### Instructions for filling in the Emission Test Template

This Information Collection Request (ICR) spreadsheet is intended to collect information about emission data from fossil fuel burning power plants and which test methods were used to do so for cases where the test methods are not currently supported by the Electronic Reporting Tool (ERT). This spreadsheet should only be used if the method is not in the ERT or if you do not have access to a lab which performs methods that are in the ERT. You must complete at least 3 separate runs or sampling events for each of the requested constituents. This spreadsheet is intended to be used for one boiler of 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 populate 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 worksheet. 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. On each spreadsheet, you must enter boiler operating information during sampling, fuel input information, and emission test results. There are generally 1 to 3 emission test results records to be entered depending on the constituent or constituent family. For example, CO only requires 1 record with 3 sample events, while Mercury requires that you enter both Hg Hg +2 

### , or if the Ontario

- Hydro Method was used, you would need to enter Hg 0

### , 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 instructions 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 field. 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 samples, 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 field.

Emission Data

### 1. Some constituents ask for the emission rate results of each run in two different units of measure, while others do not. If emission rate results are requested in two different units of measure (ex. lb/MMBtu (Pounds per million BTU) and ppmvd @ 7% O 2 

### (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 field. 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 field. 4. If data sheets and QA/QC documentation tables are provided for the test method you are entering data for please also enter these data.

### This Information Collection Request (ICR) spreadsheet is intended to collect information about emission data from fossil fuel burning power plants and which test methods were used to do so for cases where the test methods are not currently supported by the Electronic Reporting Tool (ERT). This spreadsheet should only be used if the method is not in the ERT or if you do not have access to a lab which performs methods that are in the ERT. You must complete at least 3 separate This spreadsheet is intended to be used for one boiler of one facility. Data for multiple boilers should be handled by using separate copies of this spreadsheet. Fields shaded in down lists. You do not need to populate cells shaded in gray, as they are automatically populated from the Boiler Information worksheet. Please name each resulting spreadsheet with the following naming convention: [FacilityID]_Unit_[BoilerID]_EmisTestMethods.xls

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

The emission data worksheets are provided for each constituent or constituent family required for this analysis. On each spreadsheet, you must enter boiler operating information during sampling, fuel input information, and emission test results. There are generally 1 to 3 emission test results records to be entered depending on the constituent or constituent family. For example, CO only requires 1 record with 3 sample events, while Mercury requires that you enter both Hg 0 

### and , HgP, and Hg +2 

### . However, both the Speciated Volatile Organic HAP worksheets allow you to use a drop

- down provided in the

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

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

downs in the Fuel Type Selection field. 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 samples,

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

### 1. Some constituents ask for the emission rate results of each run in two different units of measure, while others do not. If emission rate results are requested in two different units of measure (ex. lb/MMBtu (Pounds per million BTU) and

(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 field. 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 field. 4. If data sheets and QA/QC documentation tables are provided for the test method you are entering data for please alsoEIA

Facility Code Facility Name Boiler ID

1210003 Progress Energy Unit 3Control Device ConfiguratonEIA

Facility Code Facility Name Boiler ID

1210003 Progress Energy Unit 3

1 2/26/2010 12:45 2 2/26/2010 16:25 3 2/27/2010 8:27 Run Number Test Start Date Test Start TimeMe asured Value (ppm) Basis (Wet or Dry)

2/26/2010 14:57 0.362 We t 2/26/2010 18:41 0.351 We t 2/27/2010 10:47 0.59 We t

Test End Time Test End Date Me thane Emission Test ResultsTest Method Used Data Flag (ADL, BDL, DDL) Test Method Comments lb/mmBtu ppmdv @ 7% O 2

U.S. EPA Method 18 DDL J: Estimated value. Below the MDL and above the LOQ. 0.00038 0.65 U.S. EPA Method 18 DDL J: Estimated value. Below the MDL and above the LOQ. 0.00042 0.74 U.S. EPA Method 18 DDL J: Estimated value. Below the MDL and above the LOQ. 0.00056 0.97 Me thane Emission Test Results Calculated Emission RateFuel Input Rate 543.25 561.5 5.657419 6.729 12.73 220025.131 312.5 5059.752 542.75 486.5 14.15835 6.422 13.175 201589.1174 314.2 5057.773 543.25 615.4 10.91545 7.729 11.433 208077.6978 308.5 5127.543 Flue Gas Moisture (%) Flue Gas CO 2(%) Flue Gas

O 2(%) Flue Gas

Flow Rate (dscfm) Steam Output (1000 lb/hr) Total Heat

Input (mmBtu/hr) Flue Gas Temperat ure (F)Fuel Type Units of Me asure Me asurement

Me thod Fuel

Input Rate Fuel Type Units of

Me asure Me asurement

Me thod Fuel

Input Rate No.6 Fuel Oil (residual or bunker C)

gallon/m inute

gas fuel meter No.6 Fuel Oil (residual or bunker C)

gallon/m inute

gas fuel meter No.6 Fuel Oil (residual or bunker C)

gallon/m inute

gas fuel meter Fuel #1 Fuel #2Fuel Type Units of Me asure Me asurement

Me thod Fuel

Input Rate Fuel Type Units of

Me asure Me asurement

Me thod Fuel #4 Fuel #3MDL=0.0702ppm , LOQ=2.99ppm

Other Supporting InformationEIA

Facility Code Facility Name Boiler ID

1210003 Progress Energy Unit 3

1 2/23/2010 8:45 2/23/2010 10:46 2 2/23/2010 17:02 2/23/2010 19:43 3 2/24/2010 8:05 2/24/2010 10:05 4 2/24/2010 15:30 2/24/2010 17:30 5 2/25/2010 8:02 2/25/2010 10:03 6 2/25/2010 15:45 2/25/2010 17:58 Run Number Test Start Date Test Start Time Test End Time Test End DatePlease note QA/QC documentation starting in Column "AI"

Me asured Value (μg/dscm) Basis (Wet or Dry) Test Method Used Data Flag (ADL, BDL, DDL) Test Method

Comments

0.247 Dry U.S. EPA Method 30B ADL 0.5332 Dry U.S. EPA Method 30B ADL 0.480 Dry U.S. EPA Method 30B ADL 0.5004 Dry U.S. EPA Method 30B ADL 0.432 Dry U.S. EPA Method 30B ADL 0.4859 Dry U.S. EPA Method 30B ADL Total Vapor Phase Mercury Emission Test Results(lb/mmBtu)

0.0000003270 545.75 621.2 7.131534 7.41 11.86 219980.3507 0.00000074 547.25 573.0969145 9.709013 7.1 12.21 211114.8781 0.0000006112 550.67 645.9 6.9739 7.68 11.49 219729.4408 0.00000068 545.75 610.3849005 9.651047 7.2 12.11 222292.8294 0.0000005783 543 632.3 6.098573 7.32 11.95 226171.9636 0.00000068 544.25 610.1090232 5.191741 6.98 12.35 228429.3376 Flue Gas O 2(%) Flue Gas

Flow Rate (dscfm) Flue Gas Moisture (%) Steam Output (1000 lb/hr) Total Heat

Input (mmBtu/hr) Flue Gas CO 2(%)Fuel Input Rate Fuel Type Units of Me asure Me asurement

Me thod Fuel Input

Rate Fuel Type

304.5 5063.3 No.6 Fuel Oil (residual or bunker C) gallon/m inute

gas fuel meter 308.6875 5050.05 No.6 Fuel Oil (residual or bunker C) gallon/m inute

gas fuel meter 304.9 5091.467 No.6 Fuel Oil (residual or bunker C) gallon/m inute

gas fuel meter 307.2916667 5060.325 No.6 Fuel Oil (residual or bunker C) gallon/m inute

gas fuel meter 303.1 5104.767 No.6 Fuel Oil (residual or bunker C) gallon/m inute

gas fuel meter 306.9166667 5042.8 No.6 Fuel Oil (residual or bunker C) gallon/m inute

gas fuel meter Flue Gas Temperature (F) Fuel #1 Fuel #2Units of

Me asure Me asurement

Me thod Fuel Input

Rate Fuel Type Units of Me asure Me asurement

Me thod Fuel Input

Rate Fuel Type Fuel #2 Fuel #3 Fuel #4QA /QC Documentation

Units of Me asure Me asurement

Me thod Trap ID Section 1 Ma ss (ng) Section 2

Ma ss (ng) Total

Ma ss (ng)

AU 007227 35.4 0.1 35.5 AU 007335 73.4 2.6 76 AU 007222 68.1 1.9 70 AU 007314 70.8 3.2 74 AU 007176 63.7 2.3 66 AU 007258 71 1.4 72.4 Fuel #4

Other Supporting InformationInitial

Spike (ng) Total NonSpike (ng) Sample

Volume (dscm) Volume

Difference (%) Volume Diff. Limit Breaktrough

(%) Breaktrough

Limit

0 35.5 0.144003 0.00 0.282485876 0 76 0.142528 -1.03 3.542234332 0 70 0.145942 1.33 2.790014684 0 74 0.147874 2.62 4.519774011 0 66 0.152904 5.82 3.610675039 0 72.4 0.149 3.36 1.971830986 ≤ 20% of field

recovery test ≤10% of Section 1 Hg

ma ss for Hg conc. >1

μg/dscm: or ≤ 20% of Section Trap #1Concentration

(μg/dscm) Trap ID Section 1 Ma ss Section 2

Ma ss Total

Ma ss Initial

Spike Total NonSpike Sample

Volume

0.247 AU 007280 86.4 0.3 86.7 52.14 34.56 0.143678 0.533 AU 007310 118.5 4.6 123.1 52.14 70.96 0.141941 0.480 AU 007216 117.5 4.4 121.9 52.14 69.76 0.145218 0.500 AU 007326 120.4 3.4 123.8 52.14 71.66 0.147409 0.432 AU 007342 116.6 3.1 119.7 52.14 67.56 0.152298 0.486 AU 007272 120.4 2.7 123.1 52.14 70.96 0.148515Volume

Difference (%) Volume Diff. Limit Breaktrough (%) Breaktrough Limit Concentration

(μg/dscm) Ab s. diff.

-0.22 0.347222222 0.241 0.005985 -1.45 3.88185654 0.500 0.033301 0.84 3.744680851 0.480 0.000739 2.31 2.823920266 0.486 0.014295 5.45 2.658662093 0.444 0.011963 3.04 2.242524917 0.478 0.008111 ≤ 20% of field

recovery test Trap #2 Paired Trap Agreement (RD)

≤10% of Section 1 Hg mass for Hg conc. >1

μ g/dscm: or ≤ 20% of Section 1 for Hg conc. ≤1RD (%) Limit C rec R (%) by Run Ravg (%) Limit

1.228877 0.356909 98.35066 3.223188 0.334036 90.9346 0.076936 0.359786 100.2057 1.44897 0.339415 95.95858 1.366761 0.354318 103.4942 0.841649 0.342964 97.68967 Average Recovery

, between 85 and 115% Me asured Spike Recovery ( R )

97.77223395 Paired Trap Agreement (RD)

≥ 10 % RD mass for Hg conc. >1 μg/dscm: or

≤ 20% RD or ≤ 0.2 μg/dscm abs.diff. for Hg conc. ≤1EIA

Facility Code Facility Name Boiler ID

1210003 Progress Energy Unit 3

Speciated Volatile Organic HAP Emission Data

Dichlorodifluoromethane (Freon 12) 1 2/26/2010 12:45 PM 1,2-Chloro-1,1,2,2-Tetrafluoroethane 1 2/26/2010 12:45 PM Chloromethane 1 2/26/2010 12:45 PM Vinyl Chloride 1 2/26/2010 12:45 PM 1,3-Butadiene 1 2/26/2010 12:45 PM Bromomethane 1 2/26/2010 12:45 PM Chloroethane 1 2/26/2010 12:45 PM Trichloromonofluoromethane 1 2/26/2010 12:45 PM 1,1-Dichloroethene 1 2/26/2010 12:45 PM 1,1,2-Trichloro-1,2,2-trifluoroethane 1 2/26/2010 12:45 PM Ethanol 1 2/26/2010 12:45 PM Carbon disulfide 1 2/26/2010 12:45 PM Isopropyl alcohol 1 2/26/2010 12:45 PM Methylene chloride 1 2/26/2010 12:45 PM Acetone 1 2/26/2010 12:45 PM t-1,2-dichloroethene 1 2/26/2010 12:45 PM Hexane 1 2/26/2010 12:45 PM Methyl-t-butyl ether (MTBE) 1 2/26/2010 12:45 PM 1,1-Dichloroethane 1 2/26/2010 12:45 PM Vinyl acetate 1 2/26/2010 12:45 PM cis-1,2-dichloroethene 1 2/26/2010 12:45 PM Cyclohexane 1 2/26/2010 12:45 PM Chloroform 1 2/26/2010 12:45 PM Ethyl Acetate 1 2/26/2010 12:45 PM Tetrahydrofuran 1 2/26/2010 12:45 PM 1,1,1-trichloroethane 1 2/26/2010 12:45 PM Carbon Tetrachloride 1 2/26/2010 12:45 PM 2-Butanone 1 2/26/2010 12:45 PM Heptane 1 2/26/2010 12:45 PM Benzene 1 2/26/2010 12:45 PM 1,2-dichloroethane 1 2/26/2010 12:45 PM Trichloroethylene 1 2/26/2010 12:45 PM 1,2-dichloropropane 1 2/26/2010 12:45 PM Bromodichloromethane 1 2/26/2010 12:45 PM 1,4-dioxane 1 2/26/2010 12:45 PM cis-1,3-dichloropropene 1 2/26/2010 12:45 PM Toluene 1 2/26/2010 12:45 PM 4-Methyl-2-pentanone (MIBK) 1 2/26/2010 12:45 PM t-1,3-dichloropropene 1 2/26/2010 12:45 PM Tetrachloroethylene 1 2/26/2010 12:45 PM 1,1,2-trichloroethane 1 2/26/2010 12:45 PM Dibromochloromethane 1 2/26/2010 12:45 PM 1,2-dibromoethane 1 2/26/2010 12:45 PM 2-Hexanone 1 2/26/2010 12:45 PM Ethylbenzene 1 2/26/2010 12:45 PM Chlorobenzene 1 2/26/2010 12:45 PM m/p-Xylene 1 2/26/2010 12:45 PM

Compound (use drop down to define for as many rows as

needed) Run Number Test Start Date Test Start Timeo-Xylene 1 2/26/2010 12:45 PM

Styrene 1 2/26/2010 12:45 PM Tribromomethane 1 2/26/2010 12:45 PM 1,1,2,2-tetrachloroethane 1 2/26/2010 12:45 PM 1-ethyl-4-methylbenzene 1 2/26/2010 12:45 PM 1,3,5-trimethylbenzene 1 2/26/2010 12:45 PM 1,2,4-trimethylbenzene 1 2/26/2010 12:45 PM 1,3-dichlorobenzene 1 2/26/2010 12:45 PM 1,4-dichlorobenzene 1 2/26/2010 12:45 PM Benzyl chloride 1 2/26/2010 12:45 PM 1,2-dichlorobenzene 1 2/26/2010 12:45 PM 1,1,2,3,4,4-hexachloro-1,3-butadiene 1 2/26/2010 12:45 PM 1,2,4-trichlorobenzene 1 2/26/2010 12:45 PM Dichlorodifluoromethane (Freon 12) 2 2/26/2010 4:26 PM 1,2-Chloro-1,1,2,2-Tetrafluoroethane 2 2/26/2010 4:26 PM Chloromethane 2 2/26/2010 4:26 PM Vinyl Chloride 2 2/26/2010 4:26 PM 1,3-Butadiene 2 2/26/2010 4:26 PM Bromomethane 2 2/26/2010 4:26 PM Chloroethane 2 2/26/2010 4:26 PM Trichloromonofluoromethane 2 2/26/2010 4:26 PM 1,1-Dichloroethene 2 2/26/2010 4:26 PM 1,1,2-Trichloro-1,2,2-trifluoroethane 2 2/26/2010 4:26 PM Ethanol 2 2/26/2010 4:26 PM Carbon disulfide 2 2/26/2010 4:26 PM Isopropyl alcohol 2 2/26/2010 4:26 PM Methylene chloride 2 2/26/2010 4:26 PM Acetone 2 2/26/2010 4:26 PM t-1,2-dichloroethene 2 2/26/2010 4:26 PM Hexane 2 2/26/2010 4:26 PM Methyl-t-butyl ether (MTBE) 2 2/26/2010 4:26 PM 1,1-Dichloroethane 2 2/26/2010 4:26 PM Vinyl acetate 2 2/26/2010 4:26 PM cis-1,2-dichloroethene 2 2/26/2010 4:26 PM Cyclohexane 2 2/26/2010 4:26 PM Chloroform 2 2/26/2010 4:26 PM Ethyl Acetate 2 2/26/2010 4:26 PM Tetrahydrofuran 2 2/26/2010 4:26 PM 1,1,1-trichloroethane 2 2/26/2010 4:26 PM Carbon Tetrachloride 2 2/26/2010 4:26 PM 2-Butanone 2 2/26/2010 4:26 PM Heptane 2 2/26/2010 4:26 PM Benzene 2 2/26/2010 4:26 PM 1,2-dichloroethane 2 2/26/2010 4:26 PM Trichloroethylene 2 2/26/2010 4:26 PM 1,2-dichloropropane 2 2/26/2010 4:26 PM Bromodichloromethane 2 2/26/2010 4:26 PM 1,4-dioxane 2 2/26/2010 4:26 PM cis-1,3-dichloropropene 2 2/26/2010 4:26 PM Toluene 2 2/26/2010 4:26 PM 4-Methyl-2-pentanone (MIBK) 2 2/26/2010 4:26 PM t-1,3-dichloropropene 2 2/26/2010 4:26 PM Tetrachloroethylene 2 2/26/2010 4:26 PM 1,1,2-trichloroethane 2 2/26/2010 4:26 PM Dibromochloromethane 2 2/26/2010 4:26 PM1,2-dibromoethane 2 2/26/2010 4:26 PM

2-Hexanone 2 2/26/2010 4:26 PM Ethylbenzene 2 2/26/2010 4:26 PM Chlorobenzene 2 2/26/2010 4:26 PM m/p-Xylene 2 2/26/2010 4:26 PM o-Xylene 2 2/26/2010 4:26 PM Styrene 2 2/26/2010 4:26 PM Tribromomethane 2 2/26/2010 4:26 PM 1,1,2,2-tetrachloroethane 2 2/26/2010 4:26 PM 1-ethyl-4-methylbenzene 2 2/26/2010 4:26 PM 1,3,5-trimethylbenzene 2 2/26/2010 4:26 PM 1,2,4-trimethylbenzene 2 2/26/2010 4:26 PM 1,3-dichlorobenzene 2 2/26/2010 4:26 PM 1,4-dichlorobenzene 2 2/26/2010 4:26 PM Benzyl chloride 2 2/26/2010 4:26 PM 1,2-dichlorobenzene 2 2/26/2010 4:26 PM 1,1,2,3,4,4-hexachloro-1,3-butadiene 2 2/26/2010 4:26 PM 1,2,4-trichlorobenzene 2 2/26/2010 4:26 PM Dichlorodifluoromethane (Freon 12) 3 2/27/2010 8:27 AM 1,2-Chloro-1,1,2,2-Tetrafluoroethane 3 2/27/2010 8:27 AM Chloromethane 3 2/27/2010 8:27 AM Vinyl Chloride 3 2/27/2010 8:27 AM 1,3-Butadiene 3 2/27/2010 8:27 AM Bromomethane 3 2/27/2010 8:27 AM Chloroethane 3 2/27/2010 8:27 AM Trichloromonofluoromethane 3 2/27/2010 8:27 AM 1,1-Dichloroethene 3 2/27/2010 8:27 AM 1,1,2-Trichloro-1,2,2-trifluoroethane 3 2/27/2010 8:27 AM Ethanol 3 2/27/2010 8:27 AM Carbon disulfide 3 2/27/2010 8:27 AM Isopropyl alcohol 3 2/27/2010 8:27 AM Methylene chloride 3 2/27/2010 8:27 AM Acetone 3 2/27/2010 8:27 AM t-1,2-dichloroethene 3 2/27/2010 8:27 AM Hexane 3 2/27/2010 8:27 AM Methyl-t-butyl ether (MTBE) 3 2/27/2010 8:27 AM 1,1-Dichloroethane 3 2/27/2010 8:27 AM Vinyl acetate 3 2/27/2010 8:27 AM cis-1,2-dichloroethene 3 2/27/2010 8:27 AM Cyclohexane 3 2/27/2010 8:27 AM Chloroform 3 2/27/2010 8:27 AM Ethyl Acetate 3 2/27/2010 8:27 AM Tetrahydrofuran 3 2/27/2010 8:27 AM 1,1,1-trichloroethane 3 2/27/2010 8:27 AM Carbon Tetrachloride 3 2/27/2010 8:27 AM 2-Butanone 3 2/27/2010 8:27 AM Heptane 3 2/27/2010 8:27 AM Benzene 3 2/27/2010 8:27 AM 1,2-dichloroethane 3 2/27/2010 8:27 AM Trichloroethylene 3 2/27/2010 8:27 AM 1,2-dichloropropane 3 2/27/2010 8:27 AM Bromodichloromethane 3 2/27/2010 8:27 AM 1,4-dioxane 3 2/27/2010 8:27 AM cis-1,3-dichloropropene 3 2/27/2010 8:27 AM Toluene 3 2/27/2010 8:27 AM4-Methyl-2-pentanone (MIBK) 3 2/27/2010 8:27 AM

t-1,3-dichloropropene 3 2/27/2010 8:27 AM Tetrachloroethylene 3 2/27/2010 8:27 AM 1,1,2-trichloroethane 3 2/27/2010 8:27 AM Dibromochloromethane 3 2/27/2010 8:27 AM 1,2-dibromoethane 3 2/27/2010 8:27 AM 2-Hexanone 3 2/27/2010 8:27 AM Ethylbenzene 3 2/27/2010 8:27 AM Chlorobenzene 3 2/27/2010 8:27 AM m/p-Xylene 3 2/27/2010 8:27 AM o-Xylene 3 2/27/2010 8:27 AM Styrene 3 2/27/2010 8:27 AM Tribromomethane 3 2/27/2010 8:27 AM 1,1,2,2-tetrachloroethane 3 2/27/2010 8:27 AM 1-ethyl-4-methylbenzene 3 2/27/2010 8:27 AM 1,3,5-trimethylbenzene 3 2/27/2010 8:27 AM 1,2,4-trimethylbenzene 3 2/27/2010 8:27 AM 1,3-dichlorobenzene 3 2/27/2010 8:27 AM 1,4-dichlorobenzene 3 2/27/2010 8:27 AM Benzyl chloride 3 2/27/2010 8:27 AM 1,2-dichlorobenzene 3 2/27/2010 8:27 AM 1,1,2,3,4,4-hexachloro-1,3-butadiene 3 2/27/2010 8:27 AM 1,2,4-trichlorobenzene 3 2/27/2010 8:27 AMMe asured Value (μg/m3) Data Flag (ADL, BDL, DDL) lb/mmBtu

2/26/2010 2:57 PM 8.983776031 ADL 1.31849E-05 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 52.86121684 ADL 7.75811E-05 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 0.65295013 ADL 9.58294E-07 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 1.384114541 ADL 2.03138E-06 2/26/2010 2:57 PM 2.963625126 ADL 4.34953E-06 2/26/2010 2:57 PM 4.557525318 ADL 6.6888E-06 2/26/2010 2:57 PM 0.704053623 ADL 1.0333E-06 2/26/2010 2:57 PM 54.78291732 ADL 8.04015E-05 2/26/2010 2:57 PM 10.88218689 ADL 1.59711E-05 2/26/2010 2:57 PM 30.7509369 ADL 4.51312E-05 2/26/2010 2:57 PM 312.5852223 ADL 0.000458762 2/26/2010 2:57 PM 377.3051463 ADL 0.000553747 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 19.13900649 ADL 2.80891E-05 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 1.030657314 ADL 1.51263E-06 2/26/2010 2:57 PM 0.769851819 ADL 1.12986E-06 2/26/2010 2:57 PM 5.094587258 ADL 7.47701E-06 2/26/2010 2:57 PM 3.659268062 ADL 5.37048E-06 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 0.815390781 ADL 1.1967E-06 2/26/2010 2:57 PM 20.88730925 ADL 3.0655E-05 2/26/2010 2:57 PM 5.229653712 ADL 7.67524E-06 2/26/2010 2:57 PM 50.13603835 ADL 7.35816E-05 2/26/2010 2:57 PM 3.501616345 ADL 5.13911E-06 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 393.6909194 ADL 0.000577796 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 5.751038235 ADL 8.44044E-06 2/26/2010 2:57 PM 3.463147036 ADL 5.08265E-06 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 0.543551567 ADL 7.97737E-07 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 20.5364913 ADL 3.01401E-05 2/26/2010 2:57 PM 1.179094596 ADL 1.73048E-06 2/26/2010 2:57 PM 0.638366677 DDL 9.36891E-07 2/26/2010 2:57 PM 0.638366677 DDL 9.36891E-07 Calculated Emission Rate Test End Date Test End Time2/26/2010 2:57 PM 0.747524756 ADL 1.0971E-06

2/26/2010 2:57 PM 1.010317616 ADL 1.48278E-06 2/26/2010 2:57 PM 0.879811572 ADL 1.29124E-06 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 0.604556009 ADL 8.87269E-07 2/26/2010 2:57 PM 0.589032865 ADL 8.64487E-07 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM 9.185223931 ADL 1.34806E-05 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 2:57 PM [<0.638] BDL [<9.3689E-07] 2/26/2010 6:41 PM 3.422314772 ADL 5.31205E-06 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 15.05073038 ADL 2.33615E-05 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 0.718397808 ADL 1.11508E-06 2/26/2010 6:41 PM 2.906806347 ADL 4.51189E-06 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 1.88800913 ADL 2.93053E-06 2/26/2010 6:41 PM 6.375497889 ADL 9.89593E-06 2/26/2010 6:41 PM 0.677329722 ADL 1.05134E-06 2/26/2010 6:41 PM 25.41509308 ADL 3.94488E-05 2/26/2010 6:41 PM 1.954148588 ADL 3.03319E-06 2/26/2010 6:41 PM 8.887461409 ADL 1.3795E-05 2/26/2010 6:41 PM 519.7976726 ADL 0.00080682 2/26/2010 6:41 PM 137.9303153 ADL 0.000214093 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 2.038626086 ADL 3.16432E-06 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 0.885782327 ADL 1.38122E-06 2/26/2010 6:41 PM 0.337625084 ADL 5.24055E-07 2/26/2010 6:41 PM 1.918162642 ADL 2.97734E-06 2/26/2010 6:41 PM 1.134453037 ADL 1.76088E-06 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 0.584762816 ADL 9.07658E-07 2/26/2010 6:41 PM 6.762354785 ADL 1.04964E-05 2/26/2010 6:41 PM 1.745160495 ADL 2.70881E-06 2/26/2010 6:41 PM 20.26960877 ADL 3.14621E-05 2/26/2010 6:41 PM 0.659533333 ADL 1.02372E-06 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 83.48182498 ADL 0.000129579 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 4.465794878 ADL 6.93172E-06 2/26/2010 6:41 PM 5.951650213 ADL 9.23804E-06 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06]2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06]

2/26/2010 6:41 PM 8.215841732 ADL 1.27525E-05 2/26/2010 6:41 PM 1.65581091 ADL 2.57012E-06 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 0.646556149 DDL 1.00357E-06 2/26/2010 6:41 PM 0.987412078 ADL 1.53264E-06 2/26/2010 6:41 PM 2.353808563 ADL 3.65354E-06 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 0.678184032 ADL 1.05266E-06 2/26/2010 6:41 PM 0.614167148 ADL 9.53299E-07 2/26/2010 6:41 PM 0.591858534 ADL 9.18672E-07 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM 1.676286598 ADL 2.6019E-06 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/26/2010 6:41 PM [<0.6465] BDL [<1.003E-06] 2/27/2010 10:47 AM 3.532991416 ADL 4.47478E-06 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 44.70667291 ADL 5.66241E-05 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 0.848995695 ADL 1.07531E-06 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 13.713427 ADL 1.7369E-05 2/27/2010 10:47 AM 10.02305126 ADL 1.26949E-05 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 50.71955316 ADL 6.42398E-05 2/27/2010 10:47 AM 10.06856195 ADL 1.27525E-05 2/27/2010 10:47 AM 49.90055808 ADL 6.32025E-05 2/27/2010 10:47 AM 544.2718057 ADL 0.000689357 2/27/2010 10:47 AM 258.4388973 ADL 0.000327331 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 4.477423327 ADL 5.67096E-06 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 1.878918929 ADL 2.37978E-06 2/27/2010 10:47 AM 0.725767968 ADL 9.19235E-07 2/27/2010 10:47 AM 3.129714435 ADL 3.964E-06 2/27/2010 10:47 AM 2.644524794 ADL 3.34947E-06 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 0.635703458 ADL 8.05162E-07 2/27/2010 10:47 AM 12.10735201 ADL 1.53348E-05 2/27/2010 10:47 AM 2.590973639 ADL 3.28165E-06 2/27/2010 10:47 AM 31.54277239 ADL 3.99511E-05 2/27/2010 10:47 AM 2.194116436 ADL 2.779E-06 2/27/2010 10:47 AM 0.552320143 ADL 6.99551E-07 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 250.6191783 ADL 0.000317426 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 15.06269985 ADL 1.90779E-052/27/2010 10:47 AM 1.510822911 ADL 1.91356E-06

2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 10.33557876 ADL 1.30907E-05 2/27/2010 10:47 AM 1.046215296 ADL 1.3251E-06 2/27/2010 10:47 AM 0.648155436 DDL 8.20933E-07 2/27/2010 10:47 AM 0.648155436 DDL 8.20933E-07 2/27/2010 10:47 AM 1.022941614 ADL 1.29563E-06 2/27/2010 10:47 AM 2.880103192 ADL 3.64785E-06 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 0.57209568 ADL 7.24598E-07 2/27/2010 10:47 AM 1.372219467 ADL 1.73801E-06 2/27/2010 10:47 AM 0.63381964 ADL 8.02776E-07 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM 5.992218951 ADL 7.58956E-06 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07] 2/27/2010 10:47 AM [<0.6481] BDL [<8.209E-07]ug/dscm @ 7% O2

15.28451491 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

89.93524041 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

1.110894347 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

2.354858276 543.3 561.5 5.657418781 5.042152907 543.3 561.5 5.657418781 7.753929243 543.3 561.5 5.657418781 1.197839089 543.3 561.5 5.657418781 93.20471857 543.3 561.5 5.657418781 18.51436938 543.3 561.5 5.657418781 52.31799546 543.3 561.5 5.657418781 531.8157393 543.3 561.5 5.657418781 641.9267483 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

32.56207959 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

1.753505101 543.3 561.5 5.657418781 1.309784613 543.3 561.5 5.657418781 8.667657637 543.3 561.5 5.657418781 6.225682505 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

1.387262162 543.3 561.5 5.657418781 35.53654817 543.3 561.5 5.657418781 8.897452459 543.3 561.5 5.657418781 85.29876781 543.3 561.5 5.657418781 5.957462326 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

669.8046241 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

9.784508135 543.3 561.5 5.657418781 5.892012704 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

0.924769496 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

34.93968532 543.3 561.5 5.657418781 2.006048333 543.3 561.5 5.657418781 1.086082841 543.3 561.5 5.657418781 1.086082841 543.3 561.5 5.657418781 Calculated Emission Rate Steam Output (1000 lb/hr) Total Heat Input (mmBtu/hr) Flue Gas Moisture (%)1.271798544 543.3 561.5 5.657418781 1.718900227 543.3 561.5 5.657418781 1.496864242 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

1.028559183 543.3 561.5 5.657418781 1.002148937 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

15.62724757 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781 [<1.08608] 543.3 561.5 5.657418781

6.157951499 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

27.08157312 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

1.292651073 542.75 486.5 14.1583512 5.230369997 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

3.397194421 542.75 486.5 14.1583512 11.47176966 542.75 486.5 14.1583512 1.218755099 542.75 486.5 14.1583512 45.73071764 542.75 486.5 14.1583512 3.516202638 542.75 486.5 14.1583512 15.99167813 542.75 486.5 14.1583512 935.299372 542.75 486.5 14.1583512 248.1852922 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

3.668207455 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

1.601169249 542.75 486.5 14.1583512 0.607506624 542.75 486.5 14.1583512 3.451451226 542.75 486.5 14.1583512 2.041281193 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

1.052194581 542.75 486.5 14.1583512 12.16786168 542.75 486.5 14.1583512 3.140159338 542.75 486.5 14.1583512 36.4721763 542.75 486.5 14.1583512 1.186733117 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

150.2132514 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

8.035540297 542.75 486.5 14.1583512 10.70911818 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512[<1.16338] 542.75 486.5 14.1583512 14.78319742 542.75 486.5 14.1583512 2.979387916 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

1.163382585 542.75 486.5 14.1583512 1.77670264 542.75 486.5 14.1583512 4.235331912 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

1.220292303 542.75 486.5 14.1583512 1.105103347 542.75 486.5 14.1583512 1.064962281 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

3.016230902 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512 [<1.16338] 542.75 486.5 14.1583512

5.187343475 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

65.6409373 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

1.246544857 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

20.13485109 543.25 615.4 10.91544742 14.71642681 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

74.4693978 543.25 615.4 10.91544742 14.78324824 543.25 615.4 10.91544742 73.26690159 543.25 615.4 10.91544742 799.1315199 543.25 615.4 10.91544742 379.4550198 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

6.574013335 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

2.758738049 543.25 615.4 10.91544742 1.065614741 543.25 615.4 10.91544742 4.595228758 543.25 615.4 10.91544742 3.882845108 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

0.93337679 543.25 615.4 10.91544742 17.77671839 543.25 615.4 10.91544742 3.804218187 543.25 615.4 10.91544742 46.31293295 543.25 615.4 10.91544742 3.221529361 543.25 615.4 10.91544742 0.810948557 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

367.9736535 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

22.11593197 543.25 615.4 10.915447422.218278067 543.25 615.4 10.91544742

[<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

15.17529786 543.25 615.4 10.91544742 1.536114145 543.25 615.4 10.91544742 0.951659508 543.25 615.4 10.91544742 0.951659508 543.25 615.4 10.91544742 1.501942372 543.25 615.4 10.91544742 4.228735013 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

0.83998415 543.25 615.4 10.91544742 2.01477243 543.25 615.4 10.91544742 0.930610859 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742

8.798124371 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.91544742 [<0.95166] 543.25 615.4 10.915447426.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 Flue Gas O 2(%) Flue Gas Flow Rate (scfm) Flue Gas Temperature (F) Flue Gas CO 2(%)6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.729 12.73 220025.131 312.5 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.26.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 6.422 13.175 201589.1174 314.2 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.57.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5 7.729 11.433 208077.6978 308.5Fuel Input Rate Fuel Type Units of Measure Me asurement Method

5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter Fuel #15059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5059.752 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5057.7725 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meter 5127.543 No.6 Fuel Oil (residual or bunker C) gallon/m inute gas fuel meterFuel Input Rate Fuel Type Units of Measure Me asurement Method Fuel #2Fuel Input Rate Fuel Type Units of Measure Me asurement Method Fuel #3Fuel Input Rate Fuel Type Units of Measure Me asurement Method Fuel #4Sam ples were analy zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Trichloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Tetrachloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Ethylbenzene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Other Supporting InformationSam ples were analy zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Trichloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Tetrachloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low.Sam ples were analy zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Ethylbenzene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Trichloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low.Sam ples were analy zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Tetrachloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Ethylbenzene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low.Sam ples were analy zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Trichloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Tetrachloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Ethylbenzene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low.Sam ples were analy zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Trichloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Tetrachloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low.Sam ples were analy zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Ethylbenzene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Trichloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low.Sam ples were analy zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Tetrachloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Ethylbenzene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low. Sam ples were analy

zed from 5 to 10 days outside of the method 14 day holding tim e. Therefore some analyes may be biased low.Trichloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations

Tetrachloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations

Ethylbenzene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrationsTrichloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations

Tetrachloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrationsEthylbenzene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations

Trichloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrationsTetrachloroethylene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrations

Ethylbenzene was typically less than 5 times the field blank, method blank and/or blank tube concentrations. Therefor this compound may not be accurately

quantified with this method. Low sample concentration vs the blank concentrationsEIA

Facility Code Facility Name Boiler ID

1210003 Progress Energy

Unit 3

Speciated Semi-Volatile Organic HAP Emission Data

N-Nitrosodimethylam ine 1 2/26/2010 12:45 PM Phenol (CCC) 1 2/26/2010 12:45 PM Aniline 1 2/26/2010 12:45 PM bis(2-Chloroethyl)ether 1 2/26/2010 12:45 PM 2-Chlorophenol 1 2/26/2010 12:45 PM 1,3-Dichlorobenzene 1 2/26/2010 12:45 PM 1,4-Dichlorobenzene (CCC) 1 2/26/2010 12:45 PM Benzyl alcohol 1 2/26/2010 12:45 PM 1,2-Dichlorobenzene 1 2/26/2010 12:45 PM 2-Methylphenol 1 2/26/2010 12:45 PM 3/4-Methylphenol 1 2/26/2010 12:45 PM N-Nitrso-di-n-propylam ine (SPCC) 1 2/26/2010 12:45 PM Hexachloroethane 1 2/26/2010 12:45 PM Nitrobenzene 1 2/26/2010 12:45 PM Isophorone 1 2/26/2010 12:45 PM 2,4-Dimethylphenol 1 2/26/2010 12:45 PM 2-Nitrophenol (CCC) 1 2/26/2010 12:45 PM bis(2-Chloroethoxy)methane 1 2/26/2010 12:45 PM 2,4-Dichlorophenol (CCC) 1 2/26/2010 12:45 PM 1,2,4-Trichlorobenzene 1 2/26/2010 12:45 PM 4-Chloroaniline 1 2/26/2010 12:45 PM Hexachlorobutadiene (CCC) 1 2/26/2010 12:45 PM 4-Chloro-3 methylphenol (CCC) 1 2/26/2010 12:45 PM 1-Methylnaphthalene 1 2/26/2010 12:45 PM Hexachlorocyclopentadiene (SPCC) 1 2/26/2010 12:45 PM 2,4,6-Trichlorophenol (CCC) 1 2/26/2010 12:45 PM 2,4,5-Trichlorophenol 1 2/26/2010 12:45 PM 2-Chloronaphthalene 1 2/26/2010 12:45 PM 1,4-Dinitrobenzene 1 2/26/2010 12:45 PM Dim ethylphthalate 1 2/26/2010 12:45 PM 1,3-Dinitrobenzene 1 2/26/2010 12:45 PM 2,6-Dinitrotoluene 1 2/26/2010 12:45 PM 1,2-Dinitrobenzene 1 2/26/2010 12:45 PM 2,4-Dinitrophenol (SPCC) 1 2/26/2010 12:45 PM 4-Nitrophenol (SPCC) 1 2/26/2010 12:45 PM 2,4-Dinitrotoluene 1 2/26/2010 12:45 PM Dibenzofuran 1 2/26/2010 12:45 PM 2,3,5,6-Tetrachlorophenol 1 2/26/2010 12:45 PM 2,3,4,6-Tetrachlorophenol 1 2/26/2010 12:45 PM Diethlyphthalate 1 2/26/2010 12:45 PM 4-Chlorophenyl-phenylether 1 2/26/2010 12:45 PM 4,6-Dinitro2-methylphenol 1 2/26/2010 12:45 PM N-Nitrosodiphenylam ine (CCC) 1 2/26/2010 12:45 PM Azobenzene 1 2/26/2010 12:45 PM 4-Bromophenyl-phenylether 1 2/26/2010 12:45 PM Hexachlorobenzene 1 2/26/2010 12:45 PM

Compound (use drop down to define for as many rows as

needed) Run Number Test Start Date Test Start TimePentachlorophenol (CCC) 1 2/26/2010 12:45 PM

Carbazole 1 2/26/2010 12:45 PM Di-n-butylphthalate 1 2/26/2010 12:45 PM Benzidine 1 2/26/2010 12:45 PM Butylbenzylphthalate 1 2/26/2010 12:45 PM 3,3-Dimethylbenzidine 1 2/26/2010 12:45 PM bis(2-Ethylhexyl)phthalate 1 2/26/2010 12:45 PM 3,3'-Dichlorobenzidine 1 2/26/2010 12:45 PM Di-n-octylphthalate (CCC) 1 2/26/2010 12:45 PM Naphthalene 1 2/26/2010 12:45 PM 2-Methylnaphthalene 1 2/26/2010 12:45 PM Acenaphthylene 1 2/26/2010 12:45 PM Acenaphthene (CCC) 1 2/26/2010 12:45 PM Fluorene 1 2/26/2010 12:45 PM Phenanthrene 1 2/26/2010 12:45 PM Anthracene 1 2/26/2010 12:45 PM Fluoranthene (CCC) 1 2/26/2010 12:45 PM Pyrene 1 2/26/2010 12:45 PM Benzo(a)anthracene 1 2/26/2010 12:45 PM Chrysene 1 2/26/2010 12:45 PM Benzo(b)fluoranthene 1 2/26/2010 12:45 PM Benzo(k)fluoranthene 1 2/26/2010 12:45 PM Benzo(e)pyrene 1 2/26/2010 12:45 PM Benzo(a)pyrene (CCC) 1 2/26/2010 12:45 PM Perylene 1 2/26/2010 12:45 PM Indeno(1,2,3-cd)pyrene 1 2/26/2010 12:45 PM Dibenz(a,h)anthracene 1 2/26/2010 12:45 PM Benzo(g,h,i)perylene 1 2/26/2010 12:45 PM N-Nitrosodimethylam ine 2 2/26/2010 4:25 PM Phenol (CCC) 2 2/26/2010 4:25 PM Aniline 2 2/26/2010 4:25 PM bis(2-Chloroethyl)ether 2 2/26/2010 4:25 PM 2-Chlorophenol 2 2/26/2010 4:25 PM 1,3-Dichlorobenzene 2 2/26/2010 4:25 PM 1,4-Dichlorobenzene (CCC) 2 2/26/2010 4:25 PM Benzyl alcohol 2 2/26/2010 4:25 PM 1,2-Dichlorobenzene 2 2/26/2010 4:25 PM 2-Methylphenol 2 2/26/2010 4:25 PM 3/4-Methylphenol 2 2/26/2010 4:25 PM N-Nitrso-di-n-propylam ine (SPCC) 2 2/26/2010 4:25 PM Hexachloroethane 2 2/26/2010 4:25 PM Nitrobenzene 2 2/26/2010 4:25 PM Isophorone 2 2/26/2010 4:25 PM 2,4-Dimethylphenol 2 2/26/2010 4:25 PM 2-Nitrophenol (CCC) 2 2/26/2010 4:25 PM bis(2-Chloroethoxy)methane 2 2/26/2010 4:25 PM 2,4-Dichlorophenol (CCC) 2 2/26/2010 4:25 PM 1,2,4-Trichlorobenzene 2 2/26/2010 4:25 PM 4-Chloroaniline 2 2/26/2010 4:25 PM Hexachlorobutadiene (CCC) 2 2/26/2010 4:25 PM 4-Chloro-3 methylphenol (CCC) 2 2/26/2010 4:25 PM 1-Methylnaphthalene 2 2/26/2010 4:25 PM Hexachlorocyclopentadiene (SPCC) 2 2/26/2010 4:25 PM 2,4,6-Trichlorophenol (CCC) 2 2/26/2010 4:25 PM 2,4,5-Trichlorophenol 2 2/26/2010 4:25 PM2-Chloronaphthalene 2 2/26/2010 4:25 PM

1,4-Dinitrobenzene 2 2/26/2010 4:25 PM Dim ethylphthalate 2 2/26/2010 4:25 PM 1,3-Dinitrobenzene 2 2/26/2010 4:25 PM 2,6-Dinitrotoluene 2 2/26/2010 4:25 PM 1,2-Dinitrobenzene 2 2/26/2010 4:25 PM 2,4-Dinitrophenol (SPCC) 2 2/26/2010 4:25 PM 4-Nitrophenol (SPCC) 2 2/26/2010 4:25 PM 2,4-Dinitrotoluene 2 2/26/2010 4:25 PM Dibenzofuran 2 2/26/2010 4:25 PM 2,3,5,6-Tetrachlorophenol 2 2/26/2010 4:25 PM 2,3,4,6-Tetrachlorophenol 2 2/26/2010 4:25 PM Diethlyphthalate 2 2/26/2010 4:25 PM 4-Chlorophenyl-phenylether 2 2/26/2010 4:25 PM 4,6-Dinitro2-methylphenol 2 2/26/2010 4:25 PM N-Nitrosodiphenylam ine (CCC) 2 2/26/2010 4:25 PM Azobenzene 2 2/26/2010 4:25 PM 4-Bromophenyl-phenylether 2 2/26/2010 4:25 PM Hexachlorobenzene 2 2/26/2010 4:25 PM Pentachlorophenol (CCC) 2 2/26/2010 4:25 PM Carbazole 2 2/26/2010 4:25 PM Di-n-butylphthalate 2 2/26/2010 4:25 PM Benzidine 2 2/26/2010 4:25 PM Butylbenzylphthalate 2 2/26/2010 4:25 PM 3,3-Dimethylbenzidine 2 2/26/2010 4:25 PM bis(2-Ethylhexyl)phthalate 2 2/26/2010 4:25 PM 3,3'-Dichlorobenzidine 2 2/26/2010 4:25 PM Di-n-octylphthalate (CCC) 2 2/26/2010 4:25 PM Naphthalene 2 2/26/2010 4:25 PM 2-Methylnaphthalene 2 2/26/2010 4:25 PM Acenaphthylene 2 2/26/2010 4:25 PM Acenaphthene (CCC) 2 2/26/2010 4:25 PM Fluorene 2 2/26/2010 4:25 PM Phenanthrene 2 2/26/2010 4:25 PM Anthracene 2 2/26/2010 4:25 PM Fluoranthene (CCC) 2 2/26/2010 4:25 PM Pyrene 2 2/26/2010 4:25 PM Benzo(a)anthracene 2 2/26/2010 4:25 PM Chrysene 2 2/26/2010 4:25 PM Benzo(b)fluoranthene 2 2/26/2010 4:25 PM Benzo(k)fluoranthene 2 2/26/2010 4:25 PM Benzo(e)pyrene 2 2/26/2010 4:25 PM Benzo(a)pyrene (CCC) 2 2/26/2010 4:25 PM Perylene 2 2/26/2010 4:25 PM Indeno(1,2,3-cd)pyrene 2 2/26/2010 4:25 PM Dibenz(a,h)anthracene 2 2/26/2010 4:25 PM Benzo(g,h,i)perylene 2 2/26/2010 4:25 PM N-Nitrosodimethylam ine 3 2/27/2010 8:27 AM Phenol (CCC) 3 2/27/2010 8:27 AM Aniline 3 2/27/2010 8:27 AM bis(2-Chloroethyl)ether 3 2/27/2010 8:27 AM 2-Chlorophenol 3 2/27/2010 8:27 AM 1,3-Dichlorobenzene 3 2/27/2010 8:27 AM 1,4-Dichlorobenzene (CCC) 3 2/27/2010 8:27 AM Benzyl alcohol 3 2/27/2010 8:27 AM1,2-Dichlorobenzene 3 2/27/2010 8:27 AM

2-Methylphenol 3 2/27/2010 8:27 AM 3/4-Methylphenol 3 2/27/2010 8:27 AM N-Nitrso-di-n-propylam ine (SPCC) 3 2/27/2010 8:27 AM Hexachloroethane 3 2/27/2010 8:27 AM Nitrobenzene 3 2/27/2010 8:27 AM Isophorone 3 2/27/2010 8:27 AM 2,4-Dimethylphenol 3 2/27/2010 8:27 AM 2-Nitrophenol (CCC) 3 2/27/2010 8:27 AM bis(2-Chloroethoxy)methane 3 2/27/2010 8:27 AM 2,4-Dichlorophenol (CCC) 3 2/27/2010 8:27 AM 1,2,4-Trichlorobenzene 3 2/27/2010 8:27 AM 4-Chloroaniline 3 2/27/2010 8:27 AM Hexachlorobutadiene (CCC) 3 2/27/2010 8:27 AM 4-Chloro-3 methylphenol (CCC) 3 2/27/2010 8:27 AM 1-Methylnaphthalene 3 2/27/2010 8:27 AM Hexachlorocyclopentadiene (SPCC) 3 2/27/2010 8:27 AM 2,4,6-Trichlorophenol (CCC) 3 2/27/2010 8:27 AM 2,4,5-Trichlorophenol 3 2/27/2010 8:27 AM 2-Chloronaphthalene 3 2/27/2010 8:27 AM 1,4-Dinitrobenzene 3 2/27/2010 8:27 AM Dim ethylphthalate 3 2/27/2010 8:27 AM 1,3-Dinitrobenzene 3 2/27/2010 8:27 AM 2,6-Dinitrotoluene 3 2/27/2010 8:27 AM 1,2-Dinitrobenzene 3 2/27/2010 8:27 AM 2,4-Dinitrophenol (SPCC) 3 2/27/2010 8:27 AM 4-Nitrophenol (SPCC) 3 2/27/2010 8:27 AM 2,4-Dinitrotoluene 3 2/27/2010 8:27 AM Dibenzofuran 3 2/27/2010 8:27 AM 2,3,5,6-Tetrachlorophenol 3 2/27/2010 8:27 AM 2,3,4,6-Tetrachlorophenol 3 2/27/2010 8:27 AM Diethlyphthalate 3 2/27/2010 8:27 AM 4-Chlorophenyl-phenylether 3 2/27/2010 8:27 AM 4,6-Dinitro2-methylphenol 3 2/27/2010 8:27 AM N-Nitrosodiphenylam ine (CCC) 3 2/27/2010 8:27 AM Azobenzene 3 2/27/2010 8:27 AM 4-Bromophenyl-phenylether 3 2/27/2010 8:27 AM Hexachlorobenzene 3 2/27/2010 8:27 AM Pentachlorophenol (CCC) 3 2/27/2010 8:27 AM Carbazole 3 2/27/2010 8:27 AM Di-n-butylphthalate 3 2/27/2010 8:27 AM Benzidine 3 2/27/2010 8:27 AM Butylbenzylphthalate 3 2/27/2010 8:27 AM 3,3-Dimethylbenzidine 3 2/27/2010 8:27 AM bis(2-Ethylhexyl)phthalate 3 2/27/2010 8:27 AM 3,3'-Dichlorobenzidine 3 2/27/2010 8:27 AM Di-n-octylphthalate (CCC) 3 2/27/2010 8:27 AM Naphthalene 3 2/27/2010 8:27 AM 2-Methylnaphthalene 3 2/27/2010 8:27 AM Acenaphthylene 3 2/27/2010 8:27 AM Acenaphthene (CCC) 3 2/27/2010 8:27 AM Fluorene 3 2/27/2010 8:27 AM Phenanthrene 3 2/27/2010 8:27 AM Anthracene 3 2/27/2010 8:27 AM Fluoranthene (CCC) 3 2/27/2010 8:27 AMPyrene 3 2/27/2010 8:27 AM

Benzo(a)anthracene 3 2/27/2010 8:27 AM Chrysene 3 2/27/2010 8:27 AM Benzo(b)fluoranthene 3 2/27/2010 8:27 AM Benzo(k)fluoranthene 3 2/27/2010 8:27 AM Benzo(e)pyrene 3 2/27/2010 8:27 AM Benzo(a)pyrene (CCC) 3 2/27/2010 8:27 AM Perylene 3 2/27/2010 8:27 AM Indeno(1,2,3-cd)pyrene 3 2/27/2010 8:27 AM Dibenz(a,h)anthracene 3 2/27/2010 8:27 AM Benzo(g,h,i)perylene 3 2/27/2010 8:27 AMFootnotes: * Front Half Composite contains particulate filter, front half of the filter holder, and probe solvent rinses ** Back Half Composite contains XAD-2 resin tube, back half of the filter holder, and coil condenser solvent rinses *** Condensate Composite contains condensate and Impinger contents and the glassware solvent rinses

Me asured Value (μg/m3) Basis (Wet or Dry)

2/26/2010 2:57 PM [<15.0979] Dry 2/26/2010 2:57 PM 22.83258429 Dry 2/26/2010 2:57 PM [<13.5724312639982] Dry 2/26/2010 2:57 PM [<15.4107720980268] Dry 2/26/2010 2:57 PM [<12.2034540471684] Dry 2/26/2010 2:57 PM [<10.9127040998718] Dry 2/26/2010 2:57 PM [<10.3259995783733] Dry 2/26/2010 2:57 PM [<13.6897721682979] Dry 2/26/2010 2:57 PM [<10.9127040998718] Dry 2/26/2010 2:57 PM [<13.2595221858657] Dry 2/26/2010 2:57 PM [<11.5385222561368] Dry 2/26/2010 2:57 PM [<16.2712720628912] Dry 2/26/2010 2:57 PM {12.3599085862347] Dry 2/26/2010 2:57 PM [<15.9583629847587] Dry 2/26/2010 2:57 PM 26.88410496 Dry 2/26/2010 2:57 PM [<14.2373630550298] Dry 2/26/2010 2:57 PM [<13.1030676467994] Dry 2/26/2010 2:57 PM [<14.3155903245629] Dry 2/26/2010 2:57 PM [<12.7510449339003] Dry 2/26/2010 2:57 PM [<12.0861131428687] Dry 2/26/2010 2:57 PM [<16.5841811410237] Dry 2/26/2010 2:57 PM [<11.9296586038025] Dry 2/26/2010 2:57 PM [<12.9466131077332] Dry 2/26/2010 2:57 PM [<12.0078858733356] Dry 2/26/2010 2:57 PM [<158.801357152256] Dry 2/26/2010 2:57 PM [<14.4329312288626] Dry 2/26/2010 2:57 PM [<10.5606813869727] Dry 2/26/2010 2:57 PM [<12.7510449339003] Dry 2/26/2010 2:57 PM [<13.142181281566] Dry 2/26/2010 2:57 PM [<15.841022080459] Dry 2/26/2010 2:57 PM [<15.9974766195253] Dry 2/26/2010 2:57 PM [<15.1760902894274] Dry 2/26/2010 2:57 PM [<15.215203924194] Dry 2/26/2010 2:57 PM [<98.9574959594106] Dry 2/26/2010 2:57 PM [<113.038404475374] Dry 2/26/2010 2:57 PM [<15.7236811761593] Dry 2/26/2010 2:57 PM [<13.4550903596985] Dry 2/26/2010 2:57 PM [<14.8631812112949] Dry 2/26/2010 2:57 PM [<13.6897721682979] Dry 2/26/2010 2:57 PM [<19.9479537309484] Dry 2/26/2010 2:57 PM [<14.7458403069952] Dry 2/26/2010 2:57 PM [<100.913177697739] Dry 2/26/2010 2:57 PM [<14.0026812464304] Dry 2/26/2010 2:57 PM [<19.4003628442165] Dry 2/26/2010 2:57 PM [<13.1030676467994] Dry 2/26/2010 2:57 PM [<10.6780222912724] Dry Test End Date Test End Time2/26/2010 2:57 PM [<11.069158638938] Dry

2/26/2010 2:57 PM [<13.8071130725976] Dry 2/26/2010 2:57 PM [<20.2999764438475] Dry 2/26/2010 2:57 PM [<445.24354242607] Dry 2/26/2010 2:57 PM [<15.841022080459] Dry 2/26/2010 2:57 PM [<210.822491391788] Dry 2/26/2010 2:57 PM 43.87246033 Dry 2/26/2010 2:57 PM [<183.051810707526] Dry 2/26/2010 2:57 PM [<12.5945903948341] Dry 2/26/2010 2:57 PM 0.532923274 Dry 2/26/2010 2:57 PM 0.606196149 Dry 2/26/2010 2:57 PM {<0.195568173832827] Dry 2/26/2010 2:57 PM [<1.03162211696816] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM 0.229368873 Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 2:57 PM [<0.195568] Dry 2/26/2010 6:41 PM [<19.1071494513223] Dry 2/26/2010 6:41 PM [<16.0876258333672] Dry 2/26/2010 6:41 PM [<17.1766343513182] Dry 2/26/2010 6:41 PM [<19.503152548759] Dry 2/26/2010 6:41 PM [<15.4441208000325] Dry 2/26/2010 6:41 PM [<13.810608023106] Dry 2/26/2010 6:41 PM [<13.0681022154121] Dry 2/26/2010 6:41 PM [<17.325135512857] Dry 2/26/2010 6:41 PM [<13.810608023106] Dry 2/26/2010 6:41 PM [<16.7806312538815] Dry 2/26/2010 6:41 PM [<14.6026142179795] Dry 2/26/2010 6:41 PM [<20.59216106671] Dry 2/26/2010 6:41 PM [<15.6421223487509] Dry 2/26/2010 6:41 PM [<20.1961579692733] Dry 2/26/2010 6:41 PM [<18.5131448051672] Dry 2/26/2010 6:41 PM [<18.0181409333713] Dry 2/26/2010 6:41 PM [<16.5826297051631] Dry 2/26/2010 6:41 PM [<18.1171417077304] Dry 2/26/2010 6:41 PM [<16.1371262205468] Dry 2/26/2010 6:41 PM [<15.2956196384937] Dry 2/26/2010 6:41 PM [<20.9881641641467] Dry 2/26/2010 6:41 PM [<15.0976180897754] Dry 2/26/2010 6:41 PM [<16.3846281564447] Dry 2/26/2010 6:41 PM [<15.1966188641345] Dry 2/26/2010 6:41 PM [<200.971571949141] Dry 2/26/2010 6:41 PM [<18.2656428692692] Dry 2/26/2010 6:41 PM [<13.3651045384897] Dry2/26/2010 6:41 PM [<16.1371262205468] Dry

2/26/2010 6:41 PM [<16.6321300923427] Dry 2/26/2010 6:41 PM [<20.0476568077345] Dry 2/26/2010 6:41 PM [<20.2456583564529] Dry 2/26/2010 6:41 PM [<19.2061502256814] Dry 2/26/2010 6:41 PM [<19.255650612861] Dry 2/26/2010 6:41 PM [<125.235979564366] Dry 2/26/2010 6:41 PM [<143.056118949019] Dry 2/26/2010 6:41 PM [<19.8991556461957] Dry 2/26/2010 6:41 PM [<17.0281331897794] Dry 2/26/2010 6:41 PM [<18.8101471282447] Dry 2/26/2010 6:41 PM [<17.325135512857] Dry 2/26/2010 6:41 PM [<25.2451974615916] Dry 2/26/2010 6:41 PM [<18.6616459667059] Dry 2/26/2010 6:41 PM [<127.710998923346] Dry 2/26/2010 6:41 PM [<17.7211386102937] Dry 2/26/2010 6:41 PM [<24.5521920410773] Dry 2/26/2010 6:41 PM [<16.5826297051631] Dry 2/26/2010 6:41 PM [<13.5136057000284] Dry 2/26/2010 6:41 PM [<14.0086095718244] Dry 2/26/2010 6:41 PM [<17.4736366743957] Dry 2/26/2010 6:41 PM [<25.6907009462079] Dry 2/26/2010 6:41 PM [<563.479407394348] Dry 2/26/2010 6:41 PM [<20.0476568077345] Dry 2/26/2010 6:41 PM [<266.807086897997] Dry 2/26/2010 6:41 PM 51.10914976 Dry 2/26/2010 6:41 PM [<231.661812000488] Dry 2/26/2010 6:41 PM [<15.9391246718284] Dry 2/26/2010 6:41 PM 0.523879098 Dry 2/26/2010 6:41 PM [<0.256040752686436] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM 0.307727407 Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/26/2010 6:41 PM [<0.2475] Dry 2/27/2010 10:47 AM [<18.9166669816673] Dry 2/27/2010 10:47 AM 19.36589698 Dry 2/27/2010 10:47 AM [<17.005397519789] Dry 2/27/2010 10:47 AM [<19.3087222558988] Dry 2/27/2010 10:47 AM [<15.2901556950265] Dry 2/27/2010 10:47 AM [<13.6729276888217] Dry 2/27/2010 10:47 AM [<12.9378240496378] Dry 2/27/2010 10:47 AM [<17.1524182476258] Dry2/27/2010 10:47 AM [<13.6729276888217] Dry

2/27/2010 10:47 AM [<16.6133422455576] Dry 2/27/2010 10:47 AM [<14.4570382372846] Dry 2/27/2010 10:47 AM [<20.3868742600353] Dry 2/27/2010 10:47 AM [<15.4861833321422] Dry 2/27/2010 10:47 AM [<19.9948189858038] Dry 2/27/2010 10:47 AM 23.47430954 Dry 2/27/2010 10:47 AM [<17.8385149775309] Dry 2/27/2010 10:47 AM [<16.4173146084419] Dry 2/27/2010 10:47 AM [<17.9365287960887] Dry 2/27/2010 10:47 AM [<15.9762524249315] Dry 2/27/2010 10:47 AM [<15.1431349671897] Dry 2/27/2010 10:47 AM [<20.7789295342667] Dry 2/27/2010 10:47 AM [<14.9471073300739] Dry 2/27/2010 10:47 AM 17.8916058 Dry 2/27/2010 10:47 AM [<15.0451211486318] Dry 2/27/2010 10:47 AM [<198.96805167246] Dry 2/27/2010 10:47 AM [<18.0835495239255] Dry 2/27/2010 10:47 AM [<13.2318655053114] Dry 2/27/2010 10:47 AM [<15.9762524249315] Dry 2/27/2010 10:47 AM [<16.4663215177208] Dry 2/27/2010 10:47 AM [<19.847798257967] Dry 2/27/2010 10:47 AM [<20.0438258950828] Dry 2/27/2010 10:47 AM [<19.0146808002252] Dry 2/27/2010 10:47 AM [<19.0636877095041] Dry 2/27/2010 10:47 AM [<123.987480475695] Dry 2/27/2010 10:47 AM [<141.62996781611] Dry 2/27/2010 10:47 AM [<19.7007775301302] Dry 2/27/2010 10:47 AM [<16.8583767919522] Dry 2/27/2010 10:47 AM [<18.6226255259938] Dry 2/27/2010 10:47 AM [<17.1524182476258] Dry 2/27/2010 10:47 AM [<24.9935237322548] Dry 2/27/2010 10:47 AM [<18.475604798157] Dry 2/27/2010 10:47 AM [<126.437825939642] Dry 2/27/2010 10:47 AM [<17.5444735218573] Dry 2/27/2010 10:47 AM [<24.3074270023497] Dry 2/27/2010 10:47 AM [<16.4173146084419] Dry 2/27/2010 10:47 AM [<13.3788862331481] Dry 2/27/2010 10:47 AM [<13.8689553259375] Dry 2/27/2010 10:47 AM [<17.2994389754626] Dry 2/27/2010 10:47 AM [<25.4345859157652] Dry 2/27/2010 10:47 AM [<557.861983958497] Dry 2/27/2010 10:47 AM [<19.847798257967] Dry 2/27/2010 10:47 AM [<264.147241013438] Dry 2/27/2010 10:47 AM 53.04997929 Dry 2/27/2010 10:47 AM [<229.352335425397] Dry 2/27/2010 10:47 AM [<15.7802247878158] Dry 2/27/2010 10:47 AM [<0.640765338822022] Dry 2/27/2010 10:47 AM 0.283014901 Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM 0.628105221 Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM 0.264596471 Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM [<0.24503] Dry2/27/2010 10:47 AM 0.299758928 Dry

2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM [<0.24503] Dry 2/27/2010 10:47 AM [<0.24503] Dry* Front Half Composite contains particulate filter, front half of the filter holder, and probe solvent rinses ** Back Half Composite contains XAD-2 resin tube, back half of the filter holder, and coil condenser solvent rinses *** Condensate Composite 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 -846 Method 8270C BDL [<38600] U.S. EPA Method 0010 with SW -846 Method 8270C [<32500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<34700] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<39400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<31200] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<26400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<29500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<41600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<31600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40800] U.S. EPA Method 0010 with SW -846 Method 8270C DDL 75000 U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<36400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<36600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<32600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<30900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<42400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<30500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33100] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<30700] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<406000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<36900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<32600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38800] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<253000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<289000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40200] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<34400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<51000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<37700] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<258000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35800] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<49600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27300]

Semi-Volatile Organic HAP Emission Test ResultsU.S. EPA Method 0010 with SW -846 Method 8270C BDL [<28300] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35300] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<51900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<1138000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<539000] U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<87100] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<468000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<32200] U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1030 U.S. EPA Method 0010 with SW -846 Method 8270C DDL 1732 U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3065 U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<32500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<34700] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<39400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<31200] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<26400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<29500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<41600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<31600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40800] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<37400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<36400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<36600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<32600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<30900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<42400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<30500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33100] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<30700] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<406000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<36900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27000]U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<32600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38800] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<253000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<289000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40200] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<34400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<51000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<37700] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<258000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35800] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<49600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27300] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<28300] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35300] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<51900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<1138000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<539000] U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<87100] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<468000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<32200] U.S. EPA Method 0010 with SW -846 Method 8270C ADL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38600] U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<32500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<34700] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<39400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<31200] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<26400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35000]U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<29500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<41600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<31600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40800] U.S. EPA Method 0010 with SW -846 Method 8270C DDL 50000 U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<36400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<36600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<32600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<30900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<42400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<30500] U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<33100] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<30700] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<406000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<36900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<32600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38800] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<253000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<289000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40200] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<34400] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<38000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<51000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<37700] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<258000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35800] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<49600] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<33500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<27300] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<28300] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<35300] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<51900] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<1138000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<40500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<539000] U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<87100] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<468000] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<32200] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C DDL 1438 U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500]U.S. EPA Method 0010 with SW -846 Method 8270C DDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500] U.S. EPA Method 0010 with SW -846 Method 8270C BDL [<500]Back Half mass* (ng) Condensate Mass*** (ng) Total Composite (ng)

[<3860] [<3860] [<46320] 34300 [<3250] 70050 [<3470] [<3470] [<41640] [<3940] [<3940] [<47280] [<3120] [<3120] [<37440] [<2790] [<2790] [<33480] [<2640] [<2640] [<31680] [<3500] [<3500] [<42000] [<2790] [<2790] [<33480] [<3390] [<3390] [<40680] [<2950] [<2950] [<35400] [<4160] [<4160] [<49920] [<3160] [<3160] [<37920] [<4080] [<4080] [<48960] [<3740] [<3740] 82480 [<3640] [<3640] [<43680] [<3350] [<3350] [<40200] [<3660] [<3660] [<43920] [<3260] [<3260] [<39120] [<3090] [<3090] [<37080] [<4240] [<4240] [<50880] [<3050] [<3050] [<36600] [<3310] [<3310] [<39720] [<3070] [<3070] [<36840] [<40600] [<40600] [<487200] [<3690] [<3690] [<44280] [<2700] [<2700] [<32400] [<3260] [<3260] [<39120] [<3360] [<3360] [<40320] [<4050] [<4050] [<48600] [<4090] [<4090] [<49080] [<3880] [<3880] [<46560] [<3890] [<3890] [<46680] [<25300] [<25300] [<303600] [<28900] [<28900] [<346800] [<4020] [<4020] [<48240] [<3440] [<3440] [<41280] [<3800] [<3800] [<45600] [<3500] [<3500] [<42000] [<5100] [<5100] [<61200] [<3770] [<3770] [<45240] [<25800] [<25800] [<309600] [<3580] [<3580] [<42960] [<4960] [<4960] [<59520] [<3350] [<3350] [<40200] [<2730] [<2730] [<32760] Semi-Volatile Organic HAP Emission Test Results[<2830] [<2830] [<33960]

[<3530] [<3530] [<42360] [<5190] [<5190] [<62280] [<114000] [<114000] [<1366000] [<4050] [<4050] [<48600] [<53900] [<53900] [<646800] 24700 22800 134600 [<46800] [<46800] [<561600] [<3220] [<3220] [<38640] 555 [<50] 1635 77.8 [<50] 1859.8 [<50] [<50] [<600] [<50] [<50] 3165 [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] 95.7 108 703.7 [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<3860] [<3860] [<46320] [<3250] [<3250] [<39000] [<3470] [<3470] [<41640] [<3940] [<3940] [<47280] [<3120] [<3120] [<37440] [<2790] [<2790] [<33480] [<2640] [<2640] [<31680] [<3500] [<3500] [<42000] [<2790] [<2790] [<33480] [<3390] [<3390] [<40680] [<2950] [<2950] [<35400] [<4160] [<4160] [<49920] [<3160] [<3160] [<37920] [<4080] [<4080] [<48960] [<3740] [<3740] [<44880] [<3640] [<3640] [<43680] [<3350] [<3350] [<40200] [<3660] [<3660] [<43920] [<3260] [<3260] [<39120] [<3090] [<3090] [<37080] [<4240] [<4240] [<50880] [<3050] [<3050] [<36600] [<3310] [<3310] [<39720] [<3070] [<3070] [<36840] [<40600] [<40600] [<487200] [<3690] [<3690] [<44280] [<2700] [<2700] [<32400][<3260] [<3260] [<39120]

[<3360] [<3360] [<40320] [<4050] [<4050] [<48600] [<4090] [<4090] [<49080] [<3880] [<3880] [<46560] [<3890] [<3890] [<46680] [<25300] [<25300] [<303600] [<28900] [<28900] [<346800] [<4020] [<4020] [<48240] [<3440] [<3440] [<41280] [<3800] [<3800] [<45600] [<3500] [<3500] [<42000] [<5100] [<5100] [<61200] [<3770] [<3770] [<45240] [<25800] [<25800] [<309600] [<3580] [<3580] [<42960] [<4960] [<4960] [<59520] [<3350] [<3350] [<40200] [<2730] [<2730] [<32760] [<2830] [<2830] [<33960] [<3530] [<3530] [<42360] [<5190] [<5190] [<62280] [<114000] [<114000] [<1366000] [<4050] [<4050] [<48600] [<53900] [<53900] [<646800] 19400 17400 123900 [<46800] [<46800] [<561600] [<3220] [<3220] [<38640] 720 [<50] 1270 70.7 [<50] 620.7 [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] 127 119 746 [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<3860] [<3860] [<46320] 10900 4020 47420 [<3470] [<3470] [<41640] [<3940] [<3940] [<47280] [<3120] [<3120] [<37440] [<2790] [<2790] [<33480] [<2640] [<2640] [<31680] [<3500] [<3500] [<42000][<2790] [<2790] [<33480]

[<3390] [<3390] [<40680] [<2950] [<2950] [<35400] [<4160] [<4160] [<49920] [<3160] [<3160] [<37920] [<4080] [<4080] [<48960] [<3740] [<3740] 57480 [<3640] [<3640] [<43680] [<3350] [<3350] [<40200] [<3660] [<3660] [<43920] [<3260] [<3260] [<39120] [<3090] [<3090] [<37080] [<4240] [<4240] [<50880] [<3050] [<3050] [<36600] [<3310] 7400 43810 [<3070] [<3070] [<36840] [<40600] [<40600] [<487200] [<3690] [<3690] [<44280] [<2700] [<2700] [<32400] [<3260] [<3260] [<39120] [<3360] [<3360] [<40320] [<4050] [<4050] [<48600] [<4090] [<4090] [<49080] [<3880] [<3880] [<46560] [<3890] [<3890] [<46680] [<25300] [<25300] [<303600] [<28900] [<28900] [<346800] [<4020] [<4020] [<48240] [<3440] [<3440] [<41280] [<3800] [<3800] [<45600] [<3500] [<3500] [<42000] [<5100] [<5100] [<61200] [<3770] [<3770] [<45240] [<25800] [<25800] [<309600] [<3580] [<3580] [<42960] [<4960] [<4960] [<59520] [<3350] [<3350] [<40200] [<2730] [<2730] [<32760] [<2830] [<2830] [<33960] [<3530] [<3530] [<42360] [<5190] [<5190] [<62280] [<114000] [<114000] [<1366000] [<4050] [<4050] [<48600] [<53900] [<53900] [<646800] 20400 22400 129900 [<46800] [<46800] [<561600] [<3220] [<3220] [<38640] 1019 [<50] 1569 143 [<50] 693 [<50] [<50] [<600] [<50] [<50] 1538 [<50] [<50] [<600] 97.9 [<50] 647.9 [<50] [<50] [<600] [<50] [<50] [<600]130 104 734

[<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600] [<50] [<50] [<600]Test Method Comments lb/mmBtu ug/dscm @ 7% O2

[<0.0000222] [<25.687] 0.0000335 38.846 [<0.0000199] [<23.091] [<0.0000226] [<26.219] [<0.0000179] [<20.762] [<0.0000160] [<18.566] [<0.0000152] [<17.568] [<0.0000201] [<23.291] [<0.0000160] [<18.566] [<0.0000195] [<22.559] [<0.0000169] [<19.631] [<0.0000239] [<27.683] [<0.0000181] [<21.028] [<0.0000234] [<27.151] 0.0000395 45.739 [<0.0000209] [<24.223] [<0.0000192] [<22.293] [<0.0000210] [<24.356] [<0.0000187] [<21.694] [<0.0000177] [<20.563] [<0.0000243] [<28.215] [<0.0000175] [<20.296] [<0.0000190] [<22.027] [<0.0000176] [<20.430] [<0.0002331] [<270.176] [<0.0000212] [<24.555] [<0.0000155] [<17.967] [<0.0000187] [<21.694] [<0.0000193] [<22.359] [<0.0000232] [<26.951] [<0.0000235] [<27.217] [<0.0000223] [<25.820] [<0.0000223] [<25.886] [<0.0001452] [<168.361] [<0.0001659] [<192.317] [<0.0000231] [<26.751] [<0.0000197] [<22.892] [<0.0000218] [<25.287] [<0.0000201] [<23.291] [<0.0000293] [<33.938] [<0.0000216] [<25.088] [<0.0001481] [<171.688] [<0.0000206] [<23.823] [<0.0000285] [<33.007] [<0.0000192] [<22.293] [<0.0000157] [<18.167]

Calculated Emission Rate[<0.0000162] [<18.832] [<0.0000203] [<23.491] [<0.0000298] [<34.537] [<0.0006535] [<757.513] [<0.0000232] [<26.951] [<0.0003094] [<358.682] 0.0000644 74.642 [<0.0002687] [<311.435] [<0.0000185] [<21.428] 0.000000782 0.907 The reported concentrations for 2-methylnaphthlene in all thrre runs were less than 5 times the field blank concentrations. Therefor this compound may not be accurately

quantified with this method. FLD BNK: FH=543ng, BH=120ng, condensate <50 ng; total = 663ng 0.000000890 1.031 [<0.000000287] [<0.333] 0.000001514 1.755 [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.000000287] [<0.333] The reported concentrations for pyrene in all thrre runs were less than 5 times the field blank concentrations. Therefor this compound may not be accurately

quantified with this method. FLD BNK: FH=106ng, BH=92.8ng, condensate 107 ng total = 305.8ng 0.000000337 0.390 [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.000000287] [<0.333] [<0.0000297] [<34.381] [<0.0000250] [<28.947] [<0.0000267] [<30.907] [<0.0000303] [<35.093] [<0.0000240] [<27.789] [<0.0000214] [<24.850] [<0.0000203] [<23.514] [<0.0000269] [<31.174] [<0.0000214] [<24.850] [<0.0000260] [<30.194] [<0.0000227] [<26.275] [<0.0000320] [<37.053] [<0.0000243] [<28.146] [<0.0000313] [<36.340] [<0.0000287] [<33.312] [<0.0000280] [<32.421] [<0.0000257] [<29.838] [<0.0000281] [<32.599] [<0.0000250] [<29.036] [<0.0000237] [<27.522] [<0.0000326] [<37.765] [<0.0000234] [<27.166] [<0.0000254] [<29.482] [<0.0000236] [<27.344] [<0.0003119] [<361.619] [<0.0000284] [<32.866] [<0.0000207] [<24.049][<0.0000250] [<29.036] [<0.0000258] [<29.927] [<0.0000311] [<36.073] [<0.0000314] [<36.429] [<0.0000298] [<34.559] [<0.0000299] [<34.648] [<0.0001944] [<225.344] [<0.0002220] [<257.408] [<0.0000309] [<35.806] [<0.0000264] [<30.640] [<0.0000292] [<33.846] [<0.0000269] [<31.174] [<0.0000392] [<45.425] [<0.0000290] [<33.579] [<0.0001982] [<229.797] [<0.0000275] [<31.887] [<0.0000381] [<44.178] [<0.0000257] [<29.838] [<0.0000210] [<24.316] [<0.0000217] [<25.206] [<0.0000271] [<31.441] [<0.0000399] [<46.227] [<0.0008746] [<1,013.898] [<0.0000311] [<36.073] [<0.0004141] [<480.080] 0.0000793 91.963 [<0.0003596] [<416.841] [<0.0000247] [<28.680] 0.000000813 0.943 The reported concentrations for 2-methylnaphthlene in all thrre runs were less than 5 times the field blank concentrations. Therefor this compound may not be accurately

quantified with this method. FLD BNK: FH=543ng, BH=120ng, condensate <50 ng; total = 663ng 0.000000397 0.461 [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] The reported concentrations for pyrene in all thrre runs were less than 5 times the field blank concentrations. Therefor this compound may not be accurately

quantified with this method. FLD BNK: FH=106ng, BH=92.8ng, condensate 107 ng total = 305.8ng 0.000000478 0.554 [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.000000384] [<0.445] [<0.0000240] [<27.775] 0.0000245 28.434 [<0.0000215] [<24.968] [<0.0000245] [<28.350] [<0.0000194] [<22.450] [<0.0000173] [<20.075] [<0.0000164] [<18.996] [<0.0000217] [<25.184][<0.0000173] [<20.075] [<0.0000210] [<24.393] [<0.0000183] [<21.227] [<0.0000258] [<29.933] [<0.0000196] [<22.738] [<0.0000253] [<29.358] 0.0000297 34.466 [<0.0000226] [<26.192] [<0.0000208] [<24.105] [<0.0000227] [<26.335] [<0.0000202] [<23.457] [<0.0000192] [<22.234] [<0.0000263] [<30.509] [<0.0000189] [<21.946] 0.0000227 26.269 [<0.0000191] [<22.090] [<0.0002520] [<292.136] [<0.0000229] [<26.551] [<0.0000168] [<19.428] [<0.0000202] [<23.457] [<0.0000209] [<24.177] [<0.0000251] [<29.142] [<0.0000254] [<29.430] [<0.0000241] [<27.918] [<0.0000241] [<27.990] [<0.0001570] [<182.046] [<0.0001794] [<207.949] [<0.0000250] [<28.926] [<0.0000214] [<24.752] [<0.0000236] [<27.343] [<0.0000217] [<25.184] [<0.0000317] [<36.697] [<0.0000234] [<27.127] [<0.0001601] [<185.643] [<0.0000222] [<25.760] [<0.0000308] [<35.690] [<0.0000208] [<24.105] [<0.0000169] [<19.644] [<0.0000176] [<20.363] [<0.0000219] [<25.400] [<0.0000322] [<37.345] [<0.0007066] [<819.085] [<0.0000251] [<29.142] [<0.0003346] [<387.836] 0.0000672 77.891 [<0.0002905] [<336.748] [<0.0000200] [<23.169] 0.000000812 0.941 The reported concentrations for 2-methylnaphthlene in all thrre runs were less than 5 times the field blank concentrations. Therefor this compound may not be accurately

quantified with this method. FLD BNK: FH=543ng, BH=120ng, condensate <50 ng; total = 663ng 0.000000358 0.416 [<0.000000310] [<0.360] 0.000000796 0.922 [<0.000000310] [<0.360] 0.000000335 0.388 [<0.000000310] [<0.360] [<0.000000310] [<0.360]The reported concentrations for pyrene in all thrre runs were less than 5 times the field blank concentrations. Therefor this compound may not be accurately

quantified with this method. FLD BNK: FH=106ng, BH=92.8ng, condensate 107 ng total = 305.8ng 0.000000380 0.440 [<0.000000310] [<0.360] [<0.000000310] [<0.360] [<0.000000310] [<0.360] [<0.000000310] [<0.360] [<0.000000310] [<0.360] [<0.000000310] [<0.360] [<0.000000310] [<0.360] [<0.000000310] [<0.360] [<0.000000310] [<0.360] [<0.000000310] [<0.360]543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 Steam Output (1000 lb/hr) Total Heat Input (mmBtu/hr) Flue Gas Moisture (%)543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 543.25 561.5 5.657418781 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 542.75 486.5 14.1583512 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.91544742 543.25 615.4 10.915447426.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131

Flue Gas O 2(%) Flue Gas Flow Rate (scfm) Flue Gas CO 2(%)6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.729 12.73 220025.131 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.11746.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 6.422 13.175 201589.1174 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.69787.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.69787.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978 7.729 11.433 208077.6978Fuel Input Rate Fuel Type

312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) Flue Gas Temperature (F) Fuel #1312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 312.5 5059.752 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C)314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 314.2 5057.7725 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C)308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C)308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C) 308.5 5127.543 No.6 Fuel Oil (residual or bunker C)Units of Measure Me asurement Method Fuel Input Rate

gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter Fuel #1gallon/m inute gas fuel meter

gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel metergallon/m inute gas fuel meter

gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel metergallon/m inute gas fuel meter

gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel metergallon/m inute gas fuel meter

gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meter gallon/m inute gas fuel meterFuel Type Units of Measure Me asurement Method Fuel #2Fuel Input Rate Fuel Type Units of Measure Fuel #3Me asurement Method Fuel Input Rate Fuel Type Fuel #4Units of Measure Me asurement Method

Internal standard recoveries in the front half of the sampling train for each of the three runs were below acceptable criteria. These samples were reanaly zed and reported at a 10-fold dilution due to matrix interferences. The diluted analyses may be biased high due to elevated detection lim its. Fuel #4 Other Supporting InformationBenzidine was not recovered in the laboratory control sample. The results are likely biased low.Benzidine was not recovered in the laboratory control sample. The results are likely biased low.Benzidine was not recovered in the laboratory control sample. The results are likely biased low.Internal standard recoveries in the front half of the sampling train for each of the three runs were below acceptable criteria. These samples were reanaly zed and reported at a 10-fold dilution due to matrix interferences. The diluted analyses may be biased high due to elevated detection lim its.Benzidine was not recovered in the laboratory control sample. The results are likely biased low.Benzidine was not recovered in the laboratory control sample. The results are likely biased low.Benzidine was not recovered in the laboratory control sample. The results are likely biased low.Internal standard recoveries in the front half of the sampling train for each of the three runs were below acceptable criteria. These samples were reanaly zed and reported at a 10-fold dilution due to matrix interferences. The diluted analyses may be biased high due to elevated detection lim its.Internal standard recoveries in the front half of the sampling train for each of the three runs were below acceptable criteria. These samples were reanaly zed and reported at a 10-fold dilution due to matrix interferences. The diluted analyses may be biased high due to elevated detection lim its.EIA

Facility Code Facility Name Boiler ID

1210003 Progress Energy Unit 3

1 2/28/2010 13:42 2/28/2010 15:00 2 3/5/2010 8:24 3/5/2010 10:04 3 3/5/2010 12:09 3/5/2010 13:38 Run Number Test Start Date Test Start Time Test End Time Test End DateMe asured Value

(ppm) Basis (Wet or Dry) Test Method Used Data Flag (ADL, BDL, DDL) [<0.0000674032] Dry U.S. EPA Conditional Test Method 033 (CTM-033) BDL [<0.00010828] Dry U.S. EPA Conditional Test Method 033 (CTM-033) BDL [<0.00010173998] Dry U.S. EPA Conditional Test Method 033 (CTM-033) BDL Hydrogen Cyanide Emission Test ResultsTest Method

Comments <0.076m g/dscm [< 0.00012] 547.3 511.5 6.6 6.375 13.12 <0.122m g/dscm [< 0.00024] 539.3 414.1 6.8 5.136 14.708 <0.114m g/dscm [< 0.00027] 539.3 346.7 6.8 4.308 15.761 Steam Output (1000 lb/hr) Total Heat

Input (mmBtu/hr) Calculated Emission Rate (lb/mmBtu) Flue Gas Moisture (%) Flue Gas CO 2(%) Flue Gas

O 2(%)Fuel Input Rate Fuel Type Units of Me asure Me asurement

Me thod Fuel Input

Rate Fuel Type

210466.6788 315.4 5103.104 No.6 Fuel Oil (residual or bunker C) gallon/m inute

gas fuel meter 214086.1006 303.7 5035.367 No.6 Fuel Oil (residual or bunker C) gallon/m inute

gas fuel meter 215984.2052 307.8 4995.7 No.6 Fuel Oil (residual or bunker C) gallon/m inute

gas fuel meter Flue Gas Flow Rate (dscfm) Flue Gas

Temperature (F) Fuel #1 Fuel #2Units of

Me asure Me asurement

Me thod Fuel Input Rate Fuel Type Units of Me asure Me asurement

Me thod Fuel Input

Rate Fuel Type

Fuel #4 Fuel #2 Fuel #3Units of

Me asure Me asurement

Me thod Fuel #4 Other Supporting Information