Instructions for filling in the Emission Test Template

This Information Collection Request (ICR) spreadsheet is intended to collect information about emission data fro

fuel burning power plants and which test methods were used to do so for cases where the test methods are not 

supported by the Electronic Reporting Tool (ERT). This spreadsheet should only be used if the method is not in t

if you do not have access to a lab which performs methods that are in the ERT. You must complete at least 3 se

runs or sampling events for each of the requested constituents. This spreadsheet is intended to be used for one 

one facility. Data for multiple boilers should be handled by using separate copies of this spreadsheet.

yellow are required. All cells that are shaded in green are populated using drop-down lists. You do not need to 

cells shaded in gray, as they are automatically populated from the Boiler Information worksheet. 

resulting spreadsheet with the following naming convention: [FacilityID]_Unit_[BoilerID]_EmisTestMethods.xls 

(example: 8100_Unit_2_EmisTestMethods.xls).

Please refer to the following steps when using these spreadsheets.

Boiler Information Worksheet

1. Please enter the EIA Facility Code, Facility Name and Boiler ID of your boiler on the Boiler Information worksh

2. Please enter the control device configuration.

Emission Data Worksheets

The emission data worksheets are provided for each constituent or constituent family required for this analysis. 

spreadsheet, you must enter boiler operating information during sampling, fuel input information, and emission 

results. There are generally 1 to 3 emission test results records to be entered depending on the constituent or c

family. For example, CO only requires 1 record with 3 sample events, while Mercury requires that you enter bot

Hg+2, or if the Ontario-Hydro Method was used, you would need to enter Hg0, HgP, and Hg

Volatile Organic HAP and Speciated Semi-Volatile Organic HAP worksheets allow you to use a drop

Constituent field to define as many records as needed to record each HAP that you have results for. General ins

follow for these worksheets:

Boiler Operation Information

1. Please provide the values of all requested parameters for each of test run/sample.

2. Please provide any other supporting information or comments in the Other Supporting Information field.

Fuel Information

1. Please enter what types of fuel are being used in your boiler using the drop-downs in the Fuel Type Selection 

You may enter up to 4 fuel types. If you are not burning one or more of the fuel types entered in one or more sa

then enter an input rate of zero. 

2. Please enter the unit of measure using the drop down provided.

3. Please enter the test method used to determine the fuel input rate.

4. Please provide any other information that you feel may be important in the Other Supporting Information fie

Emission Data
1. Some constituents ask for the emission rate results of each run in two different units of measure, while other

If emission rate results are requested in two different units of measure (ex. lb/MMBtu (Pounds per million BTU) 

ppmvd @ 7% O2(parts per million by volume dry basis at 7 percent oxygen)), you are required to provide both.

2. Please provide the test method used. This may or may not match the example given in the Test Method Used 

Please ensure that the name includes the owning organization of the test method (ex. U.S. EPA Method 0010).

3. Please provide any other information that you feel may be important in the Other Supporting Information fie

4. If data sheets and QA/QC documentation tables are provided for the test method you are entering data for p

enter these data.
nformation about emission data from fossil 

ses where the test methods are not currently 

nly be used if the method is not in the ERT or 

T. You must complete at least 3 separate 

sheet is intended to be used for one boiler of 

copies of this spreadsheet. Fields shaded in 

down lists. You do not need to populate 

rmation worksheet. Please name each 

nit_[BoilerID]_EmisTestMethods.xls 

ler on the Boiler Information worksheet. 

ent family required for this analysis. On each 

fuel input information, and emission test 

d depending on the constituent or constituent 

Mercury requires that you enter both Hg0 and 

, HgP, and Hg+2. However, both the Speciated 

low you to use a drop-down provided in the 

at you have results for. General instructions 

er Supporting Information field.

downs in the Fuel Type Selection field. 

fuel types entered in one or more samples, 

he Other Supporting Information field.
erent units of measure, while others do not. 

b/MMBtu (Pounds per million BTU) and 

, you are required to provide both.

mple given in the Test Method Used field. 

ethod (ex. U.S. EPA Method 0010).

he Other Supporting Information field.

 method you are entering data for please also 
EIA Facility Code Facility Name Boiler ID

IN_Wabash River Station Wabash River StationUnit 4
Control Device Configuraton
EIA Facility Code Facility Name Boiler ID

IN_Wabash River Station Wabash River Station Unit 4

Run Number Test Start Date Test Start Time
Measured Value (ppm)

Test End Date Test End Time
Basis (Wet or Dry) Test Method Used Data Flag (ADL, BDL, DDL)

CO Emission Test Results
Test Method Comments lb/mmBtu ppmdv @ 7% O2

Calculated Emission Rate
Steam Output (1000 lb/hr) Total Heat Input 

(mmBtu/hr) Flue Gas Moisture (%)
Flue Gas CO

2

 (%) Flue Gas O

2

 (%) Flue Gas Flow Rate 

(dscfm)
Fuel Input Rate Fuel Type

Flue Gas Temperature (F)

Fuel #1
Units of Measure Measurement Method Fuel Input Rate

Fuel #1
Fuel Type Units of Measure Measurement Method

Fuel #2
Fuel Input Rate Fuel Type Units of Measure

Fuel #3
Measurement Method Fuel Input Rate Fuel Type

Fuel #4
Units of Measure Measurement Method

Fuel #4

Other Supporting 

Information
EIA Facility Code Facility Name Boiler ID

IN_Wabash River Station Wabash River Station Unit 4

1 6/5/2010 8:40 6/5/2010

2 6/5/2010 11:35 6/5/2010

3 6/5/2010 14:27 6/5/2010

Run Number Test Start Date Test Start Time Test End Date
Measured Value 

(ppm) Basis (Wet or Dry) Test Method Used Data Flag (ADL, BDL, DDL)

11:09 1.00E-03 Dry U.S. EPA Method 316 ADL

14:01 [<4.62E-05] Dry U.S. EPA Method 316 BDL

16:53 2.10E-04 Dry U.S. EPA Method 316 ADL

Test End Time

Formaldehyde Emission Test Results
Test Method 

Comments lb/mmBtu ppmdv @ 7% O2

Method Blank Contamination5.90E-03 1.02E-03

[<2.72E-04] [<4.73E-05]

Method Blank Contamination1.15E-03 2.14E-04

Calculated Emission Rate Steam Output (1000 

lb/hr)

Total Heat Input 

(mmBtu/hr)
Fuel Input 

Rate Fuel Type Units of Measure

9.6 12.13 7.3 1,260,476 275

9.9 12.16 7.32 1,258,887 279

9.8 12.12 7.28 1,177,497 279

Flue Gas 

Moisture (%)

Flue Gas 

CO2 (%)

Flue Gas 

O2 (%)

Flue Gas Flow 

Rate (dscfm)

Flue Gas 

Temperature 

(F)

Fuel #1
Measurement 

Method

Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel Input 

Rate Fuel Type Units of Measure

Fuel #2 Fuel #3
Measurement 

Method

Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel #4

Other Supporting Information
EIA Facility Code Facility Name Boiler ID

IN_Wabash River Station Wabash River Station Unit 4

Run Number Test Start Date Test Start Time
Measured Value (ppm) Basis (Wet or Dry)

Methane Emission T

Test End Date Test End Time
Test Method Used Data Flag (ADL, 

BDL, DDL)

Test Method 

Comments lb/mmBtu

Methane Emission Test Results Calculated Emission Rate
ppmdv @ 7% O2

Flue Gas 

O2 (%)

Flue Gas 

Flow Rate 

(dscfm)

lated Emission Rate

Steam Output 

(1000 lb/hr)

Total Heat 

Input 

(mmBtu/hr)

Flue Gas 

Moisture 

(%)

Flue Gas 

CO2 (%)
Fuel 

Input 

Rate

Fuel Type Units of 

Measure

Measurement 

Method

Fuel 

Input 

Rate

Fuel Type Units of 

Measure

Flue Gas 

Temperat

ure (F)

Fuel #1 Fuel #2
Measurement 

Method

Fuel 

Input 

Rate

Fuel Type Units of 

Measure

Measurement 

Method

Fuel 

Input 

Rate

Fuel Type Units of 

Measure

Fuel #3 Fuel #4
Measurement 

Method

Other Supporting 

Information
EIA Facility Code Facility Name Boiler ID

IN_Wabash River Station Wabash River Station Unit 4

Run Number Test Start Date Test Start Time Test End Date
Measured Value 

(ppm) Basis (Wet or Dry) Test Method Used 

SO2 Emission Test Results

Test End Time
Data Flag (ADL, 

BDL, DDL)

Test Method 

Comments lb/mmBtu ppmdv @ 7% O

2

Calculated Emission Rate Steam Output 

(1000 lb/hr)
Fuel Input 

Rate Fuel Type

Flue Gas 

Temperature 

(F)

Fuel #1 Flue Gas 

O2 (%)

Flue Gas 

Flow Rate 

(dscfm)

Total Heat 

Input 

(mmBtu/hr)

Flue Gas 

Moisture 

(%)

Flue Gas 

CO2 (%)
Units of 

Measure

Measurement 

Method

Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel Input 

Rate Fuel Type

Fuel #1 Fuel #2 Fuel #3
Units of 

Measure

Measurement 

Method

Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel #3 Fuel #4
Other Supporting Information
EIA Facility Code Facility Name Boiler ID

IN_Wabash River Station Wabash River Station Unit 4

1 6/9/2010 8:08

2 6/9/2010 13:03

3 6/10/2010 7:40

Run Number Test Start Date Test Start Time
Please note QA/QC documentation starting in Column "AI"

Measured Value 

(μg/dscm) Basis (Wet or Dry)

6/9/2010 9:21 6.92 Dry

6/9/2010 14:35 6.68 Dry

6/10/2010 8:57 6.83 Dry

Test End Date Test End Time

Total Vapor Phase Mercury Em
 starting in Column "AI"

Test Method Used Data Flag (ADL, 

BDL, DDL)

Test Method 

Comments (lb/mmBtu)

U.S. EPA Method 30B ADL 6.50E-06

U.S. EPA Method 30B ADL 6.31E-06

U.S. EPA Method 30B ADL 6.32E-06

Steam Output 

(1000 lb/hr)

Total Vapor Phase Mercury Emission Test Results
Fuel Input Rate

9.01 11.5 7.3 1,163,199 265.8

8.75 11.4 7.4 1,204,758 275.1

8.82 11.9 7.1 1,255,300 270.6

Total Heat 

Input 

(mmBtu/hr)

Flue Gas 

CO2 (%)

Flue Gas 

Moisture 

(%)

Flue Gas 

O2 (%)

Flue Gas 

Flow Rate 

(dscfm)

Flue Gas 

Temperature (F)
Fuel Type Units of 

Measure

Measurement 

Method

Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel Input 

Rate

Fuel #1 Fuel #2
Fuel Type Units of 

Measure

Measurement 

Method

Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel #3 Fuel #4
 QA/QC Documentation

Trap ID Section 1 

Mass (ng)

Section 2 

Mass (ng)

Total 

Mass (ng)

Initial 

Spike 

(ng)

Total NonSpike (ng)

65446 173 1.2 174.2 100 74.2

73185 173 1 174 100 74

73207 179 0.5 179.5 100 79.5

Other Supporting Information
Sample 

Volume 

(dscm)

Volume 

Difference (%)

Volume Diff. 

Limit

Breaktrough 

(%)

Breaktrough 

Limit

Concentration 

(μg/dscm) Trap ID

0.0114 0.693641618 6.527518534 68281

0.0112 0.578034682 6.599428522 73338

0.0114 0.279329609 6.966915951 73336

#DIV/0! #DIV/0!

#DIV/0! #DIV/0!

#DIV/0! #DIV/0!

≤20% of field 

recovery test

≤ 10% of 

Section 1 Hg 

mass for Hg 

conc. >1 

μg/dscm: or ≤ 

20% of Section 

Trap #1
Section 1 

Mass

Section 2 

Mass

Total 

Mass

Initial 

Spike

Total NonSpikeSample 

Volume

Volume 

Difference (%)

Volume Diff. 

Limit

78 0.6 78.6 78.6 0.0114 0.123

74 0.8 74.8 74.8 0.0112 0.151

77 0.8 77.8 77.8 0.0114 0.187 ≤20% of field 

recovery test

Trap #2
Breaktrough (%) Breaktrough 

Limit

Concentration 

(μg/dscm) Abs. diff. RD (%) Limit Crec

0.769230769 6.923097527 0.395579 2.940973 8.4016

1.081081081 6.680887057 0.081459 0.613378 8.8367

1.038961039 6.830693096 0.136223 0.987293 8.8996

#DIV/0! #DIV/0! #DIV/0! #DIV/0!

#DIV/0! #DIV/0! #DIV/0! #DIV/0!

#DIV/0! #DIV/0! #DIV/0! #DIV/0!

≥10 % RD mass 

for Hg conc. >1 

μg/dscm: or 

≤20% RD or ≤0.2 

μg/dscm abs.diff. 

for Hg conc. ≤1 

≤ 10% of Section 

1 Hg mass for 

Hg conc. >1 

μg/dscm: or ≤ 

20% of Section 1 

for Hg conc.≤1 

Paired Trap Agreement (RD) Measured Spik
R (%) by 

Run Ravg (%) Limit

95.50

99.09

101.55

Average 

Recovery, 

between 85 and 

115%

Measured Spike Recovery ( R )

98.7147993
EIA Facility Code Facility Name Boiler ID

IN_Wabash River Station Wabash River Station Unit 4

Run Number Test Start Date Test Start Time
Measured Hg

0

 Value 

(μg/dscm)

Measured Hg+2 Value 

(μg/dscm)

Test End Date Test End Time
Measured HgP

 Value 

(μg/dscm)

Basis (Wet or Dry) Test Method Used Data Flag (ADL, BDL, DDL)

Total Vapor Phase Mercury Emission Test Results
Test Method 

Comments

Total Mercury 

(lb/mmBtu)

Flue Gas 

CO

2

 (%)

Steam Output 

(1000 lb/hr)

Total Heat 

Input 

(mmBtu/hr)

Flue Gas 

Moisture (%)
Fuel Input Rate Fuel Type Units of 

Measure

Measurement 

Method

Fuel #1 Flue Gas 

O2 (%)

Flue Gas 

Flow Rate 

(dscfm)

Flue Gas 

Temperature 

(F)
Fuel Input Rate Fuel Type Units of 

Measure

Measurement 

Method

Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel #2 Fuel #3
Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Other Supporting Information

Fuel #4
EIA Facility Code Facility Name Boiler ID

IN_Wabash River Station Wabash River Station Unit 4

Speciated Volatile Organic HAP Emission Data

1,1,1,2-Tetrachloroethane 1 6/5/2010

1,1,1,2-Tetrachloroethane 2 6/5/2010

1,1,1,2-Tetrachloroethane 3 6/5/2010

1,1,1-Trichloroethane 1 6/5/2010

1,1,1-Trichloroethane 2 6/5/2010

1,1,1-Trichloroethane 3 6/5/2010

1,1,2,2-Tetrachloroethane 1 6/5/2010

1,1,2,2-Tetrachloroethane 2 6/5/2010

1,1,2,2-Tetrachloroethane 3 6/5/2010

1,1,2-Trichloroethane 1 6/5/2010

1,1,2-Trichloroethane 2 6/5/2010

1,1,2-Trichloroethane 3 6/5/2010

1,1-Dichloroethane 1 6/5/2010

1,1-Dichloroethane 2 6/5/2010

1,1-Dichloroethane 3 6/5/2010

1,1-Dichloroethene 1 6/5/2010

1,1-Dichloroethene 2 6/5/2010

1,1-Dichloroethene 3 6/5/2010

1,1-Dichloropropene 1 6/5/2010

1,1-Dichloropropene 2 6/5/2010

1,1-Dichloropropene 3 6/5/2010

1,2,3-Trichlorobenzene 1 6/5/2010

1,2,3-Trichlorobenzene 2 6/5/2010

1,2,3-Trichlorobenzene 3 6/5/2010

1,2,3-Trichloropropane 1 6/5/2010

1,2,3-Trichloropropane 2 6/5/2010

1,2,3-Trichloropropane 3 6/5/2010

1,2,4-Trichlorobenzene 1 6/5/2010

1,2,4-Trichlorobenzene 2 6/5/2010

1,2,4-Trichlorobenzene 3 6/5/2010

1,2,4-Trimethylbenzene 1 6/5/2010

1,2,4-Trimethylbenzene 2 6/5/2010

1,2,4-Trimethylbenzene 3 6/5/2010

1,2-Dibromo-3-chloropropane 1 6/5/2010

1,2-Dibromo-3-chloropropane 2 6/5/2010

1,2-Dibromo-3-chloropropane 3 6/5/2010

1,2-Dibromoethane 1 6/5/2010

1,2-Dibromoethane 2 6/5/2010

1,2-Dibromoethane 3 6/5/2010

1,2-Dichlorobenzene 1 6/5/2010

1,2-Dichlorobenzene 2 6/5/2010

1,2-Dichlorobenzene 3 6/5/2010

1,2-Dichloroethane 1 6/5/2010

1,2-Dichloroethane 2 6/5/2010

1,2-Dichloroethane 3 6/5/2010

1,2-Dichloropropane 1 6/5/2010

1,2-Dichloropropane 2 6/5/2010

Compound 

(use drop down to define for as many rows as 

needed)

Run Number Test Start Date
1,2-Dichloropropane

3 6/5/2010

1,3,5-Trimethylbenzene1 6/5/2010

1,3,5-Trimethylbenzene2 6/5/2010

1,3,5-Trimethylbenzene3 6/5/2010

1,3-Dichlorobenzene1 6/5/2010

1,3-Dichlorobenzene2 6/5/2010

1,3-Dichlorobenzene3 6/5/2010

1,3-Dichloropropane1 6/5/2010

1,3-Dichloropropane2 6/5/2010

1,3-Dichloropropane3 6/5/2010

1,4-Dichlorobenzene1 6/5/2010

1,4-Dichlorobenzene2 6/5/2010

1,4-Dichlorobenzene3 6/5/2010

2,2-Dichloropropane1 6/5/2010

2,2-Dichloropropane2 6/5/2010

2,2-Dichloropropane3 6/5/2010

2-Butanone1 6/5/2010

2-Butanone2 6/5/2010

2-Butanone3 6/5/2010

2-Chlorotoluene1 6/5/2010

2-Chlorotoluene2 6/5/2010

2-Chlorotoluene3 6/5/2010

2-Hexanone1 6/5/2010

2-Hexanone2 6/5/2010

2-Hexanone3 6/5/2010

4-Chlorotoluene1 6/5/2010

4-Chlorotoluene2 6/5/2010

4-Chlorotoluene3 6/5/2010

4-Methyl-2-pentanone1 6/5/2010

4-Methyl-2-pentanone2 6/5/2010

4-Methyl-2-pentanone3 6/5/2010

Acetone1 6/5/2010

Acetone2 6/5/2010

Acetone3 6/5/2010

Benzene1 6/5/2010

Benzene2 6/5/2010

Benzene3 6/5/2010

Bromobenzene1 6/5/2010

Bromobenzene2 6/5/2010

Bromobenzene3 6/5/2010

Bromochloromethane1 6/5/2010

Bromochloromethane2 6/5/2010

Bromochloromethane3 6/5/2010

Bromodichloromethane1 6/5/2010

Bromodichloromethane2 6/5/2010

Bromodichloromethane3 6/5/2010

Bromoform1 6/5/2010

Bromoform2 6/5/2010

Bromoform3 6/5/2010

Bromomethane1 6/5/2010

Bromomethane2 6/5/2010

Bromomethane3 6/5/2010

Carbon disulfide1 6/5/2010

Carbon disulfide2 6/5/2010

Carbon disulfide3 6/5/2010
Carbon tetrachloride

1 6/5/2010

Carbon tetrachloride2 6/5/2010

Carbon tetrachloride3 6/5/2010

Chlorobenzene1 6/5/2010

Chlorobenzene2 6/5/2010

Chlorobenzene3 6/5/2010

Chlorodibromomethane1 6/5/2010

Chlorodibromomethane2 6/5/2010

Chlorodibromomethane3 6/5/2010

Chloroethane1 6/5/2010

Chloroethane2 6/5/2010

Chloroethane3 6/5/2010

Chloroform1 6/5/2010

Chloroform2 6/5/2010

Chloroform3 6/5/2010

Chloromethane1 6/5/2010

Chloromethane2 6/5/2010

Chloromethane3 6/5/2010

cis-1,2-Dichloroethene1 6/5/2010

cis-1,2-Dichloroethene2 6/5/2010

cis-1,2-Dichloroethene3 6/5/2010

cis-1,3-Dichloropropene1 6/5/2010

cis-1,3-Dichloropropene2 6/5/2010

cis-1,3-Dichloropropene3 6/5/2010

Dibromomethane1 6/5/2010

Dibromomethane2 6/5/2010

Dibromomethane3 6/5/2010

Dichlorodifluoromethane1 6/5/2010

Dichlorodifluoromethane2 6/5/2010

Dichlorodifluoromethane3 6/5/2010

Ethylbenzene1 6/5/2010

Ethylbenzene2 6/5/2010

Ethylbenzene3 6/5/2010

Hexachlorobutadiene1 6/5/2010

Hexachlorobutadiene2 6/5/2010

Hexachlorobutadiene3 6/5/2010

Isopropylbenzene1 6/5/2010

Isopropylbenzene2 6/5/2010

Isopropylbenzene3 6/5/2010

Methylene chloride1 6/5/2010

Methylene chloride2 6/5/2010

Methylene chloride3 6/5/2010

m-Xylene & p-Xylene1 6/5/2010

m-Xylene & p-Xylene2 6/5/2010

m-Xylene & p-Xylene3 6/5/2010

Naphthalene1 6/5/2010

Naphthalene2 6/5/2010

Naphthalene3 6/5/2010

n-Butylbenzene1 6/5/2010

n-Butylbenzene2 6/5/2010

n-Butylbenzene3 6/5/2010

n-Propylbenzene1 6/5/2010

n-Propylbenzene2 6/5/2010

n-Propylbenzene3 6/5/2010

o-Xylene1 6/5/2010
o-Xylene

2 6/5/2010

o-Xylene3 6/5/2010

p-Isopropyltoluene1 6/5/2010

p-Isopropyltoluene2 6/5/2010

p-Isopropyltoluene3 6/5/2010

sec-Butylbenzene1 6/5/2010

sec-Butylbenzene2 6/5/2010

sec-Butylbenzene3 6/5/2010

Styrene1 6/5/2010

Styrene2 6/5/2010

Styrene3 6/5/2010

tert-Butylbenzene1 6/5/2010

tert-Butylbenzene2 6/5/2010

tert-Butylbenzene3 6/5/2010

Tetrachloroethene1 6/5/2010

Tetrachloroethene2 6/5/2010

Tetrachloroethene3 6/5/2010

Toluene1 6/5/2010

Toluene2 6/5/2010

Toluene3 6/5/2010

trans-1,2-Dichloroethene1 6/5/2010

trans-1,2-Dichloroethene2 6/5/2010

trans-1,2-Dichloroethene3 6/5/2010

trans-1,3-Dichloropropene1 6/5/2010

trans-1,3-Dichloropropene2 6/5/2010

trans-1,3-Dichloropropene3 6/5/2010

Trichloroethene1 6/5/2010

Trichloroethene2 6/5/2010

Trichloroethene3 6/5/2010

Trichlorofluoromethane1 6/5/2010

Trichlorofluoromethane2 6/5/2010

Trichlorofluoromethane3 6/5/2010

Vinyl chloride1 6/5/2010

Vinyl chloride2 6/5/2010

Vinyl chloride3 6/5/2010




Measured Value (μg/m3 

@ 7% O2)

8:40 AM 6/5/2010 10:17 AM [< 0.122]

11:35 AM 6/5/2010 1:15 PM [< 0.108]

2:27 PM 6/5/2010 4:13 PM [< 0.12]

8:40 AM 6/5/2010 10:17 AM [< 0.111]

11:35 AM 6/5/2010 1:15 PM [< 0.098]

2:27 PM 6/5/2010 4:13 PM [< 0.109]

8:40 AM 6/5/2010 10:17 AM [< 0.32]

11:35 AM 6/5/2010 1:15 PM [< 0.284]

2:27 PM 6/5/2010 4:13 PM [< 0.315]

8:40 AM 6/5/2010 10:17 AM [< 1.159]

11:35 AM 6/5/2010 1:15 PM [< 0.979]

2:27 PM 6/5/2010 4:13 PM [< 1.088]

8:40 AM 6/5/2010 10:17 AM [< 0.111]

11:35 AM 6/5/2010 1:15 PM [< 0.098]

2:27 PM 6/5/2010 4:13 PM [< 0.109]

8:40 AM 6/5/2010 10:17 AM [< 0.166]

11:35 AM 6/5/2010 1:15 PM [< 0.147]

2:27 PM 6/5/2010 4:13 PM [< 0.163]

8:40 AM 6/5/2010 10:17 AM [< 0.111]

11:35 AM 6/5/2010 1:15 PM [< 0.098]

2:27 PM 6/5/2010 4:13 PM [< 0.109]

8:40 AM 6/5/2010 10:17 AM [< 0.111]

11:35 AM 6/5/2010 1:15 PM [< 0.098]

2:27 PM 6/5/2010 4:13 PM [< 0.109]

8:40 AM 6/5/2010 10:17 AM [< 2.756]

11:35 AM 6/5/2010 1:15 PM [< 2.214]

2:27 PM 6/5/2010 4:13 PM [< 2.719]

8:40 AM 6/5/2010 10:17 AM [< 0.177]

11:35 AM 6/5/2010 1:15 PM [< 0.157]

2:27 PM 6/5/2010 4:13 PM [< 0.174]

8:40 AM 6/5/2010 10:17 AM [< 0.192]

11:35 AM 6/5/2010 1:15 PM [< 0.147]

2:27 PM 6/5/2010 4:13 PM [< 0.163]

8:40 AM 6/5/2010 10:17 AM [< 1.432]

11:35 AM 6/5/2010 1:15 PM [< 1.272]

2:27 PM 6/5/2010 4:13 PM [< 1.414]

8:40 AM 6/5/2010 10:17 AM [< 0.155]

11:35 AM 6/5/2010 1:15 PM [< 0.207]

2:27 PM 6/5/2010 4:13 PM [< 0.152]

8:40 AM 6/5/2010 10:17 AM [< 0.199]

11:35 AM 6/5/2010 1:15 PM [< 0.176]

2:27 PM 6/5/2010 4:13 PM [< 0.196]

8:40 AM 6/5/2010 10:17 AM [< 0.27]

11:35 AM 6/5/2010 1:15 PM [< 0.879]

2:27 PM 6/5/2010 4:13 PM [< 0.185]

8:40 AM 6/5/2010 10:17 AM [< 0.188]

11:35 AM 6/5/2010 1:15 PM [< 0.166]

Test Start Time Test End Date Test End Time
2:27 PM 6/5/2010 4:13 PM [< 0.185]

8:40 AM 6/5/2010 10:17 AM [< 0.256]

11:35 AM 6/5/2010 1:15 PM [< 0.176]

2:27 PM 6/5/2010 4:13 PM [< 0.196]

8:40 AM 6/5/2010 10:17 AM [< 0.155]

11:35 AM 6/5/2010 1:15 PM [< 0.137]

2:27 PM 6/5/2010 4:13 PM [< 0.152]

8:40 AM 6/5/2010 10:17 AM [< 0.155]

11:35 AM 6/5/2010 1:15 PM [< 0.137]

2:27 PM 6/5/2010 4:13 PM [< 0.152]

8:40 AM 6/5/2010 10:17 AM [< 0.168]

11:35 AM 6/5/2010 1:15 PM [< 0.147]

2:27 PM 6/5/2010 4:13 PM [< 0.174]

8:40 AM 6/5/2010 10:17 AM [< 0.111]

11:35 AM 6/5/2010 1:15 PM [< 0.098]

2:27 PM 6/5/2010 4:13 PM [< 0.109]

8:40 AM 6/5/2010 10:17 AM [< 11.009]

11:35 AM 6/5/2010 1:15 PM [< 9.788]

2:27 PM 6/5/2010 4:13 PM [< 10.877]

8:40 AM 6/5/2010 10:17 AM [< 0.133]

11:35 AM 6/5/2010 1:15 PM [< 0.117]

2:27 PM 6/5/2010 4:13 PM [< 0.131]

8:40 AM 6/5/2010 10:17 AM [< 0.749]

11:35 AM 6/5/2010 1:15 PM [< 0.666]

2:27 PM 6/5/2010 4:13 PM [< 0.74]

8:40 AM 6/5/2010 10:17 AM [< 0.155]

11:35 AM 6/5/2010 1:15 PM [< 0.137]

2:27 PM 6/5/2010 4:13 PM [< 0.152]

8:40 AM 6/5/2010 10:17 AM [< 11.009]

11:35 AM 6/5/2010 1:15 PM [< 9.788]

2:27 PM 6/5/2010 4:13 PM [< 10.877]

8:40 AM 6/5/2010 10:17 AM 100.137

11:35 AM 6/5/2010 1:15 PM [< 59.33]

2:27 PM 6/5/2010 4:13 PM 80.918

8:40 AM 6/5/2010 10:17 AM [< 4.177]

11:35 AM 6/5/2010 1:15 PM [< 6.371]

2:27 PM 6/5/2010 4:13 PM [< 3.685]

8:40 AM 6/5/2010 10:17 AM [< 0.222]

11:35 AM 6/5/2010 1:15 PM [< 0.196]

2:27 PM 6/5/2010 4:13 PM [< 0.218]

8:40 AM 6/5/2010 10:17 AM [< 0.309]

11:35 AM 6/5/2010 1:15 PM [< 0.274]

2:27 PM 6/5/2010 4:13 PM [< 0.305]

8:40 AM 6/5/2010 10:17 AM [< 0.149]

11:35 AM 6/5/2010 1:15 PM [< 0.127]

2:27 PM 6/5/2010 4:13 PM [< 0.141]

8:40 AM 6/5/2010 10:17 AM [< 1.104]

11:35 AM 6/5/2010 1:15 PM [< 0.979]

2:27 PM 6/5/2010 4:13 PM [< 1.088]

8:40 AM 6/5/2010 10:17 AM [< 8.491]

11:35 AM 6/5/2010 1:15 PM [< 8.925]

2:27 PM 6/5/2010 4:13 PM [< 5.962]

8:40 AM 6/5/2010 10:17 AM [< 2.135]

11:35 AM 6/5/2010 1:15 PM [< 1.534]

2:27 PM 6/5/2010 4:13 PM [< 2.085]
8:40 AM 6/5/2010 10:17 AM [< 0.176]

11:35 AM 6/5/2010 1:15 PM [< 0.144]

2:27 PM 6/5/2010 4:13 PM [< 0.168]

8:40 AM 6/5/2010 10:17 AM [< 0.119]

11:35 AM 6/5/2010 1:15 PM [< 0.163]

2:27 PM 6/5/2010 4:13 PM [< 0.332]

8:40 AM 6/5/2010 10:17 AM [< 0.221]

11:35 AM 6/5/2010 1:15 PM [< 0.196]

2:27 PM 6/5/2010 4:13 PM [< 0.218]

8:40 AM 6/5/2010 10:17 AM [< 0.684]

11:35 AM 6/5/2010 1:15 PM [< 0.607]

2:27 PM 6/5/2010 4:13 PM [< 0.674]

8:40 AM 6/5/2010 10:17 AM [< 0.156]

11:35 AM 6/5/2010 1:15 PM [< 0.204]

2:27 PM 6/5/2010 4:13 PM [< 0.205]

8:40 AM 6/5/2010 10:17 AM [< 16.831]

11:35 AM 6/5/2010 1:15 PM [< 12.684]

2:27 PM 6/5/2010 4:13 PM [< 24.326]

8:40 AM 6/5/2010 10:17 AM [< 0.111]

11:35 AM 6/5/2010 1:15 PM [< 0.098]

2:27 PM 6/5/2010 4:13 PM [< 0.109]

8:40 AM 6/5/2010 10:17 AM [< 0.188]

11:35 AM 6/5/2010 1:15 PM [< 0.166]

2:27 PM 6/5/2010 4:13 PM [< 0.185]

8:40 AM 6/5/2010 10:17 AM [< 0.237]

11:35 AM 6/5/2010 1:15 PM [< 0.206]

2:27 PM 6/5/2010 4:13 PM [< 0.228]

8:40 AM 6/5/2010 10:17 AM [< 1.082]

11:35 AM 6/5/2010 1:15 PM [< 0.766]

2:27 PM 6/5/2010 4:13 PM [< 0.97]

8:40 AM 6/5/2010 10:17 AM [< 0.154]

11:35 AM 6/5/2010 1:15 PM [< 0.152]

2:27 PM 6/5/2010 4:13 PM [< 0.162]

8:40 AM 6/5/2010 10:17 AM [< 0.276]

11:35 AM 6/5/2010 1:15 PM [< 0.279]

2:27 PM 6/5/2010 4:13 PM [< 0.272]

8:40 AM 6/5/2010 10:17 AM [< 0.111]

11:35 AM 6/5/2010 1:15 PM [< 0.098]

2:27 PM 6/5/2010 4:13 PM [< 0.109]

8:40 AM 6/5/2010 10:17 AM 12.256

11:35 AM 6/5/2010 1:15 PM [< 16.905]

2:27 PM 6/5/2010 4:13 PM 10.841

8:40 AM 6/5/2010 10:17 AM [< 0.45]

11:35 AM 6/5/2010 1:15 PM [< 0.455]

2:27 PM 6/5/2010 4:13 PM [< 0.428]

8:40 AM 6/5/2010 10:17 AM [< 1.102]

11:35 AM 6/5/2010 1:15 PM [< 0.979]

2:27 PM 6/5/2010 4:13 PM [< 1.088]

8:40 AM 6/5/2010 10:17 AM [< 0.111]

11:35 AM 6/5/2010 1:15 PM [< 0.098]

2:27 PM 6/5/2010 4:13 PM [< 0.109]

8:40 AM 6/5/2010 10:17 AM [< 0.111]

11:35 AM 6/5/2010 1:15 PM [< 0.098]

2:27 PM 6/5/2010 4:13 PM [< 0.109]

8:40 AM 6/5/2010 10:17 AM [< 0.177]
11:35 AM 6/5/2010 1:15 PM [< 0.193]

2:27 PM 6/5/2010 4:13 PM [< 0.202]

8:40 AM 6/5/2010 10:17 AM [< 0.157]

11:35 AM 6/5/2010 1:15 PM [< 0.137]

2:27 PM 6/5/2010 4:13 PM [< 0.157]

8:40 AM 6/5/2010 10:17 AM [< 0.111]

11:35 AM 6/5/2010 1:15 PM [< 0.098]

2:27 PM 6/5/2010 4:13 PM [< 0.109]

8:40 AM 6/5/2010 10:17 AM [< 0.157]

11:35 AM 6/5/2010 1:15 PM [< 0.158]

2:27 PM 6/5/2010 4:13 PM [< 0.141]

8:40 AM 6/5/2010 10:17 AM [< 0.125]

11:35 AM 6/5/2010 1:15 PM [< 0.108]

2:27 PM 6/5/2010 4:13 PM [< 0.12]

8:40 AM 6/5/2010 10:17 AM [< 0.122]

11:35 AM 6/5/2010 1:15 PM [< 0.108]

2:27 PM 6/5/2010 4:13 PM [< 0.12]

8:40 AM 6/5/2010 10:17 AM 10.744

11:35 AM 6/5/2010 1:15 PM [< 11.507]

2:27 PM 6/5/2010 4:13 PM 12.342

8:40 AM 6/5/2010 10:17 AM [< 0.221]

11:35 AM 6/5/2010 1:15 PM [< 0.196]

2:27 PM 6/5/2010 4:13 PM [< 0.218]

8:40 AM 6/5/2010 10:17 AM [< 0.133]

11:35 AM 6/5/2010 1:15 PM [< 0.117]

2:27 PM 6/5/2010 4:13 PM [< 0.131]

8:40 AM 6/5/2010 10:17 AM [< 0.243]

11:35 AM 6/5/2010 1:15 PM [< 0.215]

2:27 PM 6/5/2010 4:13 PM [< 0.239]

8:40 AM 6/5/2010 10:17 AM [< 0.37]

11:35 AM 6/5/2010 1:15 PM [< 0.421]

2:27 PM 6/5/2010 4:13 PM [< 0.312]

8:40 AM 6/5/2010 10:17 AM [< 0.249]

11:35 AM 6/5/2010 1:15 PM [< 0.206]

2:27 PM 6/5/2010 4:13 PM [< 0.228]




Footnotes:

* Front half fraction contains filter, cyclone, and cartridge

** Back half fraction contains condensate, solvent, impingers

Basis Test Method Used Data Flag (ADL, BDL, 

DDL) Front Half Mass (ng)

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7.7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 23.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 20.3]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 23.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 80]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 70]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 80]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 12]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 10.5]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 12]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 200]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 158.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 200]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 12.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 12.8]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 13.9]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 10.5]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 12]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 104]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 91]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 104]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.2]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 14.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 14.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 12.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 14.4]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 19.6]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 63.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 13.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 13.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.9]
Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 13.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 14.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 12.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 14.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 9.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 9.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.2]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 12.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 10.5]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 12.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 800]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 700]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 800]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 9.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 9.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 54.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 47.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 54.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 9.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.2]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 800]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 700]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 800]

Dry U.S. EPA Method 0031 with SW ADL -846 Method 8260B 6600

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 3420]

Dry U.S. EPA Method 0031 with SW ADL -846 Method 8260B 5007

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 303]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 458.2]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 272.3]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 16]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 14]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 16]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 22.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 19.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 22.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 10.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 9.1]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 10.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 80]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 70]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 80]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 617]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 641.9]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 440.6]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 155.1]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 110.3]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 154.1]
Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 12.7]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 10.3]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 12.4]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 8.6]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 11.7]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 24.5]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 16]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 14]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 16]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 49.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 43.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 49.6]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 8.8]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 12.5]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 13.2]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 1223]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 912.5]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 1798.5]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 13.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 11.9]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 13.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 16.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 14.7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 16.8]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 78.6]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 55]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 71.6]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 11.1]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 10.9]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 11.9]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 20]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 20]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 20]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW ADL -846 Method 8260B 641

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 970.2]

Dry U.S. EPA Method 0031 with SW ADL -846 Method 8260B 547

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 27.2]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 26.4]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 25.3]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 80]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 70]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 80]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 8.6]
Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 8.8]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 9.4]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 11.4]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 9.8]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 11.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 11.3]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 11.3]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 10.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7.7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 7.7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8.8]

Dry U.S. EPA Method 0031 with SW ADL -846 Method 8260B 103.7

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 106.6]

Dry U.S. EPA Method 0031 with SW ADL -846 Method 8260B 148.8

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 16]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 14]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 16]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 9.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 8.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 9.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 17.6]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 15.4]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 17.6]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 26.5]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 30.2]

Dry U.S. EPA Method 0031 with SW DLL, Reporting limit based on MDL -846 Method 8260B [< 23]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 16.8]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 14.7]

Dry U.S. EPA Method 0031 with SW BDL, Reporting limit based on MDL -846 Method 8260B [< 16.8]




Back Half Mass (ng) Total Mass (ng) Test Method Comments lb/mmBtu

[< 0.071944] [< 8.871944] [< 0.0000001114]

[< 0.046673] [< 7.746673] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000982] sis and no results w

[< 0.046673] [< 8.846673] [< 0.0000001086]

[< 0.04232] [< 8.04232] [< 0.000000101]

[< 0.04243] [< 7.04243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000893] sis and no results w

[< 0.04243] [< 8.04243] [< 0.0000000987]

[< 0.071944] [< 23.271944] [< 0.0000002922]

[< 0.123047] [< 20.423047] Run 2 pair B anasorb tube was damaged during analy [< 0.000000259] sis and no results w

[< 0.123047] [< 23.323047] [< 0.0000002863]

[< 4.232] [< 84.232] [< 0.0000010575]

[< 0.4243] [< 70.4243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000008931] sis and no results w

[< 0.4243] [< 80.4243] [< 0.0000009872]

[< 0.04232] [< 8.04232] [< 0.000000101]

[< 0.04243] [< 7.04243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000893] sis and no results w

[< 0.04243] [< 8.04243] [< 0.0000000987]

[< 0.046552] [< 12.046552] [< 0.0000001512]

[< 0.063645] [< 10.563645] Run 2 pair B anasorb tube was damaged during analy [< 0.000000134] sis and no results w

[< 0.063645] [< 12.063645] [< 0.0000001481]

[< 0.071944] [< 8.071944] [< 0.0000001013]

[< 0.04243] [< 7.04243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000893] sis and no results w

[< 0.04243] [< 8.04243] [< 0.0000000987]

[< 0.059248] [< 8.059248] [< 0.0000001012]

[< 0.04243] [< 7.04243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000893] sis and no results w

[< 0.04243] [< 8.04243] [< 0.0000000987]

[< 0.287776] [< 200.287776] [< 0.0000025145]

[< 1.06075] [< 159.26075] Run 2 pair B anasorb tube was damaged during analy [< 0.0000020196] sis and no results w

[< 1.06075] [< 201.06075] [< 0.0000024679]

[< 0.06348] [< 12.86348] [< 0.0000001615]

[< 0.067888] [< 11.267888] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001429] sis and no results w

[< 0.067888] [< 12.867888] [< 0.0000001579]

[< 0.059248] [< 13.959248] [< 0.0000001753]

[< 0.063645] [< 10.563645] Run 2 pair B anasorb tube was damaged during analy [< 0.000000134] sis and no results w

[< 0.063645] [< 12.063645] [< 0.0000001481]

[< 0.088872] [< 104.088872] [< 0.0000013068]

[< 0.55159] [< 91.55159] Run 2 pair B anasorb tube was damaged during analy [< 0.000001161] sis and no results w

[< 0.55159] [< 104.55159] [< 0.0000012833]

[< 0.08464] [< 11.28464] [< 0.0000001417]

[< 0.059402] [< 14.859402] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001884] sis and no results w

[< 0.059402] [< 11.259402] [< 0.0000001382]

[< 0.04232] [< 14.44232] [< 0.0000001813]

[< 0.076374] [< 12.676374] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001607] sis and no results w

[< 0.076374] [< 14.476374] [< 0.0000001777]

[< 0.055016] [< 19.655016] [< 0.0000002468]

[< 0.072131] [< 63.272131] Run 2 pair B anasorb tube was damaged during analy [< 0.0000008024] sis and no results w

[< 0.072131] [< 13.672131] [< 0.0000001678]

[< 0.08464] [< 13.68464] [< 0.0000001718]

[< 0.072131] [< 11.972131] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001518] sis and no results w

Calculated Emission Rate
[< 0.072131] [< 13.672131] [< 0.0000001678]

[< 4.232] [< 18.632] [< 0.0000002339]

[< 0.076374] [< 12.676374] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001607] sis and no results w

[< 0.076374] [< 14.476374] [< 0.0000001777]

[< 0.04232] [< 11.24232] [< 0.0000001411]

[< 0.059402] [< 9.859402] Run 2 pair B anasorb tube was damaged during analy [< 0.000000125] sis and no results w

[< 0.059402] [< 11.259402] [< 0.0000001382]

[< 0.050784] [< 11.250784] [< 0.0000001412]

[< 0.059402] [< 9.859402] Run 2 pair B anasorb tube was damaged during analy [< 0.000000125] sis and no results w

[< 0.059402] [< 11.259402] [< 0.0000001382]

[< 0.04232] [< 12.24232] [< 0.0000001537]

[< 0.063645] [< 10.563645] Run 2 pair B anasorb tube was damaged during analy [< 0.000000134] sis and no results w

[< 0.063645] [< 12.863645] [< 0.0000001579]

[< 0.093104] [< 8.093104] [< 0.0000001016]

[< 0.04243] [< 7.04243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000893] sis and no results w

[< 0.04243] [< 8.04243] [< 0.0000000987]

[< 0.050784] [< 800.050784] [< 0.0000100443]

[< 4.243] [< 704.243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000089305] sis and no results w

[< 4.243] [< 804.243] [< 0.0000098717]

[< 0.04232] [< 9.64232] [< 0.0000001211]

[< 0.050916] [< 8.450916] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001072] sis and no results w

[< 0.050916] [< 9.650916] [< 0.0000001185]

[< 0.06348] [< 54.46348] [< 0.0000006838]

[< 0.288524] [< 47.888524] Run 2 pair B anasorb tube was damaged during analy [< 0.0000006073] sis and no results w

[< 0.288524] [< 54.688524] [< 0.0000006713]

[< 0.093104] [< 11.293104] [< 0.0000001418]

[< 0.059402] [< 9.859402] Run 2 pair B anasorb tube was damaged during analy [< 0.000000125] sis and no results w

[< 0.059402] [< 11.259402] [< 0.0000001382]

[< 0.067712] [< 800.067712] [< 0.0000100445]

[< 4.243] [< 704.243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000089305] sis and no results w

[< 4.243] [< 804.243] [< 0.0000098717]

677.12 7277.12 Method Blank Contamination 9.14E-05

848.6 [< 4268.6] Run 2 pair B anasorb tube was damaged during analy [< 0.0000541302] sis and no results w

975.89 5982.89 Method Blank Contamination 6.18E-05

[< 0.55016] [< 303.55016] [< 0.0000038109]

[< 0.148505] [< 458.348505] Run 2 pair B anasorb tube was damaged during analy [< 0.0000058123] sis and no results w

[< 0.148505] [< 272.448505] [< 0.0000033601]

[< 0.118496] [< 16.118496] [< 0.0000002024]

[< 0.08486] [< 14.08486] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001786] sis and no results w

[< 0.08486] [< 16.08486] [< 0.0000001974]

[< 0.055016] [< 22.455016] [< 0.0000002819]

[< 0.118804] [< 19.718804] Run 2 pair B anasorb tube was damaged during analy [< 0.0000002501] sis and no results w

[< 0.118804] [< 22.518804] [< 0.0000002764]

[< 0.4232] [< 10.8232] [< 0.0000001359]

[< 0.055159] [< 9.155159] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001161] sis and no results w

[< 0.055159] [< 10.455159] [< 0.0000001283]

[< 0.249688] [< 80.249688] [< 0.0000010075]

[< 0.4243] [< 70.4243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000008931] sis and no results w

[< 0.4243] [< 80.4243] [< 0.0000009872]

[< 0.080408] [< 617.080408] [< 0.0000077472]

[< 0.250337] [< 642.150337] Run 2 pair B anasorb tube was damaged during analy [< 0.0000081431] sis and no results w

[< 0.250337] [< 440.850337] [< 0.0000054368]

[< 0.046552] [< 155.146552] [< 0.0000019478]

[< 0.080617] [< 110.380617] Run 2 pair B anasorb tube was damaged during analy [< 0.0000013997] sis and no results w

[< 0.080617] [< 154.180617] [< 0.0000019015]
[< 0.1058] [< 12.8058] [< 0.0000001608]

[< 0.050916] [< 10.350916] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001313] sis and no results w

[< 0.050916] [< 12.450916] [< 0.000000153]

[< 0.04232] [< 8.64232] [< 0.0000001085]

[< 0.04243] [< 11.74243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001489] sis and no results w

[< 0.04243] [< 24.54243] [< 0.0000003023]

[< 0.071944] [< 16.071944] [< 0.0000002018]

[< 0.08486] [< 14.08486] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001786] sis and no results w

[< 0.08486] [< 16.08486] [< 0.0000001974]

[< 0.101568] [< 49.701568] [< 0.000000624]

[< 0.263066] [< 43.663066] Run 2 pair B anasorb tube was damaged during analy [< 0.0000005537] sis and no results w

[< 0.263066] [< 49.863066] [< 0.000000612]

[< 2.5392] [< 11.3392] [< 0.0000001424]

[< 2.20636] [< 14.70636] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001865] sis and no results w

[< 1.95178] [< 15.15178] [< 0.0000001629]

[< 0.1058] [< 1223.1058] Method Blank Contamination [< 0.0000153556]

[< 0.106075] [< 912.606075] Run 2 pair B anasorb tube was damaged during analy [< 0.0000115728] sis and no results w

[< 0.106075] [< 1798.606075] Method Blank Contamination [< 0.0000221928]

[< 0.046552] [< 8.046552] [< 0.000000101]

[< 0.04243] [< 7.04243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000893] sis and no results w

[< 0.04243] [< 8.04243] [< 0.0000000987]

[< 0.088872] [< 13.688872] [< 0.0000001719]

[< 0.072131] [< 11.972131] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001518] sis and no results w

[< 0.072131] [< 13.672131] [< 0.0000001678]

[< 0.4232] [< 17.2232] [< 0.0000002162]

[< 0.089103] [< 14.789103] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001875] sis and no results w

[< 0.089103] [< 16.889103] [< 0.0000002073]

[< 0.04232] [< 78.64232] [< 0.0000009873]

[< 0.101832] [< 55.101832] Run 2 pair B anasorb tube was damaged during analy [< 0.0000006987] sis and no results w

[< 0.101832] [< 71.701832] [< 0.0000008835]

[< 0.122728] [< 11.222728] [< 0.0000001409]

[< 0.04243] [< 10.94243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001388] sis and no results w

[< 0.04243] [< 11.94243] [< 0.0000001468]

[< 0.04232] [< 20.04232] [< 0.0000002516]

[< 0.106075] [< 20.106075] Run 2 pair B anasorb tube was damaged during analy [< 0.000000255] sis and no results w

[< 0.106075] [< 20.106075] [< 0.0000002468]

[< 0.04232] [< 8.04232] [< 0.000000101]

[< 0.04243] [< 7.04243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000893] sis and no results w

[< 0.04243] [< 8.04243] [< 0.0000000987]

249.688 890.688 Method Blank Contamination 1.12E-05

246.094 [< 1216.294] Run 2 pair B anasorb tube was damaged during analy [< 0.0000154239] sis and no results w

254.58 801.58 Method Blank Contamination 6.75E-06

[< 5.5016] [< 32.7016] [< 0.0000004106]

[< 6.3645] [< 32.7645] Run 2 pair B anasorb tube was damaged during analy [< 0.0000004155] sis and no results w

[< 6.3645] [< 31.6645] [< 0.0000003122]

[< 0.06348] [< 80.06348] [< 0.0000010052]

[< 0.4243] [< 70.4243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000008931] sis and no results w

[< 0.4243] [< 80.4243] [< 0.0000009872]

[< 0.04232] [< 8.04232] [< 0.000000101]

[< 0.04243] [< 7.04243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000893] sis and no results w

[< 0.04243] [< 8.04243] [< 0.0000000987]

[< 0.059248] [< 8.059248] [< 0.0000001012]

[< 0.04243] [< 7.04243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000893] sis and no results w

[< 0.04243] [< 8.04243] [< 0.0000000987]

[< 4.232] [< 12.832] [< 0.0000001611]
[< 5.0916] [< 13.8916] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001762] sis and no results w

[< 5.5159] [< 14.9159] [< 0.000000116]

[< 0.04232] [< 11.44232] [< 0.0000001437]

[< 0.04243] [< 9.84243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001248] sis and no results w

[< 0.04243] [< 11.64243] [< 0.0000001431]

[< 0.08464] [< 8.08464] [< 0.0000001015]

[< 0.04243] [< 7.04243] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000893] sis and no results w

[< 0.04243] [< 8.04243] [< 0.0000000987]

[< 0.076176] [< 11.376176] [< 0.0000001428]

[< 0.055159] [< 11.355159] Run 2 pair B anasorb tube was damaged during analy [< 0.000000144] sis and no results w

[< 0.055159] [< 10.455159] [< 0.0000001283]

[< 0.262384] [< 9.062384] [< 0.0000001138]

[< 0.046673] [< 7.746673] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000982] sis and no results w

[< 0.046673] [< 8.846673] [< 0.0000001086]

[< 0.076176] [< 8.876176] [< 0.0000001114]

[< 0.046673] [< 7.746673] Run 2 pair B anasorb tube was damaged during analy [< 0.0000000982] sis and no results w

[< 0.046673] [< 8.846673] [< 0.0000001086]

677.12 780.82 Method Blank Contamination 9.80E-06

721.31 [< 827.91] Run 2 pair B anasorb tube was damaged during analy [< 0.0000104988] sis and no results w

763.74 912.54 Method Blank Contamination 1.84E-06

[< 0.04232] [< 16.04232] [< 0.0000002014]

[< 0.08486] [< 14.08486] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001786] sis and no results w

[< 0.08486] [< 16.08486] [< 0.0000001974]

[< 0.046552] [< 9.646552] [< 0.0000001211]

[< 0.050916] [< 8.450916] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001072] sis and no results w

[< 0.050916] [< 9.650916] [< 0.0000001185]

[< 0.050784] [< 17.650784] [< 0.0000002216]

[< 0.093346] [< 15.493346] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001965] sis and no results w

[< 0.093346] [< 17.693346] [< 0.0000002172]

[< 0.4232] [< 26.9232] [< 0.000000338]

[< 0.072131] [< 30.272131] Run 2 pair B anasorb tube was damaged during analy [< 0.0000003839] sis and no results w

[< 0.072131] [< 23.072131] [< 0.0000002838]

[< 1.2696] [< 18.0696] [< 0.0000002269]

[< 0.089103] [< 14.789103] Run 2 pair B anasorb tube was damaged during analy [< 0.0000001875] sis and no results w

[< 0.089103] [< 16.889103] [< 0.0000002073]




ug/dscm @ 7% O2

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

alculated Emission Rate

Steam Output (1000 

lb/hr)

Total Heat Input 

(mmBtu/hr) Flue Gas Moisture (%)
9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85
9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85
9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85

9.85

9.95

9.85




12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

Flue Gas CO2 (%) Flue Gas O2 (%) Flue Gas Flow Rate 

(scfm)

Flue Gas Temperature 

(F)
12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15
12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05
12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15

12.13 7.3 1,276,364 274.05

12.16 7.32 1,280,315 277.65

12.12 7.28 1,181,530 277.15




Fuel Input Rate Fuel Type Units of Measure Measurement Method

Fuel #1







Fuel Input Rate Fuel Type Units of Measure Measurement Method

Fuel #2







Fuel Input Rate Fuel Type Units of Measure Measurement Method

Fuel #3







Fuel Input Rate Fuel Type Units of Measure Measurement Method

Fuel #4







Other Supporting 

Information







EIA Facility Code Facility Name

IN_Wabash River Station Wabash River Station

Speciated Semi-Volatile Organic HAP Emission Data

Acenaphthene 1

Acenaphthene 2

Acenaphthene 3

Acenaphthylene 1

Acenaphthylene 2

Acenaphthylene 3

Anthracene 1

Anthracene 2

Anthracene 3

Benzo(a)anthracene 1

Benzo(a)anthracene 2

Benzo(a)anthracene 3

Benzo(b)fluoranthene 1

Benzo(b)fluoranthene 2

Benzo(b)fluoranthene 3

Benzo(k)fluoranthene 1

Benzo(k)fluoranthene 2

Benzo(k)fluoranthene 3

Benzo(ghi)perylene 1

Benzo(ghi)perylene 2

Benzo(ghi)perylene 3

Benzo(a)pyrene 1

Benzo(a)pyrene 2

Benzo(a)pyrene 3

Benzo(e)pyrene 1

Benzo(e)pyrene 2

Benzo(e)pyrene 3

Chrysene 1

Chrysene 2

Chrysene 3

Dibenz(a,h)anthracene 1

Dibenz(a,h)anthracene 2

Dibenz(a,h)anthracene 3

Fluoranthene 1

Fluoranthene 2

Fluoranthene 3

Fluorene 1

Fluorene 2

Fluorene 3

Indeno(1,2,3-cd)pyrene 1

Indeno(1,2,3-cd)pyrene 2

Indeno(1,2,3-cd)pyrene 3

2-Methylnaphthalene 1

2-Methylnaphthalene 2

2-Methylnaphthalene 3

Naphthalene 1

Naphthalene 2

Compound 

(use drop down to define for as many rows as 

needed)

Run Number
Naphthalene

3

Perylene1

Perylene2

Perylene3

Phenanthrene1

Phenanthrene2

Phenanthrene3

Pyrene1

Pyrene2

Pyrene3

1,2,4-Trichlorobenzene1

1,2,4-Trichlorobenzene2

1,2,4-Trichlorobenzene3

1,2-Dichlorobenzene1

1,2-Dichlorobenzene2

1,2-Dichlorobenzene3

1,2-Diphenylhydrazine1

1,2-Diphenylhydrazine2

1,2-Diphenylhydrazine3

1,3-Dichlorobenzene1

1,3-Dichlorobenzene2

1,3-Dichlorobenzene3

1,4-Dichlorobenzene1

1,4-Dichlorobenzene2

1,4-Dichlorobenzene3

2,2'-Oxybis(1-Chloropropane)1

2,2'-Oxybis(1-Chloropropane)2

2,2'-Oxybis(1-Chloropropane)3

2,4,5-Trichlorophenol1

2,4,5-Trichlorophenol2

2,4,5-Trichlorophenol3

2,4,6-Trichlorophenol1

2,4,6-Trichlorophenol2

2,4,6-Trichlorophenol3

2,4-Dichlorophenol1

2,4-Dichlorophenol2

2,4-Dichlorophenol3

2,4-Dimethylphenol1

2,4-Dimethylphenol2

2,4-Dimethylphenol3

2,4-Dinitrophenol1

2,4-Dinitrophenol2

2,4-Dinitrophenol3

2,4-Dinitrotoluene1

2,4-Dinitrotoluene2

2,4-Dinitrotoluene3

2,6-Dinitrotoluene1

2,6-Dinitrotoluene2

2,6-Dinitrotoluene3

2-Chloronaphthalene1

2-Chloronaphthalene2

2-Chloronaphthalene3

2-Chlorophenol1

2-Chlorophenol2

2-Chlorophenol3
2-Methylphenol

1

2-Methylphenol2

2-Methylphenol3

2-Nitroaniline1

2-Nitroaniline2

2-Nitroaniline3

2-Nitrophenol1

2-Nitrophenol2

2-Nitrophenol3

3,3'-Dichlorobenzidine1

3,3'-Dichlorobenzidine2

3,3'-Dichlorobenzidine3

3-Methylphenol & 4-Methylphenol1

3-Methylphenol & 4-Methylphenol2

3-Methylphenol & 4-Methylphenol3

3-Nitroaniline1

3-Nitroaniline2

3-Nitroaniline3

4,6-Dinitro-2-methylphenol1

4,6-Dinitro-2-methylphenol2

4,6-Dinitro-2-methylphenol3

4-Bromophenyl phenyl ether1

4-Bromophenyl phenyl ether2

4-Bromophenyl phenyl ether3

4-Chloro-3-methylphenol1

4-Chloro-3-methylphenol2

4-Chloro-3-methylphenol3

4-Chloroaniline1

4-Chloroaniline2

4-Chloroaniline3

4-Chlorophenyl phenyl ether1

4-Chlorophenyl phenyl ether2

4-Chlorophenyl phenyl ether3

4-Nitroaniline1

4-Nitroaniline2

4-Nitroaniline3

4-Nitrophenol1

4-Nitrophenol2

4-Nitrophenol3

Acetophenone1

Acetophenone2

Acetophenone3

Aniline1

Aniline2

Aniline3

Benzidine1

Benzidine2

Benzidine3

Benzoic acid1

Benzoic acid2

Benzoic acid3

Benzyl alcohol1

Benzyl alcohol2

Benzyl alcohol3

bis(2-Chloroethoxy)methane1
bis(2-Chloroethoxy)methane

2

bis(2-Chloroethoxy)methane3

bis(2-Chloroethyl) ether1

bis(2-Chloroethyl) ether2

bis(2-Chloroethyl) ether3

bis(2-Ethylhexyl) phthalate1

bis(2-Ethylhexyl) phthalate2

bis(2-Ethylhexyl) phthalate3

Butyl benzyl phthalate1

Butyl benzyl phthalate2

Butyl benzyl phthalate3

Carbazole1

Carbazole2

Carbazole3

Dibenzofuran1

Dibenzofuran2

Dibenzofuran3

Diethyl phthalate1

Diethyl phthalate2

Diethyl phthalate3

Dimethyl phthalate1

Dimethyl phthalate2

Dimethyl phthalate3

Di-n-butyl phthalate1

Di-n-butyl phthalate2

Di-n-butyl phthalate3

Di-n-octyl phthalate1

Di-n-octyl phthalate2

Di-n-octyl phthalate3

Hexachlorobenzene1

Hexachlorobenzene2

Hexachlorobenzene3

Hexachlorobutadiene1

Hexachlorobutadiene2

Hexachlorobutadiene3

Hexachlorocyclopentadiene1

Hexachlorocyclopentadiene2

Hexachlorocyclopentadiene3

Hexachloroethane1

Hexachloroethane2

Hexachloroethane3

Isophorone1

Isophorone2

Isophorone3

Nitrobenzene1

Nitrobenzene2

Nitrobenzene3

N-Nitrosodimethylamine1

N-Nitrosodimethylamine2

N-Nitrosodimethylamine3

N-Nitrosodi-n-propylamine1

N-Nitrosodi-n-propylamine2

N-Nitrosodi-n-propylamine3

N-Nitrosodiphenylamine1

N-Nitrosodiphenylamine2
N-Nitrosodiphenylamine

3

Pentachlorobenzene1

Pentachlorobenzene2

Pentachlorobenzene3

Pentachloronitrobenzene1

Pentachloronitrobenzene2

Pentachloronitrobenzene3

Pentachlorophenol1

Pentachlorophenol2

Pentachlorophenol3

Phenol1

Phenol2

Phenol3

Pyridine1

Pyridine2

Pyridine3



Boiler ID

Unit 4

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

Test Start Date Test Start Time Test End Date
6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010
6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010
6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010
6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010

6/5/2010 8:40 AM 6/5/2010

6/5/2010 11:35 AM 6/5/2010

6/5/2010 2:27 PM 6/5/2010



Footnotes:

* Front Half Composite contains particulate filter, front half of the 

** Back Half Composite contains XAD-2 resin tube, back half of t

*** Condensate Composite contains condensate and Impinger con

Measured Value 

(μg/m3@7% O2) Basis (Wet or Dry)

11:09 AM [< 0.0097] Dry

2:01 PM [< 0.0115] Dry

4:53 PM [< 0.0134] Dry

11:09 AM [< 0.003] Dry

2:01 PM [< 0.0036] Dry

4:53 PM [< 0.0026] Dry

11:09 AM [< 0.0038] Dry

2:01 PM [< 0.0039] Dry

4:53 PM [< 0.0037] Dry

11:09 AM [< 0.0033] Dry

2:01 PM [< 0.0033] Dry

4:53 PM [< 0.0036] Dry

11:09 AM [< 0.0377] Dry

2:01 PM [< 0.0439] Dry

4:53 PM [< 0.036] Dry

11:09 AM [< 0.043] Dry

2:01 PM [< 0.0439] Dry

4:53 PM [< 0.0412] Dry

11:09 AM [< 0.0046] Dry

2:01 PM [< 0.0046] Dry

4:53 PM [< 0.0049] Dry

11:09 AM [< 0.0168] Dry

2:01 PM [< 0.0215] Dry

4:53 PM [< 0.0061] Dry

11:09 AM [< 0.005] Dry

2:01 PM [< 0.005] Dry

4:53 PM [< 0.0054] Dry

11:09 AM [< 0.0022] Dry

2:01 PM [< 0.0023] Dry

4:53 PM [< 0.0024] Dry

11:09 AM [< 0.0036] Dry

2:01 PM [< 0.0038] Dry

4:53 PM [< 0.0037] Dry

11:09 AM [< 0.0088] Dry

2:01 PM [< 0.0079] Dry

4:53 PM [< 0.009] Dry

11:09 AM [< 0.0115] Dry

2:01 PM [< 0.0156] Dry

4:53 PM [< 0.0144] Dry

11:09 AM [< 0.0043] Dry

2:01 PM [< 0.0044] Dry

4:53 PM [< 0.0028] Dry

11:09 AM [< 0.0567] Dry

2:01 PM [< 0.066] Dry

4:53 PM [< 0.0807] Dry

11:09 AM [< 0.2452] Dry

2:01 PM [< 0.2482] Dry

Test End Time
4:53 PM [< 0.2545] Dry

11:09 AM [< 0.0027] Dry

2:01 PM [< 0.0027] Dry

4:53 PM [< 0.0029] Dry

11:09 AM [< 0.0448] Dry

2:01 PM [< 0.0408] Dry

4:53 PM [< 0.0408] Dry

11:09 AM [< 0.0319] Dry

2:01 PM [< 0.0323] Dry

4:53 PM [< 0.0357] Dry

11:09 AM [< 2.9071] Dry

2:01 PM [< 2.9068] Dry

4:53 PM [< 3.1491] Dry

11:09 AM [< 2.9952] Dry

2:01 PM [< 2.9949] Dry

4:53 PM [< 3.2445] Dry

11:09 AM [< 2.4666] Dry

2:01 PM [< 2.4664] Dry

4:53 PM [< 2.6719] Dry

11:09 AM [< 2.9071] Dry

2:01 PM [< 2.9068] Dry

4:53 PM [< 3.1491] Dry

11:09 AM [< 2.7749] Dry

2:01 PM [< 2.7747] Dry

4:53 PM [< 3.0059] Dry

11:09 AM [< 2.9952] Dry

2:01 PM [< 2.9949] Dry

4:53 PM [< 3.2445] Dry

11:09 AM [< 2.3785] Dry

2:01 PM [< 2.3783] Dry

4:53 PM [< 2.5765] Dry

11:09 AM [< 2.5106] Dry

2:01 PM [< 2.5105] Dry

4:53 PM [< 2.7197] Dry

11:09 AM [< 2.5987] Dry

2:01 PM [< 2.5985] Dry

4:53 PM [< 2.8151] Dry

11:09 AM [< 5.8141] Dry

2:01 PM [< 5.8137] Dry

4:53 PM [< 6.2981] Dry

11:09 AM [< 37.8798] Dry

2:01 PM [< 37.877] Dry

4:53 PM [< 41.0334] Dry

11:09 AM [< 5.726] Dry

2:01 PM [< 5.7256] Dry

4:53 PM [< 6.2027] Dry

11:09 AM [< 5.8141] Dry

2:01 PM [< 5.8137] Dry

4:53 PM [< 6.2981] Dry

11:09 AM [< 2.7309] Dry

2:01 PM [< 2.7307] Dry

4:53 PM [< 2.9582] Dry

11:09 AM [< 2.6868] Dry

2:01 PM [< 2.6866] Dry

4:53 PM [< 2.9105] Dry
11:09 AM [< 2.3345] Dry

2:01 PM [< 2.3343] Dry

4:53 PM [< 2.5288] Dry

11:09 AM [< 3.6118] Dry

2:01 PM [< 3.6115] Dry

4:53 PM [< 3.9125] Dry

11:09 AM [< 3.6118] Dry

2:01 PM [< 3.6115] Dry

4:53 PM [< 3.9125] Dry

11:09 AM [< 7.3117] Dry

2:01 PM [< 7.3111] Dry

4:53 PM [< 7.9204] Dry

11:09 AM [< 4.8451] Dry

2:01 PM [< 4.8447] Dry

4:53 PM [< 5.2485] Dry

11:09 AM [< 13.8305] Dry

2:01 PM [< 13.8295] Dry

4:53 PM [< 14.982] Dry

11:09 AM [< 8.6331] Dry

2:01 PM [< 8.6324] Dry

4:53 PM [< 9.3518] Dry

11:09 AM [< 3.4356] Dry

2:01 PM [< 3.4354] Dry

4:53 PM [< 3.7216] Dry

11:09 AM [< 3.5237] Dry

2:01 PM [< 3.5234] Dry

4:53 PM [< 3.8171] Dry

11:09 AM [< 6.4308] Dry

2:01 PM [< 6.4303] Dry

4:53 PM [< 6.9661] Dry

11:09 AM [< 2.7749] Dry

2:01 PM [< 2.7747] Dry

4:53 PM [< 3.0059] Dry

11:09 AM [< 9.0735] Dry

2:01 PM [< 9.0729] Dry

4:53 PM [< 9.8289] Dry

11:09 AM [< 15.8567] Dry

2:01 PM [< 15.8555] Dry

4:53 PM [< 17.1768] Dry

11:09 AM [< 4.4487] Dry

2:01 PM [< 3.9198] Dry

4:53 PM [< 4.5328] Dry

11:09 AM [< 7.576] Dry

2:01 PM [< 7.5754] Dry

4:53 PM [< 8.2067] Dry

11:09 AM [< 52.327] Dry

2:01 PM [< 52.3231] Dry

4:53 PM [< 56.6833] Dry

11:09 AM [< 96.9019] Dry

2:01 PM [< 88.086] Dry

4:53 PM [< 104.9691] Dry

11:09 AM [< 4.9332] Dry

2:01 PM [< 4.9328] Dry

4:53 PM [< 5.3439] Dry

11:09 AM [< 2.2023] Dry
2:01 PM [< 2.2021] Dry

4:53 PM [< 2.3857] Dry

11:09 AM [< 2.863] Dry

2:01 PM [< 2.8628] Dry

4:53 PM [< 3.1014] Dry

11:09 AM [< 9.514] Dry

2:01 PM [< 9.5133] Dry

4:53 PM [< 10.3061] Dry

11:09 AM [< 3.9642] Dry

2:01 PM [< 3.9639] Dry

4:53 PM [< 4.2942] Dry

11:09 AM [< 2.6428] Dry

2:01 PM [< 2.6426] Dry

4:53 PM [< 2.8628] Dry

11:09 AM [< 2.4225] Dry

2:01 PM [< 2.4224] Dry

4:53 PM [< 2.6242] Dry

11:09 AM [< 2.863] Dry

2:01 PM [< 2.8628] Dry

4:53 PM [< 3.1014] Dry

11:09 AM [< 2.5987] Dry

2:01 PM [< 2.5985] Dry

4:53 PM [< 2.8151] Dry

11:09 AM [< 4.1404] Dry

2:01 PM [< 4.14] Dry

4:53 PM [< 4.485] Dry

11:09 AM [< 4.0523] Dry

2:01 PM [< 4.052] Dry

4:53 PM [< 4.3896] Dry

11:09 AM [< 2.9071] Dry

2:01 PM [< 2.9068] Dry

4:53 PM [< 3.1491] Dry

11:09 AM [< 2.4225] Dry

2:01 PM [< 2.4224] Dry

4:53 PM [< 2.6242] Dry

11:09 AM [< 21.1422] Dry

2:01 PM [< 21.1406] Dry

4:53 PM [< 22.9024] Dry

11:09 AM [< 2.5987] Dry

2:01 PM [< 2.5985] Dry

4:53 PM [< 2.8151] Dry

11:09 AM [< 2.5106] Dry

2:01 PM [< 2.5105] Dry

4:53 PM [< 2.7197] Dry

11:09 AM [< 2.5106] Dry

2:01 PM [< 2.5105] Dry

4:53 PM [< 2.7197] Dry

11:09 AM [< 2.7749] Dry

2:01 PM [< 2.7747] Dry

4:53 PM [< 3.0059] Dry

11:09 AM [< 2.7749] Dry

2:01 PM [< 2.7747] Dry

4:53 PM [< 3.0059] Dry

11:09 AM [< 3.1273] Dry

2:01 PM [< 3.1271] Dry
4:53 PM [< 3.3876] Dry

11:09 AM [< 2.7749] Dry

2:01 PM [< 2.7747] Dry

4:53 PM [< 3.0059] Dry

11:09 AM [< 5.9022] Dry

2:01 PM [< 5.9018] Dry

4:53 PM [< 6.3936] Dry

11:09 AM [< 7.4879] Dry

2:01 PM [< 7.4873] Dry

4:53 PM [< 8.1113] Dry

11:09 AM [< 3.788] Dry

2:01 PM [< 3.4354] Dry

4:53 PM [< 3.9125] Dry

11:09 AM [< 7.576] Dry

2:01 PM [< 7.5754] Dry

4:53 PM [< 8.2067] Dry



posite contains particulate filter, front half of the filter holder, and probe solvent rinses

posite contains XAD-2 resin tube, back half of the filter holder, and coil condenser solvent rinses

omposite contains condensate and Impinger contents and the glassware solvent rinses

Test Method Used Data Flag (ADL, BDL, DDL) Front Half mass* (ng)

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 12

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 12

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 12

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 1.8]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 1.8]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 1.8]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 28

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 42

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 18

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 13

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 15

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [<1.7]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 5.6]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 5.6]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 5.6]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 34

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 44

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 8.8

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2.8]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2.8]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2.8]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 3

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 3.3

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2.6]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 3]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 3]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 3]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 6.9

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 8.2

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 12

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 6

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 6.2

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 2

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 34

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 44

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 65

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 61

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 68

Semi-Volatile Organic HAP Emission Test Results
U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 38

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1.5]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 16

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 17

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C 12

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 60]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 60]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 60]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 14000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 14000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 14000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]
U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 4400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 4400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 4400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 10000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 10000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 10000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 10000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 10000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 10000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 15000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 15000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 15000]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 1100]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 1100]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 1100]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 5800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 5800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 5800]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 30000]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 30000]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 30000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 4600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 4600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 4600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1900]
U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1900]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1900]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 20000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 20000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 20000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1900]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1900]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1900]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2200]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2600]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3000]
U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 3000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1500]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1500]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 1500]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2000]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 2800]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW DLL, Reporting limit based on MDL -846 Method 8270C [< 2400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 5400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 5400]

U.S. EPA Method 0010 with SW BDL, Reporting limit based on MDL -846 Method 8270C [< 5400]



Back Half mass* (ng) Condensate Mass*** (ng) Total Composite (ng)

5 [< 4.8] [< 21.8]

9.2 [< 4.8] [< 26]

11 [< 4.8] [< 27.8]

4.9 [< 0.3] [< 6.7]

6.4 [< 0.3] [< 8.2]

3.6 [< 0.3] [< 5.4]

5.4 [< 1.4] [< 8.6]

5.5 [< 1.4] [< 8.7]

4.5 [< 1.4] [< 7.7]

[< 3] [< 3] [< 7.5]

[< 3] [< 3] [< 7.5]

[< 3] [< 3] [< 7.5]

[< 54] [< 3] [< 85]

[< 54] [< 3] [< 99]

[< 54] [< 3] [< 75]

[< 82] [< 2] [< 97]

[< 82] [< 2] [< 99]

[< 82] [< 2] [< 85.7]

[< 3.6] 1.2 [< 10.4]

[< 3.6] 1.2 [< 10.4]

[< 3.6] [< 1] [< 10.2]

[< 3] 1 [< 38]

3.5 0.89 [< 48.39]

[< 3] [< 0.8] [< 12.6]

[< 5.6] [< 2.8] [< 11.2]

[< 5.6] [< 2.8] [< 11.2]

[< 5.6] [< 2.8] [< 11.2]

[< 3] [< 0.44] [< 4.94]

[< 3] 0.58 [< 5.08]

[< 3] [< 0.44] [< 4.94]

[< 3.6] [< 1.6] [< 8.2]

[< 3.6] [< 1.6] [< 8.5]

[< 3.6] [< 1.6] [< 7.8]

12 [< 4.8] [< 19.8]

10 [< 4.8] [< 17.8]

11 [< 4.8] [< 18.8]

16 [< 3] [< 25.9]

24 [< 3] [< 35.2]

15 [< 3] [< 30]

[< 1.8] [< 2] [< 9.8]

[< 1.8] [< 2] [< 10]

[< 1.8] [< 2] [< 5.8]

77 [< 17] [< 128]

88 [< 17] [< 149]

86 [< 17] [< 168]

[< 460] [< 32] [< 553]

[< 460] [< 32] [< 560]

Emission Test Results
[< 460] [< 32] [< 530]

[< 3] [< 1.6] [< 6.1]

[< 3] [< 1.6] [< 6.1]

[< 3] [< 1.6] [< 6.1]

63 [< 22] [< 101]

53 [< 22] [< 92]

51 [< 22] [< 85]

8.6 [< 3.4] [< 72]

9.5 [< 3.4] [< 72.9]

11 [< 3.4] [< 74.4]

[< 2000] [< 2200] [< 6600]

[< 2000] [< 2200] [< 6600]

[< 2000] [< 2200] [< 6600]

[< 2200] [< 2200] [< 6800]

[< 2200] [< 2200] [< 6800]

[< 2200] [< 2200] [< 6800]

[< 1700] [< 1900] [< 5600]

[< 1700] [< 1900] [< 5600]

[< 1700] [< 1900] [< 5600]

[< 1800] [< 2400] [< 6600]

[< 1800] [< 2400] [< 6600]

[< 1800] [< 2400] [< 6600]

[< 1900] [< 2000] [< 6300]

[< 1900] [< 2000] [< 6300]

[< 1900] [< 2000] [< 6300]

[< 2000] [< 2200] [< 6800]

[< 2000] [< 2200] [< 6800]

[< 2000] [< 2200] [< 6800]

[< 1400] [< 1400] [< 5400]

[< 1400] [< 1400] [< 5400]

[< 1400] [< 1400] [< 5400]

[< 1900] [< 1400] [< 5700]

[< 1900] [< 1400] [< 5700]

[< 1900] [< 1400] [< 5700]

[< 1700] [< 1600] [< 5900]

[< 1700] [< 1600] [< 5900]

[< 1700] [< 1600] [< 5900]

[< 7000] [< 2800] [< 13200]

[< 7000] [< 2800] [< 13200]

[< 7000] [< 2800] [< 13200]

[< 22000] [< 50000] [< 86000]

[< 22000] [< 50000] [< 86000]

[< 22000] [< 50000] [< 86000]

[< 2200] [< 8000] [< 13000]

[< 2200] [< 8000] [< 13000]

[< 2200] [< 8000] [< 13000]

[< 2400] [< 8000] [< 13200]

[< 2400] [< 8000] [< 13200]

[< 2400] [< 8000] [< 13200]

[< 1800] [< 2000] [< 6200]

[< 1800] [< 2000] [< 6200]

[< 1800] [< 2000] [< 6200]

[< 1900] [< 2000] [< 6100]

[< 1900] [< 2000] [< 6100]

[< 1900] [< 2000] [< 6100]
[< 1700] [< 1400] [< 5300]

[< 1700] [< 1400] [< 5300]

[< 1700] [< 1400] [< 5300]

[< 2000] [< 4000] [< 8200]

[< 2000] [< 4000] [< 8200]

[< 2000] [< 4000] [< 8200]

[< 2000] [< 4000] [< 8200]

[< 2000] [< 4000] [< 8200]

[< 2000] [< 4000] [< 8200]

[< 12000] [< 1800] [< 16600]

[< 12000] [< 1800] [< 16600]

[< 12000] [< 1800] [< 16600]

[< 3400] [< 3200] [< 11000]

[< 3400] [< 3200] [< 11000]

[< 3400] [< 3200] [< 11000]

[< 20000] [< 1400] [< 31400]

[< 20000] [< 1400] [< 31400]

[< 20000] [< 1400] [< 31400]

[< 2200] [< 7400] [< 19600]

[< 2200] [< 7400] [< 19600]

[< 2200] [< 7400] [< 19600]

[< 2200] [< 2400] [< 7800]

[< 2200] [< 2400] [< 7800]

[< 2200] [< 2400] [< 7800]

[< 1400] [< 4000] [< 8000]

[< 1400] [< 4000] [< 8000]

[< 1400] [< 4000] [< 8000]

[< 8600] [< 3400] [< 14600]

[< 8600] [< 3400] [< 14600]

[< 8600] [< 3400] [< 14600]

[< 1800] [< 1700] [< 6300]

[< 1800] [< 1700] [< 6300]

[< 1800] [< 1700] [< 6300]

[< 10000] [< 8000] [< 20600]

[< 10000] [< 8000] [< 20600]

[< 10000] [< 8000] [< 20600]

[< 10000] [< 11000] [< 36000]

[< 10000] [< 11000] [< 36000]

[< 10000] [< 11000] [< 36000]

7000 [< 2000] [< 10100]

5800 [< 2000] [< 8900]

6400 [< 2000] [< 9500]

[< 10000] [< 4000] [< 17200]

[< 10000] [< 4000] [< 17200]

[< 10000] [< 4000] [< 17200]

[< 100000] [< 13000] [< 118800]

[< 100000] [< 13000] [< 118800]

[< 100000] [< 13000] [< 118800]

140000 [< 50000] [< 220000]

120000 [< 50000] [< 200000]

140000 [< 50000] [< 220000]

[< 4400] [< 2200] [< 11200]

[< 4400] [< 2200] [< 11200]

[< 4400] [< 2200] [< 11200]

[< 1500] [< 1600] [< 5000]
[< 1500] [< 1600] [< 5000]

[< 1500] [< 1600] [< 5000]

[< 1900] [< 2200] [< 6500]

[< 1900] [< 2200] [< 6500]

[< 1900] [< 2200] [< 6500]

[< 15000] [< 3200] [< 21600]

[< 15000] [< 3200] [< 21600]

[< 15000] [< 3200] [< 21600]

[< 2600] [< 3000] [< 9000]

[< 2600] [< 3000] [< 9000]

[< 2600] [< 3000] [< 9000]

[< 1000] [< 2600] [< 6000]

[< 1000] [< 2600] [< 6000]

[< 1000] [< 2600] [< 6000]

[< 1600] [< 1500] [< 5500]

[< 1600] [< 1500] [< 5500]

[< 1600] [< 1500] [< 5500]

[< 1500] [< 2000] [< 6500]

[< 1500] [< 2000] [< 6500]

[< 1500] [< 2000] [< 6500]

[< 1400] [< 1700] [< 5900]

[< 1400] [< 1700] [< 5900]

[< 1400] [< 1700] [< 5900]

[< 2200] [< 3800] [< 9400]

[< 2200] [< 3800] [< 9400]

[< 2200] [< 3800] [< 9400]

[< 3600] [< 2200] [< 9200]

[< 3600] [< 2200] [< 9200]

[< 3600] [< 2200] [< 9200]

[< 2000] [< 2000] [< 6600]

[< 2000] [< 2000] [< 6600]

[< 2000] [< 2000] [< 6600]

[< 1600] [< 1900] [< 5500]

[< 1600] [< 1900] [< 5500]

[< 1600] [< 1900] [< 5500]

[< 20000] [< 8000] [< 48000]

[< 20000] [< 8000] [< 48000]

[< 20000] [< 8000] [< 48000]

[< 2000] [< 2000] [< 5900]

[< 2000] [< 2000] [< 5900]

[< 2000] [< 2000] [< 5900]

[< 1500] [< 1600] [< 5700]

[< 1500] [< 1600] [< 5700]

[< 1500] [< 1600] [< 5700]

[< 1700] [< 2000] [< 5700]

[< 1700] [< 2000] [< 5700]

[< 1700] [< 2000] [< 5700]

[< 1900] [< 2200] [< 6300]

[< 1900] [< 2200] [< 6300]

[< 1900] [< 2200] [< 6300]

[< 1800] [< 1900] [< 6300]

[< 1800] [< 1900] [< 6300]

[< 1800] [< 1900] [< 6300]

[< 1700] [< 2400] [< 7100]

[< 1700] [< 2400] [< 7100]
[< 1700] [< 2400] [< 7100]

[< 2600] [< 2200] [< 6300]

[< 2600] [< 2200] [< 6300]

[< 2600] [< 2200] [< 6300]

[< 3400] [< 8000] [< 13400]

[< 3400] [< 8000] [< 13400]

[< 3400] [< 8000] [< 13400]

[< 3200] [< 11000] [< 17000]

[< 3200] [< 11000] [< 17000]

[< 3200] [< 11000] [< 17000]

4200 [< 2000] [< 8600]

3400 [< 2000] [< 7800]

3800 [< 2000] [< 8200]

[< 3800] [< 8000] [< 17200]

[< 3800] [< 8000] [< 17200]

[< 3800] [< 8000] [< 17200]



Test Method Comments lb/mmBtu ug/dscm @ 7% O2

Method Blank Contaminated [< 8.80E-09]

Method Blank Contaminated [< 1.05E-08]

Method Blank Contaminated [< 1.22E-08]

[< 2.70E-09]

[< 3.30E-09]

[< 2.40E-09]

[< 3.50E-09]

[< 3.50E-09]

[< 3.40E-09]

[< 3.00E-09]

[< 3.00E-09]

[< 3.30E-09]

[< 3.44E-08]

[< 4.00E-08]

[< 3.29E-08]

[< 3.92E-08]

[< 4.00E-08]

[< 3.75E-08]

Method Blank Contaminated [< 4.20E-09]

Method Blank Contaminated [< 4.20E-09]

[< 4.50E-09]

Method Blank Contaminated [< 1.54E-08]

Method Blank Contaminated [< 1.96E-08]

[< 5.50E-09]

[< 4.50E-09]

[< 4.50E-09]

[< 4.90E-09]

[< 2.00E-09]

Method Blank Contaminated [< 2.10E-09]

[< 2.20E-09]

[< 3.30E-09]

[< 3.40E-09]

[< 3.40E-09]

Method Blank Contaminated [< 8.00E-09]

Method Blank Contaminated [< 7.20E-09]

Method Blank Contaminated [< 8.20E-09]

Method Blank Contaminated [< 1.05E-08]

Method Blank Contaminated [< 1.42E-08]

Method Blank Contaminated [< 1.31E-08]

[< 4.00E-09]

[< 4.00E-09]

[< 2.50E-09]

Method Blank Contaminated [< 5.18E-08]

Method Blank Contaminated [< 6.02E-08]

Method Blank Contaminated [< 7.36E-08]

Method Blank Contaminated [< 2.24E-07]

Method Blank Contaminated [< 2.26E-07]

Calculated Emission Rate
Method Blank Contaminated [< 2.32E-07]

[< 2.50E-09]

[< 2.50E-09]

[< 2.70E-09]

Method Blank Contaminated [< 4.08E-08]

Method Blank Contaminated [< 3.72E-08]

Method Blank Contaminated [< 3.72E-08]

[< 2.91E-08]

[< 2.95E-08]

[< 3.26E-08]

[< 2.67E-06]

[< 2.67E-06]

[< 2.89E-06]

[< 2.75E-06]

[< 2.75E-06]

[< 2.98E-06]

[< 2.26E-06]

[< 2.26E-06]

[< 2.45E-06]

[< 2.67E-06]

[< 2.67E-06]

[< 2.89E-06]

[< 2.55E-06]

[< 2.55E-06]

[< 2.76E-06]

[< 2.75E-06]

[< 2.75E-06]

[< 2.98E-06]

[< 2.18E-06]

[< 2.18E-06]

[< 2.37E-06]

[< 2.30E-06]

[< 2.30E-06]

[< 2.50E-06]

[< 2.39E-06]

[< 2.39E-06]

[< 2.58E-06]

[< 5.34E-06]

[< 5.34E-06]

[< 5.78E-06]

[< 3.48E-05]

[< 3.48E-05]

[< 3.77E-05]

[< 5.26E-06]

[< 5.26E-06]

[< 5.69E-06]

[< 5.34E-06]

[< 5.34E-06]

[< 5.78E-06]

[< 2.51E-06]

[< 2.51E-06]

[< 2.72E-06]

[< 2.47E-06]

[< 2.47E-06]

[< 2.67E-06]
[< 2.14E-06]

[< 2.14E-06]

[< 2.32E-06]

[< 3.32E-06]

[< 3.32E-06]

[< 3.59E-06]

[< 3.32E-06]

[< 3.32E-06]

[< 3.59E-06]

[< 6.71E-06]

[< 6.71E-06]

[< 7.27E-06]

[< 4.45E-06]

[< 4.45E-06]

[< 4.82E-06]

[< 1.27E-05]

[< 1.27E-05]

[< 1.38E-05]

[< 7.93E-06]

[< 7.92E-06]

[< 8.59E-06]

[< 3.15E-06]

[< 3.15E-06]

[< 3.42E-06]

[< 3.23E-06]

[< 3.23E-06]

[< 3.50E-06]

[< 5.90E-06]

[< 5.90E-06]

[< 6.40E-06]

[< 2.55E-06]

[< 2.55E-06]

[< 2.76E-06]

[< 8.33E-06]

[< 8.33E-06]

[< 9.02E-06]

[< 1.46E-05]

[< 1.46E-05]

[< 1.58E-05]

[< 4.08E-06]

[< 3.60E-06]

[< 4.16E-06]

[< 6.95E-06]

[< 6.95E-06]

[< 7.53E-06]

[< 4.80E-05]

[< 4.80E-05]

[< 5.20E-05]

Method Blank Contaminated [< 8.90E-05]

Method Blank Contaminated [< 8.09E-05]

Method Blank Contaminated [< 9.64E-05]

[< 4.53E-06]

[< 4.53E-06]

[< 4.91E-06]

[< 2.02E-06]
[< 2.02E-06]

[< 2.19E-06]

[< 2.63E-06]

[< 2.63E-06]

[< 2.85E-06]

[< 8.73E-06]

[< 8.73E-06]

[< 9.46E-06]

[< 3.64E-06]

[< 3.64E-06]

[< 3.94E-06]

[< 2.43E-06]

[< 2.43E-06]

[< 2.63E-06]

[< 2.22E-06]

[< 2.22E-06]

[< 2.41E-06]

[< 2.63E-06]

[< 2.63E-06]

[< 2.85E-06]

[< 2.39E-06]

[< 2.39E-06]

[< 2.58E-06]

[< 3.80E-06]

[< 3.80E-06]

[< 4.12E-06]

[< 3.72E-06]

[< 3.72E-06]

[< 4.03E-06]

[< 2.67E-06]

[< 2.67E-06]

[< 2.89E-06]

[< 2.22E-06]

[< 2.22E-06]

[< 2.41E-06]

[< 1.94E-05]

[< 1.94E-05]

[< 2.10E-05]

[< 2.39E-06]

[< 2.39E-06]

[< 2.58E-06]

[< 2.30E-06]

[< 2.30E-06]

[< 2.50E-06]

[< 2.30E-06]

[< 2.30E-06]

[< 2.50E-06]

[< 2.55E-06]

[< 2.55E-06]

[< 2.76E-06]

[< 2.55E-06]

[< 2.55E-06]

[< 2.76E-06]

[< 2.87E-06]

[< 2.87E-06]
[< 3.11E-06]

[< 2.55E-06]

[< 2.55E-06]

[< 2.76E-06]

[< 5.42E-06]

[< 5.42E-06]

[< 5.87E-06]

[< 6.87E-06]

[< 6.87E-06]

[< 7.45E-06]

[< 3.48E-06]

[< 3.15E-06]

[< 3.59E-06]

[< 6.95E-06]

[< 6.95E-06]

[< 7.53E-06]



10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

Steam Output (1000 lb/hr) Total Heat Input 

(mmBtu/hr) Flue Gas Moisture (%)
9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9
10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1
10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10
9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9

10.1

10

9.9



12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

Flue Gas CO2 (%) Flue Gas O2 (%) Flue Gas Flow Rate (scfm)
12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563
12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251
12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742
12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563

12.13 7.3 1,292,251

12.16 7.32 1,301,742

12.12 7.28 1,185,563



Fuel Input Rate Fuel Type

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

Flue Gas Temperature (F)

Fuel #1
275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3
272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8
276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4
275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3

272.8

276.4

275.3



Units of Measure Measurement Method Fuel Input Rate

Fuel #1







Fuel Type Units of Measure Measurement Method

Fuel #2







Fuel Input Rate Fuel Type Units of Measure

Fuel #3







Measurement Method Fuel Input Rate Fuel Type

Fuel #4







Units of Measure Measurement Method

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Fuel #4 Other Supporting 

Information
Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau
Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau
Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau
Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau

Moisture results recorded for Run 2 are considered suspect becau



corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru
corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru
corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru
corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru
corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru

corded for Run 2 are considered suspect because of the high volume of water recorded during recovery. Average moisture results from Ru



ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.
ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.
ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.
ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.
ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.

ng recovery. Average moisture results from Runs 2 & 3 were therefore used in the flow rate calculation to convert to dry conditions.



 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.
 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.
 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.
 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.
 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.

 calculation to convert to dry conditions.
EIA Facility Code Facility Name Boiler ID

IN_Wabash River StationWabash River Station Unit 4

1 6/4/2010 8:33 6/4/2010

2 6/4/2010 11:35 6/4/2010

3 6/4/2010 14:44 6/4/2010

Run Number Test Start Date Test Start Time Test End Date
Measured Value 

(ppm) Basis (Wet or Dry) Test Method Used 

9:56 [<0.0209] Dry U.S. EPA Conditional Test Method 033 (CTM-033)

13:54 [<0.0204] Dry U.S. EPA Conditional Test Method 033 (CTM-033)

16:18 [<0.0224] Dry U.S. EPA Conditional Test Method 033 (CTM-033)

Hydrogen Cyanide Emission Test Results

Test End Time
Data Flag (ADL, 

BDL, DDL)

Test Method 

Comments

BDL DL based on MDL [<2.21E-05] 11.04 12.25

BDL DL based on MDL [<2.15E-05] 11.22 12.2

BDL DL based on MDL [<2.36E-05] 11.46 12.11

Calculated 

Emission Rate 

(lb/mmBtu)

Flue Gas 

Moisture 

(%)

Flue Gas 

CO2 (%)

Steam Output 

(1000 lb/hr)

Total Heat 

Input 

(mmBtu/hr)
Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel Input 

Rate

7.28 1,289,888 267.9

7.26 1,279,139 275.5

7.31 1,270,532 278.7

Flue Gas 

Temperature 

(F)

Fuel #1 Flue Gas 

O2 (%)

Flue Gas 

Flow Rate 

(dscfm)
Fuel Type Units of 

Measure

Measurement 

Method Fuel Input Rate Fuel Type Units of Measure

Measurement 

Method

Fuel Input 

Rate

Fuel #2 Fuel #3
Fuel Type Units of 

Measure

Measurement 

Method

Fuel #4

Other Supporting Information
EIA Facility Code Facility Name Boiler ID

IN_Wabash River StationWabash River Station Unit 4

Run Number Test Start Date Test Start Time Test End Date
Measured Value 

(ppm) Basis (Wet or Dry) Test Method Used Test End Time

Hydrogen Chloride Emission Test Results
Data Flag (ADL, 

BDL, DDL)

Test Method 

Comments

 Test Results

Steam Output 

(1000 lb/hr)

Total Heat 

Input 

(mmBtu/hr)

Calculated 

Emission Rate 

(lb/mmBtu)

Flue Gas 

Moisture 

(%)

Flue Gas 

CO2 (%)
Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel Input 

Rate

Flue Gas 

Flow Rate 

(dscfm)

Flue Gas 

Temperature 

(F)

Fuel #1 Flue Gas 

O2 (%)
Fuel Type Units of 

Measure

Measurement 

Method Fuel Input Rate Fuel Type Units of Measure

Measurement 

Method

Fuel Input 

Rate

Fuel #2 Fuel #3
Fuel Type Units of 

Measure

Measurement 

Method

Fuel #4

Other Supporting Information
EIA Facility Code Facility Name Boiler ID

IN_Wabash River StationWabash River Station Unit 4

Run Number Test Start Date Test Start Time Test End Date
Measured Value 

(ppm) Basis (Wet or Dry) Test Method Used 

Hydrogen Flouride Emission Test Results

Test End Time
Data Flag (ADL, 

BDL, DDL)

Test Method 

Comments

Calculated 

Emission Rate 

(lb/mmBtu)

Flue Gas 

Moisture (%)

Test Results

Steam Output 

(1000 lb/hr)

Total Heat 

Input 

(mmBtu/hr)
Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Flue Gas 

Temperature 

(F)

Fuel #1 Flue Gas 

CO2 (%)

Flue Gas 

O2 (%)

Flue Gas 

Flow Rate 

(dscfm)
Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method Fuel Input Rate Fuel Type Units of Measure

Measurement 

Method

Fuel #2 Fuel #3
Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel #4

Other Supporting Information
EIA Facility Code Facility Name Boiler ID

IN_Wabash River Station Wabash River StationUnit 4

Run Number Test Start Date Test Start Time
Measured NO (ppm) Test End Date Test End Time
Measured NO2

 (ppm) Basis (Wet or Dry) Test Method Used 

NOX Emission Test Results
Data Flag (ADL, BDL, DDL) Test Method Comments (lb/mmBtu)

Total NOX Calculated Emission Rate
ppmdv @ 7% O2

Flue Gas 

O2 (%)

 Calculated Emission Rate Steam Output 

(1000 lb/hr)

Total Heat Input 

(mmBtu/hr)

Flue Gas 

Moisture (%)

Flue Gas 

CO2 (%)
Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel Input 

Rate

Flue Gas 

Temperature 

(F)

Flue Gas Fuel #1

Flow Rate 

(dscfm)
Fuel Type Units of 

Measure

Measurement 

Method

Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel Input 

Rate

Fuel #2 Fuel #3
Fuel Type Units of 

Measure

Measurement 

Method

Fuel #4

Other Supporting Information
EIA Facility Code Facility Name Boiler ID

IN_Wabash River Station Wabash River Station Unit 4

Run Number Test Start Date Test Start Time
Total Dissolved Solids 

(mg solids/liter)

Total Suspended Solids 

(mg solids/liter)

Test End Date Test End Time
Test Method Used Data Flag (ADL, 

BDL, DDL)

Constisuent Emission Test Results
Test Method Comments Fuel Input Rate

Flue Gas 

Temperat

ure (F)

Flue Gas 

Flow Rate 

(dscfm)

Steam Output 

(1000 lb/hr)

Total Heat Input 

(mmBtu/hr)
Fuel Type Units of 

Measure

Measurement 

Method Fuel Input Rate Fuel Type Units of Measure

Measurement 

Method Fuel Input Rate

Fuel #1 Fuel #2
Fuel Type Units of 

Measure

Measurement 

Method

Fuel Input 

Rate Fuel Type Units of Measure

Measurement 

Method

Fuel #3 Fuel #4
Other Supporting Information