TABLE OF CONTENTS	PAGE

I.	INTRODUCTION	1

II.	SAMPLING DESIGN BASIS	2

III.	PCB FEED	2

IV.	DAILY RUN SUMMARIES	3

V.	CONTINUOUS EMISSION MONITORING RESULTS	4

VI.	EXHAUST GAS EMISSION RESULTS	4

VI.1	Cyclonic Flow Checks	4

VI.2	Bulk Gas Constituents	5

VI.3	Moisture Determination	5

VI.4	DRE Results for PCBs	5

VI.5	DRE Results for GB Agent	5

VI.6	PCB Emission Results	6

VI.7	PCDD/PCDF Emission Results	6

VI.8	Semivolatile Organic Emission Results	6

VI.9	Volatile Organic Emission Results	7

VII.	PROCESS SAMPLE RESULTS	7

VII.1	Recirculation Scrubber Brine	7

VII.2	Cyclone Residue	8

VII.3	HDC Ash	8

VIII.	PROPOSED PROCESS LIMITS	8

VIII.1	DFS-01/DFS(M)-1:  Rotary Kiln Temperature High-High	8

VIII.2	DFS-02/DFS(M)-2:  Flue Gas Temperature After Spray High-High	8

VIII.3	DFS-03/DFS(M)-3:  Flue Gas Temperature After Spray Low-Low	8

VIII.4	DFS-04/DFS(M)-4:  Jammed Chute	9

VIII.5	DFS-05/DFS(M)-5:  Pressure in Rotary Kiln Combustion Chamber
High-High	9

VIII.6	DFS-06/DFS(M)-6:  Temperature on Rotary Kiln Shell High-High	9

VIII.7	DFS-07/DFS(M)-7:  Loss of Flame in Both Burners of the
Afterburner	9

VIII.8	DFS-08/DFS(M)-8:  HDC Temperature Low-Low	9

TABLE OF CONTENTS	PAGE

VIII.9	DFS-09/DFS(M)-9:  Jam in Discharge Conveyor Chute	9

VIII.10	DFS-10/DFS(M)-10:  Zero Motion on HDC	10

VIII.11	DFS-11/DFS(M)-11/12:  Afterburner Exhaust Gas Flow Rate
High-High	10

VIII.12	DFS-12/DFS(M)-13:  Rotary Kiln Temperature Before Spray Low-Low
10

VIII.13	DFS(M)-14:  Rotary Kiln Temperature Before Spray Low-Low	10

VIII.14	DFS(M)-15:  Minimum Packed Bed Pressure Drop	10

VIII.15	DFS-13/DFS(M)-16:  Afterburner Temperature Low-Low	11

VIII.16	DFS-14/DFS(M)-18:  Afterburner Temperature High-High	11

VIII.17	DFS(M)-19:  Minimum Brine pH	11

VIII.18	DFS-15/DFS(M)-20:  Venturi Scrubber Pressure Low-Low	11

VIII.19	DFS-16/DFS(M)-22:  CO Concentration in PFS Exhaust Gas High-High
11

VIII.20	DFS(M)-23:  Maximum Solids Content in Clean Liquor	12

VIII.21	DFS-17/DFS(M)-24:  Waste Feed Rate High (Condition 1)	12

VIII.22	DFS-18/DFS(M)-25:  Clean Liquor to Scrubber Tower Flow Rate
Low-Low	12

VIII.23	DFS-19:  Chemical Agent Emissions High-High, Exhaust Duct	12

VIII.24	DFS-20:  Chemical Agent Emissions High-High, Cyclone Enclosure
12

VIII.25	DFS-21:  Chemical Agent Emissions High-High, Common Stack	13

VIII.26	DFS-22:  Brine Surge Tanks Level High-High	13

VIII.27	DFS-23/DFS(M)-27:  Clean Liquor to Scrubber Tower pH Low-Low	13

VIII.28	DFS-24/DFS(M)-29:  Clean Liquor to Scrubber Tower Pressure
Low-Low	13

VIII.29	DFS-25:  Quench Tower Exhaust Gas Temperature High-High	13

VIII.30	DFS-26/DFS(M)-30:  Quench Brine to Venturi Scrubber Flow Rate
Low-Low	13

VIII.31	DFS-27/DFS(M)-32:  Brine Density High-High	13

VIII.32	DFS(M)-33:  Brine Density High-High	14

VIII.33	DFS-28/DFS(M)-34:  Kiln Rotational Speed High-High	14

VIII.34	DFS-29:  O2 Concentration in PFS Exhaust Gas High-High	14

VIII.35	DFS-30/DFS(M)-35:  O2 Concentration in PFS Exhaust Gas Low-Low
14

VIII.36	DFS-31/DFS(M)-36:  Afterburner Pressure High-High	14

VIII.37	DFS-32:  Scrubber Tower Sump Liquid Level High-High	15

VIII.38	DFS-33:  Scrubber Tower Sump Liquid Level Low-Low	15

VIII.39	DFS-34/DFS(M)-37:  Flame Loss in Rotary Kiln	15

VIII.40	DFS-35/DFS(M)-38:  PFS Prefilter Differential Pressure High-High
15

VIII.41	DFS-36/DFS(M)-39:  PFS HEPA Filter Differential Pressure
High-High	15

TABLE OF CONTENTS	PAGE

VIII.42	DFS-37/DFS(M)40:  Temperature of Gas to Carbon Filter System
High-High	15

VIII.43	DFS-38/DFS(M)-41:  Moisture of Gas to Carbon Filter System
High-High	16

VIII.44	DFS-39:  Carbon Filter Bypass Valve Operation	16

VIII.45	DFS(M)-42:  Prefilter Differential Pressure Low-Low	16

VIII.46	DFS(M)-43:  HEPA Filter Differential Pressure Low-Low	16

VIII.47	DFS-40:  Chemical Agent Emissions High-High, PFS Unit	16

VIII.48	DFS-41/DFS(M )-44:  Mist Eliminator Differential Pressure
High-High	17

VIII.49	DFS-42/DFS(M)-45:  Rotary Kiln Temperature Before Spray
High-High	17

VIII.50	DFS-43:  Moisture of Gas Exiting Carbon Filter System High-High
17

IX.	RATA	17

X.	CONCLUSIONS	17

LIST OF TABLES	PAGE

1	Sampling Time Intervals	18

2	Summary of Operating Parameters for the DFS GB TSCA ATB Run 1	19

3	Summary of Operating Parameters for the DFS GB TSCA ATB Run 2	23

4	Summary of Operating Parameters for the DFS GB TSCA ATB Run 3	27

5	Summary of Operating Parameters for the DFS GB TSCA ATB Run 4	31

6	Summary of Operating Parameters for the DFS GB TSCA ATB Average	35

7	Select Criteria Pollutant Emission Results	39

8	Summary of DRE Results for PCBs	40

9	Summary of DRE Results for GB Agent	41

10	PCB Emission Results	43

11	PCDD/PCDF Emission Results	46

12	Semivolatile Organic Emission Results	49

13	Volatile Organic Emission Results	63

14	Recirculation Scrubber Brine Analytical Results	70

15	Cyclone Residue Analytical Results	71

16	HDC Ash Analytical Results	72

17	DFS AWFCO Parameters	73

LIST OF APPENDICES	VOLUME

A	PDAR System Reports	I

B	Exhaust Gas Sampling Report	I

C	Process Sampling Report	

D	QA/QC Summary	I

E	GB DRE DAAMS Report	

F	Instrument Calibration Records	I

G	Field Logs and Master Sample Checklist	I

H	Analytical Data Packages

H-1	STL Summary Package No. G5J310190 (PCBs)	I

H-2	STL Summary Package No. G5J310225 (SVOCs and PCDDs/PCDFs)	

H-3	ATL Summary Package No. 0510574 (Volatile Organics)	

H-4	STL Summary Package No. G5J310229 (Process Samples)	

I	DFS GB TSCA RATA	

LIST OF ACRONYMS AND ABBREVIATIONS

%	percent

(	degrees

<	less than

>	greater than

(F	degrees Fahrenheit

ACAMS	Automatic Continuous Air Monitoring System

ATB	agent trial burn

ATBP	agent trial burn plan

ATBR	agent trial burn report

AWFCO	automatic waste feed cutoff

CEMS	Continuous Emissions Monitoring System

CFR	Code of Federal Regulation

CO	carbon monoxide

CO2	carbon dioxide

DAAMS	Depot Area Air Monitoring System

DFS	Deactivation Furnace System

DL	detection limit

DRE	destruction and removal efficiency

EPA	Environmental Protection Agency

g/s	grams per second

gpm	gallons per minute

HDC	Heated Discharge Conveyor

12HRA	12-hour rolling average

hrs	hours

IAW	in accordance with

lbs/hr	pounds per hour

inwc	inches of water column

M0010	SW-846 Method 0010

M0023A	SW-846 Method 0023A

M0031	SW-846 Method 0031

MACT	Maximum Achievable Control Technologies

MDL	method detection limit

mg/m3	milligrams per cubic meter

2MRA	2-minute rolling average

30MRA	30-minute rolling average

LIST OF ACRONYMS AND ABBREVIATIONS (Continued)

ND	non-detect

ng/dscm	nanograms per dry standard cubic meter

NOC	Notice of Compliance

O2	oxygen

PAS	Pollution Abatement System

PCB	polychlorinated biphenyl

PCDD	polychlorinated dibenzo-p-dioxin

PCDF	polychlorinated dibenzofuran

PDAR	process data acquisition and recording

PFS	PAS Filtration System

ppm	parts per million

ppmv	parts per million by volume

psig	pounds per square inch gauge

QA	quality assurance

QC	quality control

RATA	Relative Accuracy Test Assessment

RCRA	Resources Conservation and Recovery Act

RH	relative humidity

RL	reporting limit

rockets/hr	rockets per hour

ROHA	rolling hourly

rpm	revolutions per minute

sgu	specific gravity unit

TEQ	toxicity equivalence quotient

THC	total hydrocarbon

TSCA	Toxic Substances Control Act

UMCDF	Umatilla Chemical Agent Disposal Facility

US	United States

I.	introduction

On October 26 through 30, 2005, Umatilla Chemical Agent Disposal
Facility (UMCDF) conducted a Toxic Substance Control Act (TSCA) agent
trial burn (ATB) consisting of four test runs with sampling conducted in
a horizontal duct configuration at the Deactivation Furnace System (DFS)
exhaust duct, using the UMCDF DFS GB Rocket ATB Plan (ATBP),
Revision 1.5.  The Plan was amended by a letter from the US
Environmental Protection Agency (EPA) dated August 1, 2005 noting that
only one run of volatile and semivolatile data was required.  Sampling
times and durations are summarized in Table 1.

UMCDF is required to test for the presence of polychlorinated biphenyls
(PCBs) under the “Approval to Dispose of Polychlorinated Biphenyls,”
June 6, 2002, commonly referred to as the TSCA Permit.  The shipping and
firing tubes for the M55 rockets contain PCBs varying in concentration
depending on the type of rocket shipping and firing tube (chopped,
matted, and matted/coated) as documented in the 1986-87 United States
(US) Army Environmental Hygiene Agency Study.  The amount of PCBs in the
matted shipping and firing tubes used for the ATB was 2,006 parts per
million (ppm).  The objectives of the DFS GB TSCA ATB are as follows:

Emissions of PCB’s from the DFS shall not exceed 6.25E-07 grams per
second (g/s) and a maximum of 0.2 nanograms toxicity equivalence per dry
standard cubic meters (ng-TEQ/dscm), adjusted to 7 percent (%) excess
oxygen (O2) and

Each test of the ATB shall demonstrate a minimum PCB destruction and
removal efficiency (DRE) of 99.9999%.

Process samples of recirculation scrubber brine, cyclone residue, and
Heated Discharge Conveyor (HDC) ash were collected during the DFS GB
TSCA ATB.  All process samples were sent to an off-site laboratory for
analyses after the on-site laboratory screened all samples for GB agent.
 In addition, the Process Data Acquisition and Recording (PDAR) System
captured the operating condition of the DFS during actual exhaust gas
sampling.  As summarized in Tables 2 through 6, the DFS operated within
the limits set forth in the UMCDF DFS GB Rocket ATBP for all valid test
runs.

The following test methods were utilized during the DFS GB TSCA ATB for
sampling of exhaust gas in accordance with (IAW) the approved UMCDF DFS
GB Rocket ATBP:

Volumetric Flow Rate - US EPA Method 2:  “Determination of Stack Gas
Velocity and Volumetric Flow Rate (Type S Pitot Tube),” 40 CFR Part
60, Appendix A;

Moisture Content - US EPA Method 4:  “Determination of Moisture
Content in Stack Gases,” 40 CFR Part 60, Appendix A;

O2 and Carbon Dioxide (CO2) Concentration by Orsat - US EPA Method 3B: 
“Gas Analysis for the Determination of Emission Rate Correction Factor
or Excess Air,” 40 CFR Part 60, Appendix A;

Carbon Monoxide (CO) - US EPA Method 10:  “Determination of Carbon
Monoxide Emissions from Stationary Sources,” 40 CFR Part 60, Appendix
A;

O2 - US EPA Performance Specification 4B:  “Specifications and Test
Procedures for CO and O2 Continuous Monitoring Systems in Stationary
Sources,” 40 CFR Part 60, Appendix A;

Total Hydrocarbons (THCs) - US EPA Performance Specification 8A: 
“Specifications and Test Procedures for Total Hydrocarbon Continuous
Monitoring Systems in Stationary Sources,” 40 CFR Part 60, Appendix B;

Semivolatile Organics - SW-846 Method 0010 (M0010):  “Modified Method
5 Sampling Train,” EPA 600/8-85-003;

PCBs and Polychlorinated Dibenzo-p-Dioxins/Polychlorinated Dibenzofurans
(PCDDs/PCDFs) - SW-846 Method 0023A (M0023A):  “Determination of
Polychlorinated Dibenzo-p-Dioxins (PCDDs) and Polychlorinated
Dibenzofurans (PCDFs) from Stationary Sources,”  EPA 600/8-85-003 
[NOTE:  A sampling train was conducted for PCDDs/PCDFs and an additional
sampling train was used for PCBs];

Volatile Organics - SW-846 Method 0031 (M0031):  “Sampling Method for
Volatile Organic Compounds,” EPA 600/8-85-003;

GB Agent – UMCDF Automatic Continuous Air Monitoring System (ACAMS)
and Depot Area Air Monitoring System (DAAMS) operating procedure(s).

All testing and data collection planned for the DFS GB TSCA ATB was
completed.  UMCDF has reviewed these data to assess their usability and
to determine compliance with operating conditions for the DFS.  All data
have been determined to be useable for their intended purpose. 
Operating conditions for the DFS, based on the results of this DFS GB
TSCA ATB, verify that the operating conditions are protective of human
health and the environment as the performance standards for incinerators
were met.

II.	Sampling Design Basis

Two M0023A sampling trains were used for PCBs and PCDDs/PCDFs.  The
M0023A-PCB sampling train was comprised of all glass components.  During
Run 2, a M0010 and M0031 sampling trains were also conducted.  With the
exception of calculating DRE, Run 1 samples were archived and not
analyzed.  In addition, field blanks were also taken at the DFS exhaust
duct location, as appropriate.

III.	PCB Feed

UMCDF fed an instantaneous average of 35.3, 36.0, and 37.0 rockets per
hour (rockets/hr) for Runs 2, 3, and 4, respectively, for an overall
average of 36.1 rockets/hr (see Tables 2 through 6).  UMCDF submitted
data to the US EPA dated December 10, 2004 that documented the basis of
assigning a PCB concentration of 2,006 ppm in matted shipping and firing
tubes used in the ATB.  On January 12, 2005, UMCF received a letter from
the US EPA accepting the data and allowed for the use of 2,006 ppm for
matted shipping and firing tubes.  The rockets processed during the TSCA
test runs were matted shipping and firing tubes only; thus, 2,006 ppm is
the calculated value used in determining the DRE.

IV.	DAILY RUN SUMMARIES

The following are daily accounts of the onsite test activities.  These
summaries are presented in sequential order for the entire trial burn
effort and include the preliminary measurements.  Table 1 presents a
summary of the sampling times for each test run, coinciding with the
following discussion.

October 26, 2005 - Preliminary Measurements:  Preliminary velocity
traverses and flow checks at the DFS exhaust duct at the start of the
DFS GB TSCA ATB.  A run was also conducted to verify the moisture
content of the exhaust gas.  The cyclonic flow measurements from
previous trial burns were used as they yielded results within specified
limits.  All velocity and moisture measurements made this day were
reliable indicators of actual flow and moisture conditions through the
entire DFS TSCA GB ATB and did not change appreciably from run to run.

October 27, 2005:  The Relative Accuracy Test Audit (RATA)was performed.

October 28, 2005 - Run 1:  The GB agent rocket feed to the rotary kiln
began at 0522 hours (hrs).  Exhaust gas sampling commenced at
0800 hrs.  One field blank sampling train was set up and recovered
during this run, M0023A-PCB.  Isokinetic sampling through the first port
was completed at 1000 hrs.  Sampling probes were pulled from the
exhaust duct, leak checked, moved to the second port, and leak checked
prior to entering the second port.  Sampling in second port began at
1020 hrs.  Sampling was interrupted at 1151 hrs and resumed at
1210 hrs due to a rocket miss-feed.  Sampling was interrupted again at
1211 hrs and resumed at 1510 hrs due to a feed chute jam.  During the
second sampling interruption, all sampling probes were removed from the
duct.  Leak checks were performed subsequent to removal and prior to
re-insertion for continuation of sampling.  Sampling ended at 1538 hrs.
 The sample probes were removed from the port and all sampling trains
were leak checked according to method requirements.  All leak checks
were completed successfully.  All samples were recovered, labeled, and
sealed.

October 29, 2005 - Run 2:  The GB agent rocket feed to the rotary kiln
began at 0412 hrs.  Exhaust gas sampling commenced at 0802 hrs. 
Sampling was interrupted at 0814 hrs and resumed at 0834 hrs due to an
ACAMS malfunction caused by removing more than one staggered ACAMS from
service.  Sampling was interrupted again at 0924 hrs and resumed at
1250 hrs due to rocket metering machine  repairs.  During the second
sampling interruption, all sampling probes were removed from the duct. 
Leak checks were performed subsequent to removal and prior to
re-insertion for continuation of sampling.  Isokinetic sampling through
the first port was completed at 1348 hrs.  Sampling probes were pulled
from the exhaust duct, leak checked, moved to the second port, and leak
checked prior to entering the second port.  Sampling in the second port
began at 1412 hrs.  Sampling ended at 1612 hrs.  The sample probes
were removed from the port and all sampling trains were leak checked
according to method requirements.  All leak checks were completed
successfully.  All samples were recovered, labeled, and sealed.

October 30, 2005 - Runs 3 and 4:  The GB agent rocket feed to the rotary
kiln began at 0323 hrs.  For Run 3, exhaust gas sampling commenced at
0948 hrs.  One field blank sampling train was set up and recovered
during this run, M0023A-PCDD/F.  Sampling was interrupted at 0954 hrs
and resumed at 1003 hrs due to a kiln feed malfunction.  Sampling was
interrupted again at 1109 hrs and resumed at 1112 hrs due to a tipping
gate malfunction.  Isokinetic sampling through the first port was
completed at 1200 hrs.  Sampling probes were pulled from the exhaust
duct, leak checked, moved to the second port, and leak checked prior to
entering the second port.  Sampling in the second port began at
1215 hrs.  Sampling was interrupted at 1400 hrs and resumed at
1405 hrs due to a rocket miss-feed.  Sampling ended at 1420 hrs.  The
sample probes were removed from the port and all sampling trains were
leak checked according to method requirements.  All leak checks were
completed successfully.  All samples were recovered, labeled, and
sealed.

For Run 4, exhaust gas sampling commenced at 1518 hrs.  Isokinetic
sampling through the first port was completed at 1718 hrs.  Sampling
probes were pulled from the exhaust duct, leak checked, moved to the
second port, and leak checked prior to entering the second port. 
Sampling in the second port began at 1734 hrs.  Sampling ended at
1934 hrs.  All leak checks were completed successfully.  The sample
probes were removed from the port and all sampling trains were leak
checked according to method requirements.  All leak checks were
completed successfully.  All samples were recovered, labeled, and
sealed.  This concluded the DFS TSCA GB ATB.

V.	CONTINUOUS EMISSION MONITORING RESULTS

Throughout the DFS GB TSCA ATB, Continuous Emissions Monitoring Systems
(CEMSs) were operated to provide near real-time gaseous concentrations
for THC, CO, and O2.  CO and O2 were measured by facility CEMS IAW US
EPA Performance Specification 4B and recorded by the PDAR System.  THC
was measured by a temporary CEMS (TCEMS) IAW US EPA Performance
Specification 8A and recorded.  All emissions were below the UMCDF RCRA
Permit limits and National Emission Standards for Hazardous Air
Pollutants for Hazardous Waste Combustors standards, commonly referred
to as Maximum Achievable Control Technologies (MACT), as summarized in
Table 7.

vi.	Exhaust gas emission results

This section presents a summary of the exhaust gas emission results from
the DFS GB TSCA ATB.  All supporting data are presented in the report
appendices.  The field sampling data sheets and reduced field data can
be found in Appendix B.  Supporting quality assurance (QA)/quality
control (QC) data are presented in Appendix D.  Calibration data can be
found in Appendix F.  Feed logs are presented in Appendix G.  The
analytical data reports are presented in their entirety in Appendix H.

VI.1	Cyclonic Flow Checks

Absence of cyclonic flow at the sampling location was determined on June
24, 2005.  The cyclonic flow check was conducted through Port Section G
of the exhaust blower duct prior to the start of the DFS GB Rocket ATB. 
Two ports at 90 degrees (() to each other were used to complete the
check.  To demonstrate the validity of the sampling location and to
enhance the quality of the data obtained from the sampling methods, the
cyclonic flow check was performed with all sampling probes inserted in
the duct between its traverse port location and the closest upstream
disturbance.  The ports were found to be free of cyclonic flow (less
than [<] 20() with a mean cyclonic of 3.54(.  The individual
measurements are presented in UMCDF DFS GB Rocket ATB Report (ATBR).

VI.2	Bulk Gas Constituents

Composite exhaust gas samples were collected from the M0023A-PCB
sampling train to determine the concentration of O2 and CO2 to be used
in the calculation of the exhaust gas molecular weight.  This calculated
molecular weight was used to calculate specific parameters associated
with gas flow and sampling train isokinetic results.  O2 and CO2
concentrations, as determined by US EPA Method 3B (Orsat analysis), are
presented in Table 7.

In addition, O2 concentrations, as determined by US EPA Performance
Specification 4B (facility CEMS), were utilized to calculate correction
factors for determining compliance with the UMCDF Permit emission
limits.  The O2 concentrations used for these calculations are presented
in the emission summary tables.

VI.3	Moisture Determination

US EPA Method 4 was used in conjunction with M0010, M0023A-PCDD/F, and
M0023A-PCB for the determination of moisture at the DFS exhaust duct. 
The weight gain for each sample train’s impinger configuration was
recorded and used in the calculation of exhaust gas moisture.  Results
for these moisture determinations are presented on the computer
generated data sheets presented in Appendix B.

Vi.4	DRE Results for PCBs

The UMCDF TSCA approval DRE requirement for an incinerator is 99.9999%. 
The regulation states that DRE is to be determined by dividing the
difference between the total PCBs fed and total PCBs emitted by the
total PCBs fed, all on a lbs/hr basis, and expressing the result as a
percent.  The PCB DRE for the DFS was greater than (>) 99.99998% for
Runs 2, 3, and 4, see Table 8.  The average PCB DRE at the DFS exhaust
duct was > 99.99998%, which is in compliance with the TSCA Permit limit
of 99.9999%.

Vi.5	DRE Results for GB Agent

The GB agent emissions were measured by a DAAMS that was located between
the induced draft fan and common stack where manual exhaust sampling
occurred.  A four-hour DAAMS tube was analyzed at the on-site laboratory
for GB agent concentration.  The GB agent was adjusted for purity based
on the average purity reported in the ANCDF DFS GB Rocket ATBR.  This
DRE, purity-adjusted, provides a worst-case, or lowest DRE.  The GB
agent DRE for the DFS was > 99.9999995, > 99.9999996, and > 99.9999995%
for Runs 2, 3, and 4, respectively, see Table 9.  The average GB agent
DRE was > 99.9999995%, which is in compliance with the UMCDF RCRA Permit
limit and MACT standard of 99.99%.  Supporting information is included
in Appendix E.

VI.6	PCB Emission Results

Table 10 presents the results for each test run and by three-run
average.  The M0023A-PCB sampling train yielded two sample fractions per
run, which were analyzed individually, then combined.  No blank
corrections have been made to the data.  PCB analytical data are
included in Appendix H-1.

The PCBs that are reported for the DFS exhaust duct include the total
homologues and those congeners that are on the World Health Organization
list as having toxic equivalency factors (TEQ).  The total PCB emissions
were < 2.17E-08, < 1.94E-08, and < 1.94E-08 g/s for Runs 2, 3, and 4,
respectively, with an overall average of < 2.02E-08 g/s, which is in
compliance with the UMCDF RCRA Permit limit of 6.25E-07 g/s.  The
weighted PCB concentration was < 0.0053 ng TEQ/dscm corrected to 7%
O2 for Runs 2, 3, and 4, respectively.  The overall average was < 0.0053
ng TEQ/dscm corrected to 7% O2, which is in compliance with the TSCA
Permit limit of 0.2 ng-TEQ/dscm.

VI.7	PCDD/PCDF Emission Results

Table 11 presents the results for each test run and by three-run
average.  The M0023A-PCDD/F sampling train yielded two sample fractions
per run, which were analyzed individually, then combined.  No blank
corrections have been made to the data.  PCDD/PCDF analytical data are
included in Appendix H-2.

The dioxins and furans that are reported for the DFS exhaust duct
include the total homologues and those congeners that are on the World
Health Organization list as having toxic equivalency factors.  The
weighted PCDD/PCDF emission rates were < 5.63E-11, < 5.61E-11, and
< 1.27E-10 g-TEQ/s for Runs 2, 3, and 4, respectively, with an overall
average of < 8.00E-11 g-TEQ/s which is in compliance with the UMCDF
RCRA Permit limit of 6.69E-10 g -TEQ/s.  The weighted PCDD/PCDF
concentrations corrected to 7% O2 were < 0.0139, < 0.0141, and
< 0.0316 ng-TEQ/dscm for Runs 2, 3, and 4, respectively, with an
overall average of < 0.0199 ng-TEQ/dscm which is in compliance with
the MACT standard of 0.20 ng-TEQ/dscm.

VI.8	Semivolatile Organic Emission Results

Table 12 presents the results for Run 2.  The M0010 sampling train
yielded three sample fractions per run, which were analyzed
individually, then combined.  No blank corrections have been made to the
data.  Semivolatile organic analytical data are included in Appendix H-2

Five compounds – m-cresol, diethyl phthalate, di-n-butyl phthalate,
di-n-octyl phthalate, and naphthalene – were reported exceeding the
UMCDF RCRA Permit limit at the reported concentration or non-detect (ND)
detection limit (DL).  These same compounds also exceeded the UMCDF RCRA
Permit limits using the ND method detection limit (MDL).  Emission
limits using the DL and MDL concentrations are summarized in Table 12. 
All remaining semivolatile organic emissions were in compliance with the
UMCDF RCRA Permit limits.  These results are consistent with the RCRA
ATB results for cresol and di(n)octyl phthaltate.  The other organic
results are similar to the RCRA results, albeit slightly higher.

As noted in the approved UMCDF DFS GB Rocket ATBP, Appendix B, Section
11.3, there are some results that can not demonstrate compliance with
the UMCDF RCRA Permit limits.  For these constituents, ND values at the
DLs and/or MDLs were not sufficiently low to allow a demonstration of
compliance and lowering of the DL is beyond the reporting capability of
the allowed method.  As none of these constituents were identified in
the pre-ATB risk assessment as “risk drivers,” it is not expected
that these constituents will have a measurable impact with respect to
the overall risk when incorporated into the post-ATB risk assessment
reported emission rates.

VI.9	Volatile Organic Emission Results

Table 13 presents the results for Run 2.  The M0031 sampling train
yielded 12 tubes per run (four sets of three tubes each), plus a
condensate sample.  Each set of three tubes comprised two Tenax-packed
tubes and one Anasorb-747-packed tube.  For each set, the two Tenax
tubes were analyzed as a pair, and the Anasorb-747 tube and condensate
were analyzed separately; then the results were combined.  No blank
corrections have been made to the data.  Volatile organic analytical
data are included in Appendix H-3.

Seventeen compounds were reported exceeding the UMCDF RCRA Permit limits
at the reported concentration or ND reporting limit (RL).  Of these 17
compounds, nine also exceed the UMCDF RCRA Permit limit using the ND
MDL, if available.  Emission limits using the RL and MDL concentrations
are summarized in Table 13.  All remaining volatile organic emissions
were in compliance with the UMCDF RCRA Permit limits.  There were no
volatile compounds identified during the TSCA GB ATB that were different
than those identified in the RCRA GB ATB.

As noted in the approved UMCDF DFS GB Rocket ATBP, Appendix B, Section
11.3, there are some results can not demonstrate compliance with the
UMCDF RCRA Permit limits.  For these constituents, ND values at the RLs
and/or MDLs were not sufficiently low to allow a demonstration of
compliance and lowering of the RL is beyond the reporting capability of
the allowed method.  As none of these constituents were identified in
the pre-ATB risk assessment as “risk drivers,” it is not expected
that these constituents will have a measurable impact with respect to
the overall risk when incorporated into the post-ATB risk assessment
reported emission rates.

Vii.	Process sample results

Three process streams were collected and analyzed during the DFS GB TSCA
ATB:  recirculation scrubber brine, cyclone residue, and HDC ash.  All
GB agent results were below the waste control limit (see Appendix C). 
Supporting QA/QC data are presented in Appendix D.  Process sample
analytical data is included in Appendix H-4.

VII.1	Recirculation Scrubber Brine

Table 14 contains the analytical data for the recirculation scrubber
brine.  No PCBs were detected above the detection limit in any of the
test runs.

VII.2	Cyclone Residue

Table 15 contains the analytical data for the cyclone residue.  With the
exception of 2,3,3’,4,4’-pentachlorinated biphenyl and
2,3’,4,4’,5-pentachlorinated biphenyl, no PCBs were detected above
the detection limit in any of the test runs.

VII.3	HDC Ash

Table 16 contains the analytical data for the HDC ash.  No PCBs were
detected above the detection limit in any of the test runs.

VIII.	PROPOSED PROCESS LIMITS

Based on the emission results and PDAR System data of the DFS GB RCRA
and TSCA ATBs, the following process limits were within those
established during the DFS GB ATB and demonstrates that the DFS was
operating within the operating envelope during the DFS GB TSCA ATB.  The
outline of the parameters is taken from Table 2-2 of the UMCDF DFS GB
Rocket ATBP (Appendix A).  A summary of the proposed RCRA/TSCA and MACT
automatic waste feed cutoff (AWFCO) setpoints is provided in Table 17. 
The proposed limits in Table 17 apply to the remaining agent munition
processing in the DFS.  The operating parameters discussed are those
that are identified in the TSCA Approval dated June 2002.  The operating
parameter setpoints are those that are contained in the current
Notification of Compliance (NOC) required by MACT and are based on the
RCRA GB ATB conducted in June/July 2005.

VIII.1	DFS-01/DFS(M)-1:  Rotary Kiln Temperature High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum temperature
in the rotary kiln exhaust gas before the spray (16-TAHH-182) was 1,615
degrees Fahrenheit ((F).  The average maximum instantaneous temperature
demonstrated during the DFS GB RCRA and TSCA ATB was 1,130.7 and
1,161.5(F, respectively.  This parameter was not required to be
re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.2	DFS-02/DFS(M)-2:  Flue Gas Temperature After Spray High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum temperature
of the rotary kiln exhaust gas after spray (16-TAHH-08) was 1,539(F. 
The average maximum instantaneous temperature demonstrated during the
DFS GB RCRA and TSCA ATB was 1,093.9 and 1,130.8(F, respectively.  This
parameter was not required to be re-demonstrated per the UMCDF DFS GB
Rocket ATBP.

VIII.3	DFS-03/DFS(M)-3:  Flue Gas Temperature After Spray Low-Low

The RCRA/MACT instantaneous AWFCO setpoint for the minimum temperature
of the rotary kiln exhaust gas after spray (16-TALL-08) was 949(F.  The
average minimum instantaneous temperature demonstrated during the DFS GB
RCRA and TSCA ATB was 1,011.2 and 1,081.7(F, respectively.  This
parameter was not required to be re-demonstrated per the UMCDF DFS GB
Rocket ATBP.

VIII.4	DFS-04/DFS(M)-4:  Jammed Chute

The RCRA/MACT instantaneous AWFCO setpoint for ensuring proper operation
of the feed chute (16-XS-207/209) was a switch indicating the status of
the feed chute.  The position switch indicates if the feed chute is
“jammed” or “not jammed.”  In accordance with the UMCDF DFS GB
Rocket ATBP, this parameter was not required to be demonstrated during
the ATB.  TSCA Run 1 experienced a jammed chute which created a sampling
delay.

VIII.5	DFS-05/DFS(M)-5:  Pressure in Rotary Kiln Combustion Chamber
High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum pressure in
the rotary kiln combustion chamber (16-PSHH-204) was –0.1 inches of
water column (inwc) after a 3-second delay.  In accordance with the
UMCDF DFS GB Rocket ATBP, this parameter was not required to be
demonstrated during the ATB.  During the DFS GB TSCA or RCRA ATB, this
switch was not activated.

VIII.6	DFS-06/DFS(M)-6:  Temperature on Rotary Kiln Shell High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum temperature
on the rotary kiln shell (16-TAHH-51A through E) was 1,600(F.  As noted
in the UMCDF DFS GB Rocket ATBP, this parameter is based on the
manufacturer’s recommendation; hence, the ATB was not designed to
demonstrate this parameter.  The average maximum instantaneous shell
temperature during the DFS GB RCRA and TSCA ATB ranged from 800.0 to
1,350.8(F, with the higher temperature being at the feed end of the
rotary kiln.

VIII.7	DFS-07/DFS(M)-7:  Loss of Flame in Both Burners of the
Afterburner

The RCRA/MACT instantaneous AWFCO setpoint for the presence of a flame
in both burners of the afterburner (16-BSLL-850/851) was the loss of
flame.  In accordance with the UMCDF DFS GB Rocket ATBP, this parameter
was not required to be demonstrated during the ATB.  During the DFS GB
RCRA and TSCA ATB, this switch was not activated.

VIII.8	DFS-08/DFS(M)-8:  HDC Temperature Low-Low

The MACT instantaneous AWFCO setpoint for the minimum temperature in the
HDC (16-TALL-42) was 1,012(F.  The average minimum instantaneous
temperature demonstrated during the DFS GB RCRA and TSCA ATB was 1,092.0
and 1,089.8(F, respectively.  This parameter was not required to be
re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.9	DFS-09/DFS(M)-9:  Jam in Discharge Conveyor Chute

The RCRA/MACT instantaneous AWFCO setpoint for ensuring proper operation
of the discharge conveyor chute (16-XS-58/821) was a switch indicating
the status of the chute.  This position switch indicates if the
discharge conveyor chute is “jammed” or “not jammed.”  In
accordance with the UMCDF DFS GB Rocket ATBP, this parameter was not
required to be demonstrated during the ATB.  During the DFS GB RCRA and
TSCA ATB, this switch was not activated.

VIII.10	DFS-10/DFS(M)-10:  Zero Motion on HDC

The RCRA/MACT instantaneous AWFCO setpoint for ensuring proper motion of
the HDC (16-SSL-57) was a switch indicating “zero speed” of the HDC.
 In accordance with the UMCDF DFS GB Rocket ATBP, this parameter was not
required to be demonstrated during the ATB.  During the DFS GB RCRA and
TSCA ATB, this switch was not activated in Runs 2, 3, and 4.

VIII.11	DFS-11/DFS(M)-11/12:  Afterburner Exhaust Gas Flow Rate
High-High

The RCRA/MACT instantaneous AWFCO setpoints for the maximum exhaust gas
flow rate indirectly measured with a pressure differential indicating
transmitter (16-PDAHH-813) were 0.92 and 1.02 inwc, respectively.  The
average maximum instantaneous flow rate demonstrated during the DFS GB
RCRA and TSCA ATB was 0.869 and 0.674 inwc, respectively.  The UMCDF DFS
GB Rocket ATBP states that the set point would be established based on
the arithmetic mean of the highest five (5) minute rolling average flue
gas flow rate measured during the valid test runs.  The use of one (1)
minute data, aggregated from five (5) second data is more conservative. 
The RCRA setpoint of 0.869 inwc is noted in Table 17.

VIII.12	DFS-12/DFS(M)-13:  Rotary Kiln Temperature Before Spray Low-Low

The RCRA/MACT instantaneous AWFCO setpoint for the minimum temperature
of the rotary kiln exhaust gas before the spray (16-TALL-182) was
1,000(F.  The average minimum instantaneous temperature demonstrated
during the DFS GB RCRA and TSCA ATB was 1,066.9 and 1,091.4(F,
respectively.  This parameter was not required to be re-demonstrated per
the UMCDF DFS GB Rocket ATBP.

VIII.13	DFS(M)-14:  Rotary Kiln Temperature Before Spray Low-Low

The RCRA/MACT rolling hourly average (ROHA) AWFCO setpoint for the
minimum temperature of the rotary kiln exhaust gas before the spray
(16-TALL-182A) was 1,012(F.  The average minimum ROHA temperature
demonstrated during the DFS GB RCRA and TSCA ATB was 1,097.1 and
1,122.5(F, respectively.  The average of the average temperature
demonstrated during the DFS GB RCRA and TSCA ATB was 1,117.0 and
1,128.2(F, respectively.  This parameter was required to be
re-demonstrated per the UMCDF DFS GB Rocket ATBP.  The ROHA value will
be 1,117 F as measured by 16-TALL-182C which is a calculated utilizing
temperature data from either 16-TIC-182 or 16-TIC-20, whichever is not
in control of the burner.  The TSCA ROHA is higher because the MACT/RCRA
operational setpoint was in place prior to the TSCA test to ensure
compliance with permits and regulations other than TSCA.

VIII.14	DFS(M)-15:  Minimum Packed Bed Pressure Drop

The MACT ROHA AWFCO setpoint for the minimum pressure drop across the
packed bed scrubber (24-PDALL-25A) was 0.3 inwc.  The average minimum
ROHA pressure drop demonstrated during the DFS GB RCRA and TSCA ATB was
0.84 and 0.68 inwc, respectively.  This parameter was not required to be
re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.15	DFS-13/DFS(M)-16:  Afterburner Temperature Low-Low

The RCRA/MACT instantaneous AWFCO setpoints for the minimum temperature
of the afterburner (16-TALL-92) was 2,050(F.  The average minimum
instantaneous temperature demonstrated during the DFS GB RCRA and TSCA
ATB was 2,046.3 and 2,092.7(F, respectively, and the average of the
average was 2,050.1 and 2,100.2(F, respectively.  This parameter was
required to be demonstrated during the ATB.  A minimum temperature
setpoint of 2,050(F is in place.

VIII.16	DFS-14/DFS(M)-18:  Afterburner Temperature High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum temperature
in the afterburner (16-TAHH-92) was 2,200(F.  The average maximum
instantaneous temperature demonstrated during the DFS GB RCRA and TSCA
ATB was 2,056.5 and 2,104.9(F, respectively.  This parameter was not
required to be re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.17	DFS(M)-19:  Minimum Brine pH

The MACT ROHA AWFCO setpoints for the minimum pH of the quench brine
(24-AALL-07A/B) was 8.5 pH units.  The average minimum ROHA pH
demonstrated during the DFS GB RCRA and TSCA ATB was 8.90 pH units. 
This parameter was not required to be re-demonstrated per the UMCDF DFS
GB Rocket ATBP.

VIII.18	DFS-15/DFS(M)-20:  Venturi Scrubber Pressure Low-Low

The RCRA/MACT instantaneous AWFCO setpoints for the minimum
instantaneous pressure drop across the venturi scrubber (24-PDALL-08)
was 20 inwc.  The average minimum instantaneous pressure drop
demonstrated during the DFS GB RCRA and TSCA ATB was 19.5 and
24.4 inwc, respectively, and the average of the average was 20.0 and
25.0 inwc, respectively.  This parameter was required to be demonstrated
during the ATB.  A setpoint of 20.0 inwc is in place.

VIII.19		DFS-16/DFS(M)-22:  CO Concentration in PFS Exhaust Gas
High-High

The RCRA/MACT ROHA AWFCO setpoint for the maximum CO concentration in
the PAS Filtration System (PFS) exhaust gas (24-AAHH-207C) was 100 ppm
by volume (ppmv), corrected to 7% O2, dry basis.  The average maximum
ROHA CO concentration demonstrated during the DFS GB RCRA and TSCA ATB
was 5.00 and 1.00 ppmv, respectively, and the average of the average was
2.43 and 0.233 ppmv, respectively.  This parameter is set by regulation
at 100 ppmv, dry basis, corrected to 7% O2.  UMCDF requests that TSCA
use the CO as an indicator of Combustion Efficiency.  This would allow
UMCDF to discontinue use of the current TSCA combustion efficiency which
requires carbon dioxide to be measured in relationship to carbon
monoxide.  Under this request, the carbon dioxide measurement would be
discontinued.

VIII.20	DFS(M)-23:  Maximum Solids Content of Clean Liquor

The MACT 12-hour rolling average (12HRA) AWFCO setpoints for the maximum
density (solids content) in the clean liquor to the scrubber tower
(24-DAHH-35) was 1.04 specific gravity units (sgu).  The average maximum
12HRA density demonstrated during the DFS GB RCRA and TSCA ATB was 1.000
sgu.  This parameter was required to be demonstrated during the ATB. 
The UMCDF DFS GB Rocket ATBP stated that this set point would be
established as the average of the test run average values.  Since
1.00 sgu is the specific gravity for clean water, UMCDF requests a
setpoint of 1.01 sgu to avoid nuisance AWFCOs and it is within the
accuracy range of the instrument.  The slight adjustment over what was
demonstrated can be supported by the low particulate matter emissions. 
The basis for the regulation to establish solids content is to assure
compliance with the particulate matter standard.

VIII.21	DFS-17/DFS(M)-24:  Waste Feed Rate High (Condition 1)

The RCRA/MACT ROHA AWFCO setpoint for the maximum GB agent rocket feed
rate (PDAR) was 38.5 drained rockets per hour (rockets/hr).  The average
maximum ROHA GB agent rocket feed rate demonstrated during the DFS GB
RCRA and TSCA ATB was 36.6 and 37.3 drained rockets/hr, respectively. 
The average maximum ROHA GB agent feed rate was 14.4 and 15.2 lbs/hr,
respectively.  The UMCDF DFS GB Rocket ATBP stated that the feed rate
would be established based on the average of the test run averages;
however, the MACT regulations allow for feed to be based on the maximum
of the test run averages.  A set point consistent with 36.6 rockets/hr
and a GB agent feed rate of 14.4 lbs/hr is requested.

VIII.22	DFS-18/DFS(M)-25:  Clean Liquor to Scrubber Tower Flow Rate
Low-Low

The RCRA/MACT instantaneous AWFCO setpoint for the minimum clean liquor
flow rate to the scrubber tower (24-FALL-30) was 1,475 gallons per
minute (gpm).  The average minimum instantaneous clean liquor flow rate
demonstrated during the DFS GB RCRA and TSCA ATB was 1,595.5 and 1,594.1
gpm, respectively.  This parameter was not required to be
re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.23	DFS-19:  Chemical Agent Emissions High-High, Exhaust Duct

The RCRA instantaneous AWFCO setpoint for the ACAMS located between the
exhaust blower and common stack (MON-ACAM-183) was 0.0003 milligrams per
cubic meter (mg/m3) for GB agent.  During the DFS GB RCRA and TSCA ATB,
the ACAMS located at the exhaust duct was not activated.

VIII.24	DFS-20:  Chemical Agent Emissions High-High, Cyclone Enclosure

The RCRA instantaneous AWFCO setpoint for the ACAMS located within the
cyclone enclosure (MON-ACAM-297) was 0.0003 mg/m3 for GB agent.  During
the DFS GB RCRA and TSCA ATB, the ACAMS located within the cyclone
enclosure was not activated.

VIII.25	DFS-21:  Chemical Agent Emissions High-High, Common Stack

The RCRA instantaneous AWFCO setpoint for the ACAMS located at the
common stack (MON-ACAM-129/223/225) was 0.0003 mg/m3 for GB agent. 
During the DFS GB RCRA and TSCA ATB, the ACAMS located at the common
stack was not activated.

VIII.26	DFS-22:  Brine Surge Tanks Level High-High

The RCRA instantaneous AWFCO setpoint for the maximum level in the Brine
Surge Tanks (23-LSHH-02/06/702/706) was the 18 feet-3 inches
(219 inches) level, or selection of the surge tank for feed to the BRA.
 This is not a parameter that is demonstrable.  

VIII.27	DFS-23/DFS(M)-27:  Clean Liquor to Scrubber Tower pH Low-Low

The RCRA/MACT instantaneous AWFCO setpoint for the minimum pH of the
clean liquor to the scrubber tower (24-AALL-34) was 7.1 pH units.  The
average minimum instantaneous pH demonstrated during the DFS GB RCRA and
TSCA ATB was 7.38 and 7.78 pH, respectively.  This parameter was not
required to be re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.28		DFS-24/DFS(M)-29:  Clean Liquor to Scrubber Tower Pressure
Low-Low

The RCRA/MACT instantaneous AWFCO setpoint for the minimum pressure in
the clean liquor line to the scrubber tower (114-PALL-344) was
25 pounds per square inch gauge (psig).  The average minimum
instantaneous pressure during the DFS GB RCRA and TSCA ATB was 86.7 and
84.00 psig, respectively.  This parameter was not required to be
re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.29		DFS-25:  Quench Tower Exhaust Gas Temperature High-High

The RCRA instantaneous AWFCO setpoint for the maximum temperature of the
quench tower exhaust gas (24-TSHH-01) was 225(F.  During the DFS GB RCRA
and TSCA ATB, this switch was not activated. This parameter was not
required to be re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.30		DFS-26/DFS(M)-30:  Quench Brine to Venturi Scrubber Flow Rate
Low-Low

The RCRA/MACT instantaneous AWFCO setpoints for the minimum flow of
quench brine to the venturi scrubber (24-FALL-06) was 260 gpm.  The
average minimum instantaneous flow rate during the DFS GB RCRA and TSCA
ATB was 259.0 and 283.9 gpm, respectively, and the average of the
average was 260.1 and 285.0 gpm, respectively.  This parameter was not
required to be re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.31		DFS-27/DFS(M)-32:  Brine Density High-High

The RCRA/MACT instantaneous AWFCO setpoints for the maximum density of
the quench brine (24-DAHH-33) was 1.05 sgu.  The UMCDF DFS GB Rocket
ATBP stated that the instantaneous value be established based on the
arithmetic mean of the highest five (5)-minute rolling average values
recorded during the valid test runs.  The average maximum instantaneous
density during the DFS GB RCRA and TSCA ATB was 1.065 and 1.007 sgu,
respectively.  A setpoint of 1.07 sgu is requested based on one minute
data.  This data is read every 15 seconds and recorded once per minute. 
The one minute value meets the regulatory language of reading every 15
seconds and recorded once per minute and is more stringent than the five
minute rolling average stated in the UMCDF DFS GB Rocket ATBP.

VIII.32	DFS(M)-33:  Brine Density High-High

The MACT 12HRA AWFCO setpoints for the maximum density of the quench
brine (24-DAHH-33A) was 1.04 sgu.  The average maximum 12HRA quench
brine density during the DFS GB RCRA and TSCA ATB was 1.061 and 1.010
sgu, respectively, and the average of the average was 1.061 and 1.010
sgu, respectively.  This parameter was required to be demonstrated
during the ATB as the average of the test run averages.  A setpoint of
1.06 sgu is in place.

VIII.33	DFS-28/DFS(M)-34:  Kiln Rotational Speed High-High

The RCRA/MACT instantaneous AWFCO setpoint for the kiln rotational speed
as measured by a speed sensing probe (16-SAHH-602) was 2.06 revolutions
per minute (rpm).  The average maximum instantaneous rotational speed
during the DFS GB RCRA and TSCA ATB was 1.810 and 1.863 rpm,
respectively.  This parameter was not required to be re-demonstrated per
the UMCDF DFS GB Rocket ATBP.

VIII.34	DFS-29:  O2 Concentration in PFS Exhaust Gas High-High

The RCRA instantaneous AWFCO setpoint for the maximum O2 concentration
in the PFS exhaust gas (24-AAHH-206A/B) was 14%, dry basis. The average
maximum instantaneous O2 concentration during the DFS GB RCRA and TSCA
ATB was 10.78 and 10.20%, respectively.  This parameter was not required
to be re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.35	DFS-30/DFS(M)-35:  O2 Concentration in PFS Exhaust Gas Low-Low

The RCRA/MACT 2-minute rolling average (2MRA) AWFCO setpoint for the
minimum O2 concentration in the PFS exhaust gas (24-AALL-206A/B) was
7.7%, dry basis.  The average minimum 2MRA O2 concentration during the
DFS GB RCRA and TSCA ATB was 9.47 and 8.21%, respectively.  This
parameter was not required to be re-demonstrated per the UMCDF DFS GB
Rocket ATBP.

VIII.36	DFS-31/DFS(M)-36:  Afterburner Pressure High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum pressure in
the afterburner (16-PAHH-65) was –0.1 inwc.  The average maximum
instantaneous pressure during the DFS GB RCRA and TSCA ATB was -5.08
and -4.19 inwc, respectively.  This parameter was not required to be
re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.37	DFS-32:  Scrubber Tower Sump Liquid Level High-High

The RCRA instantaneous AWFCO setpoint for the maximum liquid level in
the scrubber tower sump (24-LSHH-10) was 69 inches above the bottom
tangent line.  During the DFS GB RCRA and TSCA ATB, this switch was not
activated.

VIII.38	DFS-33:  Scrubber Tower Sump Liquid Level Low-Low

The RCRA instantaneous AWFCO setpoint for the minimum liquid level in
the scrubber tower sump (24-LSLL-10) was 33 inches above the bottom
tangent line.  During the DFS GB RCRA and TSCA ATB, this switch was not
activated.

VIII.39	DFS-34/DFS(M)-37:  Flame Loss in Rotary Kiln

The RCRA/MACT instantaneous AWFCO setpoint for the presence of a flame
in the rotary kiln (16-BSLL-844) was the loss of flame.  During the DFS
GB RCRA and TSCA ATB, this switch was not activated.

VIII.40	DFS-35/DFS(M)-38:  PFS Prefilter Differential Pressure High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum differential
pressure across the PFS prefilters (114-PDAHH-440A/442A) was 1.5 inwc. 
[NOTE:  During the DFS GB RCRA and TSCA ATB, the common spare PFS and
PFS for the LIC1, LIC2 and MPF were not used for the DFS.]  The average
maximum instantaneous prefilter differential pressure during the DFS GB
RCRA and TSCA ATB was for 114-FILT-111/112 was 0.47/0.45 and 0.95/0.83
inwc, respectively.  This parameter was not required to be
re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.41	DFS-36/DFS(M)-39:  PFS HEPA Filter Differential Pressure
High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum differential
pressure across the inlet and outlet PFS HEPA filter (114-PDAHH-440B/H
and 442B/H) was 3.0 inwc.  [NOTE:  During the DFS GB RCRA and TSCA ATB,
the common spare PFS and PFS for the LIC1, LIC2 and MPF were not used
for the DFS.]  The average maximum instantaneous HEPA differential
pressure during the DFS RCRA GB ATB was for 114-FILT-111/112 was
0.91/0.67 and 0.94/0.68 inwc, respectively.  The average maximum
instantaneous HEPA differential pressure during the DFS TSCA GB ATB was
for 114-FILT-111/112 was 0.77/0.63 and 0.88/0.61 inwc, respectively. 
This parameter was not required to be re-demonstrated per the UMCDF DFS
GB Rocket ATBP.

VIII.42	DFS-37/DFS(M)-40:  Temperature of Gas to Carbon Filter System
High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum temperature
of the gas entering the carbon filter system (114-TSHH-430) was 180(F. 
During the DFS GB RCRA and TSCA ATB, this switch was not activated.

The RCRA/MACT ROHA AWFCO setpoint for the maximum temperature of the gas
entering the carbon filter system (114-TAHH-417) was 169°F.  The
average maximum ROHA temperature during the DFS GB RCRA and TSCA ATB was
165.3 and 165.0°F, respectively.  This parameter was not required to be
re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.43	DFS-38/DFS(M)-41:  Moisture of Gas to Carbon Filter System
High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum moisture
content of the gas entering the carbon filter system (114-MSHH-431A/B)
was 80% relative humidity (RH).  During the DFS GB RCRA and TSCA ATB,
this switch was not activated.

The RCRA/MACT ROHA AWFCO setpoint for the maximum moisture content of
the gas entering the carbon filter system (114-MAHH-431A/B) was 55% RH. 
The average maximum ROHA RH during the DFS GB RCRA and TSCA ATB was 42.0
and 31.3%, respectively.  This parameter was not required to be
re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.44	DFS-39:  Carbon Filter Bypass Valve Operation

The RCRA instantaneous AWFCO setpoint for ensuring that the carbon
filter system is online during treatment operations (114-ZS-449B) was a
switch indicating a status.  The position switch indicated if the gate
was “closed” or “not closed.”  During the DFS GB RCRA and TSCA
ATB, this switch was not activated.

VIII.45	DFS(M)-42:  Prefilter Differential Pressure Low-Low

The MACT 2MRA AWFCO setpoint for the minimum differential pressure
across the PFS prefilters (114-PDALL-440A/442A) was 0.20 inwc.  [NOTE: 
During the DFS GB RCRA and TSCA ATB, the common spare PFS and PFS for
the LIC1, LIC2 and MPF were not used for the DFS.]  The average minimum
2MRA prefilter differential pressure during the DFS GB RCRA and TSCA ATB
was for 114-FILT-111/112 was 0.44/0.41 and 0.80/0.67 inwc, respectively.
 This parameter was not required to be re-demonstrated per the UMCDF DFS
GB Rocket ATBP.

VIII.46	DFS(M)-43:  HEPA Filter Differential Pressure Low-Low

The RCRA/MACT instantaneous AWFCO setpoint for the minimum differential
pressure across the HEPA filter (114-PDAHH-440B/H and 442B/H) was 0.15
inwc.  [NOTE:  During the DFS GB RCRA and TSCA ATB, the common spare PFS
and PFS for the LIC1, LIC2 and MPF were not used for the DFS.]  The
average minimum instantaneous HEPA differential pressure during the DFS
RCRA GB ATB was for 114-FILT-111/112 was 0.86/0.62 and 0.88/0.64 inwc,
respectively.  The average minimum instantaneous HEPA differential
pressure during the DFS TSCA GB ATB was for 114-FILT-111/112 was
0.69/0.56 and 0.76/0.55 inwc, respectively.  This parameter was not
required to be re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.47	DFS-40:  Chemical Agent Emissions High-High, PFS Unit

The RCRA instantaneous AWFCO setpoint for the ACAMS located upstream of
the PFS (MON-ACAM-353) was 0.0003 mg/m3 for GB agent.  During the DFS GB
RCRA and TSCA ATB, the ACAMS located upstream of the PFS was not
activated.

VIII.48	DFS-41/DFS(M)-44:  Mist Eliminator Differential Pressure
High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum differential
pressure across the mist eliminator vessel (24-PDAHH-53) was 20 inwc. 
The average maximum instantaneous differential pressure during the DFS
GB RCRA and TSCA ATB was 1.7 and 2.9 inwc, respectively.  This
parameter was not required to be re-demonstrated per the UMCDF DFS GB
Rocket ATBP.

VIII.49	DFS-42/DFS(M)-45:  Rotary Kiln Temperature Before Spray
High-High

The RCRA/MACT instantaneous AWFCO setpoint for the maximum temperature
of the rotary kiln exhaust (16-TAHH-182A) was 1,548°F.  The average
maximum instantaneous temperature during the DFS GB RCRA and TSCA ATB
was 1,123.7 and 1,134.7°F, respectively.  This parameter was not
required to be re-demonstrated per the UMCDF DFS GB Rocket ATBP.

VIII.50	DFS-43:  Moisture of Gas Exiting Carbon Filter System High-High

The RCRA 30-minute rolling average (30MRA) AWFCO setpoint for the
maximum moisture content of the gas exiting the carbon filter system
(114-MAHH-111/112) was 55% RH.  [NOTE:  During the DFS GB RCRA and TSCA
ATB, the common spare PFS and PFS for the LIC1, LIC2 and MPF were not
used for the DFS.]  The average maximum 30MRA RH for 114-FILT-111/112
during the DFS GB RCRA and TSCA ATB was 46.6/46.0 and 47.9/52.0%,
respectively.  This parameter was not required to be re-demonstrated per
the UMCDF DFS GB Rocket ATBP.

IX.	RATA

A RATA was conducted on the CO and O2 facility CEMS installed on the DFS
exhaust duct October 27, 2005.  The results of the RATA are in
Appendix I.  The RATA was conducted IAW 40 CFR 63, Subpart EEE.

X.	Conclusions

All UMCDF TSCA approval requirements were met at the DFS exhaust duct
location.  Based on the results of the ATB testing and IAW TSCA Approval
Condition 2.b.3.B, UMCDF requests authorization to conduct interim
operations at a feed rate of less than or equal to 29.4 rockets/hr until
the UMCDF DFS GB TSCA Final ATBR and UMCDF DFS GB Rocket ATBR (RCRA) are
approved.  Upon approval of these reports, UMCDF would then request for
the Oregon Department of Environmental Quality and the EPA to grant
normal operations consistent with the rocket feed rate of 36.6
rockets/hr.

Table 1:	Sampling Time Intervals

Run	Date	1st Port Change	2nd Port Change



Start	Sampling Interruptions	Stop	Start	Sampling Interruptions	Stop

1	10/28/05	0800	Not Applicable	1000	1020	1151 to 1210(1)

1211 to 1510(2)	1538

2	10/29/05	0802	0814 to 0834(3)

0924 to 1250(4)	1348	1412	Not Applicable	1612

3	10/30/05	0948	0954 to 1003(5)

1109 to 1112(6)	1200	1215	1400 to 1405(7)	1420

4	10/30/05	1518	Not Applicable	1718	1734	Not Applicable	1934



Footnotes:

(1)	Sampling interrupted due to rocket miss-feed.

(2)	Sampling interrupted due to jammed feed chute.

(3)	Sampling interrupted due to ACAMS malfunction.

(4)	Sampling interrupted due to mechanical repairs.

(5)	Sampling interrupted due to kiln feed malfunction.

(6)	Sampling interrupted due to tipping gate malfunction.

(7)	Sampling interrupted due to rocket miss-feed.

Table 2:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 1

Parameter	AWFCO Number	Instrument	AWFCO	Run 1

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Feed Rate











GB Agent	DFS-17	DFS(M)-24	PDAR	20.6	ROHA	lbs/hr	9.3	15.7	13.4	0.94

Rockets	DFS-17	DFS(M)-24	PDAR	38.5	ROHA	rckts/hr	26.0	37.4	36.3	1.93

Rockets	---	---	PDAR	---	I	rckts/hr	---	---	35.25	---

Rotary Retort











Temperature	DFS-01/12	DFS(M)-1/13	16-TIC-182	1,000 – 1,615	I	oF
1,082.3	1,154.3	1,130.3	11.52

Temperature	DFS-42	DFS(M)-14/45	16-TIC-182A	1,012 – 1548	ROHA	oF
1,121.5	1,141.0	1,132.1	5.36

Temperature	DFS-02/03	DFS(M)-2/3	16-TIC-08	949 – 1,539	I	oF	1,081.5
1,137.0	1,116.8	8.82

Temperature	---	---	16-TIT-20	---	I	oF	1,070.0	1,319.3	1,119.5	71.91

Pressure	---	---	16-PIT-18	---	I	inwc	-1.53	-0.76	-1.11	0.129

Fuel Gas Flow Rate	---	---	16-FIT-243	---	I	scfm	48.0	140.3	59.6	19.17

Combustion Air Flow Rate	---	---	16-FIT-21	---	I	scfm	508.5	1,190.3
568.9	132.75

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51A	1,600	I	oF	800.0(1)	917.5
814.5	33.02

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51B	1,600	I	oF	877.3	1,017.0
911.0	40.87

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51C	1,600	I	oF	1,029.5	1,083.3
1,047.9	11.65

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51D	1,600	I	oF	1,022.8	1,192.0
1,145.9	32.40

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51E	1,600	I	oF	913.0	1,134.5
1,086.1	34.99

Rotational Speed	DFS-28	DFS(M)-34	16-ZS-602	2.06	I	rpm	1.855	1.865	1.860
0.0015

O2 Concentration	---	---	16-AIT-09	---	I	%	2.31	21.14	12.66	1.935

Afterburner











Flow Rate	DFS-11	DFS(M)-11	16-PDIT-813	1.02	I	inwc	0.533	0.718	0.610
0.0255

Flow Rate	---	DFS(M)-12	16-PDIT-813A	1.02	ROHA	inwc	0.600	0.630	0.607
0.0058

Temperature	DFS-13/14	DFS(M)-16/18	16-TIC-92	2,000 – 2,200	I	oF
2,092.0	2,105.5	2,100.0	1.84

Pressure	DFS-31	DFS(M)-36	16-PIT-65	-0.1	I	inwc	-5.53	-4.20	-4.80	0.228

Table 2:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 1
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 1

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Afterburner (Continued)











Fuel Gas Flow Rate	---	---	16-FIT-66	---	I	scfm	212.3	222.0	215.7	1.95

Fuel Gas Flow Rate	---	---	16-FIT-191	---	I	scfm	210.3	226.0	215.9	2.81

Combustion Air Flow Rate	---	---	16-FIT-78	---	I	scfm	1,464.0	1,607.3
1,511.5	24.33

Combustion Air Flow Rate	---	---	16-FIT-79	---	I	scfm	1,889.0	2,014.3
1,941.2	24.16

HDC











Temperature	DFS-08	DFS(M)-8	16-TIT-42	1,012	I	oF	1,089.0	1,114.8	1,100.3
4.63

Temperature	---	---	16-TIT-184	---	I	oF	1,092.0	1,110.0	1,099.8	3.16

Quench Tower











pH 	---	DFS(M)-19	24-AIT-7A/B	7.5	ROHA	PH unit	8.80	8.90	8.88	0.036

Brine Density 	DFS-27	DFS(M)-32	24-DIT-33	1.16	I	sgu	1.000	1.000	1.000
0.0000

Brine Density	---	DFS(M)-33	24-DIT-33A	1.16	12HRA	sgu	1.010	1.010	1.010
0.0000

Level	---	---	24-LIT-09	---	I	inches	3	3.8	3.6	0.12

Venturi Scrubber











Pressure Differential	DFS-15	DFS(M)-20	24-PDIT-08	15	I	inwc	24.3	25.5
25.0	0.21

Brine Flow Rate	DFS-26	DFS(M)-30	24-FIT-06	238	I	gpm	284.0	286.0	285.0
0.46

Scrubber Tower











Clean Liquor Flow Rate	DFS-18	DFS(M)-25	24-FIT-30	1,475	I	gpm	1,594.5
1,604.0	1,599.9	1.74

Packed Bed Pressure Drop	---	DFS(M)-15	24-PDIT-25A	0.3	ROHA	inwc	0.67
0.70	0.68	0.006

pH	DFS-23	DFS(M)-27	24-AIT-34	7.1	I	PH unit	7.80	8.00	7.89	0.034

Clean Liquor Pressure	DFS-24	DFS(M)-29	114-PIT-344	25	I	psig	84.0	85.0
85	0.15

Clean Liquor Density	---	DFS(M)-23	24-DIT-35A	1.08	12HRA	sgu	1.000	1.000
1.000	0.0000

Clean Liquor Return	---	---	24-TIT-274	---	I	oF	116.0	118.0	117.1	0.43

Table 2:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 1
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 1

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Mist Eliminator











Differential Pressure	DFS-41	DFS(M)-44	24-PDIT-53	20	I	inwc	2.6	2.9	2.7
0.04

Water pH	---	---	24-AIT-273	---	I	pH unit	7.50	8.48	7.88	0.326

Brine Surge Tank Level











Level (BRA-TANK-101)	---	---	23-LIT-03	---	I	inches	140.00	170.00	148.88
7.362

Level (BRA-TANK-102)	---	---	23-LIT-07	---	I	inches	192.00	195.00	193.50
0.618

Level (BRA-TANK-201)	---	---	23-LIT-703	---	I	inches	70.50	73.25	71.88
0.529

Level (BRA-TANK-202)	---	---	23-LIT-707	---	I	inches	0.00	0.00	0.00
0.000

PFS Carbon Filter











Prefilter Differential Pressure	DFS-35	DFS(M)-38	114-PDIT-440A	1.5	I
inwc	0.71	0.79	0.73	0.015

Prefilter Differential Pressure	---	DFS(M)-42	114-PDIT-440A	0.2	2MRA
inwc	0.72	0.79	0.73	0.015

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-440B	3.0	I	inwc
0.61	0.68	0.63	0.015

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-440H	3.0	I	inwc
0.57	0.63	0.59	0.014

Relative Humidity	DFS-43	---	114-MIT-111	55	30MRA	%	44.10	45.90	45.40
0.450

Prefilter Differential Pressure	DFS-35	DFS(M)-38	114-PDIT-442A	1.5	I
inwc	0.62	0.92	0.72	0.074

Prefilter Differential Pressure	---	DFS(M)-42	114-PDIT-442A	0.2	2MRA
inwc	0.62	0.91	0.72	0.074

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-442B	3.0	I	inwc
0.79	0.87	0.81	0.013

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-442H	3.0	I	inwc
0.53	0.59	0.54	0.009

Relative Humidity	DFS-43	---	114-MIT-112	55	30MRA	%	49.0	52.3	50.0	0.85

Temperature	DFS-37	DFS(M)-40	114-TIT-417R	180	ROHA	oF	165.0	165.0	165.0
0.00

Relative Humidity	DFS-38	DFS(M)-41	114-MIT-431A/B	55	ROHA	%	29.00	30.00
29.02	0.128

Table 2:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 1
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 1

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

PAS Exhaust Duct CEMS











CO Concentration	DFS-16	DFS(M)-22	24-AIT-207C	100	ROHA	ppmv	0.0	4.0	1.6
1.70

O2 Level	DFS-29	---	24-AIT-206C	14	I	%	8.51	10.58	9.30	0.285

O2 Level	DFS-30	DFS(M)-35	24-AIT-206CM2	7.7	2MRA	%	8.60	10.29	9.30	0.199



NOTES:	

(A)	DFS-04 [DFS(M)-4], DFS-05 [DFS(M)-5], DFS-07 [DFS(M)-7], DFS-09
[DFS(M)-9], DFS-10 [DFS(M)-10], DFS-32, DFS-33, DFS-34 [DFS(M)-37], and
DFS-39 are AWFCO alarms that are activated by a switch set at the AWFCO
setpoint.

(B)	DFS-19, DFS-20, DFS-21, DFS-22, and DFS-40 are AWFCO alarms
associated with ACAMS, which were not activated during the DFS GB TSCA
ATB.

Footnote:

(1)	Shell RTD does not register below 800(F.

Abbreviations:

%	percent	oF	degrees Fahrenheit

---	not applicable	ACAMS	Automatic Continuous Air Monitoring System

AIT	analyzer indicating transmitter	ATB	agent trial burn

AWFCO	automatic waste feed cut off	BRA	Brine Reduction Area

CEMS	Continuous Emissions Monitoring System	CO	carbon monoxide

DFS	Deactivation Furnace System	DIT	density indicating transmitter

FIT	flow indicating transmitter	gpm	gallons per minute

HDC	Heated Discharge Conveyor	HEPA	high efficiency particulate

12HRA	12-hour rolling average	I	instantaneous

inwc	inches of water column	lbs/hr	pounds per hour

LIT	level indicating transmitter	2MRA	2-minute rolling average

30MRA	30-minute rolling average	MACT	Maximum Achievable Control
Technologies

MIT	moisture indicating transmitter	O2	oxygen

PAS	Pollution Abatement System	PDAR	process data acquisition and
recording

PDIT	pressure differential indicating transmitter	PFS	PAS Filtration
System

PIT	pressure indicating transmitter	ppmv	parts per million by volume

psig	pounds per square inch gauge	RCRA	Resource Conservation and
Recovery Act

rckts/hr	rockets per hour	ROHA	rolling hourly average

rpm	revolutions per minute	scfm	standard cubic feet per minute

sgu	specific gravity unit	ZS	position switch

std.dev.	standard deviation	TIC	temperature indicating controller

TIT	temperature indicating transmitter	TSCA	Toxic Substances Control Act

Table 3:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 2

Parameter	AWFCO Number	Instrument	AWFCO	Run 2

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Feed Rate











GB Agent	DFS-17	DFS(M)-24	PDAR	20.6	ROHA	lbs/hr	10.6	15.9	13.7	1.37

Rockets	DFS-17	DFS(M)-24	PDAR	38.5	ROHA	rckts/hr	29.5	37.3	35.0	2.71

Rockets	---	---	PDAR	---	I	rckts/hr	---	---	35.25	---

Rotary Retort











Temperature	DFS-01/12	DFS(M)-1/13	16-TIC-182	1,000 – 1,615	I	oF
1,094.0	1,156.8	1,125.9	10.45

Temperature	DFS-42	DFS(M)-14/45	16-TIC-182A	1,012 – 1548	ROHA	oF
1,122.0	1,134.0	1,125.6	3.56

Temperature	DFS-02/03	DFS(M)-2/3	16-TIC-08	949 – 1,539	I	oF	1,085.0
1,129.0	1,109.6	7.77

Temperature	---	---	16-TIT-20	---	I	oF	1,067.3	1,295.0	1,117.8	38.27

Pressure	---	---	16-PIT-18	---	I	inwc	-1.49	-0.74	-1.10	0.128

Fuel Gas Flow Rate	---	---	16-FIT-243	---	I	scfm	47.8	133.0	58.3	14.88

Combustion Air Flow Rate	---	---	16-FIT-21	---	I	scfm	508.5	1,097.8
553.6	96.46

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51A	1,600	I	oF	800.0(1)	864.8
801.8	7.89

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51B	1,600	I	oF	866.3	955.5
905.4	19.02

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51C	1,600	I	oF	1,026.8	1,071.0
1,052.2	11.65

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51D	1,600	I	oF	1,035.8	1,145.0
1,095.2	22.15

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51E	1,600	I	oF	803.3	1,104.3
949.2	58.41

Rotational Speed	DFS-28	DFS(M)-34	16-ZS-602	2.06	I	rpm	1.853	1.865	1.859
0.0020

O2 Concentration	---	---	16-AIT-09	---	I	%	10.35	14.69	12.74	0.566

Afterburner











Flow Rate	DFS-11	DFS(M)-11	16-PDIT-813	1.02	I	inwc	0.543	0.708	0.599
0.0236

Flow Rate	---	DFS(M)-12	16-PDIT-813A	1.02	ROHA	inwc	0.590	0.608	0.598
0.0042

Temperature	DFS-13/14	DFS(M)-16/18	16-TIC-92	2,000 – 2,200	I	oF
2,091.5	2,105.3	2,100.3	2.06

Pressure	DFS-31	DFS(M)-36	16-PIT-65	-0.1	I	inwc	-5.43	-4.10	-4.75	0.222

Table 3:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 2
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 2

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Afterburner (Continued)











Fuel Gas Flow Rate	---	---	16-FIT-66	---	I	scfm	211.8	221.0	216.4	1.74

Fuel Gas Flow Rate	---	---	16-FIT-191	---	I	scfm	210.3	223.3	216.5	2.27

Combustion Air Flow Rate	---	---	16-FIT-78	---	I	scfm	1,458.3	1,573.8
1,515.3	21.32

Combustion Air Flow Rate	---	---	16-FIT-79	---	I	scfm	1,869.5	2,016.8
1,947.9	24.47

HDC











Temperature	DFS-08	DFS(M)-8	16-TIT-42	1,012	I	oF	1,086.0	1,114.3	1,100.0
5.26

Temperature	---	---	16-TIT-184	---	I	oF	1,091.0	1,110.5	1,099.0	4.28

Quench Tower











pH 	---	DFS(M)-19	24-AIT-7A/B	7.5	ROHA	PH unit	8.90	8.90	8.90	0.000

Brine Density 	DFS-27	DFS(M)-32	24-DIT-33	1.16	I	sgu	1.000	1.000	1.000
0.0000

Brine Density	---	DFS(M)-33	24-DIT-33A	1.16	12HRA	sgu	1.010	1.010	1.010
0.0000

Level	---	---	24-LIT-09	---	I	inches	3	3.7	3.4	0.21

Venturi Scrubber











Pressure Differential	DFS-15	DFS(M)-20	24-PDIT-08	15	I	inwc	24.5	25.8
25.0	0.24

Brine Flow Rate	DFS-26	DFS(M)-30	24-FIT-06	238	I	gpm	283.8	286.3	285.0
0.46

Scrubber Tower











Clean Liquor Flow Rate	DFS-18	DFS(M)-25	24-FIT-30	1,475	I	gpm	1,593.5
1,603.5	1,600.0	1.77

Packed Bed Pressure Drop	---	DFS(M)-15	24-PDIT-25A	0.3	ROHA	inwc	0.69
0.70	0.69	0.004

pH	DFS-23	DFS(M)-27	24-AIT-34	7.1	I	PH unit	7.80	7.90	7.87	0.043

Clean Liquor Pressure	DFS-24	DFS(M)-29	114-PIT-344	25	I	psig	84.0	85.0
84.5	0.38

Clean Liquor Density	---	DFS(M)-23	24-DIT-35A	1.08	12HRA	sgu	1.000	1.000
1.000	0.0000

Clean Liquor Return	---	---	24-TIT-274	---	---	oF	117.5	120.8	119.1	0.52

Table 3:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 2
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 2

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Mist Eliminator











Differential Pressure	DFS-41	DFS(M)-44	24-PDIT-53	20	I	inwc	2.6	2.9	2.7
0.04

Water pH	---	---	24-AIT-273	---	I	pH unit	7.20	9.00	8.25	0.642

Brine Surge Tank Level











Level (BRA-TANK-101)	---	---	23-LIT-03	---	I	inches	199.00	202.75	201.17
0.615

Level (BRA-TANK-102)	---	---	23-LIT-07	---	I	inches	135.75	175.25	152.46
12.777

Level (BRA-TANK-201)	---	---	23-LIT-703	---	I	inches	103.00	128.50
119.07	7.618

Level (BRA-TANK-202)	---	---	23-LIT-707	---	I	inches	0.00	0.00	0.00
0.000

PFS Carbon Filter











Prefilter Differential Pressure	DFS-35	DFS(M)-38	114-PDIT-440A	1.5	I
inwc	0.69	0.96	0.85	0.080

Prefilter Differential Pressure	---	DFS(M)-42	114-PDIT-440A	0.2	2MRA
inwc	0.70	0.96	0.85	0.079

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-440B	3.0	I	inwc
0.80	0.89	0.83	0.013

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-440H	3.0	I	inwc
0.56	0.62	0.58	0.010

Relative Humidity	DFS-43	---	114-MIT-111	55	30MRA	%	49.10	50.40	49.60
0.335

Prefilter Differential Pressure	DFS-35	DFS(M)-38	114-PDIT-442A	1.5	I
inwc	0.69	0.96	0.79	0.046

Prefilter Differential Pressure	---	DFS(M)-42	114-PDIT-442A	0.2	2MRA
inwc	0.70	0.96	0.79	0.030

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-442B	3.0	I	inwc
0.64	0.89	0.70	0.061

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-442H	3.0	I	inwc
0.56	0.65	0.61	0.023

Relative Humidity	DFS-43	---	114-MIT-112	55	30MRA	%	46.4	50.4	47.2	0.65

Temperature	DFS-37	DFS(M)-40	114-TIT-417R	180	ROHA	oF	165.0	165.0	165.0
0.00

Relative Humidity	DFS-38	DFS(M)-41	114-MIT-431A/B	55	ROHA	%	31.00	31.00
31.00	0.000

Table 3:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 2
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 2

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

PAS Exhaust Duct CEMS











CO Concentration	DFS-16	DFS(M)-22	24-AIT-207C	100	ROHA	ppmv	0.0	1.0	0.2
0.41

O2 Level	DFS-29	---	24-AIT-206C	14	I	%	8.33	10.20	9.37	0.289

O2 Level	DFS-30	DFS(M)-35	24-AIT-206CM2	7.7	2MRA	%	8.63	10.00	9.37	0.200



NOTES:	

(A)	DFS-04 [DFS(M)-4], DFS-05 [DFS(M)-5], DFS-07 [DFS(M)-7], DFS-09
[DFS(M)-9], DFS-10 [DFS(M)-10], DFS-32, DFS-33, DFS-34 [DFS(M)-37], and
DFS-39 are AWFCO alarms that are activated by a switch set at the AWFCO
setpoint.

(B)	DFS-19, DFS-20, DFS-21, DFS-22, and DFS-40 are AWFCO alarms
associated with ACAMS, which were not activated during the DFS GB TSCA
ATB.

Footnote:

(1)	Shell RTD does not register below 800(F.

Abbreviations:

%	percent	oF	degrees Fahrenheit

---	not applicable	ACAMS	Automatic Continuous Air Monitoring System

AIT	analyzer indicating transmitter	ATB	agent trial burn

AWFCO	automatic waste feed cut off	BRA	Brine Reduction Area

CEMS	Continuous Emissions Monitoring System	CO	carbon monoxide

DFS	Deactivation Furnace System	DIT	density indicating transmitter

FIT	flow indicating transmitter	gpm	gallons per minute

HDC	Heated Discharge Conveyor	HEPA	high efficiency particulate

12HRA	12-hour rolling average	I	instantaneous

inwc	inches of water column	lbs/hr	pounds per hour

LIT	level indicating transmitter	2MRA	2-minute rolling average

30MRA	30-minute rolling average	MACT	Maximum Achievable Control
Technologies

MIT	moisture indicating transmitter	O2	oxygen

PAS	Pollution Abatement System	PDAR	process data acquisition and
recording

PDIT	pressure differential indicating transmitter	PFS	PAS Filtration
System

PIT	pressure indicating transmitter	ppmv	parts per million by volume

psig	pounds per square inch gauge	RCRA	Resource Conservation and
Recovery Act

rckts/hr	rockets per hour	ROHA	rolling hourly average

rpm	revolutions per minute	scfm	standard cubic feet per minute

sgu	specific gravity unit	ZS	position switch

std.dev.	standard deviation	TIC	temperature indicating controller

TIT	temperature indicating transmitter	TSCA	Toxic Substances Control Act

Table 4:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 3

Parameter	AWFCO Number	Instrument	AWFCO	Run 3

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Feed Rate











GB Agent	DFS-17	DFS(M)-24	PDAR	20.6	ROHA	lbs/hr	12.5	16.8	14.9	0.82

Rockets	DFS-17	DFS(M)-24	PDAR	38.5	ROHA	rckts/hr	31.0	37.3	35.2	1.26

Rockets	---	---	PDAR	---	I	rckts/hr	---	---	36.0	---

Rotary Retort











Temperature	DFS-01/12	DFS(M)-1/13	16-TIC-182	1,000 – 1,615	I	oF
1,091.3	1,170.3	1,136.4	12.35

Temperature	DFS-42	DFS(M)-14/45	16-TIC-182A	1,012 – 1548	ROHA	oF
1,125.0	1,140.0	1,134.1	2.99

Temperature	DFS-02/03	DFS(M)-2/3	16-TIC-08	949 – 1,539	I	oF	1,072.8
1,123.0	1,103.8	10.06

Temperature	---	---	16-TIT-20	---	I	oF	1,069.5	1,350.8	1,110.8	49.79

Pressure	---	---	16-PIT-18	---	I	inwc	-1.47	-0.76	-1.11	0.102

Fuel Gas Flow Rate	---	---	16-FIT-243	---	I	scfm	48.0	101.0	53.4	9.77

Combustion Air Flow Rate	---	---	16-FIT-21	---	I	scfm	506.8	855.5	533.1
58.44

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51A	1,600	I	oF	800.0(1)	922.0
809.3	25.95

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51B	1,600	I	oF	872.8	1,005.0
915.2	34.56

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51C	1,600	I	oF	1,045.5	1,081.3
1,064.8	8.12

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51D	1,600	I	oF	1,092.5	1,188.8
1,151.2	19.11

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51E	1,600	I	oF	905.5	1,044.0
1,003.6	20.3

Rotational Speed	DFS-28	DFS(M)-34	16-ZS-602	2.06	I	rpm	1.853	1.865	1.859
0.0015

O2 Concentration	---	---	16-AIT-09	---	I	%	10.91	15.37	12.81	0.617

Afterburner











Flow Rate	DFS-11	DFS(M)-11	16-PDIT-813	1.02	I	inwc	0.528	0.668	0.590
0.0189

Flow Rate	---	DFS(M)-12	16-PDIT-813A	1.02	ROHA	inwc	0.580	0.600	0.588
0.0054

Temperature	DFS-13/14	DFS(M)-16/18	16-TIC-92	2,000 – 2,200	I	oF
2,090.0	2,105.5	2,100.0	2.58

Pressure	DFS-31	DFS(M)-36	16-PIT-65	-0.1	I	inwc	-5.18	-4.24	-4.66	0.180

Table 4:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 3
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 3

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Afterburner (Continued)











Fuel Gas Flow Rate	---	---	16-FIT-66	---	I	scfm	212.0	221.0	217.1	1.57

Fuel Gas Flow Rate	---	---	16-FIT-191	---	I	scfm	210.0	223.0	217.2	2.48

Combustion Air Flow Rate	---	---	16-FIT-78	---	I	scfm	1,456.3	1,590.3
1,520.3	22.23

Combustion Air Flow Rate	---	---	16-FIT-79	---	I	scfm	1,903.5	2,019.5
1,953.6	21.26

HDC











Temperature	DFS-08	DFS(M)-8	16-TIT-42	1,012	I	oF	1,092.0	1,112.0	1,100.0
4.52

Temperature	---	---	16-TIT-184	---	I	oF	1,090.0	1,108.0	1,099.3	3.63

Quench Tower











pH 	---	DFS(M)-19	24-AIT-7A/B	7.5	ROHA	pH unit	8.90	8.90	8.90	0.000

Brine Density 	DFS-27	DFS(M)-32	24-DIT-33	1.16	I	sgu	1.010	1.010	1.010
0.0000

Brine Density	---	DFS(M)-33	24-DIT-33A	1.16	12HRA	sgu	1.010	1.010	1.010
0.0000

Level	---	---	24-LIT-09	---	I	inches	3.0	3.5	3.3	0.12

Venturi Scrubber











Pressure Differential	DFS-15	DFS(M)-20	24-PDIT-08	15	I	inwc	24.3	25.7
25.0	0.23

Brine Flow Rate	DFS-26	DFS(M)-30	24-FIT-06	238	I	gpm	284.0	286.0	285.0
0.38

Scrubber Tower











Clean Liquor Flow Rate	DFS-18	DFS(M)-25	24-FIT-30	1,475	I	gpm	1,595.0
1,603.0	1,599.9	1.55

Packed Bed Pressure Drop	---	DFS(M)-15	24-PDIT-25A	0.3	ROHA	inwc	0.69
0.70	0.69	0.004

pH	DFS-23	DFS(M)-27	24-AIT-34	7.1	I	pH unit	7.75	8.00	7.91	0.039

Clean Liquor Pressure	DFS-24	DFS(M)-29	114-PIT-344	25	I	psig	84.0	85.0
84.2	0.25

Clean Liquor Density	---	DFS(M)-23	24-DIT-35A	1.08	12HRA	sgu	1.000	1.000
1.000	0.0000

Clean Liquor Return	---	---	24-TIT-274	---	I	oF	117.5	121.0	119.2	0.54

Table 4:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 3
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 3

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Mist Eliminator











Differential Pressure	DFS-41	DFS(M)-44	24-PDIT-53	20	I	inwc	2.8	3.0	2.8
0.04

Water pH	---	---	24-AIT-273	---	I	pH unit	6.80	8.28	7.32	0.535

Brine Surge Tank Level











Level (BRA-TANK-101)	---	---	23-LIT-03	---	I	inches	196.00	203.50	201.41
1.469

Level (BRA-TANK-102)	---	---	23-LIT-07	---	I	inches	69.25	81.25	75.31
3.263

Level (BRA-TANK-201)	---	---	23-LIT-703	---	I	inches	175.75	203.75
192.73	8.941

Level (BRA-TANK-202)	---	---	23-LIT-707	---	I	inches	0.00	0.00	0.00
0.000

PFS Carbon Filter











Prefilter Differential Pressure	DFS-35	DFS(M)-38	114-PDIT-440A	1.5	I
inwc	0.84	0.94	0.86	0.016

Prefilter Differential Pressure	---	DFS(M)-42	114-PDIT-440A	0.2	2MRA
inwc	0.84	0.94	0.86	0.017

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-440B	3.0	I	inwc
0.63	0.71	0.66	0.013

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-440H	3.0	I	inwc
0.55	0.64	0.58	0.021

Relative Humidity	DFS-43	---	114-MIT-111	55	30MRA	%	44.4	46.3	45.3	0.557

Prefilter Differential Pressure	DFS-35	DFS(M)-38	114-PDIT-442A	1.5	I
inwc	0.59	0.74	0.66	0.038

Prefilter Differential Pressure	---	DFS(M)-42	114-PDIT-442A	0.2	2MRA
inwc	0.59	0.74	0.66	0.038

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-442B	3.0	I	inwc
0.82	0.90	0.84	0.010

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-442H	3.0	I	inwc
0.55	0.61	0.57	0.007

Relative Humidity	DFS-43	---	114-MIT-112	55	30MRA	%	49.3	52.6	50.7	1.06

Temperature	DFS-37	DFS(M)-40	114-TIT-417R	180	ROHA	oF	165.0	165.0	165.0
0.00

Relative Humidity	DFS-38	DFS(M)-41	114-MIT-431A/B	55	ROHA	%	31.00	32.00
31.10	0.295

Table 4:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 3
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 3

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

PAS Exhaust Duct CEMS











CO Concentration	DFS-16	DFS(M)-22	24-AIT-207C	100	ROHA	ppmv	0.0	0.0	0.0
0.00

O2 Level	DFS-29	---	24-AIT-206C	14	I	%	7.83	10.41	9.37	0.338

O2 Level	DFS-30	DFS(M)-35	24-AIT-206CM2	7.7	2MRA	%	8.29	10.16	9.38	0.266



NOTES:	

(A)	DFS-04 [DFS(M)-4], DFS-05 [DFS(M)-5], DFS-07 [DFS(M)-7], DFS-09
[DFS(M)-9], DFS-10 [DFS(M)-10], DFS-32, DFS-33, DFS-34 [DFS(M)-37], and
DFS-39 are AWFCO alarms that are activated by a switch set at the AWFCO
setpoint.

(B)	DFS-19, DFS-20, DFS-21, DFS-22, and DFS-40 are AWFCO alarms
associated with ACAMS, which were not activated during the DFS GB TSCA
ATB.

Footnote:

(1)	Shell RTD does not register below 800(F.

Abbreviations:

%	percent	oF	degrees Fahrenheit

---	not applicable	ACAMS	Automatic Continuous Air Monitoring System

AIT	analyzer indicating transmitter	ATB	agent trial burn

AWFCO	automatic waste feed cut off	BRA	Brine Reduction Area

CEMS	Continuous Emissions Monitoring System	CO	carbon monoxide

DFS	Deactivation Furnace System	DIT	density indicating transmitter

FIT	flow indicating transmitter	gpm	gallons per minute

HDC	Heated Discharge Conveyor	HEPA	high efficiency particulate

12HRA	12-hour rolling average	I	instantaneous

inwc	inches of water column	lbs/hr	pounds per hour

LIT	level indicating transmitter	2MRA	2-minute rolling average

30MRA	30-minute rolling average	MACT	Maximum Achievable Control
Technologies

MIT	moisture indicating transmitter	O2	oxygen

PAS	Pollution Abatement System	PDAR	process data acquisition and
recording

PDIT	pressure differential indicating transmitter	PFS	PAS Filtration
System

PIT	pressure indicating transmitter	ppmv	parts per million by volume

psig	pounds per square inch gauge	RCRA	Resource Conservation and
Recovery Act

rckts/hr	rockets per hour	ROHA	rolling hourly average

rpm	revolutions per minute	scfm	standard cubic feet per minute

sgu	specific gravity unit	ZS	position switch

std.dev.	standard deviation	TIC	temperature indicating controller

TIT	temperature indicating transmitter	TSCA	Toxic Substances Control Act

Table 5:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 4

Parameter	AWFCO Number	Instrument	AWFCO	Run 4

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Feed Rate











GB Agent	DFS-17	DFS(M)-24	PDAR	20.6	ROHA	lbs/hr	9.7	13	10.8	0.62

Rockets	DFS-17	DFS(M)-24	PDAR	38.5	ROHA	rckts/hr	36.0	37.3	36.8	0.3

Rockets	---	---	PDAR	---	I	rckts/hr	---	---	37.0	---

Rotary Retort











Temperature	DFS-01/12	DFS(M)-1/13	16-TIC-182	1,000 – 1,615	I	oF
1,089.0	1,157.3	1,125.8	10.46

Temperature	DFS-42	DFS(M)-14/45	16-TIC-182A	1,012 – 1548	ROHA	oF
1,120.5	1,130.0	1,125.0	2.84

Temperature	DFS-02/03	DFS(M)-2/3	16-TIC-08	949 – 1,539	I	oF	1,087.3
1,140.5	1,114.2	9.44

Temperature	---	---	16-TIT-20	---	I	oF	1,069.3	1,207.3	1,117.2	26.32

Pressure	---	---	16-PIT-18	---	I	inwc	-1.39	-0.82	-1.10	0.105

Fuel Gas Flow Rate	---	---	16-FIT-243	---	I	scfm	47.5	102.3	56.9	11.2

Combustion Air Flow Rate	---	---	16-FIT-21	---	I	scfm	509.5	831.3	545.1
61.41

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51A	1,600	I	oF	800.0(1)
800.0(1)	800.0(1)	0.00

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51B	1,600	I	oF	867.8	947.8
908.8	19.07

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51C	1,600	I	oF	1,056.3	1,107.5
1,086.4	13.06

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51D	1,600	I	oF	1,118.8	1,185.8
1,152.3	13.87

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51E	1,600	I	oF	972.8	1,086.8
1,034.9	21.95

Rotational Speed	DFS-28	DFS(M)-34	16-ZS-602	2.06	I	rpm	1.850	1.860	1.856
0.0026

O2 Concentration	---	---	16-AIT-09	---	I	%	10.34	15.22	12.62	0.696

Afterburner











Flow Rate	DFS-11	DFS(M)-11	16-PDIT-813	1.02	I	inwc	0.543	0.645	0.589
0.0166

Flow Rate	---	DFS(M)-12	16-PDIT-813A	1.02	ROHA	inwc	0.580	0.600	0.590
0.0069

Temperature	DFS-13/14	DFS(M)-16/18	16-TIC-92	2,000 – 2,200	I	oF
2,096.5	2,104.0	2,100.3	1.45

Pressure	DFS-31	DFS(M)-36	16-PIT-65	-0.1	I	inwc	-5.16	-4.22	-4.67	0.167

Table 5:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 4
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 4

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Afterburner (Continued)











Fuel Gas Flow Rate	---	---	16-FIT-66	---	I	scfm	213.3	220.5	216.8	1.24

Fuel Gas Flow Rate	---	---	16-FIT-191	---	I	scfm	212.5	222.0	216.6	1.60

Combustion Air Flow Rate	---	---	16-FIT-78	---	I	scfm	1,474.3	1572..8
1,516.5	17.59

Combustion Air Flow Rate	---	---	16-FIT-79	---	I	scfm	1,894.5	2,007.0
1,951.8	20.54

HDC











Temperature	DFS-08	DFS(M)-8	16-TIT-42	1,012	I	oF	1,091.3	1,109.3	1,099.7
3.51

Temperature	---	---	16-TIT-184	---	I	oF	1,091.0	1,109.3	1,100.1	3.72

Quench Tower











pH 	---	DFS(M)-19	24-AIT-7A/B	7.5	ROHA	pH unit	8.90	8.90	8.90	0.000

Brine Density 	DFS-27	DFS(M)-32	24-DIT-33	1.16	I	sgu	1.010	1.010	1.010
0.0000

Brine Density	---	DFS(M)-33	24-DIT-33A	1.16	12HRA	sgu	1.010	1.010	1.010
0.0000

Level	---	---	24-LIT-09	---	I	inches	3	3.5	3.3	0.10

Venturi Scrubber











Pressure Differential	DFS-15	DFS(M)-20	24-PDIT-08	15	I	inwc	24.4	25.9
25.0	0.26

Brine Flow Rate	DFS-26	DFS(M)-30	24-FIT-06	238	I	gpm	284.0	286.3	285.0
0.37

Scrubber Tower











Clean Liquor Flow Rate	DFS-18	DFS(M)-25	24-FIT-30	1,475	I	gpm	1,593.8
1,604.3	1,599.9	1.78

Packed Bed Pressure Drop	---	DFS(M)-15	24-PDIT-25A	0.3	ROHA	inwc	0.67
0.70	0.69	0.008

pH	DFS-23	DFS(M)-27	24-AIT-34	7.1	I	pH unit	7.80	7.90	7.89	0.024

Clean Liquor Pressure	DFS-24	DFS(M)-29	114-PIT-344	25	I	psig	84.0	84.8
84.1	0.17

Clean Liquor Density	---	DFS(M)-23	24-DIT-35A	1.08	12HRA	sgu	1.000	1.000
1.000	0.0000

Clean Liquor Return	---	---	24-TIT-274	---	I	oF	116.0	121.0	118.3	1.20

Table 5:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 4
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 4

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Mist Eliminator











Differential Pressure	DFS-41	DFS(M)-44	24-PDIT-53	20	I	inwc	2.8	2.9	2.8
0.04

Water pH	---	---	24-AIT-273	---	I	pH unit	6.80	8.00	6.92	0.203

Brine Surge Tank Level











Level (BRA-TANK-101)	---	---	23-LIT-03	---	I	inches	177.75	190.50	183.11
2.431

Level (BRA-TANK-102)	---	---	23-LIT-07	---	I	inches	86.50	107.50	98.40
4.874

Level (BRA-TANK-201)	---	---	23-LIT-703	---	I	inches	200.75	203.75
202.22	0.504

Level (BRA-TANK-202)	---	---	23-LIT-707	---	I	inches	0.00	0.00	0.00
0.000

PFS Carbon Filter











Prefilter Differential Pressure	DFS-35	DFS(M)-38	114-PDIT-440A	1.5	I
inwc	0.87	0.94	0.89	0.011

Prefilter Differential Pressure	---	DFS(M)-42	114-PDIT-440A	0.2	2MRA
inwc	0.86	0.92	0.89	0.010

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-440B	3.0	I	inwc
0.64	0.7	0.67	0.012

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-440H	3.0	I	inwc
0.58	0.62	0.6	0.010

Relative Humidity	DFS-43	---	114-MIT-111	55	30MRA	%	44.1	46.9	45.9	0.557

Prefilter Differential Pressure	DFS-35	DFS(M)-38	114-PDIT-442A	1.5	I
inwc	0.73	0.79	0.76	0.011

Prefilter Differential Pressure	---	DFS(M)-42	114-PDIT-442A	0.2	2MRA
inwc	0.73	0.78	0.76	0.010

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-442B	3.0	I	inwc
0.81	0.86	0.83	0.010

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-442H	3.0	I	inwc
0.54	0.58	0.56	0.008

Relative Humidity	DFS-43	---	114-MIT-112	55	30MRA	%	49.1	53.0	51.4	0.87

Temperature	DFS-37	DFS(M)-40	114-TIT-417R	180	ROHA	oF	165.0	165.0	165.0
0.00

Relative Humidity	DFS-38	DFS(M)-41	114-MIT-431A/B	55	ROHA	%	29.00	31.00
30.28	0.804

Table 5:	Summary of Operating Parameters for the DFS GB TSCA ATB Run 4
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Run 4

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

PAS Exhaust Duct CEMS











CO Concentration	DFS-16	DFS(M)-22	24-AIT-207C	100	ROHA	ppmv	0.0	2.0	0.5
0.71

O2 Level	DFS-29	---	24-AIT-206C	14	I	%	8.49	10.00	9.32	0.237

O2 Level	DFS-30	DFS(M)-35	24-AIT-206CM2	7.7	2MRA	%	7.71	10.24	9.32	0.362



NOTES:	

(A)	DFS-04 [DFS(M)-4], DFS-05 [DFS(M)-5], DFS-07 [DFS(M)-7], DFS-09
[DFS(M)-9], DFS-10 [DFS(M)-10], DFS-32, DFS-33, DFS-34 [DFS(M)-37], and
DFS-39 are AWFCO alarms that are activated by a switch set at the AWFCO
setpoint.

(B)	DFS-19, DFS-20, DFS-21, DFS-22, and DFS-40 are AWFCO alarms
associated with ACAMS, which were not activated during the DFS GB TSCA
ATB.

Footnote:

(1)	Shell RTD does not register below 800(F.

Abbreviations:

%	percent	oF	degrees Fahrenheit

---	not applicable	ACAMS	Automatic Continuous Air Monitoring System

AIT	analyzer indicating transmitter	ATB	agent trial burn

AWFCO	automatic waste feed cut off	BRA	Brine Reduction Area

CEMS	Continuous Emissions Monitoring System	CO	carbon monoxide

DFS	Deactivation Furnace System	DIT	density indicating transmitter

FIT	flow indicating transmitter	gpm	gallons per minute

HDC	Heated Discharge Conveyor	HEPA	high efficiency particulate

12HRA	12-hour rolling average	I	instantaneous

inwc	inches of water column	lbs/hr	pounds per hour

LIT	level indicating transmitter	2MRA	2-minute rolling average

30MRA	30-minute rolling average	MACT	Maximum Achievable Control
Technologies

MIT	moisture indicating transmitter	O2	oxygen

PAS	Pollution Abatement System	PDAR	process data acquisition and
recording

PDIT	pressure differential indicating transmitter	PFS	PAS Filtration
System

PIT	pressure indicating transmitter	ppmv	parts per million by volume

psig	pounds per square inch gauge	RCRA	Resource Conservation and
Recovery Act

rckts/hr	rockets per hour	ROHA	rolling hourly average

rpm	revolutions per minute	scfm	standard cubic feet per minute

sgu	specific gravity unit	ZS	position switch

std.dev.	standard deviation	TIC	temperature indicating controller

TIT	temperature indicating transmitter	TSCA	Toxic Substances Control Act

Table 6:	Summary of Operating Parameters for the DFS GB TSCA ATB

Parameter	AWFCO Number	Instrument	AWFCO	Average of Average(1)

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Feed Rate











GB Agent	DFS-17	DFS(M)-24	PDAR	20.6	ROHA	lbs/hr	10.9	15.2	13.1	0.94

Rockets	DFS-17	DFS(M)-24	PDAR	38.5	ROHA	rckts/hr	32.2	37.3	35.7	1.42

Rockets	---	---	PDAR	---	I	rckts/hr	---	---	36.1	---

Rotary Retort











Temperature	DFS-01/12	DFS(M)-1/13	16-TIC-182	1,000 – 1,615	I	oF
1,091.4	1,161.5	1,129.4	11.09

Temperature	DFS-42	DFS(M)-14/45	16-TIC-182A	1,012 – 1548	ROHA	oF
1,122.5	1,134.7	1,128.2	3.13

Temperature	DFS-02/03	DFS(M)-2/3	16-TIC-08	949 – 1,539	I	oF	1,081.7
1,130.8	1,109.2	9.09

Temperature	---	---	16-TIT-20	---	I	oF	1,068.7	1,284.4	1,115.3	38.13

Pressure	---	---	16-PIT-18	---	I	inwc	-1.45	-0.77	-1.10	0.112

Fuel Gas Flow Rate	---	---	16-FIT-243	---	I	scfm	47.8	112.1	56.2	11.95

Combustion Air Flow Rate	---	---	16-FIT-21	---	I	scfm	508.3	928.2	543.9
72.10

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51A	1,600	I	oF	800.0(2)	862.3
803.7	11.28

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51B	1,600	I	oF	869.0	969.4
909.8	24.22

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51C	1,600	I	oF	1,042.9	1,086.6
1,067.8	10.94

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51D	1,600	I	oF	1,082.4	1,173.2
1,132.9	18.38

Shell Temperature	DFS-06	DFS(M)-6	16-TIT-51E	1,600	I	oF	893.9	1078.4
995.9	33.55

Rotational Speed	DFS-28	DFS(M)-34	16-ZS-602	2.06	I	rpm	1.852	1.863	1.858
0.0020

O2 Concentration	---	---	16-AIT-09	---	I	%	10.53	15.09	12.72	0.626

Afterburner











Flow Rate	DFS-11	DFS(M)-11	16-PDIT-813	1.02	I	inwc	0.538	0.674	0.593
0.0197

Flow Rate	---	DFS(M)-12	16-PDIT-813A	1.02	ROHA	inwc	0.583	0.603	0.592
0.0055

Temperature	DFS-13/14	DFS(M)-16/18	16-TIC-92	2,000 – 2,200	I	oF
2,092.7	2,104.9	2,100.2	2.03

Pressure	DFS-31	DFS(M)-36	16-PIT-65	-0.1	I	inwc	-5.26	-4.19	-4.69	0.190

Table 6:	Summary of Operating Parameters for the DFS GB TSCA ATB
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Average of Average(1)

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Afterburner (Continued)











Fuel Gas Flow Rate	---	---	16-FIT-66	---	I	scfm	212.4	220.8	216.8	1.52

Fuel Gas Flow Rate	---	---	16-FIT-191	---	I	scfm	210.9	222.8	216.8	2.12

Combustion Air Flow Rate	---	---	16-FIT-78	---	I	scfm	1,463.0	1,582.1
1,517.4	20.38

Combustion Air Flow Rate	---	---	16-FIT-79	---	I	scfm	1,889.2	2,014.4
1,951.1	22.09

HDC











Temperature	DFS-08	DFS(M)-8	16-TIT-42	1,012	I	oF	1,089.8	1,111.9	1,099.9
4.43

Temperature	---	---	16-TIT-184	---	I	oF	1,090.7	1,109.3	1,099.5	3.88

Quench Tower











pH 	---	DFS(M)-19	24-AIT-7A/B	7.5	ROHA	pH unit	8.90	8.90	8.90	0.000

Brine Density 	DFS-27	DFS(M)-32	24-DIT-33	1.16	I	sgu	1.007	1.007	1.007
0.0000

Brine Density	---	DFS(M)-33	24-DIT-33A	1.16	12HRA	sgu	1.010	1.010	1.010
0.0000

Level	---	---	24-LIT-09	---	I	inches	3.0	3.6	3.3	0.14

Venturi Scrubber











Pressure Differential	DFS-15	DFS(M)-20	24-PDIT-08	15	I	inwc	24.4	25.8
25.0	0.24

Brine Flow Rate	DFS-26	DFS(M)-30	24-FIT-06	238	I	gpm	283.9	286.2	285.0
0.40

Scrubber Tower











Clean Liquor Flow Rate	DFS-18	DFS(M)-25	24-FIT-30	1,475	I	gpm	1,594.1
1,603.6	1,599.9	1.70

Packed Bed Pressure Drop	---	DFS(M)-15	24-PDIT-25A	0.3	ROHA	inwc	0.68
0.70	0.69	0.005

pH	DFS-23	DFS(M)-27	24-AIT-34	7.1	I	pH unit	7.78	7.93	7.89	0.035

Clean Liquor Pressure	DFS-24	DFS(M)-29	114-PIT-344	25	I	psig	84.00	84.93
84.27	0.267

Clean Liquor Density	---	DFS(M)-23	24-DIT-35A	1.08	12HRA	sgu	1.000	1.000
1.000	0.0000

Clean Liquor Return	---	---	24-TIT-274	---	I	oF	117.0	120.9	118.9	0.75

Table 6:	Summary of Operating Parameters for the DFS GB TSCA ATB
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Average of Average(1)

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

Mist Eliminator











Differential Pressure	DFS-41	DFS(M)-44	24-PDIT-53	20	I	inwc	2.7	2.9	2.8
0.04

Water pH	---	---	24-AIT-273	---	I	pH unit	6.93	8.43	7.50	0.460

Brine Surge Tank Level











Level (BRA-TANK-101)	---	---	23-LIT-03	---	I	inches	190.92	198.92	195.23
1.505

Level (BRA-TANK-102)	---	---	23-LIT-07	---	I	inches	97.17	121.33	108.72
6.971

Level (BRA-TANK-201)	---	---	23-LIT-703	---	I	inches	159.83	178.67
171.34	5.688

Level (BRA-TANK-202)	---	---	23-LIT-707	---	I	inches	0.00	0.00	0.00
0.000

PFS Carbon Filter











Prefilter Differential Pressure	DFS-35	DFS(M)-38	114-PDIT-440A	1.5	I
inwc	0.80	0.95	0.87	0.036

Prefilter Differential Pressure	---	DFS(M)-42	114-PDIT-440A	0.2	2MRA
inwc	0.80	0.94	0.87	0.035

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-440B	3.0	I	inwc
0.69	0.77	0.72	0.013

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-440H	3.0	I	inwc
0.56	0.63	0.59	0.014

Relative Humidity	DFS-43	---	114-MIT-111	55	30MRA	%	45.87	47.87	46.93
0.483

Prefilter Differential Pressure	DFS-35	DFS(M)-38	114-PDIT-442A	1.5	I
inwc	0.67	0.83	0.74	0.032

Prefilter Differential Pressure	---	DFS(M)-42	114-PDIT-442A	0.2	2MRA
inwc	0.67	0.83	0.74	0.026

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-442B	3.0	I	inwc
0.76	0.88	0.79	0.027

HEPA Differential Pressure	DFS-36	DFS(M)-39	114-PDIT-442H	3.0	I	inwc
0.55	0.61	0.58	0.013

Relative Humidity	DFS-43	---	114-MIT-112	55	30MRA	%	48.3	52.0	49.8	0.86

Temperature	DFS-37	DFS(M)-40	114-TIT-417R	180	ROHA	oF	165.0	165.0	165.0
0.00

Relative Humidity	DFS-38	DFS(M)-41	114-MIT-431A/B	55	ROHA	%	30.33	31.33
30.79	0.366

Table 6:	Summary of Operating Parameters for the DFS GB TSCA ATB
(Continued)

Parameter	AWFCO Number	Instrument	AWFCO	Average of Average(1)

	RCRA	MACT

Setpoint	Type	Units	Minimum	Maximum	Average	Std. Dev.

PAS Exhaust Duct CEMS











CO Concentration	DFS-16	DFS(M)-22	24-AIT-207C	100	ROHA	ppmv	0.0	1.0	0.2
0.37

O2 Level	DFS-29	---	24-AIT-206C	14	I	%	8.22	10.20	9.35	0.288

O2 Level	DFS-30	DFS(M)-35	24-AIT-206CM2	7.7	2MRA	%	8.21	10.13	9.36	0.276



NOTES:	

(A)	DFS-04 [DFS(M)-4], DFS-05 [DFS(M)-5], DFS-07 [DFS(M)-7], DFS-09
[DFS(M)-9], DFS-10 [DFS(M)-10], DFS-32, DFS-33, DFS-34 [DFS(M)-37], and
DFS-39 are AWFCO alarms that are activated by a switch set at the AWFCO
setpoint.

(B)	DFS-19, DFS-20, DFS-21, DFS-22, and DFS-40 are AWFCO alarms
associated with ACAMS, which were not activated during the DFS GB TSCA
ATB.

Footnote:

(1)	Runs 2, 3, and 4 were used to calculate the average of the average.

(2)	Shell RTD does not register below 800(F.

Abbreviations:

%	percent	oF	degrees Fahrenheit

---	not applicable	ACAMS	Automatic Continuous Air Monitoring System

AIT	analyzer indicating transmitter	ATB	agent trial burn

AWFCO	automatic waste feed cut off	BRA	Brine Reduction Area

CEMS	Continuous Emissions Monitoring System	CO	carbon monoxide

DFS	Deactivation Furnace System	DIT	density indicating transmitter

FIT	flow indicating transmitter	gpm	gallons per minute

HDC	Heated Discharge Conveyor	HEPA	high efficiency particulate

12HRA	12-hour rolling average	I	instantaneous

inwc	inches of water column	lbs/hr	pounds per hour

LIT	level indicating transmitter	2MRA	2-minute rolling average

30MRA	30-minute rolling average	MACT	Maximum Achievable Control
Technologies

MIT	moisture indicating transmitter	O2	oxygen

PAS	Pollution Abatement System	PDAR	process data acquisition and
recording

PDIT	pressure differential indicating transmitter	PFS	PAS Filtration
System

PIT	pressure indicating transmitter	ppmv	parts per million by volume

psig	pounds per square inch gauge	RCRA	Resource Conservation and
Recovery Act

rckts/hr	rockets per hour	ROHA	rolling hourly average

rpm	revolutions per minute	scfm	standard cubic feet per minute

sgu	specific gravity unit	ZS	position switch

std.dev.	standard deviation	TIC	temperature indicating controller

TIT	temperature indicating transmitter	TSCA	Toxic Substances Control Act

Table 7:	Select Criteria Pollutant Emission Results

Parameter	Units	Run 2	Run 3	Run 4	Average	RCRA Permit Limit/MACT
Standard

Carbon Monoxide(1)	ppmv	0.2	0.0	0.5	0.2	100 ROHA

Oxygen(1)	%	9.37	9.37	9.32	9.35	7.7 (2MRA) to 14

Oxygen(2)	%	9.65	9.40	9.80	9.62	---

Total Hydrocarbons(3)	ppmv	0.0	0.0	0.0	0.0	10 ROHA



Footnotes:

(1)	PDAR System data IAW US EPA Performance Specification 4A (Monitors
of Record (24-AIT-207C [CO] and 24-AIT-206C [O2])).

(2)	US EPA Method 3B (Orsat).

(3)	THC data reported on a dry basis, corrected to 7% O2 and uncorrected
for drift in accordance with US EPA Performance Specification 8A.  The
data reported is the average of the TCEMS results for two monitoring
periods per run (during each of two test ports).  THC reported as
propane.

Abbreviations:

%	percent	---	not applicable

CEMS	Continuous Emissions Monitor System	EPA	Environmental Protection
Agency

lbs/hr	pounds per hour	2MRA	2-minute rolling average

MACT	Maximum Achievable Control Technologies	O2	oxygen

PDAR	process data acquisition and recording	ppmv	parts per million by
volume

RCRA	Resource Conservation and Recovery Act	ROHA	rolling hourly average

THC	total hydrocarbons	TCEMS	temporary reference CEMS

US	United States

Table 8:	Summary of DRE Results for PCBs

Parameter	Units	Run 2	Run 3	Run 4	Average	TSCA Permit Limit

PCB Concentration	ppm	2,006	2,006	2,006	2,006	---

Tube Feed Rate	tubes/hr	35.3	36.0	37.0	36.08	---

Tube Weight	lbs/tube	13.73	13.73	13.73	13.73	---

PCB Feed Rate	lbs/hr	0.97	0.99	1.02	0.99	---

Emission Rates	g/s	< 2.17E-08	< 1.94E-08	< 1.94E-08	< 2.01E-08	---

Emission Rates	lbs/hr	< 1.72E-07	< 1.54E-07	< 1.54E-07	< 1.60E-07	---

DRE	%	> 99.99998	> 99.99998	> 99.99998	> 99.99998	99.9999



Abbreviations:

%	percent	---	not applicable

<	less than	>	greater than

DRE	destruction and removal efficiency	g/s	grams per second

lbs/hr	pounds per hour	lbs/tube	pounds per tube

PCB	polychlorinated biphenyls	ppm	parts per million

tubes/hr	tubes per hour	TSCA	Toxic Substances Control ActTable 9:
Summary of DRE Results for GB Agent

Parameter	Units	Run 2	Run 3	Run 4	Average	RCRA Permit Limit/MACT
Standard

DAAMS Tube	---	CK980	CL160	CK924	---	---

Sample Collection Time	minutes	240	240	240	240	---

DAAMS Flow Rate(1)	sLpm	1.01	1.00	1.00	1.00	---

Total Gas Sample Volume(2)	scm	2.42E-01	2.40E-01	2.40E-01	2.41E-01	---

Dilution Air	%	92.7	89.6	89.6	90.63	---

Percent Exhaust Gas Sampled	%	7.3	10.4	10.4	9.37	---

Total Exhaust Gas Sample Volume	scm	1.77E-02	2.50E-02	2.50E-02	2.25E-02
---

Sample Analysis Result	ng	< 2.30E-02	< 2.30E-02	< 2.30E-02	< 2.30E-02
---

Exhaust Gas Flow Rate(3)	scm/hr	20,079.60	19,677.86	19,817.04	19,858.17
---

Agent Concentration	mg/scm	< 1.30E-06	< 9.21E-07	< 9.21E-07	< 1.05E-06
---

Emission Rate (Wout)	lbs/hr	< 5.75E-08	< 4.00E-08	< 4.03E-08	< 4.59E-08
---

Average Agent Feed Rate(4)	lbs/hr	13.7	14.9	10.8	13.13	---

Agent Purity(5)	%	89.5	89.5	89.5	89.50	---

Purity Corrected Agent Feed Rate (Win)	lbs/hr	12.3	13.3	9.7	11.75	---

DRE [((Win-Wout)/Win)*100]	%	> 99.9999995	> 99.9999996	> 99.9999995	>
99.9999995	99.99



Footnotes:

(1)	Flow rate is set prior to collection of the 4-hour tubes and
verified after each tube has been collected.  If the ending flow rate is
less than the starting flow rate, the ending (i.e., lower) flow rate is
used to calculate total flow.

(2)	Total sample volume represents the exhaust gas sample and diluent
volume.

(3)	Calculated using the average flow rate of all isokinetic trains for
the run.

(4)	Average agent feed rate as determined by the PDAR System
(DFS_AGENT).

(5)	Agent purity represents the average purity determined from samples
collected during the DFS GB ATB.  One sample was taken for Runs 1 and 2
and one sample for Runs 3 and 4.  The GB agent purity was 89 and 90%,
respectively, resulting in an overall average of 89.5%.

Table 9:	Summary of DRE Results for GB Agent (Continued)

Abbreviations:

%	percent	<	less than

>	greater than	ATB	agent trial burn

ATBP	agent trial burn plan	DAAMS	Depot Area Air Monitoring System

DFS	Deactivation Furnace System	DRE	destruction and removal efficiency

lbs/hr	pounds per hour	MACT	Maximum Achievable Control Technologies

mg/scm	milligrams per standard cubic meter	ND	not detected

ng	nanograms	PDAR	process data acquisition and recording

RCRA	Resource Conservation and Recovery Act	scm	standard cubic meter

scm/hr	standard cubic meter per hour	sLpm	standard liters per minute

UMCDF	Umatilla Chemical Agent Disposal Facility

Table 10:	PCB Emission Results

Parameter	Units	Run 2	Run 3	RCRA Permit Limit/MACT Standard

Sampling Location	---	PAS Exhaust Duct	PAS Exhaust Duct	---

Date	---	10/29/05	10/30/05	---

Start Time	---	0802	0948	---

Stop Time	---	1612	1420	---

Net Sampling Time	minutes	240	240	---

Sample Volume	dscf	160.831	178.930	---

Exhaust Gas Flow Rate	dscfm	10,343.5	10,408.8	---

O2 Concentration (PS4A)	%	9.37	9.37	---

Congeners	TEF(1)	Quantity Detected	Weighted TEQ	Quantity Detected
Weighted TEQ	---

Total MonoCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Total DiCB	0.0	<	2,100

<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Total TriCB	0.0	<	4,400

<	0.0	ND	<	2,000	ND	<	0.0	ND	---

3,3',4,4'-TetraCB (77)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<	0.0200	ND
---

3,4,4',5-TetraCB (81)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<	0.0200	ND
---

Total TetraCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

2,3,3',4,4'-PentaCB (105)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<	0.0200
ND	---

2,3,4,4',5-PentaCB (114)	0.0005	<	200	ND	<	0.1000	ND	<	200	ND	<	0.1000
ND	---

2,3',4,4',5-PentaCB (118)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<	0.0200
ND	---

2',3,4,4',5-PentaCB (123)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<	0.0200
ND	---

3,3',4,4',5-PentaCB (126)	0.1	<	200	ND	<	20.0	ND	<	200	ND	<	20.0	ND	---

Total PentaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

2,3,3',4,4',5-HexaCB (156)	0.0005	<	200	ND	<	0.1000	ND	<	200	ND	<	0.1000
ND	---

2,3,3',4,4',5'-HexaCB (157)	0.0005	<	200	ND	<	0.1000	ND	<	200	ND	<
0.1000	ND	---

2,3',4,4',5,5'-HexaCB (167)	0.00001	<	200	ND	<	0.00200	ND	<	200	ND	<
0.00200	ND	---

3,3',4,4',5,5'-HexaCB (169)	0.01	<	200	ND	<	2.00	ND	<	200	ND	<	2.00	ND
---

Total HexaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

2,2',3,3',4,4',5-HeptaCB (170)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<
0.0200	ND	---

2,2',3,4,4',5,5'-HeptaCB (180)	0.00001	<	200	ND	<	0.00200	ND	<	200	ND	<
0.00200	ND	---

2,3,3',4,4',5,5'-HeptaCB (189)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<
0.0200	ND	---

Total HeptaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Total OctaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Total NonaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Total DecaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Sum	pg	<	22,500

<	22.4440	ND	<	20,000	ND	<	22.4440	ND	---

Concentration	ng/dscm @ 7% O2	<	5.33

<	0.0053	ND	<	4.76	ND	<	0.0053	ND	0.2

Emission Rate	g/s	<	2.17E-08

<	2.16E-11	ND	<	1.94E-08	ND	<	2.18E-11	ND	6.25E-07

Table 10:	PCB Emission Results (Continued)

Parameter	Units	Run 4	Average	RCRA Permit Limit/TSCA Standard

Sampling Location	---	PAS Exhaust Duct	---	---

Date	---	10/30/05	---	---

Start Time	---	1518	---	---

Stop Time	---	1934	---	---

Net Sampling Time	minutes	240	240	---

Sample Volume	dscf	180.290	179.66	---

Exhaust Gas Flow Rate	dscfm	10,490.9	10,427.36	---

O2 Concentration	%	9.32	9.35	---

Congeners	TEF(1)	Quantity Detected	Weighted TEQ	Quantity Detected
Weighted TEQ	---

Total MonoCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Total DiCB	0.0	<	2,000	ND	<	0.0	ND	<	2,033

<	0.0

---

Total TriCB	0.0	<	2,000	ND	<	0.0	ND	<	2,800

<	0.0

---

3,3',4,4'-TetraCB (77)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<	0.0200	ND
---

3,4,4',5-TetraCB (81)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<	0.0200	ND
---

Total TetraCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

2,3,3',4,4'-PentaCB (105)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<	0.0200
ND	---

2,3,4,4',5-PentaCB (114)	0.0005	<	200	ND	<	0.1000	ND	<	200	ND	<	0.1000
ND	---

2,3',4,4',5-PentaCB (118)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<	0.0200
ND	---

2',3,4,4',5-PentaCB (123)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<	0.0200
ND	---

3,3',4,4',5-PentaCB (126)	0.1	<	200	ND	<	20.0	ND	<	200	ND	<	20.0	ND	---

Total PentaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

2,3,3',4,4',5-HexaCB (156)	0.0005	<	200	ND	<	0.1000	ND	<	200	ND	<	0.1000
ND	---

2,3,3',4,4',5'-HexaCB (157)	0.0005	<	200	ND	<	0.1000	ND	<	200	ND	<
0.1000	ND	---

2,3',4,4',5,5'-HexaCB (167)	0.00001	<	200	ND	<	0.00200	ND	<	200	ND	<
0.00200	ND	---

3,3',4,4',5,5'-HexaCB (169)	0.01	<	200	ND	<	2.00	ND	<	200	ND	<	2.00	ND
---

Total HexaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

2,2',3,3',4,4',5-HeptaCB (170)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<
0.0200	ND	---

2,2',3,4,4',5,5'-HeptaCB (180)	0.00001	<	200	ND	<	0.00200	ND	<	200	ND	<
0.00200	ND	---

2,3,3',4,4',5,5'-HeptaCB (189)	0.0001	<	200	ND	<	0.0200	ND	<	200	ND	<
0.0200	ND	---

Total HeptaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Total OctaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Total NonaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Total DecaCB	0.0	<	2,000	ND	<	0.0	ND	<	2,000	ND	<	0.0	ND	---

Sum	pg	<	20,000	ND	<	22.4440	ND	<	20,833

<	22.4440

---

Concentration	ng/dscm @ 7% O2	<	4.70	ND	<	0.0053	ND	<	4.93

<	0.0053

0.2

Emission Rate	g/s	<	1.94E-08	ND	<	2.18E-11	ND	<	2.02E-08

<	2.17E-11

6.25E-07

Table 10:	PCB Emission Results (Continued)

Note:

(A)	Unless noted otherwise, all reported values are in pg. 
“Non-detects” are included at the applicable detection limit, summed
for the two train components.  The detection limits per train component
are listed in the analytical data sheets per congener/isomer.

Footnote:

(1)	WHO, 1997.

Abbreviations:

---	not applicable	%	percent

<	less than	CB	chlorinated biphenyl

dscf	dry standard cubic feet	dscfm	dry standard cubic feet per minute

g/s	gram per second	ND	indicates non-detect in both train components

ng/dscm	nanograms per dry standard cubic meter	O2	oxygen

PAS	Pollution Abatement System	PCB	polychlorinated biphenyl

pg	picogram	PS4B	US EPA Performance Specification 4B

RCRA	Resource Conservation and Recovery Act	TEF	toxicity equivalence
factor

TEQ	toxicity equivalence quotient	TSCA	Toxic Substance Control Act

Table 11:	PCDD/PCDF Emission Results

Parameter	Units	Run 2	Run 3	RCRA Permit Limit/MACT Standard

Sampling Location	---	PAS Exhaust Duct	PAS Exhaust Duct	---

Date	---	10/29/05	10/30/29	---

Start Time	---	0802	0948	---

Stop Time	---	1612	1420	---

Net Sampling Time	minutes	240	240	---

Sample Volume	dscf	160.831	157.696	---

Exhaust Gas Flow Rate	dscfm	10,343.5	10,143.5	---

O2 Concentration (PS4B)	%	9.37	9.37	---

Congeners	TEF(1)	Quantity Detected	Weighted TEQ	Quantity Detected
Weighted TEQ	---

2,3,7,8 TetraCDD	1	<	10.2	ND	<	10.2	ND	<	9.9	ND	<	9.9	ND	---

Total TetraCDD	0	<	10.2	ND	<	0.0	ND	<	9.9	ND	<	0.0	ND	---

1,2,3,7,8 PentaCDD	1	<	19.9	ND	<	19.9	ND	<	19.8	ND	<	19.8	ND	---

Total PentaCDD	0	<	19.9	ND	<	0.0	ND	<	19.8	ND	<	0.0	ND	---

1,2,3,4,7,8 HexaCDD	0.1	<	24	ND	<	2.4	ND	<	23	ND	<	2.3	ND	---

1,2,3,6,7,8 HexaCDD	0.1	<	20	ND	<	2.0	ND	<	19.9	ND	<	2.0	ND	---

1,2,3,7,8,9 HexaCDD	0.1	<	22	ND	<	2.2	ND	<	22	ND	<	2.2	ND	---

Total HexaCDD	0	<	24	ND	<	0.0	ND	<	23	ND	<	0.0	ND	---

1,2,3,4,6,7,8 HeptaCDD	0.01	<	23	ND	<	0.23	ND	<	24	ND	<	0.24	ND	---

Total HeptaCDD	0	<	23	ND	<	0.0	ND	<	24	ND	<	0.0	ND	---

Total OctaCDD	0.0001	<	83	ND	<	0.0083	ND	<	118	ND	<	0.0118	ND	---

Sum	pg	<	160.1	ND	<	36.9	ND	<	194.7	ND	<	36.4	ND	---

Concentration	ng/dscm @ 7% O2	<	0.0424	ND	<	0.0098	ND	<	0.0526	ND	<
0.0098	ND	---

Emission Rate	g/s	<	1.72E-10	ND	<	3.96E-11	ND	<	2.09E-10	ND	<	3.91E-11
ND	---

2,3,7,8 TetraCDF	0.1	<	7.8	ND	<	0.8	ND	<	8.5	ND	<	0.9	ND	---

Total TCDF	0	<	7.8	ND	<	0.0	ND	<	8.5	ND	<	0.0	ND	---

1,2,3,7,8 PentaCDF 	0.05	<	12.4	ND	<	0.62	ND	<	12.6	ND	<	0.63	ND	---

2,3,4,7,8 PentaCDF 	0.5	<	12.3	ND	<	6.2	ND	<	12.4	ND	<	6.2	ND	---

Total PentaCDF	0	<	12.4	ND	<	0.0	ND	<	12.6	ND	<	0.0	ND	---

1,2,3,4,7,8 HexaCDF 	0.1	<	18.2	ND	<	1.8	ND	<	18.6	ND	<	1.9	ND	---

1,2,3,6,7,8 HexaCDF 	0.1	<	16.7	ND	<	1.7	ND	<	17.1	ND	<	1.7	ND	---

2,3,4,6,7,8 HexaCDF 	0.1	<	19.6	ND	<	2.0	ND	<	19.6	ND	<	2.0	ND	---

1,2,3,7,8,9 HexaCDF 	0.1	<	23	ND	<	2.3	ND	<	24	ND	<	2.4	ND	---

Total HexaCDF	0	<	23	ND	<	0.0	ND	<	24	ND	<	0.0	ND	---

1,2,3,4,6,7,8 HeptaCDF 	0.01	<	11.1	ND	<	0.11	ND	<	11.7	ND	<	0.12	ND	---

1,2,3,4,7,8,9 HeptaCDF 	0.01	<	13.5	ND	<	0.14	ND	<	14.1	ND	<	0.14	ND	---

Total HeptaCDF	0	<	13.5	ND	<	0.0	ND	<	14.1	ND	<	0.0	ND	---

Total OctaCDF	0.0001	<	38	ND	<	0.0038	ND	<	34	ND	<	0.0034	ND	---

Sum	pg	<	94.7	ND	<	15.5	ND	<	93.2	ND	<	15.9	ND	---

Concentration	ng/dscm @ 7% O2	<	0.0251	ND	<	0.0041	ND	<	0.0252	ND	<
0.0043	ND	---

Emission Rate	g/s	<	1.02E-10	ND	<	1.67E-11	ND	<	9.99E-11	ND	<	1.70E-11
ND	---

Total PCDD/PCDF	ng/dscm @ 7% O2	<	0.0674	ND	<	0.0139	ND	<	0.0778	ND	<
0.0141	ND	0.20

	g/s	<	2.73E-10	ND	<	5.63E-11	ND	<	3.09E-10	ND	<	5.61E-11	ND	6.69E-10

Table 11:	PCDD/PCDF Emission Results (Continued)

Parameter	Units	Run 4	Average	RCRA Permit Limit/MACT Standard

Sampling Location	---	PAS Exhaust Duct	---	---

Date	---	10/30/05	---	---

Start Time	---	1518	---	---

Stop Time	---	1934	---	---

Net Sampling Time	minutes	240	240	---

Sample Volume	dscf	160.025	159.52	---

Exhaust Gas Flow Rate	dscfm	10,254.9	10,247.29	---

O2 Concentration (PS4B)	%	9.32	9.35	---

Congeners	TEF(1)	Quantity Detected	Weighted TEQ	Quantity Detected
Weighted TEQ	---

2,3,7,8 TetraCDD	1	<	20.8	ND	<	20.8	ND	<	13.6 	ND	<	13.6	ND	---

Total TetraCDD	0	<	20.8	ND	<	0.0	ND	<	13.6 	ND	<	0.0	ND	---

1,2,3,7,8 PentaCDD	1	<	47.9	ND	<	47.9	ND	<	29.2 	ND	<	29.2	ND	---

Total PentaCDD	0	<	47.9	ND	<	0.0	ND	<	29.2 	ND	<	0.0	ND	---

1,2,3,4,7,8 HexaCDD	0.1	<	52	ND	<	5.2	ND	<	33.0 	ND	<	3.3	ND	---

1,2,3,6,7,8 HexaCDD	0.1	<	46.0	ND	<	4.6	ND	<	28.6 	ND	<	2.9	ND	---

1,2,3,7,8,9 HexaCDD	0.1	<	49.7	ND	<	5.0	ND	<	31.2 	ND	<	3.1	ND	---

Total HexaCDD	0	<	52	ND	<	0.0	ND	<	33.0 	ND	<	0.0	ND	---

1,2,3,4,6,7,8 HeptaCDD	0.01	<	51	ND	<	0.51	ND	<	32.7 	ND	<	0.33	ND	---

Total HeptaCDD	0	<	51	ND	<	0.0	ND	<	32.7 	ND	<	0.0	ND	---

Total OctaCDD	0.0001	<	92	ND	<	0.0092	ND	<	97.7 	ND	<	0.0098	ND	---

Sum	pg	<	263.7	ND	<	84.0	ND	<	206.2	ND	<	52.5	ND	---

Concentration	ng/dscm @ 7% O2	<	0.0698	ND	<	0.0222	ND	<	0.0550	ND	<
0.0140	ND	---

Emission Rate	g/s	<	2.82E-10	ND	<	8.97E-11	ND	<	2.21E-10	ND	<	5.62E-11
ND	---

2,3,7,8 TetraCDF	0.1	<	18.6	ND	<	1.9	ND	<	11.6 	ND	<	1.2	ND	---

Total TCDF	0	<	18.6	ND	<	0.0	ND	<	11.6 	ND	<	0.0	ND	---

1,2,3,7,8 PentaCDF 	0.05	<	30.1	ND	<	1.51	ND	<	18.4 	ND	<	0.92	ND	---

2,3,4,7,8 PentaCDF 	0.5	<	30.1	ND	<	15.1	ND	<	18.3 	ND	<	9.1	ND	---

Total PentaCDF	0	<	30.1	ND	<	0.0	ND	<	18.4 	ND	<	0.0	ND	---

1,2,3,4,7,8 HexaCDF 	0.1	<	38.1	ND	<	3.8	ND	<	25.0 	ND	<	2.5	ND	---

1,2,3,6,7,8 HexaCDF 	0.1	<	34.4	ND	<	3.4	ND	<	22.7 	ND	<	2.3	ND	---

2,3,4,6,7,8 HexaCDF 	0.1	<	40.5	ND	<	4.1	ND	<	26.6 	ND	<	2.7	ND	---

1,2,3,7,8,9 HexaCDF 	0.1	<	49	ND	<	4.9	ND	<	32.0 	ND	<	3.2	ND	---

Total HexaCDF	0	<	49	ND	<	0.0	ND	<	32.0 	ND	<	0.0	ND	---

1,2,3,4,6,7,8 HeptaCDF 	0.01	<	28.5	ND	<	0.29	ND	<	17.1 	ND	<	0.17	ND
---

1,2,3,4,7,8,9 HeptaCDF 	0.01	<	33.9	ND	<	0.34	ND	<	20.5 	ND	<	0.21	ND
---

Total HeptaCDF	0	<	33.9	ND	<	0.0	ND	<	20.5 	ND	<	0.0	ND	---

Total OctaCDF	0.0001	<	97	ND	<	0.0097	ND	<	56.3 	ND	<	0.0056	ND	---

Sum	pg	<	228.6	ND	<	35.2	ND	<	138.8	ND	<	22.2	ND	---

Concentration	ng/dscm @ 7% O2	<	0.0605	ND	<	0.0093	ND	<	0.0370	ND	<
0.0059	ND	---

Emission Rate	g/s	<	2.44E-10	ND	<	3.76E-11	ND	<	1.49E-10	ND	<	2.38E-11
ND	---

Total PCDD/PCDF	ng/dscm @ 7% O2	<	0.1304	ND	<	0.0316	ND	<	0.0920	ND	<
0.0199	ND	0.20

	g/s	<	5.26E-10	ND	<	1.27E-10	ND	<	3.69E-10	ND	<	8.00E-11	ND	6.69E-10

Table 11:	PCDD/PCDF Emission Results (Continued)

Note:

(A)	Unless noted otherwise, all reported values are in pg. 
“Non-detects” are included at the applicable detection limit, summed
for the two train components.  The detection limits per train component
are listed in the analytical data sheets per congener/isomer.

Footnote:

(1)	WHO, 1997.

Abbreviations:

---	not applicable	%	percent

<	less than	dscf	dry standard cubic feet

dscfm	dry standard cubic feet per minute	g/s	gram per second

CDD	chlorinated dibenzo-p-dioxin	CDF	chlorinated dibenzofuran

MACT	Maximum Achievable Control Technologies	ng/dscm	nanogram per dry
standard cubic meter

ND	not detected	O2	oxygen

PAS	Pollution Abatement System	PCDD	polychlorinated dibenzo-p-dioxin

PCDF	polychlorinated dibenzofuran	pg	picogram

PS4B	US EPA Performance Specification 4B	RCRA	Resource Conservation and
Recovery Act

TEF	toxicity equivalence factor	TEQ	toxicity equivalence quotient

Table 12:	Semivolatile Organic Emission Results

Parameter

Units

Run 2

RCRA Permit Limit

Sampling Location

---	PAS Exhaust Duct	---

Date

---

10/29/05

---

Start Time

---

0802

---

Stop Time

---

1612

---

Net Sampling Time

minutes

240

---

Sample Volume

dscf

150.221

---

Gas Flow Rate

dscfm

9,861.7

---

Gas Temperature

oF

173.6

---

Gas Moisture

%

12.48

---

O2 Concentration (PS4A)

%

9.37

---

CO2 Concentration (M3B)

%

7.7

---









Acenaphthene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Acenaphthylene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





Acetophenone	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





2-Acetylaminofluorene	Total Catch	ug	<	300	ND	---

	Concentration	ug/dscm

70.52 

---

	Emission Rate	lbs/hr

2.61E-03

---

	Emission Rate	g/s

3.28E-04

---









4-Aminobiphenyl	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









3-Amino-9-ethylcarbazole	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Aniline	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Anthracene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Aramite	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









Benzidine	Total Catch	ug	<	300	ND	---

	Concentration	ug/dscm

70.52 

---

	Emission Rate	lbs/hr

2.61E-03

---

	Emission Rate	g/s

3.28E-04

---









Benzoic acid	Total Catch	ug	<	251

---

	Concentration	ug/dscm

59.00 

---

	Emission Rate	lbs/hr

2.18E-03

---

	Emission Rate	g/s

2.75E-04

3.80E-04

Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

Benzo (a) anthracene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Benzo (b) fluoranthrene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





Benzo (j) fluoranthrene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---







---

Benzo (k) fluoranthrene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Benzo (g,h,i) perylene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





Benzo (a) pyrene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Benzo (e) pyrene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





Benzyl alcohol	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

2.06E-03









Benzaldehyde	Total Catch	ug	<	28

---

	Concentration	ug/dscm

6.58 

---

	Emission Rate	lbs/hr

2.43E-04

---

	Emission Rate	g/s

3.06E-05

---









Benzenethiol	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Biphenyl	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





bis(2-Chloroethoxy)-methane	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---







---

bis(2-Chloroethyl) ether	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

bis(2-Chloroisopropyl) ether	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





bis(2-Ethylhexyl)-phthalate	Total Catch	ug	<	27.3

---

	Concentration	ug/dscm

6.42 

---

	Emission Rate	lbs/hr

2.37E-04

---

	Emission Rate	g/s

2.99E-05

9.93E-05









4-Bromophenyl phenyl ether	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





Butyl benzyl phthalate	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





2-sec-Butyl-4,6-dinitro-phenol	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









4-Chloroaniline	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Chlorobenzilate	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





4-Chloro-3-methylphenol	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









1-Chloronaphthalene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









2-Chloronaphthalene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









2-Chlorophenol	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---



 





4-Chlorophenyl phenyl ether	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Chrysene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

4,4’-DDE	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Diallate	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









Dibenz(a,j)acridine	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









Dibenz(a,h)anthracene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Dibenzofuran	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









1,2-Dibromo-3-chloropropane	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Di-n-butyl phthalate	Total Catch	ug	<	37

---

  [Using DL]	Concentration	ug/dscm

8.70 

---

	Emission Rate	lbs/hr

3.21E-04

---

	Emission Rate	g/s

4.05E-05

1.10E-05









Di-n-butyl phthalate	Total Catch	ug	<	22.4

---

  [Using MDL]	Concentration	ug/dscm

5.28

---

	Emission Rate	lbs/hr

1.95E-04

---

	Emission Rate	g/s

2.46E-05

1.10E-05









1,2-Dichlorobenzene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









N,N’-Diisopropylcarbodiimide	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









1,3-Dichlorobenzene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









1,4-Dichlorobenzene	Total Catch	ug	<	26 

---

	Concentration	ug/dscm

6.11 

---

	Emission Rate	lbs/hr

2.26E-04

---

	Emission Rate	g/s

2.84E-05

---









3,3’-Dichlorobenzidine	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

2,4-Dichlorophenol	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









2,6-Dichlorophenol	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Diethyl phthalate	Total Catch	ug	<	24.4

---

  [Using DL]	Concentration	ug/dscm

5.74 

---

	Emission Rate	lbs/hr

2.12E-04

---

	Emission Rate	g/s

2.67E-05

9.93E-06









Diethyl phthalate	Total Catch	ug	<	19.4

---

  [Using MDL]	Concentration	ug/dscm

4.56 

---

	Emission Rate	lbs/hr

1.68E-04

---

	Emission Rate	g/s

2.12E-05

9.93E-06









Dihydrosafrole	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









p-Dimethylaminoazobenzene	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









7,12-Dimethylbenz(a)-anthracene	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









3,3’-Dimethylbenzidine	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









a,a-Dimethylphenethyl-amine	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









2,4-Dimethylphenol	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Dimethyl phthalate	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

4.23E-04









1,3-Dinitrobenzene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









4,6-Dinitro-2-methylphenol	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

2,4-Dinitrophenol	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









2,4-Dinitrotoluene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









2,6-Dinitrotoluene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Dioxathion	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Diphenylamine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









1,2-Diphenylhydrazine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Di-n-octyl phthalate	Total Catch	ug	<	30	ND	---

  [Using DL]	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

1.02E-05









Di-n-octyl phthalate	Total Catch	ug	<	12	ND	---

  [Using MDL]	Concentration	ug/dscm

2.81

---

	Emission Rate	lbs/hr

1.04E-04

---

	Emission Rate	g/s

1.31E-05

1.02E-05









Ethyl methanesulfonate	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Ethyl Parathion	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









Fluoranthene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Fluorene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Heptachlor	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

Hexachlorobenzene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Hexachlorobutadiene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Hexachlorocyclopentadiene	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









Hexachloroethane	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Hexachlorophene	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Hexachloropropene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Indeno(1,2,3-cd)pyrene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Isophorone	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Isosafrole	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









Methapyrilene	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









Methoxychlor	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Methylcyclohexane	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









3-Methylcholanthrene	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

Methyl methanesulfonate	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









2-Methylnapthalene	Total Catch	ug	<	22.2

---

	Concentration	ug/dscm

5.22 

---

	Emission Rate	lbs/hr

1.93E-04

---

	Emission Rate	g/s

2.43E-05

---









2-Methyl-5-nitroaniline	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









2-Methylphenol (o-Cresol)	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

1.21E-04









3-Methylphenol (m-Cresol)	Total Catch	ug	<	150	ND	---

  [Using DL]	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

1.02E-05









3-Methylphenol (m-Cresol)	Total Catch	ug	<	75	ND	---

  [Using MDL]	Concentration	ug/dscm

17.63 

---

	Emission Rate	lbs/hr

6.51E-04

---

	Emission Rate	g/s

8.21E-05

1.02E-05









Diisopropylmethylphosphonate	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









4-Methylphenol (p-Cresol)	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

1.02E-04









Naphthalene	Total Catch	ug	<	28.6

---

  [Using DL]	Concentration	ug/dscm

6.72

---

	Emission Rate	lbs/hr

2.48E-04

---

	Emission Rate	g/s

3.13E-05

1.30E-05









Naphthalene	Total Catch	ug	<	11.9

---

  [Using MDL]	Concentration	ug/dscm

2.80

---

	Emission Rate	lbs/hr

1.03E-04

---

	Emission Rate	g/s

1.30E-05

1.30E-05









1,4-Naphthoquinone	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









1-Napthylamine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









2-Napthylamine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

5-Nitroacenaphthalene	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









2-Nitroaniline	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









3-Nitroaniline	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









4-Nitroaniline	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









Nitrobenzene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









2-Nitrophenol	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









4-Nitrophenol	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









4-Nitroquinoline-l-oxide	Total Catch	ug	<	300	ND	---

	Concentration	ug/dscm

70.52 

---

	Emission Rate	lbs/hr

2.61E-03

---

	Emission Rate	g/s

3.28E-04

---









N-Nitroso-di-n-butylamine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









N-Nitrosodiethylamine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









N-Nitrosodimethylamine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









N-Nitrosomethylethylamine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









N-Nitrosodiphenylamine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

N-Nitroso-di-n-propylamine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









N-Nitrosomorpholine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









N-Nitrosopiperidine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









N-Nitrosopyrrolidine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Pentachlorobenzene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Pentachloroethane	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









Pentachloronitrobenzene	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









Pentachlorophenol	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









Perylene	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Phenacetin	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









Phenanthrene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Phenol	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









1,4-Phenylenediamine	Total Catch	ug	<	300	ND	---

	Concentration	ug/dscm

70.52 

---

	Emission Rate	lbs/hr

2.61E-03

---

	Emission Rate	g/s

3.28E-04

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

2-Picoline	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









Pronamide	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









Pyrene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









Pyridine	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









Quinoline	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Safrole	Total Catch	ug	<	60	ND	---

	Concentration	ug/dscm

14.10 

---

	Emission Rate	lbs/hr

5.21E-04

---

	Emission Rate	g/s

6.56E-05

---









1,2,4,5-Tetrachlorobenzene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









2,3,4,6-Tetrachlorophenol	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









o-Toluidine	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









p-Toluidine	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









1,2,4-Trichlorobenzene	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









2,4,5-Trichlorophenol	Total Catch	ug	<	30	ND	---

	Concentration	ug/dscm

7.05 

---

	Emission Rate	lbs/hr

2.61E-04

---

	Emission Rate	g/s

3.28E-05

---









2,4,6-Trichlorophenol	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

1,3,5-Trinitrobenzene	Total Catch	ug	<	150	ND	---

	Concentration	ug/dscm

35.26 

---

	Emission Rate	lbs/hr

1.30E-03

---

	Emission Rate	g/s

1.64E-04

---









Tributylamine	Total Catch	ug

NOT FOUND

---

	Concentration	ug/dscm

---

---

	Emission Rate	lbs/hr

---

---

	Emission Rate	g/s

---

---









Propanoic acid, 2-methyl-, met	Total Catch	ug

14

---

(TIC)	Concentration	ug/dscm

3.29 

---

547-63-7	Emission Rate	lbs/hr

1.22E-04

---

	Emission Rate	g/s

1.53E-05

---









Butonic acid, methyl ester	Total Catch	ug

24.7

---

(TIC)	Concentration	ug/dscm

5.81 

---

623-42-7	Emission Rate	lbs/hr

2.14E-04

---

	Emission Rate	g/s

2.70E-05

---









1,3,5-Cycloheptatriene	Total Catch	ug

129

---

(TIC)	Concentration	ug/dscm

30.32 

---

544-25-2	Emission Rate	lbs/hr

1.12E-03

---

	Emission Rate	g/s

1.41E-04

---









Butanoic acid, 2-methyl-, meth	Total Catch	ug

7.6

---

(TIC)	Concentration	ug/dscm

1.79 

---

868-57-5	Emission Rate	lbs/hr

6.60E-05

---

	Emission Rate	g/s

8.32E-06

---









Decane, 5-methyl-	Total Catch	ug

12.5

---

(TIC)	Concentration	ug/dscm

2.94 

---

13151-35-4	Emission Rate	lbs/hr

1.09E-04

---

	Emission Rate	g/s

1.37E-05

---









N-hexadecanoic acid	Total Catch	ug

23

---

(TIC)	Concentration	ug/dscm

5.41 

---

57-10-3	Emission Rate	lbs/hr

2.00E-04

---

	Emission Rate	g/s

2.52E-05	 	---









Octadecanoic acid	Total Catch	ug

12.2

---

(TIC)	Concentration	ug/dscm

2.87 

---

57-11-4	Emission Rate	lbs/hr

1.06E-04

---

	Emission Rate	g/s

1.33E-05

---









Docosane	Total Catch	ug

53

---

(TIC)	Concentration	ug/dscm

12.46 

---

629-97-0	Emission Rate	lbs/hr

4.60E-04

---

	Emission Rate	g/s

5.80E-05

---









Tetracosane	Total Catch	ug

129

---

(TIC)	Concentration	ug/dscm

30.32 

---

646-31-1	Emission Rate	lbs/hr

1.12E-03

---

	Emission Rate	g/s

1.41E-04

---









Decane	Total Catch	ug

4.7

---

(TIC)	Concentration	ug/dscm

1.10 

---

124-18-5	Emission Rate	lbs/hr

4.08E-05

---

	Emission Rate	g/s

5.14E-06

---









Phenol, 2,2’-methylenebis[6-(1-	Total Catch	ug

48

---

(TIC)	Concentration	ug/dscm

11.28 

---

119-47-1	Emission Rate	lbs/hr

4.17E-04

---

	Emission Rate	g/s

5.25E-05

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

Tridecane, 7-hexyl-	Total Catch	ug

52

---

(TIC)	Concentration	ug/dscm

12.22 

---

7225-66-3	Emission Rate	lbs/hr

4.52E-04

---

	Emission Rate	g/s

5.69E-05

---









Octacosane	Total Catch	ug

27

---

(TIC)	Concentration	ug/dscm

6.35 

---

630-02-4	Emission Rate	lbs/hr

2.34E-04

---

	Emission Rate	g/s

2.95E-05	 	---









Pentatriacontane	Total Catch	ug

5.7

---

(TIC)	Concentration	ug/dscm

1.34 

---

630-07-9	Emission Rate	lbs/hr

4.95E-05

---

	Emission Rate	g/s

6.24E-06

---









2-Pentanol, 4-methyl-	Total Catch	ug

11

---

(TIC)	Concentration	ug/dscm

2.59 

---

108-11-2	Emission Rate	lbs/hr

9.55E-05

---

	Emission Rate	g/s

1.20E-05

---









Decane, 3-methyl-	Total Catch	ug

5.1

---

(TIC)	Concentration	ug/dscm

1.20 

---

13151-34-3	Emission Rate	lbs/hr

4.43E-05

---

	Emission Rate	g/s

5.58E-06

---









Nonanoic acid	Total Catch	ug

6.9

---

(TIC)	Concentration	ug/dscm

1.62 

---

112-05-0	Emission Rate	lbs/hr

5.99E-05

---

	Emission Rate	g/s

7.55E-06

---









4-Ethylbenzoic acid	Total Catch	ug

4.2

---

(TIC)	Concentration	ug/dscm

0.99 

---

619-64-7	Emission Rate	lbs/hr

3.65E-05

---

	Emission Rate	g/s

4.60E-06

---









Benzaldehyde, 3-hydroxy-4-meth	Total Catch	ug

7.3

---

(TIC)	Concentration	ug/dscm

1.72 

---

621-59-0	Emission Rate	lbs/hr

6.34E-05

---

	Emission Rate	g/s

7.99E-06

---









1,2-Benzenedicarboxylic acid	Total Catch	ug

34

---

(TIC)	Concentration	ug/dscm

7.99 

---

84-69-5	Emission Rate	lbs/hr

2.95E-04

---

	Emission Rate	g/s

3.72E-05	 	---









Hexadecanoic acid, methyl este	Total Catch	ug

6.0

---

(TIC)	Concentration	ug/dscm

1.41 

---

112-39-0	Emission Rate	lbs/hr

5.21E-05

---

	Emission Rate	g/s

6.56E-06

---









Octadecanoic acid, methyl este	Total Catch	ug

5.7

---

(TIC)	Concentration	ug/dscm

1.34 

---

112-61-8	Emission Rate	lbs/hr

4.95E-05

---

	Emission Rate	g/s

6.24E-06

---









Heneicosane	Total Catch	ug

4.8

---

(TIC)	Concentration	ug/dscm

1.13 

---

629-94-7	Emission Rate	lbs/hr

4.17E-05

---

	Emission Rate	g/s

5.25E-06

---









1-Eicosanol	Total Catch	ug

9.8

---

(TIC)	Concentration	ug/dscm

2.30 

---

629-96-9	Emission Rate	lbs/hr

8.51E-05

---

	Emission Rate	g/s

1.07E-05

---









Table 12:	Semivolatile Organic Emission Results (Continued)

Parameter

Units

Run 2

RCRA Permit Limit

Triphenylphosphine oxide	Total Catch	ug

7.5

---

(TIC)	Concentration	ug/dscm

1.76 

---

791-28-6	Emission Rate	lbs/hr

6.51E-05

---

	Emission Rate	g/s

8.21E-06

---









Acetic acid, (triphenylphospho	Total Catch	ug

12

---

(TIC)	Concentration	ug/dscm

2.82 

---

2605-67-6	Emission Rate	lbs/hr

1.04E-04

---

	Emission Rate	g/s

1.31E-05

---



 







Notes:

(A)	SHADING denotes the RCRA Permit Limit could not be demonstrated
because of laboratory reporting conventions (See UMCDF DFS GB Rocket
ATBP, Appendix B, Section 11.3 and Table 11-2).

(B)	Blank corrections have not been made to these data.

(C)	Results have been reported considering both the DL and MDL as
reported on the analytical results page for each fraction.  To provide
the most conservative emission estimates, calibrated target compounds
that are not detected are reported at the DL.  Values reported between
the DL and MDL are incorporated into the emission estimate as reported. 
When identified, TICs are reported at the reported estimated
concentrations.

(D)	“NOT FOUND” indicates that a non-calibrated target compound was
not found using an ion-specific forward library search.  An estimated DL
or MDL is not available for these compounds.

(E)	In instances where a TIC was identified more than once in one or
more sample fractions, the reported value represents the sum of all
reported values.

Abbreviations:

%	percent	<	less than

(F	degrees Fahrenheit	---	not applicable

CO2	carbon dioxide	DL	detection limit

dscf	dry standard cubic feet	dscfm	dry standard cubic feet per minute

g/s	grams per second	lbs/hr	pounds per hour

MDL	method detection limit	ND	not detected

O2	oxygen	PAS	Pollution Abatement System

PS4B	US EPA Performance Specification 4B	RCRA	Resource Conservation and
Recovery Act

TIC	tentatively identified compound	ug	microgram

ug/dscm	microgram per dry standard cubic meter

Table 13:	Volatile Organic Emission Results

Parameter

Units	Run 2	RCRA Permit Limit

Sampling Location

---	PAS Exhaust Duct	---

Date

---	10/29/05	---

Start Time

---	0802	---

Stop Time

---	1612	---

Net Sampling Time

minutes	120	---

Sample Volume

liters	77.88	---

Gas Flow Rate(1)

dscfm	288.63	---







Acetone	Total Catch	ng

68,171

---

	Concentration	ug/dscm

875.33 

---

	Emission Rate	lbs/hr

3.34E-02

---

	Emission Rate	g/s

4.21E-03

7.18E-02









Benzene	Total Catch	ng	<	569

---

	Concentration	ug/dscm

7.31 

---

	Emission Rate	lbs/hr

2.79E-04

---

	Emission Rate	g/s

3.52E-05

1.11E-04









Bromodichloromethane	Total Catch	ng	<	132.7

---

  [Using RL]	Concentration	ug/dscm

1.70 

---

	Emission Rate	lbs/hr

6.51E-05

---

	Emission Rate	g/s

8.20E-06

3.31E-06









Bromodichloromethane	Total Catch	ng	<	24.58

---

  [Using MDL]	Concentration	ug/dscm

0.32

---

	Emission Rate	lbs/hr

1.21E-05

---

	Emission Rate	g/s

1.52E-06

3.31E-06









Bromoform	Total Catch	ng	<	150.4

---

	Concentration	ug/dscm

1.93 

---

	Emission Rate	lbs/hr

7.38E-05

---

	Emission Rate	g/s

9.29E-06

6.44E-05









Bromomethane	Total Catch	ng	<	1,315.6

---

	Concentration	ug/dscm

16.89 

---

	Emission Rate	lbs/hr

6.45E-04

---

	Emission Rate	g/s

8.13E-05

---









1,3-Butadiene	Total Catch	ng	<	800	ND	---

	Concentration	ug/dscm

10.27

---

	Emission Rate	lbs/hr

3.92E-04

---

	Emission Rate	g/s

4.94E-05

---









2-Butanone	Total Catch	ng	<	800	ND	---

  (Methyl Ethyl Ketone)	Concentration	ug/dscm

10.27

---

	Emission Rate	lbs/hr

3.92E-04

---

	Emission Rate	g/s

4.94E-05

7.33E-04









Carbon Disulfide	Total Catch	ng	<	147

---

  [Using RL]	Concentration	ug/dscm

1.89 

---

	Emission Rate	lbs/hr

7.21E-05

---

	Emission Rate	g/s

9.08E-06

7.33E-07









Carbon Disulfide	Total Catch	ng	<	87.59

---

  [Using MDL]	Concentration	ug/dscm

1.12

---

	Emission Rate	lbs/hr

4.30E-05

---

	Emission Rate	g/s

5.41E-06

7.33E-07









Carbon Tetrachloride	Total Catch	ng	<	128

---

  [Using RL]	Concentration	ug/dscm

1.64 

---

	Emission Rate	lbs/hr

6.28E-05

---

	Emission Rate	g/s

7.91E-06

7.33E-07









Table 13:	Volatile Organic Emission Results (Continued)

Parameter

Units	Run 2	RCRA Permit Limit

Carbon Tetrachloride	Total Catch	ng	<	21.56

---

  [Using MDL]	Concentration	ug/dscm

0.28

---

	Emission Rate	lbs/hr

1.06E-05

---

	Emission Rate	g/s

1.33E-06

7.33E-07









Chlorobenzene	Total Catch	ng	<	80	ND	---

  [Using RL]	Concentration	ug/dscm

1.03

---

	Emission Rate	lbs/hr

3.92E-05

---

	Emission Rate	g/s

4.94E-06

2.35E-06









Chlorobenzene	Total Catch	ng	<	17.28	ND	---

  [Using MDL]	Concentration	ug/dscm

0.22

---

	Emission Rate	lbs/hr

8.47E-06

---

	Emission Rate	g/s

1.07E-06

2.35E-06









Chloroethane	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









Chloroform	Total Catch	ng	<	152

---

	Concentration	ug/dscm

1.96 

---

	Emission Rate	lbs/hr

7.47E-05

---

	Emission Rate	g/s

9.42E-06

8.38E-05









Chloromethane	Total Catch	ng	<	879.6

---

  [Using RL]	Concentration	ug/dscm

11.29 

---

	Emission Rate	lbs/hr

4.31E-04

---

	Emission Rate	g/s

5.44E-05

7.33E-07









Chloromethane	Total Catch	ng	<	790.5

---

  [Using MDL]	Concentration	ug/dscm

10.15 

---

	Emission Rate	lbs/hr

3.88E-04

---

	Emission Rate	g/s

4.88E-05

7.33E-07









2-Chloropropane	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









Dibromochloromethane	Total Catch	ng	<	160	ND	---

  [Using RL]	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	4.89E-06









Dibromochloromethane	Total Catch	ng	<	19.68	ND	---

  [Using MDL]	Concentration	ug/dscm

0.25 

---

	Emission Rate	lbs/hr

9.65E-06

---

	Emission Rate	g/s

1.22E-06

4.89E-06









1,2-Dibromoethane	Total Catch	ng	<	160	ND	---

  (Ethylene Dibromide)	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









Dibromomethane	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









cis-1,4-Dichloro-2-butene	Total Catch	ng	<	800	ND	---

	Concentration	ug/dscm

10.27

---

	Emission Rate	lbs/hr

3.92E-04

---

	Emission Rate	g/s

4.94E-05

---









Table 13:	Volatile Organic Emission Results (Continued)

Parameter

Units	Run 2	RCRA Permit Limit

trans-1,4-Dichloro-2-butene	Total Catch	ng	<	800	ND	---

	Concentration	ug/dscm

10.27

---

	Emission Rate	lbs/hr

3.92E-04

---

	Emission Rate	g/s

4.94E-05

---









1,1-Dichloroethane	Total Catch	ng	<	160	ND	---

  [Using RL]	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	7.33E-07









1,1-Dichloroethane	Total Catch	ng	<	19.36	ND	---

  [Using MDL]	Concentration	ug/dscm

0.25 

---

	Emission Rate	lbs/hr

9.49E-06

---

	Emission Rate	g/s

1.20E-06

7.33E-07









1,2-Dichloroethane	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









1,1-Dichloroethene	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









trans-1,2-Dichloroethene	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









Dichlorodifluoromethane	Total Catch	ng	<	167

---

  (Freon 12)	Concentration	ug/dscm

2.14 

---

	Emission Rate	lbs/hr

8.19E-05

---

	Emission Rate	g/s

1.03E-05

---









1,2-Dichloropropane	Total Catch	ng	<	160	ND	---

  (Propylene Dichloride)	Concentration	ug/dscm

2.05 	 	---

  [Using RL]	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	7.33E-07









1,2-Dichloropropane	Total Catch	ng	<	18.40	ND	---

  (Propylene Dichloride)	Concentration	ug/dscm

0.24 

---

  [Using MDL]	Emission Rate	lbs/hr

9.02E-06

---

	Emission Rate	g/s

1.14E-06

7.33E-07









cis-1,3-Dichloropropene	Total Catch	ng	<	155.2

---

  [Using RL]	Concentration	ug/dscm

1.99 

---

	Emission Rate	lbs/hr

7.61E-05

---

	Emission Rate	g/s

9.59E-06

7.33E-07









cis-1,3-Dichloropropene	Total Catch	ng	<	26.2

---

  [Using MDL]	Concentration	ug/dscm

0.34

---

	Emission Rate	lbs/hr

1.28E-05

---

	Emission Rate	g/s

1.62E-06

7.33E-07









trans-1,3-Dichloropropene	Total Catch	ng	<	160	ND	---

  [Using RL]	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	7.33E-07









trans-1,3-Dichloropropene	Total Catch	ng	<	19.36	ND	---

  [Using MDL]	Concentration	ug/dscm

0.25	 	---

	Emission Rate	lbs/hr

9.49E-06	 	---

	Emission Rate	g/s

1.20E-06	 	7.33E-07









Table 13:	Volatile Organic Emission Results (Continued)

Parameter

Units	Run 2	RCRA Permit Limit

Ethyl Benzene	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	2.25E-05









Hexane	Total Catch	ng	<	134.8

---

	Concentration	ug/dscm

1.73 

---

	Emission Rate	lbs/hr

6.61E-05

---

	Emission Rate	g/s

8.33E-06

---









2-Hexanone	Total Catch	ng	<	800	ND	---

  [Using RL]	Concentration	ug/dscm

10.27

---

	Emission Rate	lbs/hr

3.92E-04

---

	Emission Rate	g/s

4.94E-05

7.33E-07









Iodomethane	Total Catch	ng	<	800	ND	---

	Concentration	ug/dscm

10.27 

---

	Emission Rate	lbs/hr

3.92E-04

---

	Emission Rate	g/s

4.94E-05

---









4-Methyl-2-pentanone	Total Catch	ng	<	800	ND	---

  (Methyl Isobutyl Ketone)	Concentration	ug/dscm

10.27

---

  [Using RL]	Emission Rate	lbs/hr

3.92E-04

---

	Emission Rate	g/s

4.94E-05

7.33E-07









Methylene Chloride	Total Catch	ng	<	3,957.6

---

	Concentration	ug/dscm

50.82 

---

	Emission Rate	lbs/hr

1.94E-03

---

	Emission Rate	g/s

2.45E-04

1.20E-02









2-Propanol	Total Catch	ng	<	24,000	ND	---

	Concentration	ug/dscm

308.17 	 	---

	Emission Rate	lbs/hr

1.18E-02	 	---

	Emission Rate	g/s

1.48E-03	 	---









Styrene	Total Catch	ng	<	143.4

---

	Concentration	ug/dscm

1.84 

---

	Emission Rate	lbs/hr

7.03E-05

---

	Emission Rate	g/s

8.86E-06

1.11E-04









1,1,1,2-Tetrachloroethane	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









1,1,2,2-Tetrachloroethane	Total Catch	ng	<	160	ND	---

  [Using RL]	Concentration	ug/dscm

2.05 

---

	Emission Rate	lbs/hr

7.85E-05

---

	Emission Rate	g/s

9.89E-06

7.33E-07









1,1,2,2-Tetrachloroethane	Total Catch	ng	<	34.56	ND	---

  [Using MDL]	Concentration	ug/dscm

0.44

---

	Emission Rate	lbs/hr

1.69E-05

---

	Emission Rate	g/s

2.14E-06

7.33E-07









Tetrachloroethene	Total Catch	ng	<	80	ND	---

  (Tetrachloroethylene)	Concentration	ug/dscm

1.03

---

  [Using RL]	Emission Rate	lbs/hr

3.92E-05

---

	Emission Rate	g/s

4.94E-06

7.33E-07









Tetrachloroethene	Total Catch	ng	<	26.08	ND	---

  (Tetrachloroethylene)	Concentration	ug/dscm

0.33

---

  [Using MDL]	Emission Rate	lbs/hr

1.28E-05

---

	Emission Rate	g/s

1.61E-06

7.33E-07









Table 13:	Volatile Organic Emission Results (Continued)

Parameter

Units	Run 2	RCRA Permit Limit

Toluene	Total Catch	ng	<	151.7

---

	Concentration	ug/dscm

1.95 

---

	Emission Rate	lbs/hr

7.44E-05

---

	Emission Rate	g/s

9.37E-06

6.17E-03









1,1,1-Trichloroethane	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









1,1,2-Trichloroethane	Total Catch	ng	<	160	ND	---

  (Methyl Chloroform)	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	1.22E-04









Trichloroethene	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









Trichlorofluoromethane	Total Catch	ng	<	160	ND	---

  (Freon 11)	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









1,2,3-Trichloropropane	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









1,1,2-Trichloro-1,2,2-trifluoroethane	Total Catch	ng	<	160	ND	---

  (Freon 113)	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	---









m,p-Xylene	Total Catch	ng	<	152

---

	Concentration	ug/dscm

1.95 

---

	Emission Rate	lbs/hr

7.45E-05

---

	Emission Rate	g/s

9.39E-06

---









o-Xylene	Total Catch	ng	<	160	ND	---

	Concentration	ug/dscm

2.05 

---

	Emission Rate	lbs/hr

7.85E-05

---

	Emission Rate	g/s

9.89E-06

---









Total Xylenes(2)	Total Catch	ng	<	312

---

  [Using RL]	Concentration	ug/dscm

4.01 

---

	Emission Rate	lbs/hr

1.53E-04

---

	Emission Rate	g/s

1.93E-05

1.58E-05









Total Xylenes(2)	Total Catch	ng	<	44.38

---

  [Using MDL]	Concentration	ug/dscm

0.57

---

	Emission Rate	lbs/hr

2.18E-05

---

	Emission Rate	g/s

2.74E-06

1.58E-05









Vinyl Acetate	Total Catch	ng	<	800	ND	---

  [Using RL]	Concentration	ug/dscm

10.27

---

	Emission Rate	lbs/hr

3.92E-04

---

	Emission Rate	g/s

4.94E-05

7.33E-07









Vinyl Bromide	Total Catch	ng	<	800	ND	---

	Concentration	ug/dscm

10.27

---

	Emission Rate	lbs/hr

3.92E-04

---

	Emission Rate	g/s

4.94E-05

---









Table 13:	Volatile Organic Emission Results (Continued)

Parameter

Units	Run 2	RCRA Permit Limit

Vinyl Chloride	Total Catch	ng	<	160	ND	---

  [Using RL]	Concentration	ug/dscm

2.05 	 	---

	Emission Rate	lbs/hr

7.85E-05	 	---

	Emission Rate	g/s

9.89E-06	 	1.62E-06









Vinyl Chloride	Total Catch	ng	<	18.24	ND	---

  [Using MDL]	Concentration	ug/dscm

0.23	 	---

	Emission Rate	lbs/hr

8.95E-06	 	---

	Emission Rate	g/s

1.13E-06	 	1.62E-06









Ethane, 1,1,1,2-tetrafluoro	Total Catch	ng

1,290

---

(TIC)	Concentration	ug/dscm

16.56 

---

(811-97-2)	Emission Rate	lbs/hr

6.33E-04

---

	Emission Rate	g/s

7.97E-05

---









Benzaldehyde	Total Catch	ng

125

---

(TIC)	Concentration	ug/dscm

1.61 

---

(100-52-7)	Emission Rate	lbs/hr

6.13E-05

---

	Emission Rate	g/s

7.72E-06

---









Ethanone, 1-phenyl-	Total Catch	ng

219

---

(TIC)	Concentration	ug/dscm

2.81 

---

(98-86-2)	Emission Rate	lbs/hr

1.07E-04

---

	Emission Rate	g/s

1.35E-05

---









Benzonitrile	Total Catch	ng

55

---

(TIC)	Concentration	ug/dscm

0.71 

---

(100-47-0)	Emission Rate	lbs/hr

2.70E-05

---

	Emission Rate	g/s

3.40E-06

---









Methane, nitro-	Total Catch	ng

61

---

(TIC)	Concentration	ug/dscm

0.78 

---

(75-52-5)	Emission Rate	lbs/hr

2.99E-05

---

	Emission Rate	g/s

3.77E-06

---









1-Propene	Total Catch	ng

78

---

(TIC)	Concentration	ug/dscm

1.00 

---

(115-07-1)	Emission Rate	lbs/hr

3.83E-05

---

	Emission Rate	g/s

4.82E-06

---











Notes:

(A)	SHADING denotes the RCRA Permit Limit could not be demonstrated
because of laboratory reporting conventions (See UMCDF DFS GB Rocket
ATBP, Appendix B, Section 11.3 and Table 11-2).

(B)	No blank corrections have been made to these data.  If undetected in
the analysis, the detection limit is reported.

(C)	Results have been reported considering both the RL and MDL as
reported on the laboratory results page for each fraction.  To provide
the most conservative emission estimates, calibrated target compounds
that are not detected are reported at the RL.  Values reported between
the RL and MDL are incorporated into the emission estimate as reported. 
When identified, TICs are reported at the reported estimated
concentrations.

(D)	Note that only TICs detected in multiple runs are averaged.  If
detected in only a single run, that value is reported in the
“Average” column.  “NO TIC” is reported for the runs in which
the TIC was not found.

Footnotes:

(1)	Taken from the flow rates measured by the M0010, M0023A-PCB, and
M0023A-PCDD/F sampling trains during Runs 2, 3, and 4.

(2)	The total xylene catch was derived by adding the m,p-xylene and
o-xylene catches and comparing that value to the RCRA Permit limit.

Table 13:	Volatile Organic Emission Results (Continued)

Abbreviations:

<	less than	---	not applicable

dscfm	dry standard cubic feet per minute	g/s	grams per second

lbs/hr	pounds per hour	M0010	SW-846 Method 0010

M0023A	SW-846 Method 0023A	MDL	method detection limit

ND	not detected	ng	nanograms

PAS	Pollution Abatement System	PCB	polychlorinated biphenyl

PCDD/F	polychlorinated dibenzo-p-dioxin/furan	RCRA	Resource Conservation
and Recovery Act

RL	reporting limit	TIC	tentatively identified compound

ug/dscm	micrograms per dry standard cubic meter

Table 14:	Recirculation Scrubber Brine Analytical Results

Analyte	Units	Run 2	Run 3	Run 4	Average

Total MonoCB	pg/L	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total DiCB	pg/L	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total TriCB	pg/L	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

3,4,4',5-TetraCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

3,3',4,4'-TetraCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

Total TetraCB	pg/L	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

2,3,3',4,4'-PentaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3,4,4',5-PentaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3',4,4',5-PentaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2',3,4,4',5-PentaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

3,3',4,4',5-PentaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

Total PentaCB	pg/L	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

2,3,3',4,4',5-HexaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3,3',4,4',5'-HexaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3',4,4',5,5'-HexaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

3,3',4,4',5,5'-HexaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

Total HexaCB	pg/L	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

2,3,3',4,4',5,5'-HeptaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100
[ND]

2,2',3,4,4',5,5'-HeptaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100
[ND]

2,2',3,3',4,4', 5-HeptaCB	pg/L	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100
[ND]

Total HeptaCB	pg/L	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total OctaCB	pg/L	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total NonaCB	pg/L	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total DecaCB	pg/L	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]



Abbreviations:

<	less than	CB	chlorinated biphenyl

ND	not detected	pg/L	picograms per liter

Table 15:	Cyclone Residue Analytical Results

Analyte	Units	Run 2	Run 3	Run 4	Average

Total MonoCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total DiCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total TriCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

3,4,4',5-TetraCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

3,3',4,4'-TetraCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

Total TetraCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

2,3,3',4,4'-PentaCB	pg/g	130	160	120	136.67

2,3,4,4',5-PentaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3',4,4',5-PentaCB	pg/g	350	380	290	340.00

2',3,4,4',5-PentaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

3,3',4,4',5-PentaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

Total PentaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

2,3,3',4,4',5-HexaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3,3',4,4',5'-HexaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3',4,4',5,5'-HexaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

3,3',4,4',5,5'-HexaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

Total HexaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

2,3,3',4,4',5,5'-HeptaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100
[ND]

2,2',3,4,4',5,5'-HeptaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100
[ND]

2,2',3,3',4,4', 5-HeptaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100
[ND]

Total HeptaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total OctaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total NonaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total DecaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]



Abbreviations:

<	less than	CB	chlorinated biphenyl

ND	not detected	pg/g	picograms per grams

Table 16:	HDC Ash Analytical Results

Analyte	Units	Run 2	Run 3	Run 4	Average

Total MonoCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total DiCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total TriCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

3,4,4',5-TetraCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

3,3',4,4'-TetraCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

Total TetracCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

2,3,3',4,4'-PentaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3,4,4',5-PentaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3',4,4',5-PentaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2',3,4,4',5-PentaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

3,3',4,4',5-PentaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

Total PentaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

2,3,3',4,4',5-HexaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3,3',4,4',5'-HexaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

2,3',4,4',5,5'-HexaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

3,3',4,4',5,5'-HexaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100 [ND]

Total HexaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

2,3,3',4,4',5,5'-HeptaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100
[ND]

2,2',3,4,4',5,5'-HeptaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100
[ND]

2,2',3,3',4,4', 5-HeptaCB	pg/g	< 100 [ND]	< 100 [ND]	< 100 [ND]	< 100
[ND]

Total HeptaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total OctaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total NonaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]

Total DecaCB	pg/g	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]	< 1,000 [ND]



Abbreviations:

<	less than	CB	chlorinated biphenyl

ND	not detected	pg/g	picograms per grams

Table 17:	DFS AWFCO Parameters

RCRA [MACT]

Item Number	AWFCO Alarm

Tag Number	Process Data Description	RCRA AWFCO for Normal Agent
Operations

DFS-01

[DFS(M)-1]	16-TAHH-182	Rotary Kiln

Temperature (Before Spray)

High-High	1,615(F

(instantaneous)

DFS-02

[DFS(M)-2]	16-TAHH-08	Rotary Kiln

Temperature (After Spray)

High-High	1,539oF

(instantaneous)

DFS-03

[DFS(M)-3]	16-TALL-08	Rotary Kiln

Temperature (After Spray)

Low-Low	949(F

(instantaneous)

DFS-04

[DFS(M)-4]	16-XS-207

16-XS-209	Feed Chute Operation	Jammed

(instantaneous)

DFS-05

[DFS(M)-5]	16-PSHH-204	Rotary Kiln

Pressure

High-High	-0.1 inwc

with 3-second delay

(instantaneous)

DFS-06

[DFS(M)-6]	16-TAHH-51A through E	Rotary Kiln Shell

Temperature

High-High	1,600oF

(instantaneous)

DFS-07

[DFS(M)-7]	16-BSLL-850/851	Afterburner

Flame Loss

Low-Low	Flame Loss

(both burners)

(instantaneous)

DFS-08

[DFS(M)-8]	16-TALL-42	HDC

Temperature

Low-Low	1,012(F

(instantaneous)

DFS-09

[DFS(M)-9	16-XS-58

16-XS-821	Discharge Conveyor Operation	Jammed

(instantaneous)

DFS-10

[DFS(M)-10]	16-SSL-57	HDC Operation	Zero speed

(instantaneous)

DFS-11

[DFS(M)-11]	16-PDAHH-813	Afterburner

Exhaust Gas Flow Rate

High-High	0.92 inwc

(instantaneous)

[DFS(M)-12]	16-PDAHH-813A

0.92 inwc

(ROHA)

DFS-12

[DFS(M)-13]	16-TALL-182/20	Rotary Kiln

Temperature (Before Spray)

Low-Low	1,000oF

 (instantaneous)

[DFS(M)-14]	16-TALL-182C

1,117oF

(ROHA)

[DFS(M)-15]	24-PDALL-25A	Scrubber Tower Packed Bed

Differential Pressure

Low-Low	0.3 inwc

(ROHA)

Table 17:	DFS AWFCO Parameters (Continued)

RCRA [MACT]

Item Number	AWFCO Alarm

Tag Number	Process Data Description	RCRA AWFCO for Normal Agent
Operations

DFS-13

[DFS(M)-16]	16-TALL-92	Afterburner

Temperature

Low-Low	2,050oF

 (instantaneous)

DFS-14

[DFS(M)-18]	16-TAHH-92	Afterburner

Temperature

High-High	2,200oF

(instantaneous)

[DFS(M)-19]	24-AALL-07A/B	Quench Brine

Brine pH

Low-Low	8.5 pH units

(ROHA)

DFS-15

[DFS(M)-20]	24-PDALL-08	Venturi Scrubber

Differential Pressure

Low-Low	20 inwc

(instantaneous)

DFS-16

[DFS(M)-22]	24-AAHH-207C	PFS Exhaust Duct

CO Concentration

High-High	100 ppmv

7% O2, dry basis

(ROHA)

[DFS(M)-23]	24-DAHH-35	Scrubber Tower

Clean Liquor Solids Content

High-High	1.01 sgu

(12HRA)

DFS-17

[DFS(M)-24	PDAR	Waste Feed Rate

High	See Section 8.5.21

DFS-18

[DFS(M)-25]	24-FALL-30	Scrubber Tower

Clean Liquor Flow Rate

Low-Low	1,475 gpm

(instantaneous)

DFS-19	MON-ACAM-183	Chemical Agent Emissions

Exhaust Blower Duct

High-High	0.0003 mg/m3 GB

(instantaneous)

DFS-20	MON-ACAM-297	Chemical Agent Emissions

Cyclone Enclosure

High-High	0.0003 mg/m3 GB

(instantaneous)

DFS-21	MON-ACAM-129/223/225	Chemical Agent Emissions

Common Stack

High-High	0.0003 mg/m3 GB

(instantaneous)

DFS-22	23-LSHH-02/06/702/706	Brine Surge Tank(s)

Level

High High	Unavailable is when the level high-high at 18 feet 3 inches or
tank is selected for feed to the BRA

DFS-23

[DFS(M)-27]	24-AALL-34	Scrubber Tower

Clean Liquor pH

Low-Low	7.1 pH units

(instantaneous)

Table 17:	DFS AWFCO Parameters (Continued)

RCRA [MACT]

Item Number	AWFCO Alarm

Tag Number	Process Data Description	RCRA AWFCO for Normal Agent
Operations

DFS-24

[DFS(M)-29]	114-PALL-344	Scrubber Tower

Clean Liquor Pressure

Low-Low	25 psig

(instantaneous)

DFS-25	24-TSHH-01	Quench Tower

Exhaust Gas Temperature

High-High	225(F

(instantaneous)

DFS-26

[DFS(M)-30]	24-FALL-06	Venturi Scrubber

Quench Brine Flow Rate

Low-Low	260 gpm

(instantaneous)

DFS-27

[DFS(M)-32]	24-DAHH-33	Quench Tower

Brine Density

High-High	1.06 sgu

(instantaneous)

[DFS(M)-33]	24-DAHH-33A

1.06 sgu

(12HRA)

DFS-28

[DFS(M)-34]	16-SAHH-602	Kiln

Rotational Speed

High-High	2.06 rpm

DFS-29	24-AAHH-206A/B	PFS Exhaust Duct

O2 Concentration

High-High	14%

dry basis

(instantaneous)

DFS-30

[DFS(M)-35]	24-AALL-206A/B	PFS Exhaust Duct

O2 Concentration

Low-Low	7.7%

dry basis

(2MRA)

DFS-31

[DFS(M)-36]	16-PAHH-65	Afterburner

Pressure

High-High	-0.1 inwc

(instantaneous)

DFS-32	24-LSHH-10	Scrubber Tower

Sump Liquid Level

High-High	69 inches above bottom tangent line

(instantaneous)

DFS-33	24-LSLL-10	Scrubber Tower

Sump Liquid Level

Low-Low	33 inches above bottom tangent line

(instantaneous)

DFS-34

[DFS(M)-37]	16-BSLL-844	Rotary Kiln

Flame Loss	Flame Loss

(instantaneous)

DFS-35

[DFS(M)-38]	114-PDAHH-440A/442A/ 454A/436A/ 438A/487A	PFS Prefilter

Differential Pressure

High-High	1.5 inwc

(instantaneous)

DFS-36

[DFS(M)-39]	114-PDAHH-440B/H/442B/H454B/H/436B/H438B/H/487B/H	PFS HEPA
Filter

Differential Pressure

High-High	3.0 inwc

(instantaneous)

Table 17:	DFS AWFCO Parameters (Continued)

RCRA [MACT]

Item Number	AWFCO Alarm

Tag Number	Process Data Description	RCRA AWFCO for Normal Agent
Operations

DFS-37

[DFS(M)-40]	114-TSHH-430	Carbon Filter System

Inlet Temperature

High-High	180(F

(instantaneous)

	114-TAHH-417

169(F

(ROHA)

DFS-38

[DFS(M)-41]	114-MSHH-431A/B	Carbon Filter System

Inlet Moisture Level

High-High	80% RH

(instantaneous)

	114-MAHH-431A/B

55% RH

(ROHA)

DFS-39	114-ZS-449B	Carbon Filter System

Bypass Valve Operation	Not Closed

(instantaneous)

[DFS(M)-42]	114-PDALL-440A/442A/ 454A/436A/ 438A/487A	PFS Prefilter

Differential Pressure

Low-Low	0.20 inwc

(instantaneous)

[DFS(M)-43]	114-PDALL-440B/H/442B/H454B/H/436B/H438B/H487B/H	PFS HEPA
Filter

Differential Pressure

Low-Low	0.15 inwc

(instantaneous)

DFS-40	MON-ACAM-353	Chemical Agent Emissions

Upstream of PFS

High-High	0.0003 mg/m3 GB

(instantaneous)

DFS-41

[DFS(M)-44]	24-PDAHH-312/53	Mist Eliminator

Differential Pressure

High-High	20 inwc

(instantaneous)

DFS-42

[DFS(M)-45]	16-TAHH-182A	Rotary Kiln

Temperature (Before Spray)

High-High	1,548ºF

(ROHA)

DFS-43	114-MAHH-111/112/113/109/209/110	Carbon Filter System

Outlet Moisture Level

High-High	55% RH

(30MRA)



Abbreviations:

%	percent	12HRA	12-hour rolling hourly average

2MRA	2-minute rolling average	AAHH	analyzing alarm high-high

AALL	analyzing alarm low-low	AWFCO	automatic waste feed cutoff

BRA	Brine Reduction Area	BSLL	burner switch low-low

CO	carbon monoxide	DAHH	density alarm high-high

DFS	Deactivation Furnace System	(F	degrees Fahrenheit

FALL	flow alarm low-low	gpm	gallons per minute

HDC	Heated Discharge Conveyor	HEPA	high efficiency particulate air

inwc	inches of water column	LSHH	level switch high-high

LSLL	level switch low-low	MACT	Maximum Achievable Control Technologies

MAHH	moisture alarm high-high	mg/m3	milligrams per cubic meter

MSHH	moisture switch high-high	O2	oxygen

PAHH	pressure alarm high-high	PAS	Pollution Abatement System

Table 17:	DFS AWFCO Parameters (Continued)

Abbreviations (Continued):

PDAHH	pressure differential alarm high-high	PDALL	pressure differential
alarm low-low

PDAR	process data acquisition and recording	PFS	PAS Filtration System

ppmv	parts per million volume	PSHH	pressure switch high-high

psig	pounds per square inch gauge	RCRA	Resource Conservation and
Recovery Act

RH	relative humidity	ROHA	rolling hourly average

rpm	revolutions per minute	SAHH	speed alarm high-high

sgu	specific gravity units	SSL	speed switch low

TAHH	temperature alarm high-high	TALL	temperature alarm low-low

TSHH	temperature switch high-high	XS	unclassified switch

ZS	position switch

UMCDF DFS GB TSCA ATBR, Revision 0	January 2006



  PAGE  ii 

  PAGE  77 

UMCDF DFS GB TSCA ATBR, Revision 0	January 2006



UMCDF DFS GB TSCA ATBR, Revision 0	January 2006



UMCDF DFS GB TSCA ATBR, Revision 0	January 2006



UMCDF DFS GB TSCA ATBR, Revision 0	January 2006



UMCDF DFS GB TSCA ATBR, Revision 0	January 2006



UMCDF DFS GB TSCA ATBR, Revision 0	January 2006



UMCDF DFS GB TSCA ATBR, Revision 0	January 2006



UMCDF

Deactivation Furnace System GB Rocket Toxic Substances Control Act Agent
Final Trial Burn Report

Revision 0, January 2006

Volume 1 of 4

(Main Report to Appendix G)

Submitted to:	National Program Chemicals Division

Submitted by:	U.S. Army Chemical Materials Agency UMCDF Field Office

	Umatilla Chemical Depot

