (using lined burn pans) and one detonation
pit Detonation pits are usually prepared augers, and then the reactive wastes are placed in the pit
uncovered and detonated.
The M-225 treatment unit was evaluated as two treatment sources in the modeling analysis:
• Source 1 - representing OB in pans (1.1, 1.3, and contaminated trash)
• Source 2 - representing OD in pit (1.1 and 1.3 propellants)
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This modeling analysis assumed that treatment will be conducted in accordance with the treatment
schedule shown in Table 2-2 between 0600 to 1800. Each source was modeled at a unit emission rate.
Due to the relative small size of the M-225 treatment area, M-225 Source 1 and Source 2 were assigned
the same location coordinate.
2.7 M-136 TREATMENT QUANTITY SCENARIOS
Table 2-1 presents a listing of the M-136 modeled sources, associated burn stations, waste categories,
modeled per event treatment quantity, treatment schedule, total annual treatment quantities and
applicable emission factors for each source. The M-136 applicable emission factors are discussed in
Section 2.9.1 and are presented in Tables 2-5 and 2-6. Although M-136 treats a variety of wastes (1.1,
1.3, etc.) as described in the modeling protocol (Tetra Tech, 2011), ATK has agreed to use the
1.3 ODOBi emission factors for all M-136 modeled sources.
2.8 M-225 TREATMENT QUANTITY SCENARIOS
Table 2-2 presents a listing of the M-225 modeled sources, associated burn stations, waste categories,
modeled per event treatment quantity, treatment schedule, total annual treatment quantities and
applicable emission factors for each source. The M-225 applicable emission factors are discussed in
Section 2.9.1 and are presented in Tables 2-5 and 2-6. Although M-225 treats a variety of wastes (1.1,
1.3, etc.), ATK has agreed to use the 1.3 ODOBi emission factors for all M-225 modeled sources.
2.9 SOURCE PARAMETERS
The selection of M-136 and M-225 source parameters used in OBODM is based on information provided
by ATK, and guidance associated with HHRAP. A summary of the source parameters for the M-136 and
M-225 treatment units are shown in Tables 2-3 and 2-4, respectively.
All OB and OD sources were assumed to treat the same class of materials (1.3) as tested in the Open
Detonation Open Burning Improved (ODOBi) test chamber from June 7 to 15, 2006 (URS, 2009). The
results of the ODOBi testing produced a list of emission factors that were used in this analysis to compute
air concentrations and deposition rates. Further information regarding the testing program and the
emission factors used in this analysis is discussed in Section 2.9.1. The class of material simulated in the
model was assumed to have a heat content value of 1,471 calories/gram (cal/gm).
2.9.1 ODOBi Emissions Testing and Emission Factors
Representative characterization of treatment emissions is a necessary component for predicting impacts
to the environment and supporting the risk assessment process. The UDSHW has required ATK to
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MARCH 2012
conduct emissions testing of Class 1.3 materials in order to establish emission factors for the major class
of propellants (Class 1.3) treated at the ATK facilities. The goal of the emission testing program was to
identify and quantify emissions from OB of these Class 1.3 propellant waste (PW) materials.
The ODOBi test chamber was used to determine emission factors for airborne compounds from three
different compositions of ATK Class 1.3 process waste (PW) materials.. Three test items were studied.
The first material was 100% Class 1.3 propellant The other two test materials consisted of a mixture of
Class 1.3 propellant blended with different percentages of materials such as cloth, paper, paper wipes,
plastics, and cleaning items. The tests were conducted from June 7 to 15, 2006 (URS, 2009).
Emissions were measured from simulated OB events containing the following propellant wastes mixtures:
• Test Material 1 - PW100: 100% ammonium perchlorate (AP) propellant
• Test Material 2 - PW85-15: 85% AP + 15% trash
• Test Material 3 - PW65-35: 65% AP + 35% trash
The airborne target analytes measured included:
Carbon dioxide (CO2);
Carbon monoxide (CO);
Carbonyls;
Dioxins/Furans;
Hydrogen chloride (HCI), chlorine (CI2), and ammonia (NH3);
Hydrogen cyanide (HCN);
Metals
Nitrogen oxides (NOx)
Particulate matter smaller than 2.5 microns (PM2.5);
Particulate matter smaller than 10 microns (PMIO);
Perchlorates;
Semivolatile organic compounds (SVOCs);
Sulfur dioxide (SO2)
Total suspended solids (TSP);
Tracer compound sulfur hexafluoride (SF6); and
Volatile organic compounds (VOCs).
Average and maximum emission factors were developed from the test results for each detected
compound after applying the "non-detect rules." Each emission factor represents the pounds of
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MARCH 2012
compound emitted per pound of waste material treated. Since many of the compounds measured may
be already present in ambient air, "corrected" emission factors were determined by subtracting the
background concentrations. In addition, a more conservative set of emission factors were also developed
based on replacing all nondetect results with the minimum detection limit (MDL) and background/blank
correction was not performed. The emission factors were also adjusted to compensate for dilution that
occurred during sampling. The ODOBi testing did not determine the size distribution of particulate
emissions. A condense summary of the test results are presented below:
Particulate Material - Particulate material and inorganic gases were the primary emissions from all
items. The PW85-15 trash sample produced the highest particulate emissions. PM2.5 constituted
30-40% ofthe total particulate emissions from all test items.
Metals and Perchlorates - Aluminum was the predominant metal product in the air samples from each
test. Aluminum was a constituent of each test item. Other metals were found at lower levels. The
highest emissions were produced by the PW85-15 sample. Perchlorate was not detected in any of the
test samples.
VOCs and SVOCs - SVOCs were emitted at lower levels. VOCs were generally measured at higher
levels than SVOCs. The PW65-35 sample produced the highest concentration of VOCs. Non-methane
organic compounds constituted the majority of the VOC emissions.
Dioxins and Furans - Most dioxin/furan isomers were reported at picogram levels. Some isomers in the
PW85-15 and PW65-35 samples were reported at nanogram levels. The highest emissions were
measured from the PW85-15 sample.
Carbonyls - Carbonyls were generally measured at very low levels in most samples.
HCI, CI2, NH3, and HCN - HCI concentrations were highest in the pure propellant sample. Chlorine
levels were not high enough to be distinguished from the backgrounds and blanks. Ammonia and
cyanide were found at low levels in some samples. 1
Continuous Emissions Monitoring - The primary gas-phase compound from all test items was CO2.
Very little CO was produced in each test, indicating good combustion of the trash samples. NOx was
measured at lower levels in all tests. SO2 was too low to be reliably measured.
Including the ODOBi testing results, there were other proposed emission factor databases for the
treatment of 1.3, 1.1 and category E wastes at M-136 and M-225. Although the emission factors for 1.3
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MARCH 2012
and 1.1 materials are based on actual ATK matenals emissions testing, the emission factors for
addressing impacts from the treatment of category E wastes while not actual ATK wastes, they are
similar and represent the best available at this time.
Discussions were conducted between ATK and UDSHW regarding the best approach to represent the
maximum impact from all ATK operations and comply with UDSHW's desire to establish a lower and
upper bound for ATK emissions. It was determined that the ODOBi 1.3 reactive propellant "conservative"
and "corrected" emission factors presented in Tables 2-5 and 2-6, respectively, represent a conservative
estimate of ATK emissions. As a result, it was agreed that ATK agreed to utilize the 1.3 ODOBi
propellant emission factors given in Tables 2-5 and 2-6 for all emissions sources at M-136 and M-225,
regardless of waste category, in order to establish conservative lower and upper bounds for risk
assessment Tables 2-5 and 2-6 also highlight the target analytes that were not detected during the
OBODi testing.
2.10 MODELING ASSUMPTIONS FOR M-136 AND M-225
The following assumptions were used in the modeling analysis for the M-136 and M-225 treatment units:
M-136 Treatment Unit
• OB source release is quasi-continuous (volume source).
• OD source release is instantaneous (volume source).
• Assume the 5 source areas are at the same elevation as Burn Stations 1-12; Elevation = 4,587 feet
amsl. The net elevation difference between the 3 source locations is only 36 feet (11 meters).
• Run OBODM for each model type (gas, particulate, and deposition) to give the contribution from each
M-136 source identified in Table 2-1.
• Source dimensions for OB at M-136 are based on average pan size for that treatment area:
- Average dimension of pans in Burn Stations 1-12 = 8' x 13'
- Average dimension of pans in Burn Stations 13 = 6'X 9'
- Dimension of Burn Station 14 rocket motor assumed to be 5' x 50'
• The release height for OB at Sources 1, 2, 3, and 5 = 1.0 meter..
• The release height for OD at Source 4 is ground level..
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MARCH 2012
• OD pit diameter is 1.5 meters.
• Gas, particulate, and deposition phase OBODM modeling was conducted using a unit emission rate.
• Default OBODM particulate and mass distributions were assumed for particulate and deposition
. modeling.
• OBODM 1-hour air concentrations were used to calculate air concentrations for longer averaging
periods using the assumption that only one treatment event occurs per hour. One-hour
concentrations were converted to other short term averaging periods using USEPA screening factors
(USEPA, 1992).
• The OBODM model does not calculate particle bounding concentration. As a result, ATK has
assumed that OBODM calculated particulate concentrations are equal to particle-bound
concentrations and modeled particulate gravitational deposition is equal to particle-bound
gravitational deposition. The values of Fv, fraction of COPC concentration in the vapor phase, found
in the HHRAP Companion Data Base will be used in the human health risk assessment to determine
the amount of particle-bound constituent that behaves as a gas and (1-Fv) will be used to determine
the amount that behaves as particulate.
Annual and 1-hour gas, particulate, and deposition ADFs calculated for each M-136 sburce are presented
in Appendices G, H, and I, respectively.
M-225 Treatment Unit
• OB source release is quasi-continuous (volume source).
• OD source release is instantaneous (volume source).
• Both M-225 sources have the same coordinate and elevation; elevation = 4,597 feet AMSL to
consolidate model runs.
• Run OBODM for each model type (gas, particulate, and deposition) to give the contribution from each
M-225 source identified in Table 2-2. All OBODM input and output files for gas, particulate, and
deposition modeling are provided in Appendices D, E, and F, respectively
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MARCH 2012
• Each source configuration based on average pan size
- Average dimension of pans = 6' x 17' .
.- OD pit diameter is 1.5 meter diameter.
• Release height for OB = 1.0 meter.
• Release height for OD is ground level.
• Default OBODM particulate and mass distnbutions were assumed for particulate and deposition
modeling.
• OBODM 1-hour air concentrations were used to calculate air concentrations for longer averaging
periods using the assumption that only one treatment event occurs per hour One-hour
concentrations were converted to other short term averaging periods using USEPA screening factors
(USEPA, 1992).
• The OBODM model does not calculate particle bounding concentration. As a result, ATK has
assumed that OBODM calculated particulate concentrations are equal to particle-bound
concentrations and modeled particulate gravitational deposition is equal to particle-bound
gravitational deposition. The values of Fv, fraction of COPC concentration in the vapor phase, found
in the HHRAP Companion Data Base will be used in the human health risk assessment to determine
the amount of particle-bound constituent that behaves as a gas and (1-Fv) will be used to determine
the amount that behaves as particulate.
Annual and 1-hour gas, particulate, and deposition ADFs calculated for each M-225 source are presented
in Appendices G, H, and I, respectively.
2.11 DEPOSITION MODELING
In addition to calculating 1-hour and annual average ADFs for gases and particulates, OBODM also
calculated 1-hour and annual deposition ADFs. Due to the limitations of OBODM, separate model runs
were required for the deposition phase. The deposition mechanisms applicable to the M-136 and M-225
treatment units included gravitational settling of particulates.
It is important to note that wet deposition is not calculated by OBODM. However, this deposition
mechanism is not applicable in the case of ATK because treatment operations are not conducted during
precipitation events. Also, OBODM does not calculate deposition of particulates for complex terrain
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MARCH 2012
receptors. However, ATK will use OBODM model 1-hour and annual air concentration (pg/m^) results for
the "gas" phase at complex terrain receptors to determine complex terrain deposition rates. This
approach is consistent with OBODM guidance and HHRAP (USEPA, September, 2005) and is
considered to represent a conservative bias because the gas air concentrations calculated are
nondepleted (e.g., removal of mass from the cloud as a function of downwind distance is not accounted
for).
A conservative deposition velocity of 0.03 meters/seconds (m/s) was used for this assessment, which is
the default value specified in the HHRAP (U.S.EPA, September, 2005) guidance. As a comparison, the
gravitational settling velocity for particles of 2 g/cm^ and 10 pm diameters is reported as approximately
0.01 m/s (DOE 1984, page 755). Deposition in complex terrain will be calculated as follows:
Complex terrain 1-hour/annual gravitational dry deposition (pg/m^) = 1-hour or annual gas concentration
(pg/m^) x deposition velocity (m/s)
The input requirements for OBODM deposition modeling included particle size and mass distribution,
median particle size, and specific gravity for calculating the gravitational settling velocity of a particle.
This type of information is not available for the sources at M-136 and M-225. In the absence of available
particle size information, alternate sources [(NASA, 1973) and (DOE, 1984)] of particle size information
were used to establish input parameters for OBODM particulate and deposition modeling.
Based on available information, a simple, but conservative approach for conducting the deposition
modeling was developed based on the following assumptions:
• Assumed density of 2.7 g/cm^ for particulates, which is the density of aluminum. Results from the
ODOBi testing indicate aluminum to be the most abundant metal in the OB and OD emissions.
• Assumed mass median particle diameter of 30.0 pm.
• Assumed particle size standard deviation of 2.0 pm in order to account for a reasonable measure of
size distribution variability.
• Used OBODM default logarithmic particle size and mass distribution on 10 particle size categories for
particulate modeling.
• A separate particle bound mass distribution was created using guidance found in Section 3.2.3 of the
HHRAP (U.S. EPA, 2005) in support of the human health risk assessment
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MARCH 2012
Table 2-7 provides a summary of the gravitational settling parameters that were used for particulate
deposition from the M-136 and M-225 treatment unit emissions in OBODM.
2.12 RECEPTOR NETWORKS
All receptors used in this modeling analysis are based on a Cartesian grid system (x,y). Two types of
receptor networks were used in the anal/sis: general and discrete. A general receptor network is
designed to determine the location of the maximum on-site and off-site short term and long term ground
level concentrations. The discrete receptor network consists of special human or ecological receptors
that are of concern to UDSHW and wilt be evaluated in the human health and ecological risk
assessments.
Due to the large number of general grid receptors and the OBOD limit of 100 receptors per model run,
separate general grid sectors were developed for each ATK treatment unit due to their separation
distance (approximately 9 km) and are illustrated in Figures 2-2 through 2-5. Each receptor is assigned a
Universal Transverse Mercator (UTM) northing and easting coordinate and terrain elevation. This data
was obtained from USGS Digital Elevation Maps (DEM) grids of 1:24,000 at a resolution of 1 meter.
2.12.1 General Receptor Networks
The general receptor network for each treatment unit extended out to 10 km and is made up of two
separate sub-networks that have different receptor spacing increments. For example, the receptor grid
spacing^from the source out to a distance of 3 km is 100 meters. The receptor spacing from 3 km out to
10 km is 500 meters.
There are no general grid receptors located beyond 10 km because modeling experience with OB/OD
sources has shown that the maximum short term and long term impacts occur well within 10 km (usually
within 3 km) of the source. In fact, the initial preliminary air dispersion modeling analysis conducted in
October 2011 indicated that maximum offsite impacts from M-136 and M-225 sources occur near or within
5 kilometers for both treatment units. Due to the large separation distance between the M-136 and M-225
treatment units, separate general grid systems were established for M-136 and M-225 treatment units
and included both flat terrain and complex terrain receptors. The proposed 0-3 and 3-10 km general grid
networks for the M-136 and M-225 treatment units are shown in Figures 2-2 through 2-5. The general
grid extending from the M-136 and M-225 treatment areas out to 3 km also includes on-site receptors. At
the request of UDSHW, these receptors were used to evaluate on-site worker exposure for non-OB/OD
workers located outside of the quantity-distance (Q-D) areas imposed by ATK.
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MARCH 2012
As stated previously the OBODM model has a limit of only 100 receptors per model run, which
necessitates a very large number of model runs for large receptor grids. Based on the general receptor
grids shown in Table 2-2 through 2-5, there are a total of more than 10,000 receptor points. In order to
address all of these receptors, it was necessary to break up the 0-3 km and 3-10 km receptor grids for
each treatment unit into subsector of 50 receptors or less. The assigned general grid receptor sectors for
M-136 and M-225 are shown in Figures 2-2 through 2-5.
2.12.2 Discrete Receptor Network
Discrete receptors are defined as special receptors that exist within and beyond the ATK boundary.
These locations include the facility boundary, nearby residential dwellings, a local, dairy farm, the closest
population centers, and worker exposure at commercial businesses (Autoliv). All discrete receptors, with
the exception of Boundary 1 and Autoliv, are located in flat terrain. The' Boundary 1 and Autoliv receptors
have elevations that are above the release elevations at M-136 and M-225.
The following is a list of discrete receptors that were evaluated in this modeling analysis:
• The Adam's Ranch, which is the closest domestic dwelling to M-136 and is located approximately
3 km south-southwest of M-136.
• The Holmgren Ranch Pond, which is the closest domestic dwelling to M-225 and is located
approximately 2 km east-southeast of M-225.
• . The South Plant Administration Building and Main Manufacturing Area is an occupational receptor
located approximately 2.5 km south of M-136.
• The North Plant Administration Building and Main Manufacturing Area is an occupational receptor
located approximately 6.5 km north of M-136.
• Four facility boundary receptors that were selected based on the annual prevailing wind directions
that were measured over a five-year period (1997 through 2001) at the M-245 meteorological
monitoring station. Boundary 1 is a complex terrain receptor. _AII other boundary receptors are
located in flat terrain.
• Autoliv Facility. This is the commercial business that is located between the M-136 and M-225
treatment units. This receptor is located in complex terrain.
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• Christensen Ranch. This residential dwelling is located due north of ATK.
• Blue Creek perennial stream, which runs along the western boundary of ATK.
• Salt Creek Waterfowl Management area located approximately 10 km due east of M-225.
• The ATK Ranch Pond, which is located approximately 14 km southwest of M-225.
• Howell Dairy Farm located approximately 8 km due north ofthe ATK property boundary.
• The town of Thatcher, which is located approximately 12 km east of M-136 and approximately 9 km
northeast of M-225.
• The town of Penrose, which is located approximately 12 km southeast of M-136 and 6 km east-
northeast of M-225.
All.discrete receptors, including UTM coordinates, are shown in Figure 2-6 and listed in Table 2-8.
2.13 METEOROLOGICAL DATA
The meteorological data requirements for OBODM are historical hourly averages of wind speed and wind
direction, atmospheric stability class, air temperature, and urban or rural mixing height These
meteorological parameters represent a combination of surface and upper air data and are available from
several different sources including the National Weather Service (NWS), military installations or as part of
an on-site measurement program.
The meteorological data used in an air dispersion modeling analysis should be selected based on spatial
and climatological representativeness, as well as, the ability of the data to characterize the transport and
dispersion in the area of concern. Spatial and geographical representativeness is best achieved by using
validated on-site meteorological data. As a result, "site-specific" measured data is therefore preferred as
modeling input (U.S. EPA, 2000), provided appropriate instrumentation and quality assurance procedures
are followed and the data is compatible with the requirements of'the dispersion model.
2.13.1 Surface Data
This the dispersion modeling analysis utilize five years (1997 through 2001) of on-site meteorological data
collected at the ATK M-245 meteorological monitoring station. ATK operates the on-site monitoring
station approximately 1.5 km southwest of the M-225 treatment unit at an elevation of about 5,000 feet
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amsl (see Figure 2-1).. The monitoring station is operated in accordance with the U.S. EPA monitoring
guidance for the collection of on-site meteorological data (U.S.EPA,. 2000).
The monitoring station consists of a 10-meter tower that collects the following data at the 10-meter level;
Wind speed
Wind direction
The standard deviation of the horizontal wind (sigma theta)
Temperature
Relative humidity
Barometric pressure; and
Solar radiation
The meteorological parameters used by OBODM are wind speed, wind direction, and air temperature,
The data recovery statistics for these parameters in 1997 through 2001, after validation, exceeded the
U.S. EPA recommended minimum criteria for an annual meteorological database. Data recovery
statistics are presented in Appendix B.
Wind roses showing the frequency distribution of wind direction for each year from 1997 through 2001 at
the M-245 meteorological monitoring station are presented in Appendix C.
2.13.2 Upper Air Observations (Mixing Height Data)
Upper air data, also known as mixing height data, is required to run OBODM. Twice daily mixing heights
available from upper air sounding stations are used by the meteorological preprocessor program
PCRAMMET (U.S.EPA, 1995b) to calculate hourly rural or urban mixing height for input into OBODM.
Upper air sounding data is typically obtained from NWS upper air reporting stations. The number of
upper air reporting stations in the United States is limited due to operational requirements and budgetary
constraints. As a result, this condition can severely limit the availability of upper air reporting stations
near a source.
. The closest NWS upper air reporting station to ATK is located in Salt Lake City, which is about 60 miles
south of ATK. The next closest NWS upper air reporting station is located in Lander, Wyoming, which is
about 190 miles northeast of ATK. Although considerable site-to-site variability is possible for
measurements taken close to the surface as compared to upper air measurements, the upper air
sounding measurements from Salt Lake City are considered generally representative of a much larger
spatial domain, which includes the northern Utah valley.
031209/P 2-17
MARCH 2012
2.13.3 Meteorological Preprocessor
The surface observation and mixing height data files for each annual period were preprocessed for input
into OBODM using the PCRAMMET meteorological program (U.S.EPA, 1995b), as recommended in the
HHRAP guidance (U.S.EPA, 2005). PCRAMMET requires data for all input variables and will not run if
data is missing within an hourly record. As a result substitution data must be used to fill data gaps. In
the case of the M-245 monitoring station, opaque cloud cover and ceiling height are not measured. As a
result additional meteorological data had to be acquired from a representative, local source.
The first class reporting station located at Ogden Air Force Base in Ogden, Utah was selected as the
local source of missing data. This reporting station is considered to be the closest, most representative
and readily available site for providing substitute data based on its location relative to ATK, climatology,
valley location relative to surrounding terrain, and similar land use. The Ogden reporting station is
located approximately 25 miles south of ATK within the northern Utah valley. Observations missing in
1997 from the M-245 monitoring station were substituted in accordance with U.S. EPA data substitution
guidance (U.S. EPA, 2000). Based on the land use analysis discussed in Section 2.4, rural mixing
heights were used in this modeling analysis.
2.14 OBODM MODELING METHODOLOGY
ATK completed a preliminary modeling assessment for M-136 and M-225 in October 2011 (Tetra Tech,
2011b). In this assessment, the modeling focused on determining the worst case short term and long
term impact based on treatment operating hours between 1000 and 1800 hours. Restricting treatment
operations can be problematic for ATK due to local climatological conditions which are not always
conducive to good dispersion. The revised modeling methodology presented in this protocol is intended
to give ATK the flexibility they need to conduct treatment at variable times due to the restrictive
climatological conditions and also calculate the worst case impacts associated with the treatment
schedules given in Tables 2-1 and 2-2. Rather than designating specific treatment hours in the OBODM
model, the revised protocol evaluated the impact of M-136 and M-225 treatment units on the basis of
strictly "worst case" meteorological events.
The revised modeling protocol utilizes individual worst case meteorological events associated with each
treatment source, and discrete and general grid maximum onsite and offsite receptors. The database of
worst case events for this modeling analysis were selected from five years of onsite meteorological data'
(Appendix B) for a new daily treatment time period (0600 to 1800). Applying this type of methodology is
typically referred to as a "screening" assessment and is designed to determine the worst case impact at
all receptors of interest regardless of the time of day. The screening procedure is a highly conservative
031209/P 2-18
MARCH 2012
technique that is designed to calculate the maximum, worst case air concentrations at a receptor location.
Using this technique overestimates the environmental impact because it assumes that worst case
conditions will prevail each time ATK conducts treatment during the year, when in reality it is very unlikely
that this will occur.
Sections 2.14.1 and 2.14.2 below describe the procedure used to evaluate the worst case impact
associated with individual sources at M-136 and M-225 for discrete and general grid receptors,
respectively.
2.14.1 Discrete Receptors
in the case of discrete receptors, OBODM calculated the individual impact from each treatment source to
each discrete receptor using the revised treatment quantities shown in Tables 2-1 and 2-2 using worst
case meteorological events.
OBODM produced a table of the 50 highest 1-hour ADFs and events for each source at a specific
receptor for each year of onsite meteorological data. The 50 highest ADFs for each year of
meteorological data were used to compile a master list of 250 worst case 1-hour events for each discrete
receptor and source. A database of the 250 worst case 1-hour events for each discrete receptor and
source is provided in Appendix B. The master list was then used to compile the required number of worst
case annual treatment events for each source based on the annual treatment schedules shown in Tables
2-1 and 2-2 in order to calculate annual average ADFs. Meteorological data files were created for each
discrete receptor based on the 250 worst case scenarios possible for five years of onsite meteorological
data and used in conjunction with "hourly source strength" files to limit source treatment to the number of
events for each source given in Tables 2-1 and 2-2.
The maximum model type (gas, particulate, and deposition) ADF for each source and discrete receptor
(see Appendices G, H, and I) were used in conjunction with individual source conservative and corrected,
hourly and annual emission rates (see Appendix L) to calculate averaging period concentrations and
determine compliance with short term and long term National Ambient Air Quality Standards (NAAQS).
For example, M-136 Source 1 will conduct treatment twice daily, three times a week for 52 weeks, which
is equivalent to 156 annual treatment events. The first treatment event conducted each day of the week
will result in 156 annual treatment events as will the second daily treatment event for a total of 312
treatment events at Source 1. The master list of worst case meteorological events was used to compile a
total of 156 individual worst case meteorological events to simulate the total number of annual treatment
events at Source 1. Likewise, 52 individual worst case meteorological events were identified for M-136
Sources 2 and 3. Source 3 was also evaluated for the treatment of large rocket motors that will be
031209/P 2-19
MARCH 2012
conducted only 3 times per year and therefore, only requires 3 worst case meteorological events, which
will be chosen from the list of 52 events for standard OB treatment at Source 3. Source 4 will conduct OD
6 times a year and will require 6 worst case meteorological events. The same procedure will be used for
M-225 source impacts to discrete receptors.
An example set of data files illustrating the procedure used to calculate short term and long term air
concentrations for discrete receptors is presented in Appendix J.
2.14.2 General Grid Receptors
The 2011 preliminary model assessment utilized a general receptor grid extending out to 10 km to
determine the maximum onsite and offsite impact from each source at M-136 and M-225. Due to the
OBODM limit of 100.receptors per model run, 350 individual receptor grid sectors were required to cover
the entire 10 km general grid area. Individual general grid receptor maps showing the grid sectors are
presented in Appendix K. The results of the preliminary assessment for M-136 and M,-225 indicated that
the maximum short term impact from all four M-136 sources, for each model type (gas, particulate, and
deposition) occurred within the 3 km grid network (see Figures 3-1, 3-2, 3-3, 3-4, 3-6 and 3-7). The offsite
maximum impact locations were primahly located near or along the boundary of ATK property. Using the
new lower treatment quantities shown in Table 2-1 and 2-2 is expected to result in lower final plume
heights and maximum impacts closer to the ATK boundary and are not expected to extend out beyond
3 km. .
In this modeling analysis, ATK utilized the general grid maximum onsite and offsite receptor locations
identified in the 2011 preliminary modeling assessment (Tetra Tech) as the focus of the general grid
modeling. The general grid maximum impact onsite and offsite locations identified in the 2011 preliminary
modeling assessment (UTM coordinates and Grid Sector) for M-136 and M-225 sources and each model
type are summarized in Tables 2-9 and 2-10, respectively.
In the case of the maximum onsite and offsite general grid receptors identified in Tables 2-9 and 2-10
from the preliminary model analysis in October 2011 (Tetra Tech, 2011), OBODM was used to model the
individual impact from each treatment source to each general grid maximum receptor sector using the
revised treatment quantities shown in Tables 2-1 and 2-2 for each year of meteorological data. In doing
so, OBODM produced a table of the 50 highest 1-hour ADFs and events for each source at each general
grid maximum receptor. The 50 highest ADFs for each year of meteorological data were used to compile
a master list of 250 worst case events for each sector and source.
The master list was then used to compile the required number of worst case annual treatment events for
each source based on the annual treatment schedules shown in Tables 2-1 and 2-2, in order to calculate
031209/P 2-20
MARCH 2012
annual average ADFs. The OBODM annual average modeling for each treatment source included the
maximum impact sector plus all adjacent sectors out to a distance of 1 km from the maximum impact
receptor sector. This methodology was used to facilitate the preparation of ADF iso-contours for these
general grid maximum impact areas. The proposed adjacent grid sectors for each treatment source and
model type are presented in Tables 2-9 and 2-10.
The model type (gas, particulate, and deposition) ADFs for each source and general grid receptor are
presented in Appendices G, H, and I. The 1-hour and annual average ADF for each source and general
grid receptor was used in conjunction with individual source conservative and corrected, hourly and
annual emission rates (see Appendix L) to calculate averaging period concentrations and determine
compliance with short term and long term National Ambient Air Quality Standards (NAAQS) and onsite
OSHA 8-hour exposure concentration criteria to evaluate on-site worker exposure at the predicted
maximum on-site receptor for each treatment unit The 1-hour air concentrations were used to estimate
air concentrations for longer averaging periods using USEPA established persistent factors to convert
1-hour averages to other averaging periods.
For example, the 2011 preliminary gas modeling assessment (Tetra Tech) determined the general grid
maximum impact sector for M-136 Source 1 to occur within the 3 km sector 36C3A (see Table 5-8). This
sector was used to model the individual impact from each treatment source to compile a list of 50 worst
case events for each year of meteorological data. The worst case events were based on the operating
hours 0600 to 1800 for each year of meteorological data. The 50 highest 1-hour ADFs for each year of
meteorological data within sector 36C3A were then compiled into a master list of 250 worst case events
forthe purpose of calculating annual average impacts.
In the case of maximum impact receptor 36C3A, the annual average modeling will include sector 36C3A,
plus the sectors 36C3B, 36F3D, 36F3A, 36F30, 36F10B, and 36F10H (see Table 5-8). It is important to
note the selection of adjacent sectors included the selection of adjacent 10 km sectors when the
maximum 3 km sector occurred on the outer boundary of the 3 km general grid. This situation occurred
for the general grid maximum offsite gas model impacts associated with M-136 sources 1, 2, and 3 (see
Table 2-8) and M-225 Sources 1 and 2 (see Table 2-9). The OBODM "houriy source file" option was
used to calculate annual average ADFs on the basis of worst case meteorological conditions for each
source and model type. The same procedure will be used for M-225 source impacts to general grid
receptors.
An example set of data files illustrating the procedure used to calculate short term and long term air
concentrations for discrete receptors is presented in Appendix J.
031209/P 2-21
TABLE 2-1
M-136 TREATMENT UNIT
SOURCES, WASTES TREATED, MODELED TREATMENT QUANTITIES PER EVENT,
TREATMENT SCHEDULE AND APPLICABLE EMISSION FACTORS
ATK PROMONTORY, UTAH
Modeled
Sources
Burn
Statlon(s)
Treated
Reactive
Waste
Categories
Modeled
Per Event
Treatment
Quantity
Treatment
Events Per
Day Per
Month or
Year
Total
Treatment
Events Per
Year
Total
Annual
Burn Limit
(lbs.)
Applicable Emission
Factors For Wastes
Treated At Each
Source*
Source 1
Open Burn
1,2,3,4,5,6,7,
8,9,10,11,12
A, B, C, D,
E, F, G, H 12,000 lbs.
2 events per
day, 3 days
per week
312 3,744,000 1.3 - see Tables 3-5 and
3-6
Source 2
Open Burn 13 A, B, C, D,
E, F, G, H 10,000 lbs. Once per
week 52 •520,000 1.3 - see Tables 3-5 and
3-6
Source 3
Open Burn 14 A, B, C, D 10,000 lbs. Once per
week 52 520,000 1.3 - see Tables 3-5 and
3-6
Source 4
Open
Detonation
13&14 C, D, G, H 600 lbs. Once every 2
months 6 3,600 1.3 - see Tables 3-5 and
3-6
Source 5
Open Burn 14
Large
Rocket
Motors
26,000 lbs. 3 per year 3 78,000 1.3 - see Tables 3-5 and
3-6
ATK has agreed to use 1.3 OBODi emission factors for all M-136 modeled sources.
TABLE 2-2
M-225 TREATMENT UNIT
SOURCES, WASTES TREATED, MODELED TREATMENT QUANTITIES PER EVENT,
TREATMENT SCHEDULE AND APPLICABLE EMISSION FACTORS
ATK PROMONTORY, UTAH
Treated Modeled Treatment Total Total Applicable Emission
Modeled Burn Reactive Per Event Events Per Treatment Annual Factors For Wastes
Sources Station(s) Waste Treatment Month Events Per Burn Limit Treated At Each
Categories Quantity Year (lbs.) Source*
Source 1
Open Burn 1,2,3,4 A, B, C, D,
E, F, G, H 2,000 lbs. 2 events per
month 24 48,000 1.3 - see Tables 3-5 and
3-6
Source 2
Open
Detonation
1 C, D, G, H 400 lbs. Once every
two months 6 2,400 1.3 - see Tables 3-5 and
3-6
ATK has agreed to use 1.3 OBODi emission factors for all M-225 modeled sources.
TABLE 2-3
M-136 SOURCE PARAMETERS
ATK PROMONTORY, UTAH
Source Parameter Source 1 - OB Source 2 - OB Source 3 - OB Source 4 - OD Source 5-OB
Treatment Operation OB in Pans
Burn Stations 1-12
OB in Pans
Burn Station 13
OB in Pans
Burn Stations 14
OD in Pits
Burn Stations 14
OB of Rocket Motors
Burn Station 14
Location Center of Bum
Station
Center of Burn
Station
Center of Burn
Station
Center of Burn
Station
Center of Burn
Station
Number of sources 1 1 1 1 1
Source Release Type Quasi-continuous Quasi-continuous Quasi-continuous Instantaneous Quasi-continuous
Burn/Release Duration
(OBODM calculated
based on source type)
300 seconds .300 seconds 300 seconds Instantaneous 300 seconds
Source Configuration Volume Volume Volume Volume Volume
Effective Release
Height (m) 1 meter 1 meter 1 meter Ground level 1 meter
1.3 waste heat content 1,471 calories/gram 1,471 calories/gram 1,471 calories/gram 1,471 calories/gram 1,471 calories/gram
Unit emission factor 1.0 1.0 1.0 1.0 1.0
TABLE 2-4
M-225 SOURCE PARAMETERS
ATK PROMONTORY, UTAH
Source Parameter Source 1 Source 2
Treatment Operations OB in Pans OD in pits
Location Center of M-225 Unit Center of M-225 Unit
Number of sources 1 1
Source Release Type Quasi-continuous Instantaneous
Burn/Release Duration
(OBODM calculated based
on source type)
300 seconds Instantaneous
Source Configuration Volume Volume
Effective Release Height (m) 1 meter Ground level
Source Diameter NA 1.5 meters
1.3 waste heat content 1,471 calories/gram 1,471 calories/gram
TABLE 2-5
1.3 CLASS WASTE MATERIAL
"CONSERVATIVE" MAXIMUM EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 1 OF 7
Analyte Maximum Emission Factor (lbs/lb)
Particulates
TSP 1.5E-01
PMIO 1.2E-01
PM2.5 6.0E-02
Metals
Aluminum 4.0E-02
Antimony 2.9E-05
Arsenic 5.5E-07
Barium 9.8E-06
Cadmium 6.1E-07
Chromium 2.0E-05
Cobalt 6.1E-07
Copper 2.5E-05
Lead 4.1E-05
Magnesium 8.2E-05
Manganese 9.4E-05
Mercury 7.4E-08
Nickel 5.8E-05
Phosphorus 1.1E-G4
Selenium 1.6E-06
Silver 1.2E-G6
Thallium 4.3E-06
Zinc 3.5E-05
Perchlorate 4.9E-07
SVOCs
1,2,4,5-Tetrachlorobenzene 5.5E-07
1,2,4-Trichlorobenzene 6.5E-07
1,2-Dichlorobenzene 5.6E-07
1,3,5-Trinitrobenzene 5.5E-07
1,3-Dichlorobenzene 6.2E-07
1,3-Dinitrobenzene 5.7E-07
1,4-Dichlorobenzene 5.8E-07
1 -Chloronaphthalene 5.5E-07
1-Naphthylamine l.lE-05
2,3,4,6-Tetrachlorophenol 7.1E-07
2,4,5-Trichlorophenol 1.4E-06
2,4,6-Trichlorophenol 1.3E-06
2,4-Dichlorophenol 9.3E-07
2,4-Dimethylphenol 6.9E-06
2,4-Dinitrophenol 2.4E-05
2,4-Dinitrotoluene 5.5E-07
2,6-Dichlorophenol 5.5E-07
TABLE 2-5
1.3 CLASS WASTE MATERIAL
"CONSERVATIVE" MAXIMUM EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 2 OF 7
Analyte Maximum Emission Factor (lbs/lb)
2,6-Dinitrotoluene 5.6E-07
2-Acetylaminofluorene 5.5E-07
2-Chloronaphthalene 5.5E-07
2-Chlorophenol 1.9E-06
2-Methylnaphthalene 3.6E-06
2-Methylphenol 3.3E-06
2-Naphthylamine l.lE-05
2-Nitroaniline 5.5E-07
2-Nitrophenol 5.5E-07
3,3'-Dichlorobenzidine 8.1E-06
3,3'-Dimethylbenzidine 5.5E-05
3-Methylcholanthrene 5.5E-07
3-Methylphenol & 4-Methylphenol 2.2E-06
3-Nitroaniline 2.2E-06
4,6-Dinitro-2-methylphenol 9.5E-06
4-Aminobiphenyl l.lE-05
4-Bromophenyl phenyl ether 5.5E-07
4-Chloro-3-methylphenol 6.8E-07
4-Chloroaniline 6.6E-06
4-Nitroaniline 2.2E-06
4-Nitrophenol 3.6E-06
7,12-Dimethylbenz(a)anthracene 5.6E-07
Acenaphthene 5.5E-07
Acenaphthylene 5.5E-07
Acetophenone 2.7E-06
Aniline 8.0E-06
Anthracene 5.5E-07
Benzidine 5.6E-05
Benzo(a)anthracene 6.4E-07
Benzo(a)pyrene 5.5E-07
Benzo(b)fluoranthene 1.2E-06
Benzo(ghi)perylene 6.8E-07
Benzo(k)fluoranthene 1.8E-06
Benzoic acid 6.2E-05
Benzyl alcohol 3.8E-05
bis(2-Chloroethoxy)methane 5.5E-07
bis(2-Chloroethyl) ether 6.1E-07
bis(2-Chloroisopropyl) ether 8.3E-07
bis(2-Ethylhexyl) phthalate l.lE-05
Butyl benzyl phthalate 6.7E-07
Carbazole 7.0E-07
Chrysene 7.0E-07
Dibenz(a,h)anthracene 6.6E-07
Dibenzofuran 5.5E-07
Diethyl phthalate 8.0E-07
« TABLE 2-5 -;
1.3 CLASS WASTE MATERIAL
"CONSERVATIVE" MAXIMUM EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 3 OF 7
Analyte Maximum Emission Factor (lbs/lb)
Dimethyl phthalate 5.5E-07
Di-n-butyl phthalate l.lE-05
Di-n-octyl phthalate 3.7E-06
Diphenylamine 5.5E-07
Ethyl methanesulfonate 5.5E-07
Fluoranthene 5.9E-07
Fiuorene 5.5E-07
Hexachlorobenzene 4.7E-06
Hexachlorobutadiene 8.1E-07
Hexachlorocydopentadiene l.lE-05
Hexachloroethane 5.9E-07
Hexachioropropene 7.9E-07
lndeno(1,2,3-cd)pyrene 5.9E-07
Isophorone 5.5E-07
Methyl methanesulfonate 6.0E-07
Naphthalene 1.4E-05
Nitrobenzene 6.2E-07
N-Nitro-o-toluidine 8.8E-06
N-Nitrosodiethylamine 5.5E-07
N-Nitrosodimethylamine 5.5E-07
N-Nitrosodi-n-butylamine 5.5E-07
N-Nitrosodi-n-propylamine 5.5E-07
N-Nitrosodiphenylamine 9.5E-07
N-Nitrosomethylethylamine 9.1E-07
N-Nitrosomorpholine 5.5E-07
o-Toluidine 7.0E-06
p-Dimethylaminoazobenzene 5.5E-07
Pentachlorobenzene 5.5E-07
Pentachloroethane 5.5E-07
Pentachloronitrobenzene 5.5E-07
Pentachlorophenol 2.7E-05
Phenanthrene 7.0E-07
Phenol 2.4E-06
Pyrene 5.8E-07
Pyridine 8.1E-07
DIoxIns/Furans
2,3,7,8-TCDD 2.3E-12
1,2,3,7,8-PeCDD 6.7E-12
1,2,3,4,7,8-HxCDD 3.5E-12
1,2,3,6,7,8-HxCDD 8.9E-12
1,2,3,7,8,9-HxCDD 6.1E-12
1,2,3,4,6,7,8-HpCDD 2.9E-11
OCDD 3.7E-11
2,3,7,8-TCDF 4.0E-11
TABLE 2-5
1.3 CLASS WASTE MATERIAL
"CONSERVATIVE" MAXIMUM EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 4 OF 7
Analyte Maximum Emission Factor (lbs/lb)
1,2,3,7,8-PeCDF 8.0E-11
2,3,4,7,8-PeCDF 1.6E-10
1,2,3,4,7,8-HxCDF 2.6E-10
1,2,3,6,7,8-HxCDF 1.6E-10
2,3,4,6,7,8-HxCDF 1.9E-10
1,2,3,7,8,9-HxCDF 1.2E-10
1,2,3,4,6,7,8-HpCDF 7.3E-10
1,2,3,4,7,8,9-HpCDF 1.9E-10
OCDF 5.3E-10
Carbonyls
2,5-Dimethylbenzaldehyde 2.7E-05
Acetaldehyde 9.3E-05
Acetone 3.1E-05
Benzaldehyde 1.4E-05
Crotonaldehyde 1.4E-05
Formaldehyde 4.7E-05
Hexanal 1.4E-05
Isopentanal 1.4E-05
m,p-Tolualdehyde 1.4E-05
MEK/Butyraldehydes 1.4E-05
o-Tolualdehyde 4.0E-05
Pentanal 1.7E-05
Propanal 5.2E-05
HCI/CI2/NH3
HCI 1.8E-02
CI2 1.2E-02
NHS 3.2E-05
HCN 2.2E-05
VOCs
TNMOC 9.4E-04
1,1,1-Trichloroethane 8.9E-07
1,1,2,2-Tetrachloroethane 4.2E-07
1,1,2-Trichloroethane 7.3E-07
1,1 -Dichloroethane 3.2E-07
1,1-Dichloroethene 4.3E-07
1,2,3-Trimethylbenzene 4.2E-07
1,2,4-Trichlorobenzene 1.3E-06
1,2,4-Trimethylbenzene 5.2E-06
1,2-Dibromomethane (EDB) 8.9E-07
1,2-Dichlorobenzene 4.8E-07
1,2-Dichloroethane 5.4E-07
TABLE 2-5
1.3 CLASS WASTE MATERIAL
"CONSERVATIVE" MAXIMUM EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 5 OF 7
Analyte Maximum Emission Factor (lbs/lb)
1,2-Dichloropropane 3.7E-07
1,3,5-Trimethylbenzene 2.0E-06
1,3-Butadiene 2.4E-05
1,3-Dichlorobenzene 4.4E-07
1,3-Diethylbenzene 5.0E-07
1,4-Dichlorobenzene 7.3E-07
1,4-Diethylbenzene 6.7E-07
1,4-Dioxane 6.4E-07
1-Butene 2.2E-05
1-Hexene 2.0E-G5
1-Pentene 1.2E-05
2,2,4-Trimethylpentane 2.3E-06
2,2-Dimethylbutane 8.8E-07
2,3,4-Trimethylpentane 2.8E-07
2,3-Dlmethylbutane 2.9E-06
2,3-Dimethylpentane 2.7E-06
2,4-Dimethylpentane l.lE-06
2-Butanone (MEK) 3.9E-06
2-Ethyltoluene 4.5E-07
2-Hexanone 8.7E-07
2-Methylheptane 2.7E-06
2-Methylhexane 4.4E-06
2-Methylpentane l.lE-05
2-Nltropropane 2.8E-06
2-Propanol 3.0E-07
3-Chloropropene 4.7E-06
3-Ethyltoluene 4.8E-06
3-Methylheptane 3.5E-06
3-Methylhexane 5.2E-06
3-Methylpentane 7.1E-06
4-Ethyltoluene 5.3E-06
4-Methyl-2-pentanone 7.0E-07
Acetone 2.4E-05
Acetonitrile 1.9E-05
Acetylene 9.4E-05
Acrylonitrile 1.6E-05
alpha-Chlorotoluene 5.7E-07
Benzene 4.7E-05
Bromodichloromethane 7.8E-07
Bromoform 1.3E-06
Bromomethane 6.2E-07
Butane 1.8E-05
Carbon Disulfide 9.8E-06
Carbon Tetrachloride 1.5E-05
Chloroacetonitrile l.lE-06
TABLE 2-5
1.3 CLASS WASTE MATERIAL
"CONSERVATIVE" MAXIMUM EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 6 OF 7
Analyte Maximum Emission Factor (lbs/lb)
Chlorobenzene 2.5E-06
Chloroethane 2.6E-07
Chloroform 6.1E-06
Chloromethane 1.4E-05
cis-1,2-Dichloroethene 4.6E-07
cis-1,3-Dichloropropene 1.3E-06
cis-2-Butene 1.7E-06
cis-2-Pentene 3.3E-07
Cumene 4.2E-07
Cyclohexane 2.5E-06
Cyclopentane 1.8E-06
Decane 1.7E-05
Dibromochloromethane 8.8E-07
Ethane 2.1E-05
Ethanol 1.6E-06
Ethene 1.8E-04
Ethyl benzene 2.8E-06
Ethyl ether 2.5E-06
Ethyl Methacrylate 1.6E-06
Heptane 7.2E-06
Hexachlorobutadiene 1.7E-06
Hexane 9.8E-06
Isobutane 2.8E-06
Isopentane 2.0E-05
m,p-Xylene l.lE-05
Methacrylonitrile 4.9E-06
Methyl Acrylate 1.2E-06
Methyl Methacrylate 1.6E-06
Methyl tert-butyl ether 4.2E-07
Methylcyclohexane 6.1E-06
Methylcyclopentane 5.6E-06
Methylene chloride 7.1E-06
n-Butylchloride 1.2E-05
Nonane 1.3E-05
Octane 7.5E-06
o-Xylene 3.5E-06
Pentane 1.9E-05
Propane 8.7E-G6
Propylbenzene 1.GE-G6
Propylene 4.9E-G5
Styrene 9.9E-G7
Tetrachloroethene 2.5E-G6
Tetrahydrofuran 9.GE-07
Toluene 1.9E-G5
trans-1,2-Dichloroethene 7.2E-07
TABLE 2-5
1.3 CLASS WASTE MATERIAL
"CONSERVATIVE" MAXIMUM EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 7 OF 7
Analyte Maximum Emission Factor (lbs/lb)
trans-1,3-Dichloropropene 6.1E-07
trans-2-butene 7.7E-G6
trans-2-Pentene 1.7E-06
Trichloroethene 9.4E-G7
Undecane 1.2E-05
Vinyl chloride 7.6E-G6
CEM
C02 7.2GE-01
CO 6.40E-03
NOX 6.4GE-G3
S02 5.GGE-04
Highlighted analytes were not detected during the Bang Box testing program
HCN - hydrogen cyanide
SVOCs - semi-volatile organic compounds
VOCs - volatile organic compounds
HCL - hydrogen chloride
NOX - nitrogen oxide
502 - sulfur dioxide
CO - carbon monoxide
C02 - carbon dioxide
TNMOC-total non-methane organic carbon —
OCDD - 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin
OCDF - 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-furan
CL2 - chlorine
NHS-ammonia
TSP - Total suspended particulates
PMIO - particulate matter less than 10 microns in aerodynamic diameter
PM2.5 - particulate matter less than 2.5 microns in aerodynamic diameter
TABLE 2-6
1.3 CLASS WASTE MATERIAL
"CORRECTED" EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 1 OF 7
Analyte Emission Factor (lbs/lb)
Particulates
TSP 1.4E-G1
PMIO 8.6E-G2
PM2.5 5.9E-G2
Metals
Aluminum 4.GE-G2
Antimony 2.9E-05
Arsenic S.GE-07
Barium 4.9E-06
Cadmium S.1E-07
Chromium 2.GE-05
Cobalt 3.1E-07
Copper 2.5E-05
Lead S.4E-05
Magnesium 2.9E-05
Manganese 9.3E-05
Mercury 3.7E-G8
Nickel 5.8E-G5
Phosphorus 1.0E-G4
Selenium 1.7E-06
Silver 9.5E-07
Thallium 2.1E-G6
Zinc 3.5E-05
Perchlorate 2.5E-07
SVOCs
1,2,4,5-Tetrachlorobenzene 2.7E-07
1,2,4-Trichlorobenzene 3.2E-07
1,2-Dichlorobenzene 2.8E-07
1 ,S,5-Trinitrobenzene 2.7E-07
1 ,S-Dichlorobenzene 3.1E-07
1 ,S-Dinitrobenzene 2.8E-07
1,4-Dichlorobenzene 2.9E-07
1 -Chloronaphthalene 2.7E-07
1-Naphthylamine 5.5E-G6
2,3,4,6-Tetrachlorophenol S.6E-07
2,4,5-Trichlorophenol 7.1E-07
2,4,6-Trichlorophenol #REF!
2,4-Dichlorophenol 9.SE-G7
2,4-Dimethylphenol S.5E-06
2,4-Dinitrophenol 1.2E-05
2,4-Dinitrotoluene S.1E-07
2,6-Dichlorophenol 4.0E-07
TABLE 2-6
1.3 CLASS WASTE MATERIAL
"CORRECTED" EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 2 OF 7
Analyte Emission Factor (lbs/lb)
2,6-Dinitrotoluene 5.6E-07
2-Acetylaminofluorene 2.7E-07
2-Chloronaphthalene 2.7E-07
2-Chlorophenol 1.9E-06
2-Methylnaphthalene S.6E-06
2-Methylphenol 1.6E-06
2-Naphthylamine 5.5E-G6
2-Nitroaniline 2.7E-07
2-Nitrophenol 3.9E-07
S,3'-Dichlorobenzidine 4.1E-06
S,S'-Dimethylbenzidine 2.7E-05
S-Methylcholanthrene 2.7E-07
3-Methylphenol & 4-Methylphenol 1.1E-06
3-Nitroaniline 1.1E-06
4,6-Dinitro-2-methylphenol 4.8E-06
4-Aminobiphenyl 5.5E-06
4-Bromophenyl phenyl ether 2.7E-07
4-Chloro-S-methylphenol S.4E-07
4-Chloroaniline S.SE-06
4-Nitroaniline 1.1E-06
4-Nitrophenol 1.8E-06
7,12-Dimethylbenz(a)anthracene 2.8E-07
Acenaphthene 2.7E-07
Acenaphthylene 2.7E-07
Acetophenone 2.7E-06
Aniline 4.0E-06
Anthracene 2.7E-07
Benzidine 2.8E-05
Benzo(a)anthracene S.2E-07
Benzo(a)pyrene 2.7E-07
Benzo(b)fluoranthene 6.0E-07
Benzo(ghi)perylene S.4E-07
Benzo(k)fluoranthene 8.8E-07
Benzoic acid 6.2E-05
Benzyl alcohol 1.9E-05
bis(2-Chloroethoxy)methane 2.7E-07
bis(2-Chloroethyl) ether S.1E-07
bis(2-Chloroisopropyl) ether 4.2E-07
bis(2-Ethylhexyl) phthalate 5.5E-G6
Butyl benzyl phthalate 3.SE-07
Carbazole 3.5E-07
Chrysene 3.5E-07
Dibenz(a,h)anthracene 3.3E-07
Dibenzofuran 2.7E-07
Diethyl phthalate 4.GE-G7
TABLE 2-6 !
1.3 CLASS WASTE MATERIAL
"CORRECTED" EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 3 OF 7 I
Analyte Emission Factor (lbs/lb)
Dimethyl phthalate 2.7E-07
Di-n-butyl phthalate 5.5E-06
Di-n-octyl phthalate 3.7E-06
Diphenylamine 2.7E-07
Ethyl methanesulfonate 2.7E-07
Fluoranthene 4.0E-07
Fiuorene 4.2E-07
Hexachlorobenzene 4.7E-06
Hexachlorobutadiene 4.1E-07
Hexachlorocydopentadiene 5.5E-06
Hexachloroethane 3.0E-07
Hexachioropropene 3.9E-07
lndeno(1,2,S-cd)pyrene 3.0E-07
Isophorone 2.7E-07
Methyl methanesulfonate 3.GE-07
Naphthalene 1.3E-05
Nitrobenzene 3.1E-07
N-Nitro-o-toluidine 4.4E-06
N-Nitrosodiethylamine 2.7E-07
N-Nitrosodimethylamine 2.7E-07
N-Nitrosodi-n-butylamine 2.7E-07
N-Nitrosodi-n-propylamine 2.7E-07
N-Nitrosodiphenylamine 4.8E-07
N-Nitrosomethylethylamine 4.5E-07
N-Nitrosomorpholine 2.7E-07
o-Toluidine 3.5E-06
p-Dimethylaminoazobenzene 2.7E-07
Pentachlorobenzene 3.0E-07
Pentachloroethane 2.7E-07
Pentachloronitrobenzene 2.7E-07
Pentachlorophenol 1.4E-05
Phenanthrene 7.GE-07
Phenol 2.1E-06
Pyrene 2.9E-07
Pyridine 4.1E-07
DIoxins/Furans
2,3,7,8-TCDD 1.3E-12
1,2,3,7,8-PeCDD 6.7E-12
1,2,3,4,7,8-HxCDD 3.4E-12
1,2,3,6,7,8-HxCDD 8.9E-12
1,2,3,7,8,9-HxCDD 6.1E-12
1,2,3,4,6,7,8-HpCDD 2.9E-11
OCDD 3.7E-11
2,3,7,8-TCDF 4.0E-11
TABLE 2-6
1.3 CLASS WASTE MATERIAL
"CORRECTED" EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 4 OF 7
Analyte Emission Factor (lbs/lb)
1,2,3,7,8-PeCDF 8.GE-11
2,3,4,7,8-PeCDF 1.6E-10
1,2,3,4,7,8-HxCDF 2.6E-10
1,2,3,6,7,8-HxCDF 1.6E-1G
2,3,4,6,7,8-HxCDF 1.9E-10
1,2,3,7,8,9-HxCDF 1.2E-10
1,2,3,4,6,7,8-HpCDF 7.3E-1G
1,2,3,4,7,8,9-HpCDF 1.9E-10
OCDF 5.2E-10
Carbonyls
2,5-Dimethylbenzaldehyde 1.4E-G5
Acetaldehyde 7.5E-05
Acetone 1.5E-05
Benzaldehyde 7.3E-06
Crotonaldehyde 6.8E-06
Formaldehyde 4.0E-05
Hexanal 8.2E-06
Isopentanal 6.8E-06
m,p-Tolualdehyde 6.8E-06
MEK/Butyraldehydes 1.2E-05
o-Tolualdehyde 2.3E-05
Pentanal 1.2E-05
Propanal 3.8E-05
HCI/CI2/NH3
HCI 1.8E-G2
012 1.5E-03
NH3 2.2E-05
HCN 1.2E-05
VOCs
TNMOC 8.1 E-04
1,1,1-Trichloroethane 4.5E-07
1,1,2,2-Tetrachloroethane 2.1E-07
1,1,2-Trichloroethane 3.6E-07
1,1-Dichloroethane 1.6E-07
1,1-Dichloroethene 2.2E-07
1,2,3-Trimethylbenzene 2.1E-07
1,2,4-Trichlorobenzene 6.3E-07
1,2,4-Trimethylbenzene 5.2E-06
1,2-Dibromoethane (EDB) 4.4E-07
1,2-Dichlorobenzene 2.4E-07
1,2-Dichloroethane 2.7E-G7
TABLE 2-6
1.3 CLASS WASTE MATERIAL
"CORRECTED" EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 5 OF 7
Analyte Emission Factor (lbs/lb)
1,2-Dichloropropane 1.8E-G7
1,3,5-Trimethylbenzene 2.0E-G6
1,3-Butadiene 2.0E-05
1,3-Dichlorobenzene 2.2E-07
1,3-Diethylbenzene 2.5E-07
1,4-Dichlorobenzene 3.7E-07
1,4-Diethylbenzene 3.3E-G7
1,4-Dioxane 3.2E-G7
1-Butene 2.1E-05
1-Hexene 2.GE-05
1-Pentene 1.2E-05
2,2,4-Trimethylpentane 2.3E-G6
2,2-Dimethylbutane 4.4E-G7
2,3,4-Trimethylpentane 1.4E-07
2,3-Dimethylbutane 2.9E-G6
2,3-Dimethylpentane 2.7E-06
2,4-Dimethylpentane 5.5E-07
2-Butanone (MEK) 3.9E-06
2-Ethyltoluene 2.2E-07
2-Hexanone 4.4E-07
2-Methylheptane 2.7E-06
2-Methylhexane 4.4E-06
2-Methylpentane 5.3E-06
2-Nitropropane 2.8E-06
2-Propanol 1.5E-07
3-Chloropropene 4.7E-06
3-Ethyltoluene 4.8E-06
3-Methylheptane 3.5E-06
3-Methylhexane 5.2E-06
3-Methylpentane 7.1E-06
4-Ethyltoluene 5.3E-06
4-Methyl-2-pentanone 3.5E-07
Acetone 2.3E-05
Acetonitrile 9.2E-06
Acetylene 7.4E-05
Acrylonitrile 1 .OE-05
alpha-Chlorotoluene 2.8E-07
Benzene 4.4E-05
Bromodichloromethane 3.9E-07
Bromoform 6.3E-07
Bromomethane 3.1E-07
Butane 1.8E-G5
Carbon Disulfide 9.4E-06
Carbon Tetrachloride 1.5E-G5
Chloroacetonitrile 5.6E-07
TABLE 2-6
1.3 CLASS WASTE MATERIAL
"CORRECTED" EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 6 OF 7
Analyte Emission Factor (lbs/lb)
Chlorobenzene 2.5E-06
Chloroethane 1.3E-07
Chloroform 6.1E-06
Chloromethane 1.4E-05
cis-1,2-Dichloroethene 2.3E-07
cis-1,3-Dichloropropene 1.3E-06
cis-2-Butene 1.4E-06
cis-2-Pentene 1.7E-07
Cumene 2.1E-07
Cyclohexane 2.5E-G6
Cyclopentane 1.8E-G6
Decane 1.7E-G5
Dibromochloromethane 4.4E-07
Ethane 1.7E-05
Ethanol 1.6E-06
Ethene 1.5E-04
Ethyl Benzene 2.8E-06
Ethyl Ether 1.2E-06
Ethyl Methacrylate 7.8E-07
Heptane 7.2E-06
Hexachlorobutadiene 8.5E-07
Hexane 9.8E-06
Isobutane 2.8E-G6
Isopentane 2.0E-05
m,p-Xylene 1.0E-G5
Methacrylonitrile 4.9E-G6
Methyl Acrylate 5.9E-07
Methyl Methacrylate 8.1E-07
Methyl tert-butyl ether 2.1E-07
Methylcyclohexane 6.1E-06
Methylcyclopentane 5.6E-06
Methylene Chloride 7.1E-06
n-Butylchloride 5.8E-06
Nonane 1.3E-05
Octane 7.5E-06
o-Xylene 3.5E-06
Pentane 1.9E-05
Propane 8.7E-06
Propylbenzene 1 .GE-06
Propylene 4.3E-05
Styrene 9.9E-G7
Tetrachloroethene 2.5E-G6
Tetrahydrofuran 6.4E-G7
Toluene 1.8E-05
trans-1,2-Dichloroethene 3.6E-07
TABLE 2-6
1.3 CLASS WASTE MATERIAL
•CORRECTED" EMISSION FACTORS (LBS/LB)
ATK PROMONTORY, UTAH
PAGE 7 OF 7
Analyte Emission Factor (lbs/lb)
trans-1,3-Dichloropropene 3.GE-07
trans-2-butene 7.7E-06
trans-2-Pentene 1.7E-06
Trichloroethene 9.4E-07
Undecane 1.2E-05
Vinyl Chloride 7.6E-G6
CEM
C02 6.9E-01
CO 4.7E-03
NOX 5.8E-03
S02 4.1 E-04
Highlighted analytes were not detected during the Bang Box testing program
HCN - hydrogen cyanide
SVOCs - semi-volatile organic compounds
VOCs - volatile organic compounds
HCL - hydrogen chloride
NOX - nitrogen oxide
S02 - sulfur dioxide
CO - carbon monoxide
002 - carbon dioxide
TNMOC - total non-methane organic carbon
OCDD -1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin
OCDF -1,2,3,4,6,7,8,9-Octachlorodibenzo-p-furan
CL2 - chlorine
NHS - ammonia
TSP - Total suspended particulates
PMIO - particulate matter less than 10 microns in aerodynamic diameter
PM2.5 - particulate matter less than 2.5 microns in aerodynamic diameter
TABLE 2-7
SUMMARY OF DEPOSITION MODELING PARAMETERS
ATK PROMONTORY, UTAH
Parameter Particulate/Deposition Phase
Emission Surrogate Aluminum (density of 2.7 g/cm^)
Emission Factor 1.0
Non-gravitational dry deposition No
Gravitational settling Yes
Mean particle diameter 30 i^m
Particle size standard deviation 2.0
Number of particle size classes 10
Cloud depletion Yes
OBODM Output Deposition rate (ng/m^)
TABLE 2-8
ATK MODELING ANALYSIS DISCRETE RECEPTORS
ATK LAUNCH SYSTEMS
PROMONTORY, UTAH
Discrete Receptor Name UTM Coordinate
Easting Northing Elevation
m m m ft
ATK Ranch Pond 376670 4599479 1291 4235.564
Boundary #2 379669 4612480 1321 4333.99
Adams Ranch 378256 4613483 1355 4445.538
Blue Creek 379972 4615666 1341 4399.606
Christensen Ranch 381372 4622166 1371 4498.032
Autoliv (complex terrain) 381675 4613810 1480 4855.643
Big Bear River Bird Refuge 382669 4599480 1284 4212,598
Boundary #4 386872 4608166 1295 4248.688
Boundary #3 387872 4610166 1385 4543.963
Holmgren Ranch 388372 4608666 1295 4248.688
Salt Creek Waterfowl Management Area 395169 4611480 1296 4251.969
Thatcher 392321 4616597 1319 4327.428
Penrose 391627 4611823 1300 4265.092
Boundary #1 (complex terrain) 382669 4616480 1542 5059.055
North Plant Mam Administration Building and Mam
Manufacturing Area 381140 4619873 1375 4511.155
South Plant Mam Administration Building and Mam
Manufacturing area 380488 4613356 1362 4468.504
Howell Dairy 380309 4627652 1388 4553.806
TABLE 2-9
M-136 MAXIMUM GENERAL GRID ONSITE/OFFSITE RECEPTORS
AND ASSOCIATED GRID SECTORS
ATK LAUNCH SYSTEMS
PROMONTORY, UTAH
Maximum Short Term Impact Offsite Receptor Maximum Short Term Impact Onsite Receptor
Surrounding Sectors
Within 1 KM of Maximum
Onsite Receptor Source -
Model Easting Northing Grid Sector
Surrounding Sectors Within -
1 KM of Maximum Offsite
Receptor
Source -
Model Easting Northing Grid Sector
Surrounding Sectors
Within 1 KM of Maximum
Onsite Receptor
1 - Gas 378172 4618166 36C3A 36C3B, 36F3D, 36F3A,
36F30, 36F10B, 36F10H 1 - Gas 380472 4615766 36F3H 36F3F, 36F3G, 36C3M,
36C30
2-Gas 378772 4617766 36C3A 36C3B, 36F3D, 36F3A,
36F30, 36F10B 2-Gas 380772 4615766 36F3H 36F3F, 36F3G, 36C3M,
36C30
3 - Gas 378472 4618366 36C3A 36C3B, 36F3D, 36F3A,
36F3D, 36F10B, 36F10H 3 - Gas 380772 4615766 36F3H
36F3F, 36F3G, 36C3M,
36C30
4 - Gas 378772 4616666 36C3C 36C3B, 36F3D, 36F3E,
36F3P, 36C3D, 36C3E 4-Gas 380672 4615866 36F3H
36F3F, 36F3G, 36C3M,
36C30
1 - Part 379872 4615966 36F3F
36F3G, 36F3H, 36F3E,
36F3P, 36C3D, 36C3E,
36C3F
1 - Part 380472 4615765 36F3H
36F3F, 36F3G, 36C3M,
36C30
2-Part 379872 4615666 36F3F
36F3G, 36F3H, 36F3E,
36F3P, 36C3D, 36C3E,
36C3F, 36F3I
2-Part 380772 4615766 36F3H
36F3F, 36F3G, 36C3M,
36C30
3-Part 379872 4616066 36F3F
36F3G, 36F3H,36F3E,
36F3P, 36C3D, 36C3E,
36C3F, 36C3WW
3 - Part 380772 4615766 36F3H 36F3F 36F3G, 36C3M,
36C30
4-Part 379872 4616166 36F3F
36F3G, 36F3H, 36F3E,
36F3P, 36C3D, 36C3E,
36C3F
4-Part 3.8E+05 4615866 36F3H 36F3F, 36F3G, 36C3M,
36C30
1 - Dep 379572 4616366 36F3F
36F3G, 36F3H,36F3E,
36C3WW, 36C3C, 36C3D,
36C3E, 36C3F
1 - Dep 380472 4615066 36F3H 36F3F, 36F3H, 36C3M,
36C30, 36F3E
2 - Dep 379572 4615066 36F3F
36F3G, 36F3H, 36F3E,
36F3P, 36C3D, 36C3E,
36C3F
2 - Dep 380672 4615266 36F3G 36F3F, 36F3G, 36C3M,
36C30
3 - Dep 379572 4616066 36F3F
36F3G, 36F3H, 36F3E,
36F3P, 36C3D,.36C3E,
36C3F, 36C3WW
3 - Dep 380772 4615466 36F3G 36F3F, 36F3G, 36C3M,
36C30
4-Dep 379572 4615066 36F3F
36F3G, 36F3H, 36F3E,
36F3P, 36C3D, 36C3E,
36C3F
4-Dep 380672 4615066 36F3H 36F3F, 36F3G, 36C3M,
36C30
TABLE 2-10
M-225 MAXIMUM GENERAL GRID ONSITE/OFFSITE RECEPTORS
AND ASSOCIATED GRID SECTORS
ATK LAUNCH SYSTEMS
PROMONTORY, UTAH
Maximum Short Term Impact Offsite
Receptor
Maximum Short Term Impact Onsite
Receptor Surrounding Sectors Within
1 KM of Maximum Onsite
Receptor Source -
Model Easting Northing Sector
Surrounding Sectors Within
1 KM of Maximum Offsite
Receptor
Source -
Model Easting Northing Sector
Surrounding Sectors Within
1 KM of Maximum Onsite
Receptor
1 - Gas 395669 4604980 25C10 E 25C10I, 25F10H 1 - Gas 385669 4610080 25C3I 25C3G, 25C3F,25C3E, 25C3J,
25C3H
2-Gas 387169 4612480 25C30 25C3D, 25C3L,
25C3C,25C10D, 25C10B 2 - Gas 385669 4610080 25C3I 25C3G, 25C3F,25C3E, 25C3J,
25C3H '
1 - Part 387469 4610080 25F3H
25C3M, 25F3I, 25F3G,
25F3E, 25F3F, 25C3I,
25C3H
1 - Part 386669 4609680 25F3F 25C3H, 25C3I, 25C3J, 25C3K,
25F3D, 25F3E, 25F3H
2-Part 387669 4608580 25F3M 25F3L, 25F3N, 25F10J,
25F10I 2-Part 386669 4609680 25F3F 25C3H, 25C3I, 25C3J, 25C3k,
2SF3D, 25F3E, 25F3H
1 - Dep 387469 4610080 25F3H
25C3M, 25F3I, 25F3G,
25F3E, 25F3F, 25C3I,
25C3H
1 - Dep 386769 4609480 25F3E
25F3G, 25F3H, 25F3F :
25C3I,25C3J, 25C3K, 25F3D,
25F3E
2 - Dep 387469 4610080 25F3H
25C3M, 25F3I, 25F3G,
25F3E, 25F3F, 25C3I,
25C3H
2 - Dep 386889 4609480 25F3E
25F3G, 25F3H, 25F3F,
25C3I,25C3J, 25C3K, 25F3D,
25F3E
' The maximum offsite and onsite receptors in this table represent the maximum impact location detennine with the general grid receptor network.
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APPENDIX A
ATK DISPERSION MODELING
LAND USE ANALYSES
FOR M-136 AND M-225
[_
M-136 Treatment Unit
³PGH P:\GIS\THIOKOL\MAPDOCS\MXD\M136_LAND_USE_ANALYSIS.MXD 04/19/11 JEE
1,000 1,0000
Meters
CONTRACT NUMBER
0
APPROVED BY
REVFIGURE NO.
APPROVED BY
DATE
DATE
___
____
CTO NUMBER
____
FIGURE E-1
____
3 KILOMETER RADIUS LAND USE ANALYSIS FOR
ATK PROMONTORY M-136 TREATMENT UNIT
PROMONTORY, UTAH
DATE
AS NOTED
SCALE
DATECHECKED BY
DRAWN BY
J. ENGLISH 04/19/11
J. LUCAS 04/20/11
DATEREVISED BY
___ ___
Legend
[_Treatment Unit
Land Use Analysis Grid (100m)
Rural Area
Urban Area
3-km Buffer Zone
Facility Boundary
Aerial photograph taken in 2009.
[_
M-225 Treatment Unit
³PGH P:\GIS\THIOKOL\MAPDOCS\MXD\M225_LAND_USE_ANALYSIS.MXD 04/20/11 JEE
1,000 1,0000
Meters
CONTRACT NUMBER
0
APPROVED BY
REVFIGURE NO.
APPROVED BY
DATE
DATE
___
____
CTO NUMBER
____
FIGURE E-2
____
3 KILOMETER RADIUS LAND USE ANALYSIS FOR
ATK PROMONTORY M-225 TREATMENT UNIT
PROMONTORY, UTAH
DATE
AS NOTED
SCALE
DATECHECKED BY
DRAWN BY
J. ENGLISH 04/19/11
J. LUCAS 04/20/11
DATEREVISED BY
___ ___
Legend
[_Treatment Unit
Land Use Analysis Grid (100m)
Label
Rural Area
Urban Area
3-km Buffer
Facility Boundary
Aerial photograph taken in 2009.
APPENDIX B
M-245 METEOROLOGICAL DATA AND DATA RECOVERY STATISTICS
ATK M-225 Meteorological Monitoring Station
Data Recovery Statistics After Data Validation
For The Annual Periods 1997 Through 2001
Parameter 1997 1998 1999 2000 2001
ID 100 100 100 100 100
YR 100 100 100 100 100
JD 100 100 100 100 100
HR 100 100 100 100 100
WS 94.5 99.2 90.7 99.4 97.8
WD 94.5 96 90.7 99.4 93.7
ST 94.5 96 90.7 99.4 93.7
TEMP 93.3 99.3 90.7 99.4 93.7
MAXT 93.3 99.3 90.7 99.4 93.7
TIMEX 93.3 99.3 90.7 99.4 93.7
MINT 93.3 99.3 90.7 99.4 93.7
TIMEN 93.3 99.3 90.7 99.4 93.7
PREC 94.5 99.3 90.7 99.5 93.2
PRES 94.6 99.3 90.8 99.5 93.9
SR1 94.6 99.3 90.8 99.5 93.9
SR2 94.6 99.3 90.8 99.5 93.9
APPENDIX C
ANNUAL WIND ROSE PLOTS
ATK M-245 METEOROLOGICAL STATION
FOR 1997, 1998, 1999, 2000, AND 2001
APPENDIX D
GAS MODELING RESULTS
APPENDIX E
PARTICULATE MODELING RESULTS
APPENDIX G
GAS DISPERSION FACTORS
APPENDIX H
PARTICULATE DISPERSION FACTORS
APPENDIX J
DISCRETE RECEPTOR MODELING
1. The ADFs were extracted from output files per source and imported into a text file with a special *.MET extension,
then imported into excel. These *.MET files are included in Appendix J.
2. M-136 has 312 treatment events per year; however, its divided into two separate treatments per day. Because of
this, the top 156 worst-case scenarios were used to develop the meteorological data per receptor. The worst case
ADF for Source 1 was doubled to account for two treatment events per day and 312 events per year.
Summary for Worst Case MET File Compilation and Air Dispersion Factor Calculations
OBODM was initially used to model maximum 1-hour air dispersion factors (ADFs) for gas, particulates,
and deposition sources using five years of onsite meteorological data (see Section 2.13 of this report).
For each year of onsite meteorological data, OBODM provided the top fifty 1-hour time-average ADFs. At
the conclusion of the modeling, the top fifty ADFs for each year of meteorological data were imported into
a spreadsheet1 to provide the top 250 worst-case 1-hour scenarios that would be used to develop the
meteorological (MET) files to calculate annual ADFs.
The steps below show the procedure that was used to develop these MET files. Appendix J of this report
contains a folder that includes the input files and output files used with OBODM, each spreadsheet
separated by source number, hourly source strength files per unit, and the meteorological file. The
example in Appendix J is for Adams Ranch and includes meteorological files generated for both the M-
136 and M-225 units.
1. In each spreadsheet, there is a tab labeled, “Top 250 Cases.” Because the model was ran per
year, the sort command was used to sort the ADFs from largest to smallest.
2. Also, in each spreadsheet, there is a tab labeled, “Top XXX Cases,” where XXX is the number of
annual treatment events for a given source based on the treatment scheduled shown in Tables 2-
1 and 2-2 of this report. See Table 1. These top cases were re-sorted to have the worst-case
scenarios in chronological order to create an easier and more fluid process to develop the
meteorological files.
Table 1 – Annual Treatment Events Per Unit
M-136 Annual Treatment Events M-225 Annual Treatment Events
Source 1 3122 Source 1 24
Source 2 52 Source 2 6
Source 3 52
Source 4 6
Source 5 3
3. The worst-case scenarios obtained from the initial modeling were then superimposed onto the
1997 meteorological data from all five years of meteorological data based on the spreadsheet
that was developed in Steps 1 and 2.
4. Hourly source strength files were developed to coincide with the meteorological data for both M-
136 and M-225 based on the treatment quantities shown in Tables 2-1 and 2-2 of this report. The
hourly source file option was used in OBODM annual modeling runs to calculate annual average
air dispersion factors based on the number of annual treatment events in Tables 2-1 and 2-2 and
for the remaining hours in the year when M-136 and M-225 units were not operating.
APPENDIX L
HOURLY AND ANNUAL
EMISSION FACTORFS AND EMISISON RATES
TABLE OR APPENDIX ???
1.3 CLASS WASTE MATERIAL PER EVENT (1-HOUR)
CONSERVATIVE EMISSION RATES (LBS/HR)
ATK PROMONTORY, UTAH
PAGE 1 OF 5
1 2 3 4 5 1 2
Particulates
TSP 1.5E-01 1.8E+03 1.5E+03 1.5E+03 9.0E+01 3.9E+03 3.0E+02 6.0E+01
PM10 1.2E-01 1.4E+03 1.2E+03 1.2E+03 7.2E+01 3.1E+03 2.4E+02 4.8E+01
PM2.5 6.0E-02 7.2E+02 6.0E+02 6.0E+02 3.6E+01 1.6E+03 1.2E+02 2.4E+01
Metals
Aluminum 4.0E-02 4.8E+02 4.0E+02 4.0E+02 2.4E+01 1.0E+03 8.0E+01 1.6E+01
Antimony 2.9E-05 3.5E-01 2.9E-01 2.9E-01 1.7E-02 7.5E-01 5.8E-02 1.2E-02
Arsenic 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Barium 9.8E-06 1.2E-01 9.8E-02 9.8E-02 5.9E-03 2.5E-01 2.0E-02 3.9E-03
Cadmium 6.1E-07 7.3E-03 6.1E-03 6.1E-03 3.7E-04 1.6E-02 1.2E-03 2.4E-04
Chromium 2.0E-05 2.4E-01 2.0E-01 2.0E-01 1.2E-02 5.2E-01 4.0E-02 8.0E-03
Cobalt 6.1E-07 7.3E-03 6.1E-03 6.1E-03 3.7E-04 1.6E-02 1.2E-03 2.4E-04
Copper 2.5E-05 3.0E-01 2.5E-01 2.5E-01 1.5E-02 6.5E-01 5.0E-02 1.0E-02
Lead 4.1E-05 4.9E-01 4.1E-01 4.1E-01 2.5E-02 1.1E+00 8.2E-02 1.6E-02
Magnesium 8.2E-05 9.8E-01 8.2E-01 8.2E-01 4.9E-02 2.1E+00 1.6E-01 3.3E-02
Manganese 9.4E-05 1.1E+00 9.4E-01 9.4E-01 5.6E-02 2.4E+00 1.9E-01 3.8E-02
Mercury 7.4E-08 8.9E-04 7.4E-04 7.4E-04 4.4E-05 1.9E-03 1.5E-04 3.0E-05
Nickel 5.8E-05 7.0E-01 5.8E-01 5.8E-01 3.5E-02 1.5E+00 1.2E-01 2.3E-02
Phosphorus 1.1E-04 1.3E+00 1.1E+00 1.1E+00 6.6E-02 2.9E+00 2.2E-01 4.4E-02
Selenium 1.6E-06 1.9E-02 1.6E-02 1.6E-02 9.6E-04 4.2E-02 3.2E-03 6.4E-04
Silver 1.2E-06 1.4E-02 1.2E-02 1.2E-02 7.2E-04 3.1E-02 2.4E-03 4.8E-04
Thallium 4.3E-06 5.2E-02 4.3E-02 4.3E-02 2.6E-03 1.1E-01 8.6E-03 1.7E-03
Zinc 3.5E-05 4.2E-01 3.5E-01 3.5E-01 2.1E-02 9.1E-01 7.0E-02 1.4E-02
Perchlorate 4.9E-07 5.2E-02 4.9E-03 4.9E-03 2.9E-04 1.3E-02 9.8E-04 2.0E-04

SVOCs
1,2,4,5-Tetrachlorobenzene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
1,2,4-Trichlorobenzene 6.5E-07 7.8E-03 6.5E-03 6.5E-03 3.9E-04 1.7E-02 1.3E-03 2.6E-04
1,2-Dichlorobenzene 5.6E-07 6.7E-03 5.6E-03 5.6E-03 3.4E-04 1.5E-02 1.1E-03 2.2E-04
1,3,5-Trinitrobenzene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
1,3-Dichlorobenzene 6.2E-07 7.4E-03 6.2E-03 6.2E-03 3.7E-04 1.6E-02 1.2E-03 2.5E-04
1,3-Dinitrobenzene 5.7E-07 6.8E-03 5.7E-03 5.7E-03 3.4E-04 1.5E-02 1.1E-03 2.3E-04
1,4-Dichlorobenzene 5.8E-07 7.0E-03 5.8E-03 5.8E-03 3.5E-04 1.5E-02 1.2E-03 2.3E-04
1-Chloronaphthalene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
1-Naphthylamine 1.1E-05 1.3E-01 1.1E-01 1.1E-01 6.6E-03 2.9E-01 2.2E-02 4.4E-03
2,3,4,6-Tetrachlorophenol 7.1E-07 8.5E-03 7.1E-03 7.1E-03 4.3E-04 1.8E-02 1.4E-03 2.8E-04
2,4,5-Trichlorophenol 1.4E-06 1.7E-02 1.4E-02 1.4E-02 8.4E-04 3.6E-02 2.8E-03 5.6E-04
2,4,6-Trichlorophenol 1.3E-06 1.6E-02 1.3E-02 1.3E-02 7.8E-04 3.4E-02 2.6E-03 5.2E-04
2,4-Dichlorophenol 9.3E-07 1.1E-02 9.3E-03 9.3E-03 5.6E-04 2.4E-02 1.9E-03 3.7E-04
2,4-Dimethylphenol 6.9E-06 8.3E-02 6.9E-02 6.9E-02 4.1E-03 1.8E-01 1.4E-02 2.8E-03
2,4-Dinitrophenol 2.4E-05 2.9E-01 2.4E-01 2.4E-01 1.4E-02 6.2E-01 4.8E-02 9.6E-03
2,4-Dinitrotoluene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
2,6-Dichlorophenol 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
2,6-Dinitrotoluene 5.6E-07 6.7E-03 5.6E-03 5.6E-03 3.4E-04 1.5E-02 1.1E-03 2.2E-04
2-Acetylaminofluorene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
2-Chloronaphthalene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
2-Chlorophenol 1.9E-06 2.3E-02 1.9E-02 1.9E-02 1.1E-03 4.9E-02 3.8E-03 7.6E-04
2-Methylnaphthalene 3.6E-06 4.3E-02 3.6E-02 3.6E-02 2.2E-03 9.4E-02 7.2E-03 1.4E-03
2-Methylphenol 3.3E-06 4.0E-02 3.3E-02 3.3E-02 2.0E-03 8.6E-02 6.6E-03 1.3E-03
2-Naphthylamine 1.1E-05 1.3E-01 1.1E-01 1.1E-01 6.6E-03 2.9E-01 2.2E-02 4.4E-03
2-Nitroaniline 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
2-Nitrophenol 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
3,3'-Dichlorobenzidine 8.1E-06 9.7E-02 8.1E-02 8.1E-02 4.9E-03 2.1E-01 1.6E-02 3.2E-03
3,3'-Dimethylbenzidine 5.5E-05 6.6E-01 5.5E-01 5.5E-01 3.3E-02 1.4E+00 1.1E-01 2.2E-02
3-Methylcholanthrene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
3-Methylphenol & 4-Methylphenol 2.2E-06 2.6E-02 2.2E-02 2.2E-02 1.3E-03 5.7E-02 4.4E-03 8.8E-04
3-Nitroaniline 2.2E-06 2.6E-02 2.2E-02 2.2E-02 1.3E-03 5.7E-02 4.4E-03 8.8E-04
4,6-Dinitro-2-methylphenol 9.5E-06 1.1E-01 9.5E-02 9.5E-02 5.7E-03 2.5E-01 1.9E-02 3.8E-03
4-Aminobiphenyl 1.1E-05 1.3E-01 1.1E-01 1.1E-01 6.6E-03 2.9E-01 2.2E-02 4.4E-03
4-Bromophenyl phenyl ether 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
4-Chloro-3-methylphenol 6.8E-07 8.2E-03 6.8E-03 6.8E-03 4.1E-04 1.8E-02 1.4E-03 2.7E-04
4-Chloroaniline 6.6E-06 7.9E-02 6.6E-02 6.6E-02 4.0E-03 1.7E-01 1.3E-02 2.6E-03
4-Nitroaniline 2.2E-06 2.6E-02 2.2E-02 2.2E-02 1.3E-03 5.7E-02 4.4E-03 8.8E-04
4-Nitrophenol 3.6E-06 4.3E-02 3.6E-02 3.6E-02 2.2E-03 9.4E-02 7.2E-03 1.4E-03
7,12-Dimethylbenz(a)anthracene 5.6E-07 6.7E-03 5.6E-03 5.6E-03 3.4E-04 1.5E-02 1.1E-03 2.2E-04
Acenaphthene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Acenaphthylene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Acetophenone 2.7E-06 3.2E-02 2.7E-02 2.7E-02 1.6E-03 7.0E-02 5.4E-03 1.1E-03
Aniline 8.0E-06 9.6E-02 8.0E-02 8.0E-02 4.8E-03 2.1E-01 1.6E-02 3.2E-03
Analyte
Conservative
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/hour)M-225 Quantities
(lbs/hr)
TABLE OR APPENDIX ???
1.3 CLASS WASTE MATERIAL PER EVENT (1-HOUR)
CONSERVATIVE EMISSION RATES (LBS/HR)
ATK PROMONTORY, UTAH
PAGE 2 OF 5
1 2 3 4 5 1 2
Analyte
Conservative
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/hour)M-225 Quantities
(lbs/hr)
Anthracene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Benzidine 5.6E-05 6.7E-01 5.6E-01 5.6E-01 3.4E-02 1.5E+00 1.1E-01 2.2E-02
Benzo(a)anthracene 6.4E-07 7.7E-03 6.4E-03 6.4E-03 3.8E-04 1.7E-02 1.3E-03 2.6E-04
Benzo(a)pyrene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Benzo(b)fluoranthene 1.2E-06 1.4E-02 1.2E-02 1.2E-02 7.2E-04 3.1E-02 2.4E-03 4.8E-04
Benzo(ghi)perylene 6.8E-07 8.2E-03 6.8E-03 6.8E-03 4.1E-04 1.8E-02 1.4E-03 2.7E-04
Benzo(k)fluoranthene 1.8E-06 2.2E-02 1.8E-02 1.8E-02 1.1E-03 4.7E-02 3.6E-03 7.2E-04
Benzoic acid 6.2E-05 7.4E-01 6.2E-01 6.2E-01 3.7E-02 1.6E+00 1.2E-01 2.5E-02
Benzyl alcohol 3.8E-05 4.6E-01 3.8E-01 3.8E-01 2.3E-02 9.9E-01 7.6E-02 1.5E-02
bis(2-Chloroethoxy)methane 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
bis(2-Chloroethyl) ether 6.1E-07 7.3E-03 6.1E-03 6.1E-03 3.7E-04 1.6E-02 1.2E-03 2.4E-04
bis(2-Chloroisopropyl) ether 8.3E-07 1.0E-02 8.3E-03 8.3E-03 5.0E-04 2.2E-02 1.7E-03 3.3E-04
bis(2-Ethylhexyl) phthalate 1.1E-05 1.3E-01 1.1E-01 1.1E-01 6.6E-03 2.9E-01 2.2E-02 4.4E-03
Butyl benzyl phthalate 6.7E-07 8.0E-03 6.7E-03 6.7E-03 4.0E-04 1.7E-02 1.3E-03 2.7E-04
Carbazole 7.0E-07 8.4E-03 7.0E-03 7.0E-03 4.2E-04 1.8E-02 1.4E-03 2.8E-04
Chrysene 7.0E-07 8.4E-03 7.0E-03 7.0E-03 4.2E-04 1.8E-02 1.4E-03 2.8E-04
Dibenz(a,h)anthracene 6.6E-07 7.9E-03 6.6E-03 6.6E-03 4.0E-04 1.7E-02 1.3E-03 2.6E-04
Dibenzofuran 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Diethyl phthalate 8.0E-07 9.6E-03 8.0E-03 8.0E-03 4.8E-04 2.1E-02 1.6E-03 3.2E-04
Dimethyl phthalate 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Di-n-butyl phthalate 1.1E-05 1.3E-01 1.1E-01 1.1E-01 6.6E-03 2.9E-01 2.2E-02 4.4E-03
Di-n-octyl phthalate 3.7E-06 4.4E-02 3.7E-02 3.7E-02 2.2E-03 9.6E-02 7.4E-03 1.5E-03
Diphenylamine 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Ethyl methanesulfonate 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Fluoranthene 5.9E-07 7.1E-03 5.9E-03 5.9E-03 3.5E-04 1.5E-02 1.2E-03 2.4E-04
Fluorene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Hexachlorobenzene 4.7E-06 5.6E-02 4.7E-02 4.7E-02 2.8E-03 1.2E-01 9.4E-03 1.9E-03
Hexachlorobutadiene 8.1E-07 9.7E-03 8.1E-03 8.1E-03 4.9E-04 2.1E-02 1.6E-03 3.2E-04
Hexachlorocyclopentadiene 1.1E-05 1.3E-01 1.1E-01 1.1E-01 6.6E-03 2.9E-01 2.2E-02 4.4E-03
Hexachloroethane 5.9E-07 7.1E-03 5.9E-03 5.9E-03 3.5E-04 1.5E-02 1.2E-03 2.4E-04
Hexachloropropene 7.9E-07 9.5E-03 7.9E-03 7.9E-03 4.7E-04 2.1E-02 1.6E-03 3.2E-04
Indeno(1,2,3-cd)pyrene 5.9E-07 7.1E-03 5.9E-03 5.9E-03 3.5E-04 1.5E-02 1.2E-03 2.4E-04
Isophorone 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Methyl methanesulfonate 6.0E-07 7.2E-03 6.0E-03 6.0E-03 3.6E-04 1.6E-02 1.2E-03 2.4E-04
Naphthalene 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
Nitrobenzene 6.2E-07 7.4E-03 6.2E-03 6.2E-03 3.7E-04 1.6E-02 1.2E-03 2.5E-04
N-Nitro-o-toluidine 8.8E-06 1.1E-01 8.8E-02 8.8E-02 5.3E-03 2.3E-01 1.8E-02 3.5E-03
N-Nitrosodiethylamine 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
N-Nitrosodimethylamine 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
N-Nitrosodi-n-butylamine 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
N-Nitrosodi-n-propylamine 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
N-Nitrosodiphenylamine 9.5E-07 1.1E-02 9.5E-03 9.5E-03 5.7E-04 2.5E-02 1.9E-03 3.8E-04
N-Nitrosomethylethylamine 9.1E-07 1.1E-02 9.1E-03 9.1E-03 5.5E-04 2.4E-02 1.8E-03 3.6E-04
N-Nitrosomorpholine 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
o-Toluidine 7.0E-06 8.4E-02 7.0E-02 7.0E-02 4.2E-03 1.8E-01 1.4E-02 2.8E-03
p-Dimethylaminoazobenzene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Pentachlorobenzene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Pentachloroethane 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Pentachloronitrobenzene 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
Pentachlorophenol 2.7E-05 3.2E-01 2.7E-01 2.7E-01 1.6E-02 7.0E-01 5.4E-02 1.1E-02
Phenanthrene 7.0E-07 8.4E-03 7.0E-03 7.0E-03 4.2E-04 1.8E-02 1.4E-03 2.8E-04
Phenol 2.4E-06 2.9E-02 2.4E-02 2.4E-02 1.4E-03 6.2E-02 4.8E-03 9.6E-04
Pyrene 5.8E-07 7.0E-03 5.8E-03 5.8E-03 3.5E-04 1.5E-02 1.2E-03 2.3E-04
Pyridine 8.1E-07 9.7E-03 8.1E-03 8.1E-03 4.9E-04 2.1E-02 1.6E-03 3.2E-04

Dioxins/Furans
2,3,7,8-TCDD 2.3E-12 2.8E-08 2.3E-08 2.3E-08 1.4E-09 6.0E-08 4.6E-09 9.2E-10
1,2,3,7,8-PeCDD 6.7E-12 8.0E-08 6.7E-08 6.7E-08 4.0E-09 1.7E-07 1.3E-08 2.7E-09
1,2,3,4,7,8-HxCDD 3.5E-12 4.2E-08 3.5E-08 3.5E-08 2.1E-09 9.1E-08 7.0E-09 1.4E-09
1,2,3,6,7,8-HxCDD 8.9E-12 1.1E-07 8.9E-08 8.9E-08 5.3E-09 2.3E-07 1.8E-08 3.6E-09
1,2,3,7,8,9-HxCDD 6.1E-12 7.3E-08 6.1E-08 6.1E-08 3.7E-09 1.6E-07 1.2E-08 2.4E-09
1,2,3,4,6,7,8-HpCDD 2.9E-11 3.5E-07 2.9E-07 2.9E-07 1.7E-08 7.5E-07 5.8E-08 1.2E-08
OCDD 3.7E-11 4.4E-07 3.7E-07 3.7E-07 2.2E-08 9.6E-07 7.4E-08 1.5E-08
2,3,7,8-TCDF 4.0E-11 4.8E-07 4.0E-07 4.0E-07 2.4E-08 1.0E-06 8.0E-08 1.6E-08
1,2,3,7,8-PeCDF 8.0E-11 9.6E-07 8.0E-07 8.0E-07 4.8E-08 2.1E-06 1.6E-07 3.2E-08
2,3,4,7,8-PeCDF 1.6E-10 1.9E-06 1.6E-06 1.6E-06 9.6E-08 4.2E-06 3.2E-07 6.4E-08
1,2,3,4,7,8-HxCDF 2.6E-10 3.1E-06 2.6E-06 2.6E-06 1.6E-07 6.8E-06 5.2E-07 1.0E-07
1,2,3,6,7,8-HxCDF 1.6E-10 1.9E-06 1.6E-06 1.6E-06 9.6E-08 4.2E-06 3.2E-07 6.4E-08
2,3,4,6,7,8-HxCDF 1.9E-10 2.3E-06 1.9E-06 1.9E-06 1.1E-07 4.9E-06 3.8E-07 7.6E-08
1,2,3,7,8,9-HxCDF 1.2E-10 1.4E-06 1.2E-06 1.2E-06 7.2E-08 3.1E-06 2.4E-07 4.8E-08
1,2,3,4,6,7,8-HpCDF 7.3E-10 8.8E-06 7.3E-06 7.3E-06 4.4E-07 1.9E-05 1.5E-06 2.9E-07
TABLE OR APPENDIX ???
1.3 CLASS WASTE MATERIAL PER EVENT (1-HOUR)
CONSERVATIVE EMISSION RATES (LBS/HR)
ATK PROMONTORY, UTAH
PAGE 3 OF 5
1 2 3 4 5 1 2
Analyte
Conservative
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/hour)M-225 Quantities
(lbs/hr)
1,2,3,4,7,8,9-HpCDF 1.9E-10 2.3E-06 1.9E-06 1.9E-06 1.1E-07 4.9E-06 3.8E-07 7.6E-08
OCDF 5.3E-10 6.4E-06 5.3E-06 5.3E-06 3.2E-07 1.4E-05 1.1E-06 2.1E-07

Carbonyls
2,5-Dimethylbenzaldehyde 2.7E-05 3.2E-01 2.7E-01 2.7E-01 1.6E-02 7.0E-01 5.4E-02 1.1E-02
Acetaldehyde 9.3E-05 1.1E+00 9.3E-01 9.3E-01 5.6E-02 2.4E+00 1.9E-01 3.7E-02
Acetone 3.1E-05 3.7E-01 3.1E-01 3.1E-01 1.9E-02 8.1E-01 6.2E-02 1.2E-02
Benzaldehyde 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
Crotonaldehyde 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
Formaldehyde 4.7E-05 5.6E-01 4.7E-01 4.7E-01 2.8E-02 1.2E+00 9.4E-02 1.9E-02
Hexanal 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
Isopentanal 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
m,p-Tolualdehyde 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
MEK/Butyraldehydes 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
o-Tolualdehyde 4.0E-05 4.8E-01 4.0E-01 4.0E-01 2.4E-02 1.0E+00 8.0E-02 1.6E-02
Pentanal 1.7E-05 2.0E-01 1.7E-01 1.7E-01 1.0E-02 4.4E-01 3.4E-02 6.8E-03
Propanal 5.2E-05 6.2E-01 5.2E-01 5.2E-01 3.1E-02 1.4E+00 1.0E-01 2.1E-02
HCl/Cl2/NH3
HCl 1.8E-02 2.2E+02 1.8E+02 1.8E+02 1.1E+01 4.7E+02 3.6E+01 7.2E+00
Cl2 1.2E-02 1.4E+02 1.2E+02 1.2E+02 7.2E+00 3.1E+02 2.4E+01 4.8E+00
NH3 3.2E-05 3.8E-01 3.2E-01 3.2E-01 1.9E-02 8.3E-01 6.4E-02 1.3E-02
HCN 2.2E-05 2.6E-01 2.2E-01 #REF!1.3E-02 5.7E-01 4.4E-02 8.8E-03

VOCs
TNMOC 9.4E-04 1.1E+01 9.4E+00 9.4E+00 5.6E-01 2.4E+01 1.9E+00 3.8E-01
1,1,1-Trichloroethane 8.9E-07 1.1E-02 8.9E-03 8.9E-03 5.3E-04 2.3E-02 1.8E-03 3.6E-04
1,1,2,2-Tetrachloroethane 4.2E-07 5.0E-03 4.2E-03 4.2E-03 2.5E-04 1.1E-02 8.4E-04 1.7E-04
1,1,2-Trichloroethane 7.3E-07 8.8E-03 7.3E-03 7.3E-03 4.4E-04 1.9E-02 1.5E-03 2.9E-04
1,1-Dichloroethane 3.2E-07 3.8E-03 3.2E-03 3.2E-03 1.9E-04 8.3E-03 6.4E-04 1.3E-04
1,1-Dichloroethene 4.3E-07 5.2E-03 4.3E-03 4.3E-03 2.6E-04 1.1E-02 8.6E-04 1.7E-04
1,2,3-Trimethylbenzene 4.2E-07 5.0E-03 4.2E-03 4.2E-03 2.5E-04 1.1E-02 8.4E-04 1.7E-04
1,2,4-Trichlorobenzene 1.3E-06 1.6E-02 1.3E-02 1.3E-02 7.8E-04 3.4E-02 2.6E-03 5.2E-04
1,2,4-Trimethylbenzene 5.2E-06 6.2E-02 5.2E-02 5.2E-02 3.1E-03 1.4E-01 1.0E-02 2.1E-03
1,2-Dibromomethane (EDB)8.9E-07 1.1E-02 8.9E-03 8.9E-03 5.3E-04 2.3E-02 1.8E-03 3.6E-04
1,2-Dichlorobenzene 4.8E-07 5.8E-03 4.8E-03 4.8E-03 2.9E-04 1.2E-02 9.6E-04 1.9E-04
1,2-Dichloroethane 5.4E-07 6.5E-03 5.4E-03 5.4E-03 3.2E-04 1.4E-02 1.1E-03 2.2E-04
1,2-Dichloropropane 3.7E-07 4.4E-03 3.7E-03 3.7E-03 2.2E-04 9.6E-03 7.4E-04 1.5E-04
1,3,5-Trimethylbenzene 2.0E-06 2.4E-02 2.0E-02 2.0E-02 1.2E-03 5.2E-02 4.0E-03 8.0E-04
1,3-Butadiene 2.4E-05 2.9E-01 2.4E-01 2.4E-01 1.4E-02 6.2E-01 4.8E-02 9.6E-03
1,3-Dichlorobenzene 4.4E-07 5.3E-03 4.4E-03 4.4E-03 2.6E-04 1.1E-02 8.8E-04 1.8E-04
1,3-Diethylbenzene 5.0E-07 6.0E-03 5.0E-03 5.0E-03 3.0E-04 1.3E-02 1.0E-03 2.0E-04
1,4-Dichlorobenzene 7.3E-07 8.8E-03 7.3E-03 7.3E-03 4.4E-04 1.9E-02 1.5E-03 2.9E-04
1,4-Diethylbenzene 6.7E-07 8.0E-03 6.7E-03 6.7E-03 4.0E-04 1.7E-02 1.3E-03 2.7E-04
1,4-Dioxane 6.4E-07 7.7E-03 6.4E-03 6.4E-03 3.8E-04 1.7E-02 1.3E-03 2.6E-04
1-Butene 2.2E-05 2.6E-01 2.2E-01 2.2E-01 1.3E-02 5.7E-01 4.4E-02 8.8E-03
1-Hexene 2.0E-05 2.4E-01 2.0E-01 2.0E-01 1.2E-02 5.2E-01 4.0E-02 8.0E-03
1-Pentene 1.2E-05 1.4E-01 1.2E-01 1.2E-01 7.2E-03 3.1E-01 2.4E-02 4.8E-03
2,2,4-Trimethylpentane 2.3E-06 2.8E-02 2.3E-02 2.3E-02 1.4E-03 6.0E-02 4.6E-03 9.2E-04
2,2-Dimethylbutane 8.8E-07 1.1E-02 8.8E-03 8.8E-03 5.3E-04 2.3E-02 1.8E-03 3.5E-04
2,3,4-Trimethylpentane 2.8E-07 3.4E-03 2.8E-03 2.8E-03 1.7E-04 7.3E-03 5.6E-04 1.1E-04
2,3-Dimethylbutane 2.9E-06 3.5E-02 2.9E-02 2.9E-02 1.7E-03 7.5E-02 5.8E-03 1.2E-03
2,3-Dimethylpentane 2.7E-06 3.2E-02 2.7E-02 2.7E-02 1.6E-03 7.0E-02 5.4E-03 1.1E-03
2,4-Dimethylpentane 1.1E-06 1.3E-02 1.1E-02 1.1E-02 6.6E-04 2.9E-02 2.2E-03 4.4E-04
2-Butanone (MEK)3.9E-06 4.7E-02 3.9E-02 3.9E-02 2.3E-03 1.0E-01 7.8E-03 1.6E-03
2-Ethyltoluene 4.5E-07 5.4E-03 4.5E-03 4.5E-03 2.7E-04 1.2E-02 9.0E-04 1.8E-04
2-Hexanone 8.7E-07 1.0E-02 8.7E-03 8.7E-03 5.2E-04 2.3E-02 1.7E-03 3.5E-04
2-Methylheptane 2.7E-06 3.2E-02 2.7E-02 2.7E-02 1.6E-03 7.0E-02 5.4E-03 1.1E-03
2-Methylhexane 4.4E-06 5.3E-02 4.4E-02 4.4E-02 2.6E-03 1.1E-01 8.8E-03 1.8E-03
2-Methylpentane 1.1E-05 1.3E-01 1.1E-01 1.1E-01 6.6E-03 2.9E-01 2.2E-02 4.4E-03
2-Nitropropane 2.8E-06 3.4E-02 2.8E-02 2.8E-02 1.7E-03 7.3E-02 5.6E-03 1.1E-03
2-Propanol 3.0E-07 3.6E-03 3.0E-03 3.0E-03 1.8E-04 7.8E-03 6.0E-04 1.2E-04
3-Chloropropene 4.7E-06 5.6E-02 4.7E-02 4.7E-02 2.8E-03 1.2E-01 9.4E-03 1.9E-03
3-Ethyltoluene 4.8E-06 5.8E-02 4.8E-02 4.8E-02 2.9E-03 1.2E-01 9.6E-03 1.9E-03
3-Methylheptane 3.5E-06 4.2E-02 3.5E-02 3.5E-02 2.1E-03 9.1E-02 7.0E-03 1.4E-03
3-Methylhexane 5.2E-06 6.2E-02 5.2E-02 5.2E-02 3.1E-03 1.4E-01 1.0E-02 2.1E-03
3-Methylpentane 7.1E-06 8.5E-02 7.1E-02 7.1E-02 4.3E-03 1.8E-01 1.4E-02 2.8E-03
4-Ethyltoluene 5.3E-06 6.4E-02 5.3E-02 5.3E-02 3.2E-03 1.4E-01 1.1E-02 2.1E-03
4-Methyl-2-pentanone 7.0E-07 8.4E-03 7.0E-03 7.0E-03 4.2E-04 1.8E-02 1.4E-03 2.8E-04
Acetone 2.4E-05 2.9E-01 2.4E-01 2.4E-01 1.4E-02 6.2E-01 4.8E-02 9.6E-03
TABLE OR APPENDIX ???
1.3 CLASS WASTE MATERIAL PER EVENT (1-HOUR)
CONSERVATIVE EMISSION RATES (LBS/HR)
ATK PROMONTORY, UTAH
PAGE 4 OF 5
1 2 3 4 5 1 2
Analyte
Conservative
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/hour)M-225 Quantities
(lbs/hr)
Acetonitrile 1.9E-05 2.3E-01 1.9E-01 1.9E-01 1.1E-02 4.9E-01 3.8E-02 7.6E-03
Acetylene 9.4E-05 1.1E+00 9.4E-01 9.4E-01 5.6E-02 2.4E+00 1.9E-01 3.8E-02
Acrylonitrile 1.6E-05 1.9E-01 1.6E-01 1.6E-01 9.6E-03 4.2E-01 3.2E-02 6.4E-03
alpha-Chlorotoluene 5.7E-07 6.8E-03 5.7E-03 5.7E-03 3.4E-04 1.5E-02 1.1E-03 2.3E-04
Benzene 4.7E-05 5.6E-01 4.7E-01 4.7E-01 2.8E-02 1.2E+00 9.4E-02 1.9E-02
Bromodichloromethane 7.8E-07 9.4E-03 7.8E-03 7.8E-03 4.7E-04 2.0E-02 1.6E-03 3.1E-04
Bromoform 1.3E-06 1.6E-02 1.3E-02 1.3E-02 7.8E-04 3.4E-02 2.6E-03 5.2E-04
Bromomethane 6.2E-07 7.4E-03 6.2E-03 6.2E-03 3.7E-04 1.6E-02 1.2E-03 2.5E-04
Butane 1.8E-05 2.2E-01 1.8E-01 1.8E-01 1.1E-02 4.7E-01 3.6E-02 7.2E-03
Carbon Disulfide 9.8E-06 1.2E-01 9.8E-02 9.8E-02 5.9E-03 2.5E-01 2.0E-02 3.9E-03
Carbon Tetrachloride 1.5E-05 1.8E-01 1.5E-01 1.5E-01 9.0E-03 3.9E-01 3.0E-02 6.0E-03
Chloroacetonitrile 1.1E-06 1.3E-02 1.1E-02 1.1E-02 6.6E-04 2.9E-02 2.2E-03 4.4E-04
Chlorobenzene 2.5E-06 3.0E-02 2.5E-02 2.5E-02 1.5E-03 6.5E-02 5.0E-03 1.0E-03
Chloroethane 2.6E-07 3.1E-03 2.6E-03 2.6E-03 1.6E-04 6.8E-03 5.2E-04 1.0E-04
Chloroform 6.1E-06 7.3E-02 6.1E-02 6.1E-02 3.7E-03 1.6E-01 1.2E-02 2.4E-03
Chloromethane 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
cis-1,2-Dichloroethene 4.6E-07 5.5E-03 4.6E-03 4.6E-03 2.8E-04 1.2E-02 9.2E-04 1.8E-04
cis-1,3-Dichloropropene 1.3E-06 1.6E-02 1.3E-02 1.3E-02 7.8E-04 3.4E-02 2.6E-03 5.2E-04
cis-2-Butene 1.7E-06 2.0E-02 1.7E-02 1.7E-02 1.0E-03 4.4E-02 3.4E-03 6.8E-04
cis-2-Pentene 3.3E-07 4.0E-03 3.3E-03 3.3E-03 2.0E-04 8.6E-03 6.6E-04 1.3E-04
Cumene 4.2E-07 5.0E-03 4.2E-03 4.2E-03 2.5E-04 1.1E-02 8.4E-04 1.7E-04
Cyclohexane 2.5E-06 3.0E-02 2.5E-02 2.5E-02 1.5E-03 6.5E-02 5.0E-03 1.0E-03
Cyclopentane 1.8E-06 2.2E-02 1.8E-02 1.8E-02 1.1E-03 4.7E-02 3.6E-03 7.2E-04
Decane 1.7E-05 2.0E-01 1.7E-01 1.7E-01 1.0E-02 4.4E-01 3.4E-02 6.8E-03
Dibromochloromethane 8.8E-07 1.1E-02 8.8E-03 8.8E-03 5.3E-04 2.3E-02 1.8E-03 3.5E-04
Ethane 2.1E-05 2.5E-01 2.1E-01 2.1E-01 1.3E-02 5.5E-01 4.2E-02 8.4E-03
Ethanol 1.6E-06 1.9E-02 1.6E-02 1.6E-02 9.6E-04 4.2E-02 3.2E-03 6.4E-04
Ethene 1.8E-04 2.2E+00 1.8E+00 1.8E+00 1.1E-01 4.7E+00 3.6E-01 7.2E-02
Ethyl benzene 2.8E-06 3.4E-02 2.8E-02 2.8E-02 1.7E-03 7.3E-02 5.6E-03 1.1E-03
Ethyl ether 2.5E-06 3.0E-02 2.5E-02 2.5E-02 1.5E-03 6.5E-02 5.0E-03 1.0E-03
Ethyl Methacrylate 1.6E-06 1.9E-02 1.6E-02 1.6E-02 9.6E-04 4.2E-02 3.2E-03 6.4E-04
Heptane 7.2E-06 8.6E-02 7.2E-02 7.2E-02 4.3E-03 1.9E-01 1.4E-02 2.9E-03
Hexachlorobutadiene 1.7E-06 2.0E-02 1.7E-02 1.7E-02 1.0E-03 4.4E-02 3.4E-03 6.8E-04
Hexane 9.8E-06 1.2E-01 9.8E-02 9.8E-02 5.9E-03 2.5E-01 2.0E-02 3.9E-03
Isobutane 2.8E-06 3.4E-02 2.8E-02 2.8E-02 1.7E-03 7.3E-02 5.6E-03 1.1E-03
Isopentane 2.0E-05 2.4E-01 2.0E-01 2.0E-01 1.2E-02 5.2E-01 4.0E-02 8.0E-03
m,p-Xylene 1.1E-05 1.3E-01 1.1E-01 1.1E-01 6.6E-03 2.9E-01 2.2E-02 4.4E-03
Methacrylonitrile 4.9E-06 5.9E-02 4.9E-02 4.9E-02 2.9E-03 1.3E-01 9.8E-03 2.0E-03
Methyl Acrylate 1.2E-06 1.4E-02 1.2E-02 1.2E-02 7.2E-04 3.1E-02 2.4E-03 4.8E-04
Methyl Methacrylate 1.6E-06 1.9E-02 1.6E-02 1.6E-02 9.6E-04 4.2E-02 3.2E-03 6.4E-04
Methyl tert-butyl ether 4.2E-07 5.0E-03 4.2E-03 4.2E-03 2.5E-04 1.1E-02 8.4E-04 1.7E-04
Methylcyclohexane 6.1E-06 7.3E-02 6.1E-02 6.1E-02 3.7E-03 1.6E-01 1.2E-02 2.4E-03
Methylcyclopentane 5.6E-06 6.7E-02 5.6E-02 5.6E-02 3.4E-03 1.5E-01 1.1E-02 2.2E-03
Methylene chloride 7.1E-06 8.5E-02 7.1E-02 7.1E-02 4.3E-03 1.8E-01 1.4E-02 2.8E-03
n-Butylchloride 1.2E-05 1.4E-01 1.2E-01 1.2E-01 7.2E-03 3.1E-01 2.4E-02 4.8E-03
Nonane 1.3E-05 1.6E-01 1.3E-01 1.3E-01 7.8E-03 3.4E-01 2.6E-02 5.2E-03
Octane 7.5E-06 9.0E-02 7.5E-02 7.5E-02 4.5E-03 2.0E-01 1.5E-02 3.0E-03
o-Xylene 3.5E-06 4.2E-02 3.5E-02 3.5E-02 2.1E-03 9.1E-02 7.0E-03 1.4E-03
Pentane 1.9E-05 2.3E-01 1.9E-01 1.9E-01 1.1E-02 4.9E-01 3.8E-02 7.6E-03
Propane 8.7E-06 1.0E-01 8.7E-02 8.7E-02 5.2E-03 2.3E-01 1.7E-02 3.5E-03
Propylbenzene 1.0E-06 1.2E-02 1.0E-02 1.0E-02 6.0E-04 2.6E-02 2.0E-03 4.0E-04
Propylene 4.9E-05 5.9E-01 4.9E-01 4.9E-01 2.9E-02 1.3E+00 9.8E-02 2.0E-02
Styrene 9.9E-07 1.2E-02 9.9E-03 9.9E-03 5.9E-04 2.6E-02 2.0E-03 4.0E-04
Tetrachloroethene 2.5E-06 3.0E-02 2.5E-02 2.5E-02 1.5E-03 6.5E-02 5.0E-03 1.0E-03
Tetrahydrofuran 9.0E-07 1.1E-02 9.0E-03 9.0E-03 5.4E-04 2.3E-02 1.8E-03 3.6E-04
Toluene 1.9E-05 2.3E-01 1.9E-01 1.9E-01 1.1E-02 4.9E-01 3.8E-02 7.6E-03
trans-1,2-Dichloroethene 7.2E-07 8.6E-03 7.2E-03 7.2E-03 4.3E-04 1.9E-02 1.4E-03 2.9E-04
trans-1,3-Dichloropropene 6.1E-07 7.3E-03 6.1E-03 6.1E-03 3.7E-04 1.6E-02 1.2E-03 2.4E-04
trans-2-butene 7.7E-06 9.2E-02 7.7E-02 7.7E-02 4.6E-03 2.0E-01 1.5E-02 3.1E-03
trans-2-Pentene 1.7E-06 2.0E-02 1.7E-02 1.7E-02 1.0E-03 4.4E-02 3.4E-03 6.8E-04
Trichloroethene 9.4E-07 1.1E-02 9.4E-03 9.4E-03 5.6E-04 2.4E-02 1.9E-03 3.8E-04
Undecane 1.2E-05 1.4E-01 1.2E-01 1.2E-01 7.2E-03 3.1E-01 2.4E-02 4.8E-03
Vinyl chloride 7.6E-06 9.1E-02 7.6E-02 7.6E-02 4.6E-03 2.0E-01 1.5E-02 3.0E-03

CEM
CO2 7.20E-01 8.6E+03 7.2E+03 7.2E+03 4.3E+02 1.9E+04 1.4E+03 2.9E+02
CO 6.40E-03 7.7E+01 6.4E+01 6.4E+01 3.8E+00 1.7E+02 1.3E+01 2.6E+00
NOX 6.40E-03 7.7E+01 6.4E+01 6.4E+01 3.8E+00 1.7E+02 1.3E+01 2.6E+00
SO2 5.00E-04 6.0E+00 5.0E+00 5.0E+00 3.0E-01 1.3E+01 1.0E+00 2.0E-01
Highlighted analytes were not detected during the Bang Box testing program
TABLE OR APPENDIX ???
1.3 CLASS WASTE MATERIAL PER EVENT (1-HOUR)
CONSERVATIVE EMISSION RATES (LBS/HR)
ATK PROMONTORY, UTAH
PAGE 5 OF 5
1 2 3 4 5 1 2
Analyte
Conservative
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/hour)M-225 Quantities
(lbs/hr)
CEM - Continuous Emissions Monitoring
CL2 - chlorine
CO - carbon monoxide
CO2 - carbon dioxide
HCL - hydrogen chloride
HCN - hydrogen cyanide
NH3 - ammonia
NOX - nitrogen oxide
OCDD - 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin
OCDF - 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-furan
PM10 - particulate matter less than 10 microns in aerodynamic diameter
PM2.5 - particulate matter less than 2.5 microns in aerodynamic diameter
SO2 - sulfur dioxide
SVOCs - semi-volatile organic compounds
TNMOC - total non-methane organic carbon
TSP - Total suspended particulates
VOCs - volatile organic compounds
TABLE OR APPENDIX 3-???
1.3 CLASS WASTE MATERIAL
CONSERVATIVE ANNUAL EMISSION RATES (LBS/YR)
ATK PROMONTORY, UTAH
PAGE 1 OF 5
1 2 3 4 5 1 2
Particulates
TSP 1.5E-01 5.6E+05 7.8E+04 7.8E+04 5.4E+02 1.2E+04 7.2E+03 3.6E+02
PM10 1.2E-01 4.5E+05 6.2E+04 6.2E+04 4.3E+02 9.4E+03 5.8E+03 2.9E+02
PM2.5 6.0E-02 2.2E+05 3.1E+04 3.1E+04 2.2E+02 4.7E+03 2.9E+03 1.4E+02
Metals
Aluminum 4.0E-02 1.5E+05 2.1E+04 2.1E+04 1.4E+02 3.1E+03 1.9E+03 9.6E+01
Antimony 2.9E-05 1.1E+02 1.5E+01 1.5E+01 1.0E-01 2.3E+00 1.4E+00 7.0E-02
Arsenic 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 1.3E-03
Barium 9.8E-06 3.7E+01 5.1E+00 5.1E+00 3.5E-02 7.6E-01 4.7E-01 2.4E-02
Cadmium 6.1E-07 2.3E+00 3.2E-01 3.2E-01 2.2E-03 4.8E-02 2.9E-02 1.5E-03
Chromium 2.0E-05 7.5E+01 1.0E+01 1.0E+01 7.2E-02 1.6E+00 9.6E-01 4.8E-02
Cobalt 6.1E-07 2.3E+00 3.2E-01 3.2E-01 2.2E-03 4.8E-02 2.9E-02 1.5E-03
Copper 2.5E-05 9.4E+01 1.3E+01 1.3E+01 9.0E-02 2.0E+00 1.2E+00 6.0E-02
Lead 4.1E-05 1.5E+02 2.1E+01 2.1E+01 1.5E-01 3.2E+00 2.0E+00 9.8E-02
Magnesium 8.2E-05 3.1E+02 4.3E+01 4.3E+01 3.0E-01 6.4E+00 3.9E+00 2.0E-01
Manganese 9.4E-05 3.5E+02 4.9E+01 4.9E+01 3.4E-01 7.3E+00 4.5E+00 2.3E-01
Mercury 7.4E-08 2.8E-01 3.8E-02 3.8E-02 2.7E-04 5.8E-03 3.6E-03 1.8E-04
Nickel 5.8E-05 2.2E+02 3.0E+01 3.0E+01 2.1E-01 4.5E+00 2.8E+00 1.4E-01
Phosphorus 1.1E-04 4.1E+02 5.7E+01 5.7E+01 4.0E-01 8.6E+00 5.3E+00 2.6E-01
Selenium 1.6E-06 6.0E+00 8.3E-01 8.3E-01 5.8E-03 1.2E-01 7.7E-02 3.8E-03
Silver 1.2E-06 4.5E+00 6.2E-01 6.2E-01 4.3E-03 9.4E-02 5.8E-02 2.9E-03
Thallium 4.3E-06 1.6E+01 2.2E+00 2.2E+00 1.5E-02 3.4E-01 2.1E-01 1.0E-02
Zinc 3.5E-05 1.3E+02 1.8E+01 1.8E+01 1.3E-01 2.7E+00 1.7E+00 8.4E-02
Perchlorate 4.9E-07 5.2E-02 2.5E-01 2.5E-01 1.8E-03 3.8E-02 2.4E-02 1.2E-03

SVOCs
1,2,4,5-Tetrachlorobenzene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 1.3E-03
1,2,4-Trichlorobenzene 6.5E-07 2.4E+00 3.4E-01 3.4E-01 2.3E-03 5.1E-02 3.1E-02 2.6E-04
1,2-Dichlorobenzene 5.6E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.4E-02 2.7E-02 2.2E-04
1,3,5-Trinitrobenzene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
1,3-Dichlorobenzene 6.2E-07 2.3E+00 3.2E-01 3.2E-01 2.2E-03 4.8E-02 3.0E-02 2.5E-04
1,3-Dinitrobenzene 5.7E-07 2.1E+00 3.0E-01 3.0E-01 2.1E-03 4.4E-02 2.7E-02 2.3E-04
1,4-Dichlorobenzene 5.8E-07 2.2E+00 3.0E-01 3.0E-01 2.1E-03 4.5E-02 2.8E-02 2.3E-04
1-Chloronaphthalene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
1-Naphthylamine 1.1E-05 4.1E+01 5.7E+00 5.7E+00 4.0E-02 8.6E-01 5.3E-01 4.4E-03
2,3,4,6-Tetrachlorophenol 7.1E-07 2.7E+00 3.7E-01 3.7E-01 2.6E-03 5.5E-02 3.4E-02 2.8E-04
2,4,5-Trichlorophenol 1.4E-06 5.2E+00 7.3E-01 7.3E-01 5.0E-03 1.1E-01 6.7E-02 5.6E-04
2,4,6-Trichlorophenol 1.3E-06 4.9E+00 6.8E-01 6.8E-01 4.7E-03 1.0E-01 6.2E-02 5.2E-04
2,4-Dichlorophenol 9.3E-07 3.5E+00 4.8E-01 4.8E-01 3.3E-03 7.3E-02 4.5E-02 3.7E-04
2,4-Dimethylphenol 6.9E-06 2.6E+01 3.6E+00 3.6E+00 2.5E-02 5.4E-01 3.3E-01 2.8E-03
2,4-Dinitrophenol 2.4E-05 9.0E+01 1.2E+01 1.2E+01 8.6E-02 1.9E+00 1.2E+00 9.6E-03
2,4-Dinitrotoluene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
2,6-Dichlorophenol 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
2,6-Dinitrotoluene 5.6E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.4E-02 2.7E-02 2.2E-04
2-Acetylaminofluorene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
2-Chloronaphthalene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
2-Chlorophenol 1.9E-06 7.1E+00 9.9E-01 9.9E-01 6.8E-03 1.5E-01 9.1E-02 7.6E-04
2-Methylnaphthalene 3.6E-06 1.3E+01 1.9E+00 1.9E+00 1.3E-02 2.8E-01 1.7E-01 1.4E-03
2-Methylphenol 3.3E-06 1.2E+01 1.7E+00 1.7E+00 1.2E-02 2.6E-01 1.6E-01 1.3E-03
2-Naphthylamine 1.1E-05 4.1E+01 5.7E+00 5.7E+00 4.0E-02 8.6E-01 5.3E-01 4.4E-03
2-Nitroaniline 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
2-Nitrophenol 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
3,3'-Dichlorobenzidine 8.1E-06 3.0E+01 4.2E+00 4.2E+00 2.9E-02 6.3E-01 3.9E-01 3.2E-03
3,3'-Dimethylbenzidine 5.5E-05 2.1E+02 2.9E+01 2.9E+01 2.0E-01 4.3E+00 2.6E+00 2.2E-02
3-Methylcholanthrene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
3-Methylphenol & 4-Methylphenol 2.2E-06 8.2E+00 1.1E+00 1.1E+00 7.9E-03 1.7E-01 1.1E-01 8.8E-04
3-Nitroaniline 2.2E-06 8.2E+00 1.1E+00 1.1E+00 7.9E-03 1.7E-01 1.1E-01 8.8E-04
4,6-Dinitro-2-methylphenol 9.5E-06 3.6E+01 4.9E+00 4.9E+00 3.4E-02 7.4E-01 4.6E-01 3.8E-03
4-Aminobiphenyl 1.1E-05 4.1E+01 5.7E+00 5.7E+00 4.0E-02 8.6E-01 5.3E-01 4.4E-03
4-Bromophenyl phenyl ether 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
4-Chloro-3-methylphenol 6.8E-07 2.5E+00 3.5E-01 3.5E-01 2.4E-03 5.3E-02 3.3E-02 2.7E-04
4-Chloroaniline 6.6E-06 2.5E+01 3.4E+00 3.4E+00 2.4E-02 5.1E-01 3.2E-01 2.6E-03
4-Nitroaniline 2.2E-06 8.2E+00 1.1E+00 1.1E+00 7.9E-03 1.7E-01 1.1E-01 8.8E-04
4-Nitrophenol 3.6E-06 1.3E+01 1.9E+00 1.9E+00 1.3E-02 2.8E-01 1.7E-01 1.4E-03
7,12-Dimethylbenz(a)anthracene 5.6E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.4E-02 2.7E-02 2.2E-04
Acenaphthene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Acenaphthylene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Acetophenone 2.7E-06 1.0E+01 1.4E+00 1.4E+00 9.7E-03 2.1E-01 1.3E-01 1.1E-03
Aniline 8.0E-06 3.0E+01 4.2E+00 4.2E+00 2.9E-02 6.2E-01 3.8E-01 3.2E-03
Analyte
Conservative
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/year)M-225 Quantities
(lbs/year)
TABLE OR APPENDIX 3-???
1.3 CLASS WASTE MATERIAL
CONSERVATIVE ANNUAL EMISSION RATES (LBS/YR)
ATK PROMONTORY, UTAH
PAGE 2 OF 5
1 2 3 4 5 1 2
Analyte
Conservative
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/year)M-225 Quantities
(lbs/year)
Anthracene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Benzidine 5.6E-05 2.1E+02 2.9E+01 2.9E+01 2.0E-01 4.4E+00 2.7E+00 2.2E-02
Benzo(a)anthracene 6.4E-07 2.4E+00 3.3E-01 3.3E-01 2.3E-03 5.0E-02 3.1E-02 2.6E-04
Benzo(a)pyrene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Benzo(b)fluoranthene 1.2E-06 4.5E+00 6.2E-01 6.2E-01 4.3E-03 9.4E-02 5.8E-02 4.8E-04
Benzo(ghi)perylene 6.8E-07 2.5E+00 3.5E-01 3.5E-01 2.4E-03 5.3E-02 3.3E-02 2.7E-04
Benzo(k)fluoranthene 1.8E-06 6.7E+00 9.4E-01 9.4E-01 6.5E-03 1.4E-01 8.6E-02 7.2E-04
Benzoic acid 6.2E-05 2.3E+02 3.2E+01 3.2E+01 2.2E-01 4.8E+00 3.0E+00 2.5E-02
Benzyl alcohol 3.8E-05 1.4E+02 2.0E+01 2.0E+01 1.4E-01 3.0E+00 1.8E+00 1.5E-02
bis(2-Chloroethoxy)methane 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
bis(2-Chloroethyl) ether 6.1E-07 2.3E+00 3.2E-01 3.2E-01 2.2E-03 4.8E-02 2.9E-02 2.4E-04
bis(2-Chloroisopropyl) ether 8.3E-07 3.1E+00 4.3E-01 4.3E-01 3.0E-03 6.5E-02 4.0E-02 3.3E-04
bis(2-Ethylhexyl) phthalate 1.1E-05 4.1E+01 5.7E+00 5.7E+00 4.0E-02 8.6E-01 5.3E-01 4.4E-03
Butyl benzyl phthalate 6.7E-07 2.5E+00 3.5E-01 3.5E-01 2.4E-03 5.2E-02 3.2E-02 2.7E-04
Carbazole 7.0E-07 2.6E+00 3.6E-01 3.6E-01 2.5E-03 5.5E-02 3.4E-02 2.8E-04
Chrysene 7.0E-07 2.6E+00 3.6E-01 3.6E-01 2.5E-03 5.5E-02 3.4E-02 2.8E-04
Dibenz(a,h)anthracene 6.6E-07 2.5E+00 3.4E-01 3.4E-01 2.4E-03 5.1E-02 3.2E-02 2.6E-04
Dibenzofuran 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Diethyl phthalate 8.0E-07 3.0E+00 4.2E-01 4.2E-01 2.9E-03 6.2E-02 3.8E-02 3.2E-04
Dimethyl phthalate 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Di-n-butyl phthalate 1.1E-05 4.1E+01 5.7E+00 5.7E+00 4.0E-02 8.6E-01 5.3E-01 4.4E-03
Di-n-octyl phthalate 3.7E-06 1.4E+01 1.9E+00 1.9E+00 1.3E-02 2.9E-01 1.8E-01 1.5E-03
Diphenylamine 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Ethyl methanesulfonate 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Fluoranthene 5.9E-07 2.2E+00 3.1E-01 3.1E-01 2.1E-03 4.6E-02 2.8E-02 2.4E-04
Fluorene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Hexachlorobenzene 4.7E-06 1.8E+01 2.4E+00 2.4E+00 1.7E-02 3.7E-01 2.3E-01 1.9E-03
Hexachlorobutadiene 8.1E-07 3.0E+00 4.2E-01 4.2E-01 2.9E-03 6.3E-02 3.9E-02 3.2E-04
Hexachlorocyclopentadiene 1.1E-05 4.1E+01 5.7E+00 5.7E+00 4.0E-02 8.6E-01 5.3E-01 4.4E-03
Hexachloroethane 5.9E-07 2.2E+00 3.1E-01 3.1E-01 2.1E-03 4.6E-02 2.8E-02 2.4E-04
Hexachloropropene 7.9E-07 3.0E+00 4.1E-01 4.1E-01 2.8E-03 6.2E-02 3.8E-02 3.2E-04
Indeno(1,2,3-cd)pyrene 5.9E-07 2.2E+00 3.1E-01 3.1E-01 2.1E-03 4.6E-02 2.8E-02 2.4E-04
Isophorone 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Methyl methanesulfonate 6.0E-07 2.2E+00 3.1E-01 3.1E-01 2.2E-03 4.7E-02 2.9E-02 2.4E-04
Naphthalene 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 5.6E-03
Nitrobenzene 6.2E-07 2.3E+00 3.2E-01 3.2E-01 2.2E-03 4.8E-02 3.0E-02 2.5E-04
N-Nitro-o-toluidine 8.8E-06 3.3E+01 4.6E+00 4.6E+00 3.2E-02 6.9E-01 4.2E-01 3.5E-03
N-Nitrosodiethylamine 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
N-Nitrosodimethylamine 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
N-Nitrosodi-n-butylamine 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
N-Nitrosodi-n-propylamine 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
N-Nitrosodiphenylamine 9.5E-07 3.6E+00 4.9E-01 4.9E-01 3.4E-03 7.4E-02 4.6E-02 3.8E-04
N-Nitrosomethylethylamine 9.1E-07 3.4E+00 4.7E-01 4.7E-01 3.3E-03 7.1E-02 4.4E-02 3.6E-04
N-Nitrosomorpholine 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
o-Toluidine 7.0E-06 2.6E+01 3.6E+00 3.6E+00 2.5E-02 5.5E-01 3.4E-01 2.8E-03
p-Dimethylaminoazobenzene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Pentachlorobenzene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Pentachloroethane 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Pentachloronitrobenzene 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 2.2E-04
Pentachlorophenol 2.7E-05 1.0E+02 1.4E+01 1.4E+01 9.7E-02 2.1E+00 1.3E+00 1.1E-02
Phenanthrene 7.0E-07 2.6E+00 3.6E-01 3.6E-01 2.5E-03 5.5E-02 3.4E-02 2.8E-04
Phenol 2.4E-06 9.0E+00 1.2E+00 1.2E+00 8.6E-03 1.9E-01 1.2E-01 9.6E-04
Pyrene 5.8E-07 2.2E+00 3.0E-01 3.0E-01 2.1E-03 4.5E-02 2.8E-02 2.3E-04
Pyridine 8.1E-07 3.0E+00 4.2E-01 4.2E-01 2.9E-03 6.3E-02 3.9E-02 3.2E-04

Dioxins/Furans
2,3,7,8-TCDD 2.3E-12 8.6E-06 1.2E-06 1.2E-06 8.3E-09 1.8E-07 1.1E-07 5.5E-09
1,2,3,7,8-PeCDD 6.7E-12 2.5E-05 3.5E-06 3.5E-06 2.4E-08 5.2E-07 3.2E-07 1.6E-08
1,2,3,4,7,8-HxCDD 3.5E-12 1.3E-05 1.8E-06 1.8E-06 1.3E-08 2.7E-07 1.7E-07 8.4E-09
1,2,3,6,7,8-HxCDD 8.9E-12 3.3E-05 4.6E-06 4.6E-06 3.2E-08 6.9E-07 4.3E-07 2.1E-08
1,2,3,7,8,9-HxCDD 6.1E-12 2.3E-05 3.2E-06 3.2E-06 2.2E-08 4.8E-07 2.9E-07 1.5E-08
1,2,3,4,6,7,8-HpCDD 2.9E-11 1.1E-04 1.5E-05 1.5E-05 1.0E-07 2.3E-06 1.4E-06 7.0E-08
OCDD 3.7E-11 1.4E-04 1.9E-05 1.9E-05 1.3E-07 2.9E-06 1.8E-06 8.9E-08
2,3,7,8-TCDF 4.0E-11 1.5E-04 2.1E-05 2.1E-05 1.4E-07 3.1E-06 1.9E-06 9.6E-08
1,2,3,7,8-PeCDF 8.0E-11 3.0E-04 4.2E-05 4.2E-05 2.9E-07 6.2E-06 3.8E-06 1.9E-07
2,3,4,7,8-PeCDF 1.6E-10 6.0E-04 8.3E-05 8.3E-05 5.8E-07 1.2E-05 7.7E-06 3.8E-07
1,2,3,4,7,8-HxCDF 2.6E-10 9.7E-04 1.4E-04 1.4E-04 9.4E-07 2.0E-05 1.2E-05 6.2E-07
1,2,3,6,7,8-HxCDF 1.6E-10 6.0E-04 8.3E-05 8.3E-05 5.8E-07 1.2E-05 7.7E-06 3.8E-07
2,3,4,6,7,8-HxCDF 1.9E-10 7.1E-04 9.9E-05 9.9E-05 6.8E-07 1.5E-05 9.1E-06 4.6E-07
1,2,3,7,8,9-HxCDF 1.2E-10 4.5E-04 6.2E-05 6.2E-05 4.3E-07 9.4E-06 5.8E-06 2.9E-07
1,2,3,4,6,7,8-HpCDF 7.3E-10 2.7E-03 3.8E-04 3.8E-04 2.6E-06 5.7E-05 3.5E-05 1.8E-06
TABLE OR APPENDIX 3-???
1.3 CLASS WASTE MATERIAL
CONSERVATIVE ANNUAL EMISSION RATES (LBS/YR)
ATK PROMONTORY, UTAH
PAGE 3 OF 5
1 2 3 4 5 1 2
Analyte
Conservative
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/year)M-225 Quantities
(lbs/year)
1,2,3,4,7,8,9-HpCDF 1.9E-10 7.1E-04 9.9E-05 9.9E-05 6.8E-07 1.5E-05 9.1E-06 4.6E-07
OCDF 5.3E-10 2.0E-03 2.8E-04 2.8E-04 1.9E-06 4.1E-05 1.1E-06 1.3E-06

Carbonyls
2,5-Dimethylbenzaldehyde 2.7E-05 1.0E+02 1.4E+01 1.4E+01 9.7E-02 2.1E+00 1.3E+00 6.5E-02
Acetaldehyde 9.3E-05 3.5E+02 4.8E+01 4.8E+01 3.3E-01 7.3E+00 4.5E+00 2.2E-01
Acetone 3.1E-05 1.2E+02 1.6E+01 1.6E+01 1.1E-01 2.4E+00 1.5E+00 7.4E-02
Benzaldehyde 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 3.4E-02
Crotonaldehyde 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 3.4E-02
Formaldehyde 4.7E-05 1.8E+02 2.4E+01 2.4E+01 1.7E-01 3.7E+00 2.3E+00 1.1E-01
Hexanal 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 3.4E-02
Isopentanal 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 3.4E-02
m,p-Tolualdehyde 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 3.4E-02
MEK/Butyraldehydes 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 3.4E-02
o-Tolualdehyde 4.0E-05 1.5E+02 2.1E+01 2.1E+01 1.4E-01 3.1E+00 1.9E+00 9.6E-02
Pentanal 1.7E-05 6.4E+01 8.8E+00 8.8E+00 6.1E-02 1.3E+00 8.2E-01 4.1E-02
Propanal 5.2E-05 1.9E+02 2.7E+01 2.7E+01 1.9E-01 4.1E+00 2.5E+00 1.2E-01
HCl/Cl2/NH3
HCl 1.8E-02 6.7E+04 9.4E+03 9.4E+03 6.5E+01 1.4E+03 8.6E+02 4.3E+01
Cl2 1.2E-02 4.5E+04 6.2E+03 6.2E+03 4.3E+01 9.4E+02 5.8E+02 2.9E+01
NH3 3.2E-05 1.2E+02 1.7E+01 1.7E+01 1.2E-01 2.5E+00 1.5E+00 7.7E-02
HCN 2.2E-05 8.2E+01 1.1E+01 #REF!7.9E-02 1.7E+00 1.1E+00 5.3E-02

VOCs
TNMOC 9.4E-04 3.5E+03 4.9E+02 4.9E+02 3.4E+00 7.3E+01 4.5E+01 2.3E+00
1,1,1-Trichloroethane 8.9E-07 3.3E+00 4.6E-01 4.6E-01 3.2E-03 6.9E-02 4.3E-02 2.1E-03
1,1,2,2-Tetrachloroethane 4.2E-07 1.6E+00 2.2E-01 2.2E-01 1.5E-03 3.3E-02 2.0E-02 1.0E-03
1,1,2-Trichloroethane 7.3E-07 2.7E+00 3.8E-01 3.8E-01 2.6E-03 5.7E-02 3.5E-02 1.8E-03
1,1-Dichloroethane 3.2E-07 1.2E+00 1.7E-01 1.7E-01 1.2E-03 2.5E-02 1.5E-02 7.7E-04
1,1-Dichloroethene 4.3E-07 1.6E+00 2.2E-01 2.2E-01 1.5E-03 3.4E-02 2.1E-02 1.0E-03
1,2,3-Trimethylbenzene 4.2E-07 1.6E+00 2.2E-01 2.2E-01 1.5E-03 3.3E-02 2.0E-02 1.0E-03
1,2,4-Trichlorobenzene 1.3E-06 4.9E+00 6.8E-01 6.8E-01 4.7E-03 1.0E-01 6.2E-02 3.1E-03
1,2,4-Trimethylbenzene 5.2E-06 1.9E+01 2.7E+00 2.7E+00 1.9E-02 4.1E-01 2.5E-01 1.2E-02
1,2-Dibromomethane (EDB)8.9E-07 3.3E+00 4.6E-01 4.6E-01 3.2E-03 6.9E-02 4.3E-02 2.1E-03
1,2-Dichlorobenzene 4.8E-07 1.8E+00 2.5E-01 2.5E-01 1.7E-03 3.7E-02 2.3E-02 1.2E-03
1,2-Dichloroethane 5.4E-07 2.0E+00 2.8E-01 2.8E-01 1.9E-03 4.2E-02 2.6E-02 1.3E-03
1,2-Dichloropropane 3.7E-07 1.4E+00 1.9E-01 1.9E-01 1.3E-03 2.9E-02 1.8E-02 8.9E-04
1,3,5-Trimethylbenzene 2.0E-06 7.5E+00 1.0E+00 1.0E+00 7.2E-03 1.6E-01 9.6E-02 4.8E-03
1,3-Butadiene 2.4E-05 9.0E+01 1.2E+01 1.2E+01 8.6E-02 1.9E+00 1.2E+00 5.8E-02
1,3-Dichlorobenzene 4.4E-07 1.6E+00 2.3E-01 2.3E-01 1.6E-03 3.4E-02 2.1E-02 1.1E-03
1,3-Diethylbenzene 5.0E-07 1.9E+00 2.6E-01 2.6E-01 1.8E-03 3.9E-02 2.4E-02 1.2E-03
1,4-Dichlorobenzene 7.3E-07 2.7E+00 3.8E-01 3.8E-01 2.6E-03 5.7E-02 3.5E-02 1.8E-03
1,4-Diethylbenzene 6.7E-07 2.5E+00 3.5E-01 3.5E-01 2.4E-03 5.2E-02 3.2E-02 1.6E-03
1,4-Dioxane 6.4E-07 2.4E+00 3.3E-01 3.3E-01 2.3E-03 5.0E-02 3.1E-02 1.5E-03
1-Butene 2.2E-05 8.2E+01 1.1E+01 1.1E+01 7.9E-02 1.7E+00 1.1E+00 5.3E-02
1-Hexene 2.0E-05 7.5E+01 1.0E+01 1.0E+01 7.2E-02 1.6E+00 9.6E-01 4.8E-02
1-Pentene 1.2E-05 4.5E+01 6.2E+00 6.2E+00 4.3E-02 9.4E-01 5.8E-01 2.9E-02
2,2,4-Trimethylpentane 2.3E-06 8.6E+00 1.2E+00 1.2E+00 8.3E-03 1.8E-01 1.1E-01 5.5E-03
2,2-Dimethylbutane 8.8E-07 3.3E+00 4.6E-01 4.6E-01 3.2E-03 6.9E-02 4.2E-02 2.1E-03
2,3,4-Trimethylpentane 2.8E-07 1.0E+00 1.5E-01 1.5E-01 1.0E-03 2.2E-02 1.3E-02 6.7E-04
2,3-Dimethylbutane 2.9E-06 1.1E+01 1.5E+00 1.5E+00 1.0E-02 2.3E-01 1.4E-01 7.0E-03
2,3-Dimethylpentane 2.7E-06 1.0E+01 1.4E+00 1.4E+00 9.7E-03 2.1E-01 1.3E-01 6.5E-03
2,4-Dimethylpentane 1.1E-06 4.1E+00 5.7E-01 5.7E-01 4.0E-03 8.6E-02 5.3E-02 2.6E-03
2-Butanone (MEK)3.9E-06 1.5E+01 2.0E+00 2.0E+00 1.4E-02 3.0E-01 1.9E-01 9.4E-03
2-Ethyltoluene 4.5E-07 1.7E+00 2.3E-01 2.3E-01 1.6E-03 3.5E-02 2.2E-02 1.1E-03
2-Hexanone 8.7E-07 3.3E+00 4.5E-01 4.5E-01 3.1E-03 6.8E-02 4.2E-02 2.1E-03
2-Methylheptane 2.7E-06 1.0E+01 1.4E+00 1.4E+00 9.7E-03 2.1E-01 1.3E-01 6.5E-03
2-Methylhexane 4.4E-06 1.6E+01 2.3E+00 2.3E+00 1.6E-02 3.4E-01 2.1E-01 1.1E-02
2-Methylpentane 1.1E-05 4.1E+01 5.7E+00 5.7E+00 4.0E-02 8.6E-01 5.3E-01 2.6E-02
2-Nitropropane 2.8E-06 1.0E+01 1.5E+00 1.5E+00 1.0E-02 2.2E-01 1.3E-01 6.7E-03
2-Propanol 3.0E-07 1.1E+00 1.6E-01 1.6E-01 1.1E-03 2.3E-02 1.4E-02 7.2E-04
3-Chloropropene 4.7E-06 1.8E+01 2.4E+00 2.4E+00 1.7E-02 3.7E-01 2.3E-01 1.1E-02
3-Ethyltoluene 4.8E-06 1.8E+01 2.5E+00 2.5E+00 1.7E-02 3.7E-01 2.3E-01 1.2E-02
3-Methylheptane 3.5E-06 1.3E+01 1.8E+00 1.8E+00 1.3E-02 2.7E-01 1.7E-01 8.4E-03
3-Methylhexane 5.2E-06 1.9E+01 2.7E+00 2.7E+00 1.9E-02 4.1E-01 2.5E-01 1.2E-02
3-Methylpentane 7.1E-06 2.7E+01 3.7E+00 3.7E+00 2.6E-02 5.5E-01 3.4E-01 1.7E-02
4-Ethyltoluene 5.3E-06 2.0E+01 2.8E+00 2.8E+00 1.9E-02 4.1E-01 2.5E-01 1.3E-02
4-Methyl-2-pentanone 7.0E-07 2.6E+00 3.6E-01 3.6E-01 2.5E-03 5.5E-02 3.4E-02 1.7E-03
Acetone 2.4E-05 9.0E+01 1.2E+01 1.2E+01 8.6E-02 1.9E+00 1.2E+00 5.8E-02
TABLE OR APPENDIX 3-???
1.3 CLASS WASTE MATERIAL
CONSERVATIVE ANNUAL EMISSION RATES (LBS/YR)
ATK PROMONTORY, UTAH
PAGE 4 OF 5
1 2 3 4 5 1 2
Analyte
Conservative
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/year)M-225 Quantities
(lbs/year)
Acetonitrile 1.9E-05 7.1E+01 9.9E+00 9.9E+00 6.8E-02 1.5E+00 9.1E-01 4.6E-02
Acetylene 9.4E-05 3.5E+02 4.9E+01 4.9E+01 3.4E-01 7.3E+00 4.5E+00 2.3E-01
Acrylonitrile 1.6E-05 6.0E+01 8.3E+00 8.3E+00 5.8E-02 1.2E+00 7.7E-01 3.8E-02
alpha-Chlorotoluene 5.7E-07 2.1E+00 3.0E-01 3.0E-01 2.1E-03 4.4E-02 2.7E-02 1.4E-03
Benzene 4.7E-05 1.8E+02 2.4E+01 2.4E+01 1.7E-01 3.7E+00 2.3E+00 1.1E-01
Bromodichloromethane 7.8E-07 2.9E+00 4.1E-01 4.1E-01 2.8E-03 6.1E-02 3.7E-02 1.9E-03
Bromoform 1.3E-06 4.9E+00 6.8E-01 6.8E-01 4.7E-03 1.0E-01 6.2E-02 3.1E-03
Bromomethane 6.2E-07 2.3E+00 3.2E-01 3.2E-01 2.2E-03 4.8E-02 3.0E-02 1.5E-03
Butane 1.8E-05 6.7E+01 9.4E+00 9.4E+00 6.5E-02 1.4E+00 8.6E-01 4.3E-02
Carbon Disulfide 9.8E-06 3.7E+01 5.1E+00 5.1E+00 3.5E-02 7.6E-01 4.7E-01 2.4E-02
Carbon Tetrachloride 1.5E-05 5.6E+01 7.8E+00 7.8E+00 5.4E-02 1.2E+00 7.2E-01 3.6E-02
Chloroacetonitrile 1.1E-06 4.1E+00 5.7E-01 5.7E-01 4.0E-03 8.6E-02 5.3E-02 2.6E-03
Chlorobenzene 2.5E-06 9.4E+00 1.3E+00 1.3E+00 9.0E-03 2.0E-01 1.2E-01 6.0E-03
Chloroethane 2.6E-07 9.7E-01 1.4E-01 1.4E-01 9.4E-04 2.0E-02 1.2E-02 6.2E-04
Chloroform 6.1E-06 2.3E+01 3.2E+00 3.2E+00 2.2E-02 4.8E-01 2.9E-01 1.5E-02
Chloromethane 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 3.4E-02
cis-1,2-Dichloroethene 4.6E-07 1.7E+00 2.4E-01 2.4E-01 1.7E-03 3.6E-02 2.2E-02 1.1E-03
cis-1,3-Dichloropropene 1.3E-06 4.9E+00 6.8E-01 6.8E-01 4.7E-03 1.0E-01 6.2E-02 3.1E-03
cis-2-Butene 1.7E-06 6.4E+00 8.8E-01 8.8E-01 6.1E-03 1.3E-01 8.2E-02 4.1E-03
cis-2-Pentene 3.3E-07 1.2E+00 1.7E-01 1.7E-01 1.2E-03 2.6E-02 1.6E-02 7.9E-04
Cumene 4.2E-07 1.6E+00 2.2E-01 2.2E-01 1.5E-03 3.3E-02 2.0E-02 1.0E-03
Cyclohexane 2.5E-06 9.4E+00 1.3E+00 1.3E+00 9.0E-03 2.0E-01 1.2E-01 6.0E-03
Cyclopentane 1.8E-06 6.7E+00 9.4E-01 9.4E-01 6.5E-03 1.4E-01 8.6E-02 4.3E-03
Decane 1.7E-05 6.4E+01 8.8E+00 8.8E+00 6.1E-02 1.3E+00 8.2E-01 4.1E-02
Dibromochloromethane 8.8E-07 3.3E+00 4.6E-01 4.6E-01 3.2E-03 6.9E-02 4.2E-02 2.1E-03
Ethane 2.1E-05 7.9E+01 1.1E+01 1.1E+01 7.6E-02 1.6E+00 1.0E+00 5.0E-02
Ethanol 1.6E-06 6.0E+00 8.3E-01 8.3E-01 5.8E-03 1.2E-01 7.7E-02 3.8E-03
Ethene 1.8E-04 6.7E+02 9.4E+01 9.4E+01 6.5E-01 1.4E+01 8.6E+00 4.3E-01
Ethyl benzene 2.8E-06 1.0E+01 1.5E+00 1.5E+00 1.0E-02 2.2E-01 1.3E-01 6.7E-03
Ethyl ether 2.5E-06 9.4E+00 1.3E+00 1.3E+00 9.0E-03 2.0E-01 1.2E-01 6.0E-03
Ethyl Methacrylate 1.6E-06 6.0E+00 8.3E-01 8.3E-01 5.8E-03 1.2E-01 7.7E-02 3.8E-03
Heptane 7.2E-06 2.7E+01 3.7E+00 3.7E+00 2.6E-02 5.6E-01 3.5E-01 1.7E-02
Hexachlorobutadiene 1.7E-06 6.4E+00 8.8E-01 8.8E-01 6.1E-03 1.3E-01 8.2E-02 4.1E-03
Hexane 9.8E-06 3.7E+01 5.1E+00 5.1E+00 3.5E-02 7.6E-01 4.7E-01 2.4E-02
Isobutane 2.8E-06 1.0E+01 1.5E+00 1.5E+00 1.0E-02 2.2E-01 1.3E-01 6.7E-03
Isopentane 2.0E-05 7.5E+01 1.0E+01 1.0E+01 7.2E-02 1.6E+00 9.6E-01 4.8E-02
m,p-Xylene 1.1E-05 4.1E+01 5.7E+00 5.7E+00 4.0E-02 8.6E-01 5.3E-01 2.6E-02
Methacrylonitrile 4.9E-06 1.8E+01 2.5E+00 2.5E+00 1.8E-02 3.8E-01 2.4E-01 1.2E-02
Methyl Acrylate 1.2E-06 4.5E+00 6.2E-01 6.2E-01 4.3E-03 9.4E-02 5.8E-02 2.9E-03
Methyl Methacrylate 1.6E-06 6.0E+00 8.3E-01 8.3E-01 5.8E-03 1.2E-01 7.7E-02 3.8E-03
Methyl tert-butyl ether 4.2E-07 1.6E+00 2.2E-01 2.2E-01 1.5E-03 3.3E-02 2.0E-02 1.0E-03
Methylcyclohexane 6.1E-06 2.3E+01 3.2E+00 3.2E+00 2.2E-02 4.8E-01 2.9E-01 1.5E-02
Methylcyclopentane 5.6E-06 2.1E+01 2.9E+00 2.9E+00 2.0E-02 4.4E-01 2.7E-01 1.3E-02
Methylene chloride 7.1E-06 2.7E+01 3.7E+00 3.7E+00 2.6E-02 5.5E-01 3.4E-01 1.7E-02
n-Butylchloride 1.2E-05 4.5E+01 6.2E+00 6.2E+00 4.3E-02 9.4E-01 5.8E-01 2.9E-02
Nonane 1.3E-05 4.9E+01 6.8E+00 6.8E+00 4.7E-02 1.0E+00 6.2E-01 3.1E-02
Octane 7.5E-06 2.8E+01 3.9E+00 3.9E+00 2.7E-02 5.9E-01 3.6E-01 1.8E-02
o-Xylene 3.5E-06 1.3E+01 1.8E+00 1.8E+00 1.3E-02 2.7E-01 1.7E-01 8.4E-03
Pentane 1.9E-05 7.1E+01 9.9E+00 9.9E+00 6.8E-02 1.5E+00 9.1E-01 4.6E-02
Propane 8.7E-06 3.3E+01 4.5E+00 4.5E+00 3.1E-02 6.8E-01 4.2E-01 2.1E-02
Propylbenzene 1.0E-06 3.7E+00 5.2E-01 5.2E-01 3.6E-03 7.8E-02 4.8E-02 2.4E-03
Propylene 4.9E-05 1.8E+02 2.5E+01 2.5E+01 1.8E-01 3.8E+00 2.4E+00 1.2E-01
Styrene 9.9E-07 3.7E+00 5.1E-01 5.1E-01 3.6E-03 7.7E-02 4.8E-02 2.4E-03
Tetrachloroethene 2.5E-06 9.4E+00 1.3E+00 1.3E+00 9.0E-03 2.0E-01 1.2E-01 6.0E-03
Tetrahydrofuran 9.0E-07 3.4E+00 4.7E-01 4.7E-01 3.2E-03 7.0E-02 4.3E-02 2.2E-03
Toluene 1.9E-05 7.1E+01 9.9E+00 9.9E+00 6.8E-02 1.5E+00 9.1E-01 4.6E-02
trans-1,2-Dichloroethene 7.2E-07 2.7E+00 3.7E-01 3.7E-01 2.6E-03 5.6E-02 3.5E-02 1.7E-03
trans-1,3-Dichloropropene 6.1E-07 2.3E+00 3.2E-01 3.2E-01 2.2E-03 4.8E-02 2.9E-02 1.5E-03
trans-2-butene 7.7E-06 2.9E+01 4.0E+00 4.0E+00 2.8E-02 6.0E-01 3.7E-01 1.8E-02
trans-2-Pentene 1.7E-06 6.4E+00 8.8E-01 8.8E-01 6.1E-03 1.3E-01 8.2E-02 4.1E-03
Trichloroethene 9.4E-07 3.5E+00 4.9E-01 4.9E-01 3.4E-03 7.3E-02 4.5E-02 2.3E-03
Undecane 1.2E-05 4.5E+01 6.2E+00 6.2E+00 4.3E-02 9.4E-01 5.8E-01 2.9E-02
Vinyl chloride 7.6E-06 2.8E+01 4.0E+00 4.0E+00 2.7E-02 5.9E-01 3.6E-01 1.8E-02

CEM
CO2 7.20E-01 2.7E+06 3.7E+05 3.7E+05 2.6E+03 5.6E+04 3.5E+04 1.7E+03
CO 6.40E-03 2.4E+04 3.3E+03 3.3E+03 2.3E+01 5.0E+02 3.1E+02 1.5E+01
NOX 6.40E-03 2.4E+04 3.3E+03 3.3E+03 2.3E+01 5.0E+02 3.1E+02 1.5E+01
SO2 5.00E-04 1.9E+03 2.6E+02 2.6E+02 1.8E+00 3.9E+01 2.4E+01 1.2E+00
Highlighted analytes were not detected during the Bang Box testing program
TABLE OR APPENDIX 3-???
1.3 CLASS WASTE MATERIAL
CONSERVATIVE ANNUAL EMISSION RATES (LBS/YR)
ATK PROMONTORY, UTAH
PAGE 5 OF 5
1 2 3 4 5 1 2
Analyte
Conservative
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/year)M-225 Quantities
(lbs/year)
CEM - Continuous Emissions Monitoring
CL2 - chlorine
CO - carbon monoxide
CO2 - carbon dioxide
HCL - hydrogen chloride
HCN - hydrogen cyanide
NH3 - ammonia
NOX - nitrogen oxide
OCDD - 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin
OCDF - 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-furan
PM10 - particulate matter less than 10 microns in aerodynamic diameter
PM2.5 - particulate matter less than 2.5 microns in aerodynamic diameter
SO2 - sulfur dioxide
SVOCs - semi-volatile organic compounds
TNMOC - total non-methane organic carbon
TSP - Total suspended particulates
VOCs - volatile organic compounds
TABLE OR APPENDIX ???
1.3 CLASS WASTE MATERIAL PER EVENT (1-HOUR)
CORRECTED EMISSION RATES (LBS/HR)
ATK PROMONTORY, UTAH
PAGE 1 OF 5
1 2 3 4 5 1 2
Particulates
TSP 1.4E-01 1.7E+03 1.4E+03 1.4E+03 8.4E+01 3.6E+03 2.8E+02 5.6E+01
PM10 8.6E-02 1.0E+03 8.6E+02 8.6E+02 5.2E+01 2.2E+03 1.7E+02 3.4E+01
PM2.5 5.9E-02 7.1E+02 5.9E+02 5.9E+02 3.5E+01 1.5E+03 1.2E+02 2.4E+01

Metals
Aluminum 4.0E-02 4.8E+02 4.0E+02 4.0E+02 2.4E+01 1.0E+03 8.0E+01 1.6E+01
Antimony 2.9E-05 3.5E-01 2.9E-01 2.9E-01 1.7E-02 7.5E-01 5.8E-02 1.2E-02
Arsenic 3.0E-07 3.6E-03 3.0E-03 3.0E-03 1.8E-04 7.8E-03 6.0E-04 1.2E-04
Barium 4.9E-06 5.9E-02 4.9E-02 4.9E-02 2.9E-03 1.3E-01 9.8E-03 2.0E-03
Cadmium 3.1E-07 3.7E-03 3.1E-03 3.1E-03 1.9E-04 8.1E-03 6.2E-04 1.2E-04
Chromium 2.0E-05 2.4E-01 2.0E-01 2.0E-01 1.2E-02 5.2E-01 4.0E-02 8.0E-03
Cobalt 3.1E-07 3.7E-03 3.1E-03 3.1E-03 1.9E-04 8.1E-03 6.2E-04 1.2E-04
Copper 2.5E-05 3.0E-01 2.5E-01 2.5E-01 1.5E-02 6.5E-01 5.0E-02 1.0E-02
Lead 3.4E-05 4.1E-01 3.4E-01 3.4E-01 2.0E-02 8.8E-01 6.8E-02 1.4E-02
Magnesium 2.9E-05 3.5E-01 2.9E-01 2.9E-01 1.7E-02 7.5E-01 5.8E-02 1.2E-02
Manganese 9.3E-05 1.1E+00 9.3E-01 9.3E-01 5.6E-02 2.4E+00 1.9E-01 3.7E-02
Mercury 3.7E-08 4.4E-04 3.7E-04 3.7E-04 2.2E-05 9.6E-04 7.4E-05 1.5E-05
Nickel 5.8E-05 7.0E-01 5.8E-01 5.8E-01 3.5E-02 1.5E+00 1.2E-01 2.3E-02
Phosphorus 1.0E-04 1.2E+00 1.0E+00 1.0E+00 6.0E-02 2.6E+00 2.0E-01 4.0E-02
Selenium 1.7E-06 2.0E-02 1.7E-02 1.7E-02 1.0E-03 4.4E-02 3.4E-03 6.8E-04
Silver 9.5E-07 1.1E-02 9.5E-03 9.5E-03 5.7E-04 2.5E-02 1.9E-03 3.8E-04
Thallium 2.1E-06 2.5E-02 2.1E-02 2.1E-02 1.3E-03 5.5E-02 4.2E-03 8.4E-04
Zinc 3.5E-05 4.2E-01 3.5E-01 3.5E-01 2.1E-02 9.1E-01 7.0E-02 1.4E-02
Perchlorate 2.5E-07 2.7E-02 2.5E-03 2.5E-03 1.5E-04 6.5E-03 5.0E-04 1.0E-04

SVOCs
1,2,4,5-Tetrachlorobenzene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
1,2,4-Trichlorobenzene 3.2E-07 3.8E-03 3.2E-03 3.2E-03 1.9E-04 8.3E-03 6.4E-04 1.3E-04
1,2-Dichlorobenzene 2.8E-07 3.4E-03 2.8E-03 2.8E-03 1.7E-04 7.3E-03 5.6E-04 1.1E-04
1,3,5-Trinitrobenzene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
1,3-Dichlorobenzene 3.1E-07 3.7E-03 3.1E-03 3.1E-03 1.9E-04 8.1E-03 6.2E-04 1.2E-04
1,3-Dinitrobenzene 2.8E-07 3.4E-03 2.8E-03 2.8E-03 1.7E-04 7.3E-03 5.6E-04 1.1E-04
1,4-Dichlorobenzene 2.9E-07 3.5E-03 2.9E-03 2.9E-03 1.7E-04 7.5E-03 5.8E-04 1.2E-04
1-Chloronaphthalene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
1-Naphthylamine 5.5E-06 6.6E-02 5.5E-02 5.5E-02 3.3E-03 1.4E-01 1.1E-02 2.2E-03
2,3,4,6-Tetrachlorophenol 3.6E-07 4.3E-03 3.6E-03 3.6E-03 2.2E-04 9.4E-03 7.2E-04 1.4E-04
2,4,5-Trichlorophenol 7.1E-07 8.5E-03 7.1E-03 7.1E-03 4.3E-04 1.8E-02 1.4E-03 2.8E-04
2,4,6-Trichlorophenol 1.30E-06 1.6E-02 1.3E-02 1.3E-02 7.8E-04 3.4E-02 2.6E-03 5.2E-04
2,4-Dichlorophenol 9.3E-07 1.1E-02 9.3E-03 9.3E-03 5.6E-04 2.4E-02 1.9E-03 3.7E-04
2,4-Dimethylphenol 3.5E-06 4.2E-02 3.5E-02 3.5E-02 2.1E-03 9.1E-02 7.0E-03 1.4E-03
2,4-Dinitrophenol 1.2E-05 1.4E-01 1.2E-01 1.2E-01 7.2E-03 3.1E-01 2.4E-02 4.8E-03
2,4-Dinitrotoluene 3.1E-07 3.7E-03 3.1E-03 3.1E-03 1.9E-04 8.1E-03 6.2E-04 1.2E-04
2,6-Dichlorophenol 4.0E-07 4.8E-03 4.0E-03 4.0E-03 2.4E-04 1.0E-02 8.0E-04 1.6E-04
2,6-Dinitrotoluene 5.6E-07 6.7E-03 5.6E-03 5.6E-03 3.4E-04 1.5E-02 1.1E-03 2.2E-04
2-Acetylaminofluorene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
2-Chloronaphthalene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
2-Chlorophenol 1.9E-06 2.3E-02 1.9E-02 1.9E-02 1.1E-03 4.9E-02 3.8E-03 7.6E-04
2-Methylnaphthalene 3.6E-06 4.3E-02 3.6E-02 3.6E-02 2.2E-03 9.4E-02 7.2E-03 1.4E-03
2-Methylphenol 1.6E-06 1.9E-02 1.6E-02 1.6E-02 9.6E-04 4.2E-02 3.2E-03 6.4E-04
2-Naphthylamine 5.5E-06 6.6E-02 5.5E-02 5.5E-02 3.3E-03 1.4E-01 1.1E-02 2.2E-03
2-Nitroaniline 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
2-Nitrophenol 3.9E-07 4.7E-03 3.9E-03 3.9E-03 2.3E-04 1.0E-02 7.8E-04 1.6E-04
3,3'-Dichlorobenzidine 4.1E-06 4.9E-02 4.1E-02 4.1E-02 2.5E-03 1.1E-01 8.2E-03 1.6E-03
3,3'-Dimethylbenzidine 2.7E-05 3.2E-01 2.7E-01 2.7E-01 1.6E-02 7.0E-01 5.4E-02 1.1E-02
3-Methylcholanthrene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
3-Methylphenol & 4-Methylphenol 1.1E-06 1.3E-02 1.1E-02 1.1E-02 6.6E-04 2.9E-02 2.2E-03 4.4E-04
3-Nitroaniline 1.1E-06 1.3E-02 1.1E-02 1.1E-02 6.6E-04 2.9E-02 2.2E-03 4.4E-04
4,6-Dinitro-2-methylphenol 4.8E-06 5.8E-02 4.8E-02 4.8E-02 2.9E-03 1.2E-01 9.6E-03 1.9E-03
4-Aminobiphenyl 5.5E-06 6.6E-02 5.5E-02 5.5E-02 3.3E-03 1.4E-01 1.1E-02 2.2E-03
4-Bromophenyl phenyl ether 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
4-Chloro-3-methylphenol 3.4E-07 4.1E-03 3.4E-03 3.4E-03 2.0E-04 8.8E-03 6.8E-04 1.4E-04
4-Chloroaniline 3.3E-06 4.0E-02 3.3E-02 3.3E-02 2.0E-03 8.6E-02 6.6E-03 1.3E-03
4-Nitroaniline 1.1E-06 1.3E-02 1.1E-02 1.1E-02 6.6E-04 2.9E-02 2.2E-03 4.4E-04
4-Nitrophenol 1.8E-06 2.2E-02 1.8E-02 1.8E-02 1.1E-03 4.7E-02 3.6E-03 7.2E-04
7,12-Dimethylbenz(a)anthracene 2.8E-07 3.4E-03 2.8E-03 2.8E-03 1.7E-04 7.3E-03 5.6E-04 1.1E-04
Acenaphthene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Acenaphthylene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Acetophenone 2.7E-06 3.2E-02 2.7E-02 2.7E-02 1.6E-03 7.0E-02 5.4E-03 1.1E-03
Aniline 4.0E-06 4.8E-02 4.0E-02 4.0E-02 2.4E-03 1.0E-01 8.0E-03 1.6E-03
Analyte
Corrected
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/hour)M-225 Quantities
(lbs/hr)
TABLE OR APPENDIX ???
1.3 CLASS WASTE MATERIAL PER EVENT (1-HOUR)
CORRECTED EMISSION RATES (LBS/HR)
ATK PROMONTORY, UTAH
PAGE 2 OF 5
1 2 3 4 5 1 2
Analyte
Corrected
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/hour)M-225 Quantities
(lbs/hr)
Anthracene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Benzidine 2.8E-05 3.4E-01 2.8E-01 2.8E-01 1.7E-02 7.3E-01 5.6E-02 1.1E-02
Benzo(a)anthracene 3.2E-07 3.8E-03 3.2E-03 3.2E-03 1.9E-04 8.3E-03 6.4E-04 1.3E-04
Benzo(a)pyrene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Benzo(b)fluoranthene 6.0E-07 7.2E-03 6.0E-03 6.0E-03 3.6E-04 1.6E-02 1.2E-03 2.4E-04
Benzo(ghi)perylene 3.4E-07 4.1E-03 3.4E-03 3.4E-03 2.0E-04 8.8E-03 6.8E-04 1.4E-04
Benzo(k)fluoranthene 8.8E-07 1.1E-02 8.8E-03 8.8E-03 5.3E-04 2.3E-02 1.8E-03 3.5E-04
Benzoic acid 6.2E-05 7.4E-01 6.2E-01 6.2E-01 3.7E-02 1.6E+00 1.2E-01 2.5E-02
Benzyl alcohol 1.9E-05 2.3E-01 1.9E-01 1.9E-01 1.1E-02 4.9E-01 3.8E-02 7.6E-03
bis(2-Chloroethoxy)methane 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
bis(2-Chloroethyl) ether 3.1E-07 3.7E-03 3.1E-03 3.1E-03 1.9E-04 8.1E-03 6.2E-04 1.2E-04
bis(2-Chloroisopropyl) ether 4.2E-07 5.0E-03 4.2E-03 4.2E-03 2.5E-04 1.1E-02 8.4E-04 1.7E-04
bis(2-Ethylhexyl) phthalate 5.5E-06 6.6E-02 5.5E-02 5.5E-02 3.3E-03 1.4E-01 1.1E-02 2.2E-03
Butyl benzyl phthalate 3.3E-07 4.0E-03 3.3E-03 3.3E-03 2.0E-04 8.6E-03 6.6E-04 1.3E-04
Carbazole 3.5E-07 4.2E-03 3.5E-03 3.5E-03 2.1E-04 9.1E-03 7.0E-04 1.4E-04
Chrysene 3.5E-07 4.2E-03 3.5E-03 3.5E-03 2.1E-04 9.1E-03 7.0E-04 1.4E-04
Dibenz(a,h)anthracene 3.3E-07 4.0E-03 3.3E-03 3.3E-03 2.0E-04 8.6E-03 6.6E-04 1.3E-04
Dibenzofuran 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Diethyl phthalate 4.0E-07 4.8E-03 4.0E-03 4.0E-03 2.4E-04 1.0E-02 8.0E-04 1.6E-04
Dimethyl phthalate 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Di-n-butyl phthalate 5.5E-06 6.6E-02 5.5E-02 5.5E-02 3.3E-03 1.4E-01 1.1E-02 2.2E-03
Di-n-octyl phthalate 3.7E-06 4.4E-02 3.7E-02 3.7E-02 2.2E-03 9.6E-02 7.4E-03 1.5E-03
Diphenylamine 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Ethyl methanesulfonate 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Fluoranthene 4.0E-07 4.8E-03 4.0E-03 4.0E-03 2.4E-04 1.0E-02 8.0E-04 1.6E-04
Fluorene 4.2E-07 5.0E-03 4.2E-03 4.2E-03 2.5E-04 1.1E-02 8.4E-04 1.7E-04
Hexachlorobenzene 4.7E-06 5.6E-02 4.7E-02 4.7E-02 2.8E-03 1.2E-01 9.4E-03 1.9E-03
Hexachlorobutadiene 4.1E-07 4.9E-03 4.1E-03 4.1E-03 2.5E-04 1.1E-02 8.2E-04 1.6E-04
Hexachlorocyclopentadiene 5.5E-06 6.6E-02 5.5E-02 5.5E-02 3.3E-03 1.4E-01 1.1E-02 2.2E-03
Hexachloroethane 3.0E-07 3.6E-03 3.0E-03 3.0E-03 1.8E-04 7.8E-03 6.0E-04 1.2E-04
Hexachloropropene 3.9E-07 4.7E-03 3.9E-03 3.9E-03 2.3E-04 1.0E-02 7.8E-04 1.6E-04
Indeno(1,2,3-cd)pyrene 3.0E-07 3.6E-03 3.0E-03 3.0E-03 1.8E-04 7.8E-03 6.0E-04 1.2E-04
Isophorone 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Methyl methanesulfonate 3.0E-07 3.6E-03 3.0E-03 3.0E-03 1.8E-04 7.8E-03 6.0E-04 1.2E-04
Naphthalene 1.3E-05 1.6E-01 1.3E-01 1.3E-01 7.8E-03 3.4E-01 2.6E-02 5.2E-03
Nitrobenzene 3.1E-07 3.7E-03 3.1E-03 3.1E-03 1.9E-04 8.1E-03 6.2E-04 1.2E-04
N-Nitro-o-toluidine 4.4E-06 5.3E-02 4.4E-02 4.4E-02 2.6E-03 1.1E-01 8.8E-03 1.8E-03
N-Nitrosodiethylamine 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
N-Nitrosodimethylamine 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
N-Nitrosodi-n-butylamine 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
N-Nitrosodi-n-propylamine 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
N-Nitrosodiphenylamine 4.8E-07 5.8E-03 4.8E-03 4.8E-03 2.9E-04 1.2E-02 9.6E-04 1.9E-04
N-Nitrosomethylethylamine 4.5E-07 5.4E-03 4.5E-03 4.5E-03 2.7E-04 1.2E-02 9.0E-04 1.8E-04
N-Nitrosomorpholine 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
o-Toluidine 3.5E-06 4.2E-02 3.5E-02 3.5E-02 2.1E-03 9.1E-02 7.0E-03 1.4E-03
p-Dimethylaminoazobenzene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Pentachlorobenzene 3.0E-07 3.6E-03 3.0E-03 3.0E-03 1.8E-04 7.8E-03 6.0E-04 1.2E-04
Pentachloroethane 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Pentachloronitrobenzene 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
Pentachlorophenol 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
Phenanthrene 7.0E-07 8.4E-03 7.0E-03 7.0E-03 4.2E-04 1.8E-02 1.4E-03 2.8E-04
Phenol 2.1E-06 2.5E-02 2.1E-02 2.1E-02 1.3E-03 5.5E-02 4.2E-03 8.4E-04
Pyrene 2.9E-07 3.5E-03 2.9E-03 2.9E-03 1.7E-04 7.5E-03 5.8E-04 1.2E-04
Pyridine 4.1E-07 4.9E-03 4.1E-03 4.1E-03 2.5E-04 1.1E-02 8.2E-04 1.6E-04

Dioxins/Furans
2,3,7,8-TCDD 1.3E-12 1.6E-08 1.3E-08 1.3E-08 7.8E-10 3.4E-08 2.6E-09 5.2E-10
1,2,3,7,8-PeCDD 6.7E-12 8.0E-08 6.7E-08 6.7E-08 4.0E-09 1.7E-07 1.3E-08 2.7E-09
1,2,3,4,7,8-HxCDD 3.4E-12 4.1E-08 3.4E-08 3.4E-08 2.0E-09 8.8E-08 6.8E-09 1.4E-09
1,2,3,6,7,8-HxCDD 8.9E-12 1.1E-07 8.9E-08 8.9E-08 5.3E-09 2.3E-07 1.8E-08 3.6E-09
1,2,3,7,8,9-HxCDD 6.1E-12 7.3E-08 6.1E-08 6.1E-08 3.7E-09 1.6E-07 1.2E-08 2.4E-09
1,2,3,4,6,7,8-HpCDD 2.9E-11 3.5E-07 2.9E-07 2.9E-07 1.7E-08 7.5E-07 5.8E-08 1.2E-08
OCDD 3.7E-11 4.4E-07 3.7E-07 3.7E-07 2.2E-08 9.6E-07 7.4E-08 1.5E-08
2,3,7,8-TCDF 4.0E-11 4.8E-07 4.0E-07 4.0E-07 2.4E-08 1.0E-06 8.0E-08 1.6E-08
1,2,3,7,8-PeCDF 8.0E-11 9.6E-07 8.0E-07 8.0E-07 4.8E-08 2.1E-06 1.6E-07 3.2E-08
2,3,4,7,8-PeCDF 1.6E-10 1.9E-06 1.6E-06 1.6E-06 9.6E-08 4.2E-06 3.2E-07 6.4E-08
1,2,3,4,7,8-HxCDF 2.6E-10 3.1E-06 2.6E-06 2.6E-06 1.6E-07 6.8E-06 5.2E-07 1.0E-07
1,2,3,6,7,8-HxCDF 1.6E-10 1.9E-06 1.6E-06 1.6E-06 9.6E-08 4.2E-06 3.2E-07 6.4E-08
2,3,4,6,7,8-HxCDF 1.9E-10 2.3E-06 1.9E-06 1.9E-06 1.1E-07 4.9E-06 3.8E-07 7.6E-08
1,2,3,7,8,9-HxCDF 1.2E-10 1.4E-06 1.2E-06 1.2E-06 7.2E-08 3.1E-06 2.4E-07 4.8E-08
1,2,3,4,6,7,8-HpCDF 7.3E-10 8.8E-06 7.3E-06 7.3E-06 4.4E-07 1.9E-05 1.5E-06 2.9E-07
TABLE OR APPENDIX ???
1.3 CLASS WASTE MATERIAL PER EVENT (1-HOUR)
CORRECTED EMISSION RATES (LBS/HR)
ATK PROMONTORY, UTAH
PAGE 3 OF 5
1 2 3 4 5 1 2
Analyte
Corrected
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/hour)M-225 Quantities
(lbs/hr)
1,2,3,4,7,8,9-HpCDF 1.9E-10 2.3E-06 1.9E-06 1.9E-06 1.1E-07 4.9E-06 3.8E-07 7.6E-08
OCDF 5.2E-10 6.2E-06 5.2E-06 5.2E-06 3.1E-07 1.4E-05 1.0E-06 2.1E-07
Carbonyls
2,5-Dimethylbenzaldehyde 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
Acetaldehyde 7.5E-05 9.0E-01 7.5E-01 7.5E-01 4.5E-02 2.0E+00 1.5E-01 3.0E-02
Acetone 1.5E-05 1.8E-01 1.5E-01 1.5E-01 9.0E-03 3.9E-01 3.0E-02 6.0E-03
Benzaldehyde 7.3E-06 8.8E-02 7.3E-02 7.3E-02 4.4E-03 1.9E-01 1.5E-02 2.9E-03
Crotonaldehyde 6.8E-06 8.2E-02 6.8E-02 6.8E-02 4.1E-03 1.8E-01 1.4E-02 2.7E-03
Formaldehyde 4.0E-05 4.8E-01 4.0E-01 4.0E-01 2.4E-02 1.0E+00 8.0E-02 1.6E-02
Hexanal 8.2E-06 9.8E-02 8.2E-02 8.2E-02 4.9E-03 2.1E-01 1.6E-02 3.3E-03
Isopentanal 6.8E-06 8.2E-02 6.8E-02 6.8E-02 4.1E-03 1.8E-01 1.4E-02 2.7E-03
m,p-Tolualdehyde 6.8E-06 8.2E-02 6.8E-02 6.8E-02 4.1E-03 1.8E-01 1.4E-02 2.7E-03
MEK/Butyraldehydes 1.2E-05 1.4E-01 1.2E-01 1.2E-01 7.2E-03 3.1E-01 2.4E-02 4.8E-03
o-Tolualdehyde 2.3E-05 2.8E-01 2.3E-01 2.3E-01 1.4E-02 6.0E-01 4.6E-02 9.2E-03
Pentanal 1.2E-05 1.4E-01 1.2E-01 1.2E-01 7.2E-03 3.1E-01 2.4E-02 4.8E-03
Propanal 3.8E-05 4.6E-01 3.8E-01 3.8E-01 2.3E-02 9.9E-01 7.6E-02 1.5E-02
HCl/Cl2/NH3
HCl 1.8E-02 2.2E+02 1.8E+02 1.8E+02 1.1E+01 4.7E+02 3.6E+01 7.2E+00
Cl2 1.5E-03 1.8E+01 1.5E+01 1.5E+01 9.0E-01 3.9E+01 3.0E+00 6.0E-01
NH3 2.2E-05 2.6E-01 2.2E-01 2.2E-01 1.3E-02 5.7E-01 4.4E-02 8.8E-03
HCN 1.2E-05 1.4E-01 1.2E-01 1.2E-01 7.2E-03 3.1E-01 2.4E-02 4.8E-03

VOCs
TNMOC 8.1E-04 9.7E+00 8.1E+00 8.1E+00 4.9E-01 2.1E+01 1.6E+00 3.2E-01
1,1,1-Trichloroethane 4.5E-07 5.4E-03 4.5E-03 4.5E-03 2.7E-04 1.2E-02 9.0E-04 1.8E-04
1,1,2,2-Tetrachloroethane 2.1E-07 2.5E-03 2.1E-03 2.1E-03 1.3E-04 5.5E-03 4.2E-04 8.4E-05
1,1,2-Trichloroethane 3.6E-07 4.3E-03 3.6E-03 3.6E-03 2.2E-04 9.4E-03 7.2E-04 1.4E-04
1,1-Dichloroethane 1.6E-07 1.9E-03 1.6E-03 1.6E-03 9.6E-05 4.2E-03 3.2E-04 6.4E-05
1,1-Dichloroethene 2.2E-07 2.6E-03 2.2E-03 2.2E-03 1.3E-04 5.7E-03 4.4E-04 8.8E-05
1,2,3-Trimethylbenzene 2.1E-07 2.5E-03 2.1E-03 2.1E-03 1.3E-04 5.5E-03 4.2E-04 8.4E-05
1,2,4-Trichlorobenzene 6.3E-07 7.6E-03 6.3E-03 6.3E-03 3.8E-04 1.6E-02 1.3E-03 2.5E-04
1,2,4-Trimethylbenzene 5.2E-06 6.2E-02 5.2E-02 5.2E-02 3.1E-03 1.4E-01 1.0E-02 2.1E-03
1,2-Dibromomethane (EDB)4.4E-07 5.3E-03 4.4E-03 4.4E-03 2.6E-04 1.1E-02 8.8E-04 1.8E-04
1,2-Dichlorobenzene 2.4E-07 2.9E-03 2.4E-03 2.4E-03 1.4E-04 6.2E-03 4.8E-04 9.6E-05
1,2-Dichloroethane 2.7E-07 3.2E-03 2.7E-03 2.7E-03 1.6E-04 7.0E-03 5.4E-04 1.1E-04
1,2-Dichloropropane 1.8E-07 2.2E-03 1.8E-03 1.8E-03 1.1E-04 4.7E-03 3.6E-04 7.2E-05
1,3,5-Trimethylbenzene 2.0E-06 2.4E-02 2.0E-02 2.0E-02 1.2E-03 5.2E-02 4.0E-03 8.0E-04
1,3-Butadiene 2.0E-05 2.4E-01 2.0E-01 2.0E-01 1.2E-02 5.2E-01 4.0E-02 8.0E-03
1,3-Dichlorobenzene 2.2E-07 2.6E-03 2.2E-03 2.2E-03 1.3E-04 5.7E-03 4.4E-04 8.8E-05
1,3-Diethylbenzene 2.5E-07 3.0E-03 2.5E-03 2.5E-03 1.5E-04 6.5E-03 5.0E-04 1.0E-04
1,4-Dichlorobenzene 3.7E-07 4.4E-03 3.7E-03 3.7E-03 2.2E-04 9.6E-03 7.4E-04 1.5E-04
1,4-Diethylbenzene 3.3E-07 4.0E-03 3.3E-03 3.3E-03 2.0E-04 8.6E-03 6.6E-04 1.3E-04
1,4-Dioxane 3.2E-07 3.8E-03 3.2E-03 3.2E-03 1.9E-04 8.3E-03 6.4E-04 1.3E-04
1-Butene 2.1E-05 2.5E-01 2.1E-01 2.1E-01 1.3E-02 5.5E-01 4.2E-02 8.4E-03
1-Hexene 2.0E-05 2.4E-01 2.0E-01 2.0E-01 1.2E-02 5.2E-01 4.0E-02 8.0E-03
1-Pentene 1.2E-05 1.4E-01 1.2E-01 1.2E-01 7.2E-03 3.1E-01 2.4E-02 4.8E-03
2,2,4-Trimethylpentane 2.3E-06 2.8E-02 2.3E-02 2.3E-02 1.4E-03 6.0E-02 4.6E-03 9.2E-04
2,2-Dimethylbutane 4.4E-07 5.3E-03 4.4E-03 4.4E-03 2.6E-04 1.1E-02 8.8E-04 1.8E-04
2,3,4-Trimethylpentane 1.4E-07 1.7E-03 1.4E-03 1.4E-03 8.4E-05 3.6E-03 2.8E-04 5.6E-05
2,3-Dimethylbutane 2.9E-06 3.5E-02 2.9E-02 2.9E-02 1.7E-03 7.5E-02 5.8E-03 1.2E-03
2,3-Dimethylpentane 2.7E-06 3.2E-02 2.7E-02 2.7E-02 1.6E-03 7.0E-02 5.4E-03 1.1E-03
2,4-Dimethylpentane 5.5E-07 6.6E-03 5.5E-03 5.5E-03 3.3E-04 1.4E-02 1.1E-03 2.2E-04
2-Butanone (MEK)3.9E-06 4.7E-02 3.9E-02 3.9E-02 2.3E-03 1.0E-01 7.8E-03 1.6E-03
2-Ethyltoluene 2.2E-07 2.6E-03 2.2E-03 2.2E-03 1.3E-04 5.7E-03 4.4E-04 8.8E-05
2-Hexanone 4.4E-07 5.3E-03 4.4E-03 4.4E-03 2.6E-04 1.1E-02 8.8E-04 1.8E-04
2-Methylheptane 2.7E-06 3.2E-02 2.7E-02 2.7E-02 1.6E-03 7.0E-02 5.4E-03 1.1E-03
2-Methylhexane 4.4E-06 5.3E-02 4.4E-02 4.4E-02 2.6E-03 1.1E-01 8.8E-03 1.8E-03
2-Methylpentane 5.3E-06 6.4E-02 5.3E-02 5.3E-02 3.2E-03 1.4E-01 1.1E-02 2.1E-03
2-Nitropropane 2.8E-06 3.4E-02 2.8E-02 2.8E-02 1.7E-03 7.3E-02 5.6E-03 1.1E-03
2-Propanol 1.5E-07 1.8E-03 1.5E-03 1.5E-03 9.0E-05 3.9E-03 3.0E-04 6.0E-05
3-Chloropropene 4.7E-06 5.6E-02 4.7E-02 4.7E-02 2.8E-03 1.2E-01 9.4E-03 1.9E-03
3-Ethyltoluene 4.8E-06 5.8E-02 4.8E-02 4.8E-02 2.9E-03 1.2E-01 9.6E-03 1.9E-03
3-Methylheptane 3.5E-06 4.2E-02 3.5E-02 3.5E-02 2.1E-03 9.1E-02 7.0E-03 1.4E-03
3-Methylhexane 5.2E-06 6.2E-02 5.2E-02 5.2E-02 3.1E-03 1.4E-01 1.0E-02 2.1E-03
3-Methylpentane 7.1E-06 8.5E-02 7.1E-02 7.1E-02 4.3E-03 1.8E-01 1.4E-02 2.8E-03
4-Ethyltoluene 5.3E-06 6.4E-02 5.3E-02 5.3E-02 3.2E-03 1.4E-01 1.1E-02 2.1E-03
4-Methyl-2-pentanone 3.5E-07 4.2E-03 3.5E-03 3.5E-03 2.1E-04 9.1E-03 7.0E-04 1.4E-04
Acetone 2.3E-05 2.8E-01 2.3E-01 2.3E-01 1.4E-02 6.0E-01 4.6E-02 9.2E-03
TABLE OR APPENDIX ???
1.3 CLASS WASTE MATERIAL PER EVENT (1-HOUR)
CORRECTED EMISSION RATES (LBS/HR)
ATK PROMONTORY, UTAH
PAGE 4 OF 5
1 2 3 4 5 1 2
Analyte
Corrected
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/hour)M-225 Quantities
(lbs/hr)
Acetonitrile 9.2E-06 1.1E-01 9.2E-02 9.2E-02 5.5E-03 2.4E-01 1.8E-02 3.7E-03
Acetylene 7.4E-05 8.9E-01 7.4E-01 7.4E-01 4.4E-02 1.9E+00 1.5E-01 3.0E-02
Acrylonitrile 1.0E-05 1.2E-01 1.0E-01 1.0E-01 6.0E-03 2.6E-01 2.0E-02 4.0E-03
alpha-Chlorotoluene 2.8E-07 3.4E-03 2.8E-03 2.8E-03 1.7E-04 7.3E-03 5.6E-04 1.1E-04
Benzene 4.4E-05 5.3E-01 4.4E-01 4.4E-01 2.6E-02 1.1E+00 8.8E-02 1.8E-02
Bromodichloromethane 3.9E-07 4.7E-03 3.9E-03 3.9E-03 2.3E-04 1.0E-02 7.8E-04 1.6E-04
Bromoform 6.3E-07 7.6E-03 6.3E-03 6.3E-03 3.8E-04 1.6E-02 1.3E-03 2.5E-04
Bromomethane 3.1E-07 3.7E-03 3.1E-03 3.1E-03 1.9E-04 8.1E-03 6.2E-04 1.2E-04
Butane 1.8E-05 2.2E-01 1.8E-01 1.8E-01 1.1E-02 4.7E-01 3.6E-02 7.2E-03
Carbon Disulfide 9.4E-06 1.1E-01 9.4E-02 9.4E-02 5.6E-03 2.4E-01 1.9E-02 3.8E-03
Carbon Tetrachloride 1.5E-05 1.8E-01 1.5E-01 1.5E-01 9.0E-03 3.9E-01 3.0E-02 6.0E-03
Chloroacetonitrile 5.6E-07 6.7E-03 5.6E-03 5.6E-03 3.4E-04 1.5E-02 1.1E-03 2.2E-04
Chlorobenzene 2.5E-06 3.0E-02 2.5E-02 2.5E-02 1.5E-03 6.5E-02 5.0E-03 1.0E-03
Chloroethane 1.3E-07 1.6E-03 1.3E-03 1.3E-03 7.8E-05 3.4E-03 2.6E-04 5.2E-05
Chloroform 6.1E-06 7.3E-02 6.1E-02 6.1E-02 3.7E-03 1.6E-01 1.2E-02 2.4E-03
Chloromethane 1.4E-05 1.7E-01 1.4E-01 1.4E-01 8.4E-03 3.6E-01 2.8E-02 5.6E-03
cis-1,2-Dichloroethene 2.3E-07 2.8E-03 2.3E-03 2.3E-03 1.4E-04 6.0E-03 4.6E-04 9.2E-05
cis-1,3-Dichloropropene 1.3E-06 1.6E-02 1.3E-02 1.3E-02 7.8E-04 3.4E-02 2.6E-03 5.2E-04
cis-2-Butene 1.4E-06 1.7E-02 1.4E-02 1.4E-02 8.4E-04 3.6E-02 2.8E-03 5.6E-04
cis-2-Pentene 1.7E-07 2.0E-03 1.7E-03 1.7E-03 1.0E-04 4.4E-03 3.4E-04 6.8E-05
Cumene 2.1E-07 2.5E-03 2.1E-03 2.1E-03 1.3E-04 5.5E-03 4.2E-04 8.4E-05
Cyclohexane 2.5E-06 3.0E-02 2.5E-02 2.5E-02 1.5E-03 6.5E-02 5.0E-03 1.0E-03
Cyclopentane 1.8E-06 2.2E-02 1.8E-02 1.8E-02 1.1E-03 4.7E-02 3.6E-03 7.2E-04
Decane 1.7E-05 2.0E-01 1.7E-01 1.7E-01 1.0E-02 4.4E-01 3.4E-02 6.8E-03
Dibromochloromethane 4.4E-07 5.3E-03 4.4E-03 4.4E-03 2.6E-04 1.1E-02 8.8E-04 1.8E-04
Ethane 1.7E-05 2.0E-01 1.7E-01 1.7E-01 1.0E-02 4.4E-01 3.4E-02 6.8E-03
Ethanol 1.6E-06 1.9E-02 1.6E-02 1.6E-02 9.6E-04 4.2E-02 3.2E-03 6.4E-04
Ethene 1.5E-04 1.8E+00 1.5E+00 1.5E+00 9.0E-02 3.9E+00 3.0E-01 6.0E-02
Ethyl benzene 2.8E-06 3.4E-02 2.8E-02 2.8E-02 1.7E-03 7.3E-02 5.6E-03 1.1E-03
Ethyl ether 1.2E-06 1.4E-02 1.2E-02 1.2E-02 7.2E-04 3.1E-02 2.4E-03 4.8E-04
Ethyl Methacrylate 7.8E-07 9.4E-03 7.8E-03 7.8E-03 4.7E-04 2.0E-02 1.6E-03 3.1E-04
Heptane 7.2E-06 8.6E-02 7.2E-02 7.2E-02 4.3E-03 1.9E-01 1.4E-02 2.9E-03
Hexachlorobutadiene 8.5E-07 1.0E-02 8.5E-03 8.5E-03 5.1E-04 2.2E-02 1.7E-03 3.4E-04
Hexane 9.8E-06 1.2E-01 9.8E-02 9.8E-02 5.9E-03 2.5E-01 2.0E-02 3.9E-03
Isobutane 2.8E-06 3.4E-02 2.8E-02 2.8E-02 1.7E-03 7.3E-02 5.6E-03 1.1E-03
Isopentane 2.0E-05 2.4E-01 2.0E-01 2.0E-01 1.2E-02 5.2E-01 4.0E-02 8.0E-03
m,p-Xylene 1.0E-05 1.2E-01 1.0E-01 1.0E-01 6.0E-03 2.6E-01 2.0E-02 4.0E-03
Methacrylonitrile 4.9E-06 5.9E-02 4.9E-02 4.9E-02 2.9E-03 1.3E-01 9.8E-03 2.0E-03
Methyl Acrylate 5.9E-07 7.1E-03 5.9E-03 5.9E-03 3.5E-04 1.5E-02 1.2E-03 2.4E-04
Methyl Methacrylate 8.1E-07 9.7E-03 8.1E-03 8.1E-03 4.9E-04 2.1E-02 1.6E-03 3.2E-04
Methyl tert-butyl ether 2.1E-07 2.5E-03 2.1E-03 2.1E-03 1.3E-04 5.5E-03 4.2E-04 8.4E-05
Methylcyclohexane 6.1E-06 7.3E-02 6.1E-02 6.1E-02 3.7E-03 1.6E-01 1.2E-02 2.4E-03
Methylcyclopentane 5.6E-06 6.7E-02 5.6E-02 5.6E-02 3.4E-03 1.5E-01 1.1E-02 2.2E-03
Methylene chloride 7.1E-06 8.5E-02 7.1E-02 7.1E-02 4.3E-03 1.8E-01 1.4E-02 2.8E-03
n-Butylchloride 5.8E-06 7.0E-02 5.8E-02 5.8E-02 3.5E-03 1.5E-01 1.2E-02 2.3E-03
Nonane 1.3E-05 1.6E-01 1.3E-01 1.3E-01 7.8E-03 3.4E-01 2.6E-02 5.2E-03
Octane 7.5E-06 9.0E-02 7.5E-02 7.5E-02 4.5E-03 2.0E-01 1.5E-02 3.0E-03
o-Xylene 3.5E-06 4.2E-02 3.5E-02 3.5E-02 2.1E-03 9.1E-02 7.0E-03 1.4E-03
Pentane 1.9E-05 2.3E-01 1.9E-01 1.9E-01 1.1E-02 4.9E-01 3.8E-02 7.6E-03
Propane 8.7E-06 1.0E-01 8.7E-02 8.7E-02 5.2E-03 2.3E-01 1.7E-02 3.5E-03
Propylbenzene 1.0E-06 1.2E-02 1.0E-02 1.0E-02 6.0E-04 2.6E-02 2.0E-03 4.0E-04
Propylene 4.3E-05 5.2E-01 4.3E-01 4.3E-01 2.6E-02 1.1E+00 8.6E-02 1.7E-02
Styrene 9.9E-07 1.2E-02 9.9E-03 9.9E-03 5.9E-04 2.6E-02 2.0E-03 4.0E-04
Tetrachloroethene 2.5E-06 3.0E-02 2.5E-02 2.5E-02 1.5E-03 6.5E-02 5.0E-03 1.0E-03
Tetrahydrofuran 6.4E-07 7.7E-03 6.4E-03 6.4E-03 3.8E-04 1.7E-02 1.3E-03 2.6E-04
Toluene 1.8E-05 2.2E-01 1.8E-01 1.8E-01 1.1E-02 4.7E-01 3.6E-02 7.2E-03
trans-1,2-Dichloroethene 3.6E-07 4.3E-03 3.6E-03 3.6E-03 2.2E-04 9.4E-03 7.2E-04 1.4E-04
trans-1,3-Dichloropropene 3.0E-07 3.6E-03 3.0E-03 3.0E-03 1.8E-04 7.8E-03 6.0E-04 1.2E-04
trans-2-butene 7.7E-06 9.2E-02 7.7E-02 7.7E-02 4.6E-03 2.0E-01 1.5E-02 3.1E-03
trans-2-Pentene 1.7E-06 2.0E-02 1.7E-02 1.7E-02 1.0E-03 4.4E-02 3.4E-03 6.8E-04
Trichloroethene 9.4E-07 1.1E-02 9.4E-03 9.4E-03 5.6E-04 2.4E-02 1.9E-03 3.8E-04
Undecane 1.2E-05 1.4E-01 1.2E-01 1.2E-01 7.2E-03 3.1E-01 2.4E-02 4.8E-03
Vinyl chloride 7.6E-06 9.1E-02 7.6E-02 7.6E-02 4.6E-03 2.0E-01 1.5E-02 3.0E-03

CEM
CO2 6.9E-01 8.3E+03 6.9E+03 6.9E+03 4.1E+02 1.8E+04 1.4E+03 2.8E+02
CO 4.7E-03 5.6E+01 4.7E+01 4.7E+01 2.8E+00 1.2E+02 9.4E+00 1.9E+00
NOX 5.8E-03 7.0E+01 5.8E+01 5.8E+01 3.5E+00 1.5E+02 1.2E+01 2.3E+00
SO2 4.1E-04 4.9E+00 4.1E+00 4.1E+00 2.5E-01 1.1E+01 8.2E-01 1.6E-01
Highlighted analytes were not detected during the Bang Box testing program
TABLE OR APPENDIX ???
1.3 CLASS WASTE MATERIAL PER EVENT (1-HOUR)
CORRECTED EMISSION RATES (LBS/HR)
ATK PROMONTORY, UTAH
PAGE 5 OF 5
1 2 3 4 5 1 2
Analyte
Corrected
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/hour)M-225 Quantities
(lbs/hr)
CEM - Continuous Emissions Monitoring
CL2 - chlorine
CO - carbon monoxide
CO2 - carbon dioxide
HCL - hydrogen chloride
HCN - hydrogen cyanide
NH3 - ammonia
NOX - nitrogen oxide
OCDD - 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin
OCDF - 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-furan
PM10 - particulate matter less than 10 microns in aerodynamic diameter
PM2.5 - particulate matter less than 2.5 microns in aerodynamic diameter
SO2 - sulfur dioxide
SVOCs - semi-volatile organic compounds
TNMOC - total non-methane organic carbon
TSP - Total suspended particulates
VOCs - volatile organic compounds
TABLE OR APPENDIX 3-???
1.3 CLASS WASTE MATERIAL
CORRECTED ANNUAL EMISSION RATES (LBS/YR)
ATK PROMONTORY, UTAH
PAGE 1 OF 5
1 2 3 4 5 1 2
Particulates
TSP 1.4E-01 5.2E+05 7.3E+04 7.3E+04 5.0E+02 1.1E+04 6.7E+03 3.4E+02
PM10 8.6E-02 3.2E+05 4.5E+04 4.5E+04 3.1E+02 6.7E+03 4.1E+03 2.1E+02
PM2.5 5.9E-02 2.2E+05 3.1E+04 3.1E+04 2.1E+02 4.6E+03 2.8E+03 1.4E+02

Metals
Aluminum 4.0E-02 1.5E+05 2.1E+04 2.1E+04 1.4E+02 3.1E+03 1.9E+03 9.6E+01
Antimony 2.9E-05 1.1E+02 1.5E+01 1.5E+01 1.0E-01 2.3E+00 1.4E+00 7.0E-02
Arsenic 3.0E-07 1.1E+00 1.6E-01 1.6E-01 1.1E-03 2.3E-02 1.4E-02 7.2E-04
Barium 4.9E-06 1.8E+01 2.5E+00 2.5E+00 1.8E-02 3.8E-01 2.4E-01 1.2E-02
Cadmium 3.1E-07 1.2E+00 1.6E-01 1.6E-01 1.1E-03 2.4E-02 1.5E-02 7.4E-04
Chromium 2.0E-05 7.5E+01 1.0E+01 1.0E+01 7.2E-02 1.6E+00 9.6E-01 4.8E-02
Cobalt 3.1E-07 1.2E+00 1.6E-01 1.6E-01 1.1E-03 2.4E-02 1.5E-02 7.4E-04
Copper 2.5E-05 9.4E+01 1.3E+01 1.3E+01 9.0E-02 2.0E+00 1.2E+00 6.0E-02
Lead 3.4E-05 1.3E+02 1.8E+01 1.8E+01 1.2E-01 2.7E+00 1.6E+00 8.2E-02
Magnesium 2.9E-05 1.1E+02 1.5E+01 1.5E+01 1.0E-01 2.3E+00 1.4E+00 7.0E-02
Manganese 9.3E-05 3.5E+02 4.8E+01 4.8E+01 3.3E-01 7.3E+00 4.5E+00 2.2E-01
Mercury 3.7E-08 1.4E-01 1.9E-02 1.9E-02 1.3E-04 2.9E-03 1.8E-03 8.9E-05
Nickel 5.8E-05 2.2E+02 3.0E+01 3.0E+01 2.1E-01 4.5E+00 2.8E+00 1.4E-01
Phosphorus 1.0E-04 3.7E+02 5.2E+01 5.2E+01 3.6E-01 7.8E+00 4.8E+00 2.4E-01
Selenium 1.7E-06 6.4E+00 8.8E-01 8.8E-01 6.1E-03 1.3E-01 8.2E-02 4.1E-03
Silver 9.5E-07 3.6E+00 4.9E-01 4.9E-01 3.4E-03 7.4E-02 4.6E-02 2.3E-03
Thallium 2.1E-06 7.9E+00 1.1E+00 1.1E+00 7.6E-03 1.6E-01 1.0E-01 5.0E-03
Zinc 3.5E-05 1.3E+02 1.8E+01 1.8E+01 1.3E-01 2.7E+00 1.7E+00 8.4E-02
Perchlorate 2.5E-07 2.7E-02 1.3E-01 1.3E-01 9.0E-04 2.0E-02 1.2E-02 6.0E-04

SVOCs
1,2,4,5-Tetrachlorobenzene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 6.5E-04
1,2,4-Trichlorobenzene 3.2E-07 1.2E+00 1.7E-01 1.7E-01 1.2E-03 2.5E-02 1.5E-02 1.3E-04
1,2-Dichlorobenzene 2.8E-07 1.0E+00 1.5E-01 1.5E-01 1.0E-03 2.2E-02 1.3E-02 1.1E-04
1,3,5-Trinitrobenzene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
1,3-Dichlorobenzene 3.1E-07 1.2E+00 1.6E-01 1.6E-01 1.1E-03 2.4E-02 1.5E-02 1.2E-04
1,3-Dinitrobenzene 2.8E-07 1.0E+00 1.5E-01 1.5E-01 1.0E-03 2.2E-02 1.3E-02 1.1E-04
1,4-Dichlorobenzene 2.9E-07 1.1E+00 1.5E-01 1.5E-01 1.0E-03 2.3E-02 1.4E-02 1.2E-04
1-Chloronaphthalene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
1-Naphthylamine 5.5E-06 2.1E+01 2.9E+00 2.9E+00 2.0E-02 4.3E-01 2.6E-01 2.2E-03
2,3,4,6-Tetrachlorophenol 3.6E-07 1.3E+00 1.9E-01 1.9E-01 1.3E-03 2.8E-02 1.7E-02 1.4E-04
2,4,5-Trichlorophenol 7.1E-07 2.7E+00 3.7E-01 3.7E-01 2.6E-03 5.5E-02 3.4E-02 2.8E-04
2,4,6-Trichlorophenol 1.30E-06 4.9E+00 6.8E-01 6.8E-01 4.7E-03 1.0E-01 6.2E-02 5.2E-04
2,4-Dichlorophenol 9.3E-07 3.5E+00 4.8E-01 4.8E-01 3.3E-03 7.3E-02 4.5E-02 3.7E-04
2,4-Dimethylphenol 3.5E-06 1.3E+01 1.8E+00 1.8E+00 1.3E-02 2.7E-01 1.7E-01 1.4E-03
2,4-Dinitrophenol 1.2E-05 4.5E+01 6.2E+00 6.2E+00 4.3E-02 9.4E-01 5.8E-01 4.8E-03
2,4-Dinitrotoluene 3.1E-07 1.2E+00 1.6E-01 1.6E-01 1.1E-03 2.4E-02 1.5E-02 1.2E-04
2,6-Dichlorophenol 4.0E-07 1.5E+00 2.1E-01 2.1E-01 1.4E-03 3.1E-02 1.9E-02 1.6E-04
2,6-Dinitrotoluene 5.6E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.4E-02 2.7E-02 2.2E-04
2-Acetylaminofluorene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
2-Chloronaphthalene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
2-Chlorophenol 1.9E-06 7.1E+00 9.9E-01 9.9E-01 6.8E-03 1.5E-01 9.1E-02 7.6E-04
2-Methylnaphthalene 3.6E-06 1.3E+01 1.9E+00 1.9E+00 1.3E-02 2.8E-01 1.7E-01 1.4E-03
2-Methylphenol 1.6E-06 6.0E+00 8.3E-01 8.3E-01 5.8E-03 1.2E-01 7.7E-02 6.4E-04
2-Naphthylamine 5.5E-06 2.1E+01 2.9E+00 2.9E+00 2.0E-02 4.3E-01 2.6E-01 2.2E-03
2-Nitroaniline 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
2-Nitrophenol 3.9E-07 1.5E+00 2.0E-01 2.0E-01 1.4E-03 3.0E-02 1.9E-02 1.6E-04
3,3'-Dichlorobenzidine 4.1E-06 1.5E+01 2.1E+00 2.1E+00 1.5E-02 3.2E-01 2.0E-01 1.6E-03
3,3'-Dimethylbenzidine 2.7E-05 1.0E+02 1.4E+01 1.4E+01 9.7E-02 2.1E+00 1.3E+00 1.1E-02
3-Methylcholanthrene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
3-Methylphenol & 4-Methylphenol 1.1E-06 4.1E+00 5.7E-01 5.7E-01 4.0E-03 8.6E-02 5.3E-02 4.4E-04
3-Nitroaniline 1.1E-06 4.1E+00 5.7E-01 5.7E-01 4.0E-03 8.6E-02 5.3E-02 4.4E-04
4,6-Dinitro-2-methylphenol 4.8E-06 1.8E+01 2.5E+00 2.5E+00 1.7E-02 3.7E-01 2.3E-01 1.9E-03
4-Aminobiphenyl 5.5E-06 2.1E+01 2.9E+00 2.9E+00 2.0E-02 4.3E-01 2.6E-01 2.2E-03
4-Bromophenyl phenyl ether 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
4-Chloro-3-methylphenol 3.4E-07 1.3E+00 1.8E-01 1.8E-01 1.2E-03 2.7E-02 1.6E-02 1.4E-04
4-Chloroaniline 3.3E-06 1.2E+01 1.7E+00 1.7E+00 1.2E-02 2.6E-01 1.6E-01 1.3E-03
4-Nitroaniline 1.1E-06 4.1E+00 5.7E-01 5.7E-01 4.0E-03 8.6E-02 5.3E-02 4.4E-04
4-Nitrophenol 1.8E-06 6.7E+00 9.4E-01 9.4E-01 6.5E-03 1.4E-01 8.6E-02 7.2E-04
7,12-Dimethylbenz(a)anthracene 2.8E-07 1.0E+00 1.5E-01 1.5E-01 1.0E-03 2.2E-02 1.3E-02 1.1E-04
Acenaphthene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Acenaphthylene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Acetophenone 2.7E-06 1.0E+01 1.4E+00 1.4E+00 9.7E-03 2.1E-01 1.3E-01 1.1E-03
Aniline 4.0E-06 1.5E+01 2.1E+00 2.1E+00 1.4E-02 3.1E-01 1.9E-01 1.6E-03
Analyte
Corrected
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/year)M-225 Quantities
(lbs/year)
TABLE OR APPENDIX 3-???
1.3 CLASS WASTE MATERIAL
CORRECTED ANNUAL EMISSION RATES (LBS/YR)
ATK PROMONTORY, UTAH
PAGE 2 OF 5
1 2 3 4 5 1 2
Analyte
Corrected
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/year)M-225 Quantities
(lbs/year)
Anthracene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Benzidine 2.8E-05 1.0E+02 1.5E+01 1.5E+01 1.0E-01 2.2E+00 1.3E+00 1.1E-02
Benzo(a)anthracene 3.2E-07 1.2E+00 1.7E-01 1.7E-01 1.2E-03 2.5E-02 1.5E-02 1.3E-04
Benzo(a)pyrene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Benzo(b)fluoranthene 6.0E-07 2.2E+00 3.1E-01 3.1E-01 2.2E-03 4.7E-02 2.9E-02 2.4E-04
Benzo(ghi)perylene 3.4E-07 1.3E+00 1.8E-01 1.8E-01 1.2E-03 2.7E-02 1.6E-02 1.4E-04
Benzo(k)fluoranthene 8.8E-07 3.3E+00 4.6E-01 4.6E-01 3.2E-03 6.9E-02 4.2E-02 3.5E-04
Benzoic acid 6.2E-05 2.3E+02 3.2E+01 3.2E+01 2.2E-01 4.8E+00 3.0E+00 2.5E-02
Benzyl alcohol 1.9E-05 7.1E+01 9.9E+00 9.9E+00 6.8E-02 1.5E+00 9.1E-01 7.6E-03
bis(2-Chloroethoxy)methane 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
bis(2-Chloroethyl) ether 3.1E-07 1.2E+00 1.6E-01 1.6E-01 1.1E-03 2.4E-02 1.5E-02 1.2E-04
bis(2-Chloroisopropyl) ether 4.2E-07 1.6E+00 2.2E-01 2.2E-01 1.5E-03 3.3E-02 2.0E-02 1.7E-04
bis(2-Ethylhexyl) phthalate 5.5E-06 2.1E+01 2.9E+00 2.9E+00 2.0E-02 4.3E-01 2.6E-01 2.2E-03
Butyl benzyl phthalate 3.3E-07 1.2E+00 1.7E-01 1.7E-01 1.2E-03 2.6E-02 1.6E-02 1.3E-04
Carbazole 3.5E-07 1.3E+00 1.8E-01 1.8E-01 1.3E-03 2.7E-02 1.7E-02 1.4E-04
Chrysene 3.5E-07 1.3E+00 1.8E-01 1.8E-01 1.3E-03 2.7E-02 1.7E-02 1.4E-04
Dibenz(a,h)anthracene 3.3E-07 1.2E+00 1.7E-01 1.7E-01 1.2E-03 2.6E-02 1.6E-02 1.3E-04
Dibenzofuran 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Diethyl phthalate 4.0E-07 1.5E+00 2.1E-01 2.1E-01 1.4E-03 3.1E-02 1.9E-02 1.6E-04
Dimethyl phthalate 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Di-n-butyl phthalate 5.5E-06 2.1E+01 2.9E+00 2.9E+00 2.0E-02 4.3E-01 2.6E-01 2.2E-03
Di-n-octyl phthalate 3.7E-06 1.4E+01 1.9E+00 1.9E+00 1.3E-02 2.9E-01 1.8E-01 1.5E-03
Diphenylamine 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Ethyl methanesulfonate 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Fluoranthene 4.0E-07 1.5E+00 2.1E-01 2.1E-01 1.4E-03 3.1E-02 1.9E-02 1.6E-04
Fluorene 4.2E-07 1.6E+00 2.2E-01 2.2E-01 1.5E-03 3.3E-02 2.0E-02 1.7E-04
Hexachlorobenzene 4.7E-06 1.8E+01 2.4E+00 2.4E+00 1.7E-02 3.7E-01 2.3E-01 1.9E-03
Hexachlorobutadiene 4.1E-07 1.5E+00 2.1E-01 2.1E-01 1.5E-03 3.2E-02 2.0E-02 1.6E-04
Hexachlorocyclopentadiene 5.5E-06 2.1E+01 2.9E+00 2.9E+00 2.0E-02 4.3E-01 2.6E-01 2.2E-03
Hexachloroethane 3.0E-07 1.1E+00 1.6E-01 1.6E-01 1.1E-03 2.3E-02 1.4E-02 1.2E-04
Hexachloropropene 3.9E-07 1.5E+00 2.0E-01 2.0E-01 1.4E-03 3.0E-02 1.9E-02 1.6E-04
Indeno(1,2,3-cd)pyrene 3.0E-07 1.1E+00 1.6E-01 1.6E-01 1.1E-03 2.3E-02 1.4E-02 1.2E-04
Isophorone 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Methyl methanesulfonate 3.0E-07 1.1E+00 1.6E-01 1.6E-01 1.1E-03 2.3E-02 1.4E-02 1.2E-04
Naphthalene 1.3E-05 4.9E+01 6.8E+00 6.8E+00 4.7E-02 1.0E+00 6.2E-01 5.2E-03
Nitrobenzene 3.1E-07 1.2E+00 1.6E-01 1.6E-01 1.1E-03 2.4E-02 1.5E-02 1.2E-04
N-Nitro-o-toluidine 4.4E-06 1.6E+01 2.3E+00 2.3E+00 1.6E-02 3.4E-01 2.1E-01 1.8E-03
N-Nitrosodiethylamine 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
N-Nitrosodimethylamine 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
N-Nitrosodi-n-butylamine 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
N-Nitrosodi-n-propylamine 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
N-Nitrosodiphenylamine 4.8E-07 1.8E+00 2.5E-01 2.5E-01 1.7E-03 3.7E-02 2.3E-02 1.9E-04
N-Nitrosomethylethylamine 4.5E-07 1.7E+00 2.3E-01 2.3E-01 1.6E-03 3.5E-02 2.2E-02 1.8E-04
N-Nitrosomorpholine 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
o-Toluidine 3.5E-06 1.3E+01 1.8E+00 1.8E+00 1.3E-02 2.7E-01 1.7E-01 1.4E-03
p-Dimethylaminoazobenzene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Pentachlorobenzene 3.0E-07 1.1E+00 1.6E-01 1.6E-01 1.1E-03 2.3E-02 1.4E-02 1.2E-04
Pentachloroethane 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Pentachloronitrobenzene 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 1.1E-04
Pentachlorophenol 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 5.6E-03
Phenanthrene 7.0E-07 2.6E+00 3.6E-01 3.6E-01 2.5E-03 5.5E-02 3.4E-02 2.8E-04
Phenol 2.1E-06 7.9E+00 1.1E+00 1.1E+00 7.6E-03 1.6E-01 1.0E-01 8.4E-04
Pyrene 2.9E-07 1.1E+00 1.5E-01 1.5E-01 1.0E-03 2.3E-02 1.4E-02 1.2E-04
Pyridine 4.1E-07 1.5E+00 2.1E-01 2.1E-01 1.5E-03 3.2E-02 2.0E-02 1.6E-04

Dioxins/Furans
2,3,7,8-TCDD 1.3E-12 4.9E-06 6.8E-07 6.8E-07 4.7E-09 1.0E-07 6.2E-08 3.1E-09
1,2,3,7,8-PeCDD 6.7E-12 2.5E-05 3.5E-06 3.5E-06 2.4E-08 5.2E-07 3.2E-07 1.6E-08
1,2,3,4,7,8-HxCDD 3.4E-12 1.3E-05 1.8E-06 1.8E-06 1.2E-08 2.7E-07 1.6E-07 8.2E-09
1,2,3,6,7,8-HxCDD 8.9E-12 3.3E-05 4.6E-06 4.6E-06 3.2E-08 6.9E-07 4.3E-07 2.1E-08
1,2,3,7,8,9-HxCDD 6.1E-12 2.3E-05 3.2E-06 3.2E-06 2.2E-08 4.8E-07 2.9E-07 1.5E-08
1,2,3,4,6,7,8-HpCDD 2.9E-11 1.1E-04 1.5E-05 1.5E-05 1.0E-07 2.3E-06 1.4E-06 7.0E-08
OCDD 3.7E-11 1.4E-04 1.9E-05 1.9E-05 1.3E-07 2.9E-06 1.8E-06 8.9E-08
2,3,7,8-TCDF 4.0E-11 1.5E-04 2.1E-05 2.1E-05 1.4E-07 3.1E-06 1.9E-06 9.6E-08
1,2,3,7,8-PeCDF 8.0E-11 3.0E-04 4.2E-05 4.2E-05 2.9E-07 6.2E-06 3.8E-06 1.9E-07
2,3,4,7,8-PeCDF 1.6E-10 6.0E-04 8.3E-05 8.3E-05 5.8E-07 1.2E-05 7.7E-06 3.8E-07
1,2,3,4,7,8-HxCDF 2.6E-10 9.7E-04 1.4E-04 1.4E-04 9.4E-07 2.0E-05 1.2E-05 6.2E-07
1,2,3,6,7,8-HxCDF 1.6E-10 6.0E-04 8.3E-05 8.3E-05 5.8E-07 1.2E-05 7.7E-06 3.8E-07
2,3,4,6,7,8-HxCDF 1.9E-10 7.1E-04 9.9E-05 9.9E-05 6.8E-07 1.5E-05 9.1E-06 4.6E-07
1,2,3,7,8,9-HxCDF 1.2E-10 4.5E-04 6.2E-05 6.2E-05 4.3E-07 9.4E-06 5.8E-06 2.9E-07
1,2,3,4,6,7,8-HpCDF 7.3E-10 2.7E-03 3.8E-04 3.8E-04 2.6E-06 5.7E-05 3.5E-05 1.8E-06
TABLE OR APPENDIX 3-???
1.3 CLASS WASTE MATERIAL
CORRECTED ANNUAL EMISSION RATES (LBS/YR)
ATK PROMONTORY, UTAH
PAGE 3 OF 5
1 2 3 4 5 1 2
Analyte
Corrected
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/year)M-225 Quantities
(lbs/year)
1,2,3,4,7,8,9-HpCDF 1.9E-10 7.1E-04 9.9E-05 9.9E-05 6.8E-07 1.5E-05 9.1E-06 4.6E-07
OCDF 5.2E-10 1.9E-03 2.7E-04 2.7E-04 1.9E-06 4.1E-05 1.0E-06 1.2E-06
Carbonyls
2,5-Dimethylbenzaldehyde 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 3.4E-02
Acetaldehyde 7.5E-05 2.8E+02 3.9E+01 3.9E+01 2.7E-01 5.9E+00 3.6E+00 1.8E-01
Acetone 1.5E-05 5.6E+01 7.8E+00 7.8E+00 5.4E-02 1.2E+00 7.2E-01 3.6E-02
Benzaldehyde 7.3E-06 2.7E+01 3.8E+00 3.8E+00 2.6E-02 5.7E-01 3.5E-01 1.8E-02
Crotonaldehyde 6.8E-06 2.5E+01 3.5E+00 3.5E+00 2.4E-02 5.3E-01 3.3E-01 1.6E-02
Formaldehyde 4.0E-05 1.5E+02 2.1E+01 2.1E+01 1.4E-01 3.1E+00 1.9E+00 9.6E-02
Hexanal 8.2E-06 3.1E+01 4.3E+00 4.3E+00 3.0E-02 6.4E-01 3.9E-01 2.0E-02
Isopentanal 6.8E-06 2.5E+01 3.5E+00 3.5E+00 2.4E-02 5.3E-01 3.3E-01 1.6E-02
m,p-Tolualdehyde 6.8E-06 2.5E+01 3.5E+00 3.5E+00 2.4E-02 5.3E-01 3.3E-01 1.6E-02
MEK/Butyraldehydes 1.2E-05 4.5E+01 6.2E+00 6.2E+00 4.3E-02 9.4E-01 5.8E-01 2.9E-02
o-Tolualdehyde 2.3E-05 8.6E+01 1.2E+01 1.2E+01 8.3E-02 1.8E+00 1.1E+00 5.5E-02
Pentanal 1.2E-05 4.5E+01 6.2E+00 6.2E+00 4.3E-02 9.4E-01 5.8E-01 2.9E-02
Propanal 3.8E-05 1.4E+02 2.0E+01 2.0E+01 1.4E-01 3.0E+00 1.8E+00 9.1E-02
HCl/Cl2/NH3
HCl 1.8E-02 6.7E+04 9.4E+03 9.4E+03 6.5E+01 1.4E+03 8.6E+02 4.3E+01
Cl2 1.5E-03 5.6E+03 7.8E+02 7.8E+02 5.4E+00 1.2E+02 7.2E+01 3.6E+00
NH3 2.2E-05 8.2E+01 1.1E+01 1.1E+01 7.9E-02 1.7E+00 1.1E+00 5.3E-02
HCN 1.2E-05 4.5E+01 6.2E+00 #REF!4.3E-02 9.4E-01 5.8E-01 2.9E-02

VOCs
TNMOC 8.1E-04 3.0E+03 4.2E+02 4.2E+02 2.9E+00 6.3E+01 3.9E+01 1.9E+00
1,1,1-Trichloroethane 4.5E-07 1.7E+00 2.3E-01 2.3E-01 1.6E-03 3.5E-02 2.2E-02 1.1E-03
1,1,2,2-Tetrachloroethane 2.1E-07 7.9E-01 1.1E-01 1.1E-01 7.6E-04 1.6E-02 1.0E-02 5.0E-04
1,1,2-Trichloroethane 3.6E-07 1.3E+00 1.9E-01 1.9E-01 1.3E-03 2.8E-02 1.7E-02 8.6E-04
1,1-Dichloroethane 1.6E-07 6.0E-01 8.3E-02 8.3E-02 5.8E-04 1.2E-02 7.7E-03 3.8E-04
1,1-Dichloroethene 2.2E-07 8.2E-01 1.1E-01 1.1E-01 7.9E-04 1.7E-02 1.1E-02 5.3E-04
1,2,3-Trimethylbenzene 2.1E-07 7.9E-01 1.1E-01 1.1E-01 7.6E-04 1.6E-02 1.0E-02 5.0E-04
1,2,4-Trichlorobenzene 6.3E-07 2.4E+00 3.3E-01 3.3E-01 2.3E-03 4.9E-02 3.0E-02 1.5E-03
1,2,4-Trimethylbenzene 5.2E-06 1.9E+01 2.7E+00 2.7E+00 1.9E-02 4.1E-01 2.5E-01 1.2E-02
1,2-Dibromomethane (EDB)4.4E-07 1.6E+00 2.3E-01 2.3E-01 1.6E-03 3.4E-02 2.1E-02 1.1E-03
1,2-Dichlorobenzene 2.4E-07 9.0E-01 1.2E-01 1.2E-01 8.6E-04 1.9E-02 1.2E-02 5.8E-04
1,2-Dichloroethane 2.7E-07 1.0E+00 1.4E-01 1.4E-01 9.7E-04 2.1E-02 1.3E-02 6.5E-04
1,2-Dichloropropane 1.8E-07 6.7E-01 9.4E-02 9.4E-02 6.5E-04 1.4E-02 8.6E-03 4.3E-04
1,3,5-Trimethylbenzene 2.0E-06 7.5E+00 1.0E+00 1.0E+00 7.2E-03 1.6E-01 9.6E-02 4.8E-03
1,3-Butadiene 2.0E-05 7.5E+01 1.0E+01 1.0E+01 7.2E-02 1.6E+00 9.6E-01 4.8E-02
1,3-Dichlorobenzene 2.2E-07 8.2E-01 1.1E-01 1.1E-01 7.9E-04 1.7E-02 1.1E-02 5.3E-04
1,3-Diethylbenzene 2.5E-07 9.4E-01 1.3E-01 1.3E-01 9.0E-04 2.0E-02 1.2E-02 6.0E-04
1,4-Dichlorobenzene 3.7E-07 1.4E+00 1.9E-01 1.9E-01 1.3E-03 2.9E-02 1.8E-02 8.9E-04
1,4-Diethylbenzene 3.3E-07 1.2E+00 1.7E-01 1.7E-01 1.2E-03 2.6E-02 1.6E-02 7.9E-04
1,4-Dioxane 3.2E-07 1.2E+00 1.7E-01 1.7E-01 1.2E-03 2.5E-02 1.5E-02 7.7E-04
1-Butene 2.1E-05 7.9E+01 1.1E+01 1.1E+01 7.6E-02 1.6E+00 1.0E+00 5.0E-02
1-Hexene 2.0E-05 7.5E+01 1.0E+01 1.0E+01 7.2E-02 1.6E+00 9.6E-01 4.8E-02
1-Pentene 1.2E-05 4.5E+01 6.2E+00 6.2E+00 4.3E-02 9.4E-01 5.8E-01 2.9E-02
2,2,4-Trimethylpentane 2.3E-06 8.6E+00 1.2E+00 1.2E+00 8.3E-03 1.8E-01 1.1E-01 5.5E-03
2,2-Dimethylbutane 4.4E-07 1.6E+00 2.3E-01 2.3E-01 1.6E-03 3.4E-02 2.1E-02 1.1E-03
2,3,4-Trimethylpentane 1.4E-07 5.2E-01 7.3E-02 7.3E-02 5.0E-04 1.1E-02 6.7E-03 3.4E-04
2,3-Dimethylbutane 2.9E-06 1.1E+01 1.5E+00 1.5E+00 1.0E-02 2.3E-01 1.4E-01 7.0E-03
2,3-Dimethylpentane 2.7E-06 1.0E+01 1.4E+00 1.4E+00 9.7E-03 2.1E-01 1.3E-01 6.5E-03
2,4-Dimethylpentane 5.5E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.3E-02 2.6E-02 1.3E-03
2-Butanone (MEK)3.9E-06 1.5E+01 2.0E+00 2.0E+00 1.4E-02 3.0E-01 1.9E-01 9.4E-03
2-Ethyltoluene 2.2E-07 8.2E-01 1.1E-01 1.1E-01 7.9E-04 1.7E-02 1.1E-02 5.3E-04
2-Hexanone 4.4E-07 1.6E+00 2.3E-01 2.3E-01 1.6E-03 3.4E-02 2.1E-02 1.1E-03
2-Methylheptane 2.7E-06 1.0E+01 1.4E+00 1.4E+00 9.7E-03 2.1E-01 1.3E-01 6.5E-03
2-Methylhexane 4.4E-06 1.6E+01 2.3E+00 2.3E+00 1.6E-02 3.4E-01 2.1E-01 1.1E-02
2-Methylpentane 5.3E-06 2.0E+01 2.8E+00 2.8E+00 1.9E-02 4.1E-01 2.5E-01 1.3E-02
2-Nitropropane 2.8E-06 1.0E+01 1.5E+00 1.5E+00 1.0E-02 2.2E-01 1.3E-01 6.7E-03
2-Propanol 1.5E-07 5.6E-01 7.8E-02 7.8E-02 5.4E-04 1.2E-02 7.2E-03 3.6E-04
3-Chloropropene 4.7E-06 1.8E+01 2.4E+00 2.4E+00 1.7E-02 3.7E-01 2.3E-01 1.1E-02
3-Ethyltoluene 4.8E-06 1.8E+01 2.5E+00 2.5E+00 1.7E-02 3.7E-01 2.3E-01 1.2E-02
3-Methylheptane 3.5E-06 1.3E+01 1.8E+00 1.8E+00 1.3E-02 2.7E-01 1.7E-01 8.4E-03
3-Methylhexane 5.2E-06 1.9E+01 2.7E+00 2.7E+00 1.9E-02 4.1E-01 2.5E-01 1.2E-02
3-Methylpentane 7.1E-06 2.7E+01 3.7E+00 3.7E+00 2.6E-02 5.5E-01 3.4E-01 1.7E-02
4-Ethyltoluene 5.3E-06 2.0E+01 2.8E+00 2.8E+00 1.9E-02 4.1E-01 2.5E-01 1.3E-02
4-Methyl-2-pentanone 3.5E-07 1.3E+00 1.8E-01 1.8E-01 1.3E-03 2.7E-02 1.7E-02 8.4E-04
Acetone 2.3E-05 8.6E+01 1.2E+01 1.2E+01 8.3E-02 1.8E+00 1.1E+00 5.5E-02
TABLE OR APPENDIX 3-???
1.3 CLASS WASTE MATERIAL
CORRECTED ANNUAL EMISSION RATES (LBS/YR)
ATK PROMONTORY, UTAH
PAGE 4 OF 5
1 2 3 4 5 1 2
Analyte
Corrected
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/year)M-225 Quantities
(lbs/year)
Acetonitrile 9.2E-06 3.4E+01 4.8E+00 4.8E+00 3.3E-02 7.2E-01 4.4E-01 2.2E-02
Acetylene 7.4E-05 2.8E+02 3.8E+01 3.8E+01 2.7E-01 5.8E+00 3.6E+00 1.8E-01
Acrylonitrile 1.0E-05 3.7E+01 5.2E+00 5.2E+00 3.6E-02 7.8E-01 4.8E-01 2.4E-02
alpha-Chlorotoluene 2.8E-07 1.0E+00 1.5E-01 1.5E-01 1.0E-03 2.2E-02 1.3E-02 6.7E-04
Benzene 4.4E-05 1.6E+02 2.3E+01 2.3E+01 1.6E-01 3.4E+00 2.1E+00 1.1E-01
Bromodichloromethane 3.9E-07 1.5E+00 2.0E-01 2.0E-01 1.4E-03 3.0E-02 1.9E-02 9.4E-04
Bromoform 6.3E-07 2.4E+00 3.3E-01 3.3E-01 2.3E-03 4.9E-02 3.0E-02 1.5E-03
Bromomethane 3.1E-07 1.2E+00 1.6E-01 1.6E-01 1.1E-03 2.4E-02 1.5E-02 7.4E-04
Butane 1.8E-05 6.7E+01 9.4E+00 9.4E+00 6.5E-02 1.4E+00 8.6E-01 4.3E-02
Carbon Disulfide 9.4E-06 3.5E+01 4.9E+00 4.9E+00 3.4E-02 7.3E-01 4.5E-01 2.3E-02
Carbon Tetrachloride 1.5E-05 5.6E+01 7.8E+00 7.8E+00 5.4E-02 1.2E+00 7.2E-01 3.6E-02
Chloroacetonitrile 5.6E-07 2.1E+00 2.9E-01 2.9E-01 2.0E-03 4.4E-02 2.7E-02 1.3E-03
Chlorobenzene 2.5E-06 9.4E+00 1.3E+00 1.3E+00 9.0E-03 2.0E-01 1.2E-01 6.0E-03
Chloroethane 1.3E-07 4.9E-01 6.8E-02 6.8E-02 4.7E-04 1.0E-02 6.2E-03 3.1E-04
Chloroform 6.1E-06 2.3E+01 3.2E+00 3.2E+00 2.2E-02 4.8E-01 2.9E-01 1.5E-02
Chloromethane 1.4E-05 5.2E+01 7.3E+00 7.3E+00 5.0E-02 1.1E+00 6.7E-01 3.4E-02
cis-1,2-Dichloroethene 2.3E-07 8.6E-01 1.2E-01 1.2E-01 8.3E-04 1.8E-02 1.1E-02 5.5E-04
cis-1,3-Dichloropropene 1.3E-06 4.9E+00 6.8E-01 6.8E-01 4.7E-03 1.0E-01 6.2E-02 3.1E-03
cis-2-Butene 1.4E-06 5.2E+00 7.3E-01 7.3E-01 5.0E-03 1.1E-01 6.7E-02 3.4E-03
cis-2-Pentene 1.7E-07 6.4E-01 8.8E-02 8.8E-02 6.1E-04 1.3E-02 8.2E-03 4.1E-04
Cumene 2.1E-07 7.9E-01 1.1E-01 1.1E-01 7.6E-04 1.6E-02 1.0E-02 5.0E-04
Cyclohexane 2.5E-06 9.4E+00 1.3E+00 1.3E+00 9.0E-03 2.0E-01 1.2E-01 6.0E-03
Cyclopentane 1.8E-06 6.7E+00 9.4E-01 9.4E-01 6.5E-03 1.4E-01 8.6E-02 4.3E-03
Decane 1.7E-05 6.4E+01 8.8E+00 8.8E+00 6.1E-02 1.3E+00 8.2E-01 4.1E-02
Dibromochloromethane 4.4E-07 1.6E+00 2.3E-01 2.3E-01 1.6E-03 3.4E-02 2.1E-02 1.1E-03
Ethane 1.7E-05 6.4E+01 8.8E+00 8.8E+00 6.1E-02 1.3E+00 8.2E-01 4.1E-02
Ethanol 1.6E-06 6.0E+00 8.3E-01 8.3E-01 5.8E-03 1.2E-01 7.7E-02 3.8E-03
Ethene 1.5E-04 5.6E+02 7.8E+01 7.8E+01 5.4E-01 1.2E+01 7.2E+00 3.6E-01
Ethyl benzene 2.8E-06 1.0E+01 1.5E+00 1.5E+00 1.0E-02 2.2E-01 1.3E-01 6.7E-03
Ethyl ether 1.2E-06 4.5E+00 6.2E-01 6.2E-01 4.3E-03 9.4E-02 5.8E-02 2.9E-03
Ethyl Methacrylate 7.8E-07 2.9E+00 4.1E-01 4.1E-01 2.8E-03 6.1E-02 3.7E-02 1.9E-03
Heptane 7.2E-06 2.7E+01 3.7E+00 3.7E+00 2.6E-02 5.6E-01 3.5E-01 1.7E-02
Hexachlorobutadiene 8.5E-07 3.2E+00 4.4E-01 4.4E-01 3.1E-03 6.6E-02 4.1E-02 2.0E-03
Hexane 9.8E-06 3.7E+01 5.1E+00 5.1E+00 3.5E-02 7.6E-01 4.7E-01 2.4E-02
Isobutane 2.8E-06 1.0E+01 1.5E+00 1.5E+00 1.0E-02 2.2E-01 1.3E-01 6.7E-03
Isopentane 2.0E-05 7.5E+01 1.0E+01 1.0E+01 7.2E-02 1.6E+00 9.6E-01 4.8E-02
m,p-Xylene 1.0E-05 3.7E+01 5.2E+00 5.2E+00 3.6E-02 7.8E-01 4.8E-01 2.4E-02
Methacrylonitrile 4.9E-06 1.8E+01 2.5E+00 2.5E+00 1.8E-02 3.8E-01 2.4E-01 1.2E-02
Methyl Acrylate 5.9E-07 2.2E+00 3.1E-01 3.1E-01 2.1E-03 4.6E-02 2.8E-02 1.4E-03
Methyl Methacrylate 8.1E-07 3.0E+00 4.2E-01 4.2E-01 2.9E-03 6.3E-02 3.9E-02 1.9E-03
Methyl tert-butyl ether 2.1E-07 7.9E-01 1.1E-01 1.1E-01 7.6E-04 1.6E-02 1.0E-02 5.0E-04
Methylcyclohexane 6.1E-06 2.3E+01 3.2E+00 3.2E+00 2.2E-02 4.8E-01 2.9E-01 1.5E-02
Methylcyclopentane 5.6E-06 2.1E+01 2.9E+00 2.9E+00 2.0E-02 4.4E-01 2.7E-01 1.3E-02
Methylene chloride 7.1E-06 2.7E+01 3.7E+00 3.7E+00 2.6E-02 5.5E-01 3.4E-01 1.7E-02
n-Butylchloride 5.8E-06 2.2E+01 3.0E+00 3.0E+00 2.1E-02 4.5E-01 2.8E-01 1.4E-02
Nonane 1.3E-05 4.9E+01 6.8E+00 6.8E+00 4.7E-02 1.0E+00 6.2E-01 3.1E-02
Octane 7.5E-06 2.8E+01 3.9E+00 3.9E+00 2.7E-02 5.9E-01 3.6E-01 1.8E-02
o-Xylene 3.5E-06 1.3E+01 1.8E+00 1.8E+00 1.3E-02 2.7E-01 1.7E-01 8.4E-03
Pentane 1.9E-05 7.1E+01 9.9E+00 9.9E+00 6.8E-02 1.5E+00 9.1E-01 4.6E-02
Propane 8.7E-06 3.3E+01 4.5E+00 4.5E+00 3.1E-02 6.8E-01 4.2E-01 2.1E-02
Propylbenzene 1.0E-06 3.7E+00 5.2E-01 5.2E-01 3.6E-03 7.8E-02 4.8E-02 2.4E-03
Propylene 4.3E-05 1.6E+02 2.2E+01 2.2E+01 1.5E-01 3.4E+00 2.1E+00 1.0E-01
Styrene 9.9E-07 3.7E+00 5.1E-01 5.1E-01 3.6E-03 7.7E-02 4.8E-02 2.4E-03
Tetrachloroethene 2.5E-06 9.4E+00 1.3E+00 1.3E+00 9.0E-03 2.0E-01 1.2E-01 6.0E-03
Tetrahydrofuran 6.4E-07 2.4E+00 3.3E-01 3.3E-01 2.3E-03 5.0E-02 3.1E-02 1.5E-03
Toluene 1.8E-05 6.7E+01 9.4E+00 9.4E+00 6.5E-02 1.4E+00 8.6E-01 4.3E-02
trans-1,2-Dichloroethene 3.6E-07 1.3E+00 1.9E-01 1.9E-01 1.3E-03 2.8E-02 1.7E-02 8.6E-04
trans-1,3-Dichloropropene 3.0E-07 1.1E+00 1.6E-01 1.6E-01 1.1E-03 2.3E-02 1.4E-02 7.2E-04
trans-2-butene 7.7E-06 2.9E+01 4.0E+00 4.0E+00 2.8E-02 6.0E-01 3.7E-01 1.8E-02
trans-2-Pentene 1.7E-06 6.4E+00 8.8E-01 8.8E-01 6.1E-03 1.3E-01 8.2E-02 4.1E-03
Trichloroethene 9.4E-07 3.5E+00 4.9E-01 4.9E-01 3.4E-03 7.3E-02 4.5E-02 2.3E-03
Undecane 1.2E-05 4.5E+01 6.2E+00 6.2E+00 4.3E-02 9.4E-01 5.8E-01 2.9E-02
Vinyl chloride 7.6E-06 2.8E+01 4.0E+00 4.0E+00 2.7E-02 5.9E-01 3.6E-01 1.8E-02

CEM
CO2 6.9E-01 2.6E+06 3.6E+05 3.6E+05 2.5E+03 5.4E+04 3.3E+04 1.7E+03
CO 4.7E-03 1.8E+04 2.4E+03 2.4E+03 1.7E+01 3.7E+02 2.3E+02 1.1E+01
NOX 5.8E-03 2.2E+04 3.0E+03 3.0E+03 2.1E+01 4.5E+02 2.8E+02 1.4E+01
SO2 4.1E-04 1.5E+03 2.1E+02 2.1E+02 1.5E+00 3.2E+01 2.0E+01 9.8E-01
Highlighted analytes were not detected during the Bang Box testing program
TABLE OR APPENDIX 3-???
1.3 CLASS WASTE MATERIAL
CORRECTED ANNUAL EMISSION RATES (LBS/YR)
ATK PROMONTORY, UTAH
PAGE 5 OF 5
1 2 3 4 5 1 2
Analyte
Corrected
Emission
Factor
(lbs/lb)
M-136 Quantities (lbs/year)M-225 Quantities
(lbs/year)
CEM - Continuous Emissions Monitoring
CL2 - chlorine
CO - carbon monoxide
CO2 - carbon dioxide
HCL - hydrogen chloride
HCN - hydrogen cyanide
NH3 - ammonia
NOX - nitrogen oxide
OCDD - 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-dioxin
OCDF - 1,2,3,4,6,7,8,9-Octachlorodibenzo-p-furan
PM10 - particulate matter less than 10 microns in aerodynamic diameter
PM2.5 - particulate matter less than 2.5 microns in aerodynamic diameter
SO2 - sulfur dioxide
SVOCs - semi-volatile organic compounds
TNMOC - total non-methane organic carbon
TSP - Total suspended particulates
VOCs - volatile organic compounds