### 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 Hg0 

### 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

10743 Morgantown Energy Facility CFB 1 & 2Control Device Configuraton

Listed (by

boiler) in the Configuration Order Section of the Facility Unit Configurations Section of the Electronic ICRListed (by boiler) in the Configuration Order Section of the Facility Unit Configurations Section of the Electronic ICREIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

1 4/29/2010 7:21 2 4/29/2010 11:17 3 4/29/2010 15:25 Run Number Test Start Date Test Start TimeMeasured Value (ppm)

4/29/2010 9:21 76.8 4/29/2010 13:17 126.6 4/29/2010 17:25 61.8

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

Dry ADL Dry ADL Dry ADL CO Emission Test ResultsTest Method Comments lb/mmBtu ppmdv @ 7% O 2

Method 10 6.90E-02 64.52 Method 10 5.62E-02 52.55 Method 10 5.46E-02 51.09 Calculated Emission Rate539 808 7.47 536 793 7.13 532 793 7.49 Steam Output (1000 lb/hr) Total Heat Input (mmBtu/hr) Flue Gas Moisture (%)14.7 4.36 163426 14.81 3.97 163351 14.77 4.09 160792 Flue Gas Flow Rate (dscfm) Flue Gas CO 2(%) Flue Gas O 2(%)Fuel Input Rate Fuel Type

414 59800 bitum inous 417 59800 bitum inous 417 59800 subbituminous Flue Gas Temperature (F) Fuel #1Units of Measure Measurement Method Fuel Input Rate

lb/hour Other lb/hour Other lb/hour Other Fuel #1Fuel Type Units of Measure Measurement Method Fuel #2Fuel Input Rate Fuel Type Units of Measure Fuel #3Measurement Method Fuel Input Rate Fuel Type Fuel #4Units of Measure Measurement Method Fuel #4 Other Supporting InformationEIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

1 4/29/2010 7:21 4/29/2010 2 4/29/2010 11:17 4/29/2010 3 4/29/2010 15:25 4/29/2010 Run Number Test Start Date Test Start Time Test End DateMeasured Value (ppm) Basis (Wet or Dry) Test Method Used Data Flag (ADL, BDL, DDL) 10:33 0.004 Dry U.S. EPA Method 0011 BDL 14:51 0.003 Dry U.S. EPA Method 0011 BDL 18:35 0.003 Dry U.S. EPA Method 0011 BDL Test End Time Formaldehyde Emission Test ResultsTest Method

Comments lb/mmBtu ppmdv @ 7% O 2 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <3.89E-06 0.003 539 808 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.57E-06 0.002 536 793 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <3.29E-06 0.003 532 793 Steam Output (1000 lb/hr) Total Heat Input

(mmBtu/hr) Calculated Emission RateFuel Input Rate Fuel Type Units of Measure 7.11 14.72 4.28 166423 415 59800 bitum inous lb/hour 7.41 14.79 4.1 163141 423 59800 bitum inous lb/hour 7.32 14.77 4.1 160841 422 59800 bitum inous lb/hour Flue Gas Temperature (F) Fuel #1 Flue Gas Moisture (%) Flue Gas

CO 2(%) Flue Gas

O 2(%) Flue Gas Flow

Rate (dscfm)Measurement

Method Fuel Input

Rate Fuel Type Units of Measure Measurement

Method Fuel Input

Rate Fuel Type Units of

Measure Other Other Other Fuel #2 Fuel #3Measurement

Method Fuel Input

Rate Fuel Type Units of

Measure Measurement

Method Fuel #4 Other Supporting InformationEIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

1 4/29/2010 7:21 2 4/29/2010 11:17 3 4/29/2010 15:25 Run Number Test Start Date Test Start TimeMeasured Value (ppm) Basis (Wet or Dry)

4/29/2010 9:21 0.43 Wet 4/29/2010 13:17 0.43 Wet 4/29/2010 17:25 0.43 Wet

Test End Time Test End Date Methane Emission Test ResultsTest Method Used Data Flag (ADL, BDL, DDL) Test Method Comments lb/mmBtu

U.S. EPA Method 18 BDL MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <0.000222 U.S. EPA Method 18 BDL MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <0.000217 U.S. EPA Method 18 BDL MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <0.000218 Methane Emission Test Results Calculated Emission Rateppmdv @ 7% O 2

0.362 539 808 7.47 14.7 4.36 163426 0.355 536 793 7.13 14.81 3.97 163351 0.357 532 793 7.49 14.77 4.09 160792 Flue Gas O 2(%) Flue Gas

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

Input (mmBtu/hr) Flue Gas

Moisture (%) Flue Gas CO 2(%)Fuel Input Rate Fuel Type Units of

Measure Measurement

Method Fuel

Input Rate Fuel Type Units of

Measure

414 59800 bitum inous lb/hour Other 417 59800 bitum inous lb/hour Other 417 59800 subbituminous lb/hour Other Flue Gas Temperat ure (F) Fuel #1 Fuel #2Measurement

Method Fuel

Input Rate Fuel Type Units of

Measure Measurement

Method Fuel

Input Rate Fuel Type Units of

Measure Fuel #4 Fuel #3Measurement

Method Other Supporting InformationEIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

1 4/29/2010 7:21 4/29/2010 2 4/29/2010 11:17 4/29/2010 3 4/29/2010 15:25 4/29/2010 Run Number Test Start Date Test Start Time Test End DateMeasured Value (ppm) Basis (Wet or Dry) Test Method Used

9:21 142 Dry 13:17 147.6 Dry 17:25 145.4 Dry Test End Time SO 2Emission Test ResultsData Flag (ADL,

BDL, DDL) Test Method

Comments lb/mmBtu ppmdv @ 7% O 2

ADL Method 6C 0.291 119.3 539 ADL Method 6C 0.298 122 536 ADL Method 6C 0.294 120.3 532 Calculated Emission Rate Steam Output (1000 lb/hr)Fuel Input Rate Fuel Type

808 7.47 14.7 4.36 163426 414 59800 bitum inous 793 7.13 14.81 3.97 163351 417 59800 bitum inous 793 7.49 14.77 4.09 160792 417 59800 subbituminous Flue Gas O 2(%) Flue Gas

Flow Rate (dscfm) Total Heat Input (mmBtu/hr) Flue Gas

Moisture (%) Flue Gas

CO 2(%) Flue Gas Temperature (F) Fuel #1Units of

Measure Measurement

Method Fuel Input

Rate Fuel Type Units of

Measure Measurement

Method Fuel Input

Rate Fuel Type

lb/hour Other lb/hour Other lb/hour Other Fuel #1 Fuel #2 Fuel #3Units of

Measure Measurement

Method Fuel Input

Rate Fuel Type Units of Measure Measurement

Method Fuel #4 Fuel #3Other Supporting InformationEIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

1 4/27/2010 15:34 2 4/28/2010 13:04 3 4/30/2010 15:48 Run Number Test Start Date Test Start TimePlease note QA/QC documentation starting in Column "AI"

Measured Value (μg/dscm) Basis (Wet or Dry)

4/27/2010 18:34 1.0171 Dry 4/28/2010 16:04 1.1544 Dry 4/30/2010 18:48 1.2237 Dry

Test End Time Test End Date Total Vapor Phase Mercury Emission Test ResultsPlease note QA/QC documentation starting in Column "AI"

Test Method Used Data Flag (ADL, BDL, DDL) Test Method

Comments (lb/mmBtu)

U.S. EPA Method 30B ADL 7.73E-07 543 U.S. EPA Method 30B ADL 8.79E-07 542 U.S. EPA Method 30B ADL 9.22E-07 528 Steam Output (1000 lb/hr) Total Vapor Phase Mercury Emission Test ResultsFuel Input Rate

782 6.49 14.72 4.28 163426 412 60800 799 7.17 14.79 4.1 163351 415 59400 782 7.82 14.77 4.1 160792 417 55500 Flue Gas Flow Rate (dscfm) Flue Gas

Temperature (F) Flue Gas O 2(%) Total Heat Input (mmBtu/hr) Flue Gas CO 2(%) Flue Gas Moisture (%)Fuel Type Units of Measure Measurement

Method Fuel Input

Rate Fuel Type Units of

Measure Measurement

Method Fuel Input

Rate

bitum inous lb/hour Other bitum inous lb/hour Other bitum inous lb/hour Other Fuel #1 Fuel #2Fuel Type Units of Measure Measurement

Method Fuel Input

Rate Fuel Type Units of Measure Measurement

Method Fuel #3 Fuel #4QA /QC Documentation

Trap ID Section 1

Mass (ng) Section 2

Mass (ng) Total

Mass (ng) Initial

Spike (ng) Total NonSpike (ng)

1 86 0.4 86.4 0 86.4 2 98 0.4 98.4 0 98.4 3 103 0.6 103.6 0 103.6 Other Supporting InformationSample

Volume (dscm) Volume

Difference (%) Volume Diff. Limit Breaktrough

(%) Breaktrough

Limit Concentration

(μg/dscm) Trap ID

0.085 0.465116279 1.016470588 1S 0.085 0.408163265 1.157647059 2S 0.085 0.582524272 1.218823529 3S #DIV/0! #DIV/0! #DIV/0! #DIV/0! #DIV/0! #DIV/0!

≤10% of Section 1 Hg

mass for Hg conc. >1

μg/dscm: or ≤ 20% of Section Trap #1

≤20% of field

recovery testSection 1

Mass Section 2

Mass Total

Mass Initial

Spike Total NonSpike Sample

Volume Volume

Difference (%) Volume Diff. Limit

183 0.7 183.7 100 83.7 0.085 190 0.5 190.5 100 90.5 0.085 198 0.3 198.3 100 98.3 0.084 ≤20% of field

recovery test Trap #2Breaktrough (%) Breaktrough Limit Concentration

(μg/dscm) Abs. diff. RD (%) Limit C rec

0.382513661 0.984705882 0.031765 1.587302 97.3 0.263157895 1.064705882 0.092941 4.182107 92.1 0.151515152 1.170238095 0.048585 2.033662 94.7 #DIV/0! #DIV/0! #DIV/0! #DIV/0! #DIV/0! #DIV/0! #DIV/0! #DIV/0! #DIV/0! #DIV/0! #DIV/0! #DIV/0! Measured Spike Recovery ( R ) 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. ≤1 ≤10% of Section 1 Hg mass for Hg conc. >1

μg/dscm: or ≤ 20% of Section 1 for Hg conc. ≤1R (%) by

Run Ravg(%) Limit

97.3 92.1 94.7 Average Recovery

, between 85 and 115% Measured Spike Recovery ( R )

94.7EIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

Run Number Test Start Date Test Start TimeMeasured Hg 0Value (μg/dscm) Measured Hg +2Value (μg/dscm) Test End Time Test End DateMeasured Hg PValue

(μg/dscm) Basis (Wet or Dry) Test Method Used Data Flag (ADL, BDL, DDL) Total Vapor Phase Mercury Emission Test ResultsTest Method

Comments Total Mercury (lb/mmBtu) Steam Output

(1000 lb/hr) Total Heat

Input (mmBtu/hr) Flue Gas

Moisture (%) Flue Gas

CO 2(%)Fuel Input Rate Fuel Type Units of Measure Measurement

Method Fuel #1 Flue Gas O 2(%) Flue Gas

Flow Rate (dscfm) Flue Gas

Temperature (F)Fuel Input Rate Fuel Type Units of Measure Measurement

Method Fuel Input

Rate Fuel Type Units of Measure Measurement

Method Fuel #2 Fuel #3Fuel Input

Rate Fuel Type Units of Measure Measurement

Method Other Supporting Information Fuel #4EIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

Speciated Volatile Organic HAP Emission Data

Acetone 1 4/29/2010 Acetone 2 4/29/2010 Acetone 3 4/29/2010 Benzene 1 4/29/2010 Benzene 2 4/29/2010 Benzene 3 4/29/2010 Bromobenzene 1 4/29/2010 Bromobenzene 2 4/29/2010 Bromobenzene 3 4/29/2010 Bromochloromethane 1 4/29/2010 Bromochloromethane 2 4/29/2010 Bromochloromethane 3 4/29/2010 Bromodichloromethane 1 4/29/2010 Bromodichloromethane 2 4/29/2010 Bromodichloromethane 3 4/29/2010 Vinyl Bromide 1 4/29/2010 Vinyl Bromide 2 4/29/2010 Vinyl Bromide 3 4/29/2010 Bromoform 1 4/29/2010 Bromoform 2 4/29/2010 Bromoform 3 4/29/2010 Bromomethane 1 4/29/2010 Bromomethane 2 4/29/2010 Bromomethane 3 4/29/2010 2-Butanone (MEK) 1 4/29/2010 2-Butanone (MEK) 2 4/29/2010 2-Butanone (MEK) 3 4/29/2010 n-Butylbenzene 1 4/29/2010 n-Butylbenzene 2 4/29/2010 n-Butylbenzene 3 4/29/2010 sec-Butylbenzene 1 4/29/2010 sec-Butylbenzene 2 4/29/2010 sec-Butylbenzene 3 4/29/2010 tert-Butylbenzene 1 4/29/2010 tert-Butylbenzene 2 4/29/2010 tert-Butylbenzene 3 4/29/2010 Carbon disulfide 1 4/29/2010 Carbon disulfide 2 4/29/2010 Carbon disulfide 3 4/29/2010 Carbon tetrachloride 1 4/29/2010 Carbon tetrachloride 2 4/29/2010 Carbon tetrachloride 3 4/29/2010 Chlorobenzene 1 4/29/2010 Chlorobenzene 2 4/29/2010 Chlorobenzene 3 4/29/2010 Chlorodibromomethane 1 4/29/2010 Chlorodibromomethane 2 4/29/2010

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

needed) Run Number Test Start DateChlorodibromomethane 3 4/29/2010

Chloroethane 1 4/29/2010 Chloroethane 2 4/29/2010 Chloroethane 3 4/29/2010 Chloroform 1 4/29/2010 Chloroform 2 4/29/2010 Chloroform 3 4/29/2010 Chloromethane 1 4/29/2010 Chloromethane 2 4/29/2010 Chloromethane 3 4/29/2010 2-Chlorotoluene 1 4/29/2010 2-Chlorotoluene 2 4/29/2010 2-Chlorotoluene 3 4/29/2010 4-Chlorotoluene 1 4/29/2010 4-Chlorotoluene 2 4/29/2010 4-Chlorotoluene 3 4/29/2010 1,2-Dibromo-3-chloropropane 1 4/29/2010 1,2-Dibromo-3-chloropropane 2 4/29/2010 1,2-Dibromo-3-chloropropane 3 4/29/2010 1,2-Dibromoethane 1 4/29/2010 1,2-Dibromoethane 2 4/29/2010 1,2-Dibromoethane 3 4/29/2010 Dibromomethane 1 4/29/2010 Dibromomethane 2 4/29/2010 Dibromomethane 3 4/29/2010 1,2-Dichlorobenzene 1 4/29/2010 1,2-Dichlorobenzene 2 4/29/2010 1,2-Dichlorobenzene 3 4/29/2010 1,3-Dichlorobenzene 1 4/29/2010 1,3-Dichlorobenzene 2 4/29/2010 1,3-Dichlorobenzene 3 4/29/2010 1,4-Dichlorobenzene 1 4/29/2010 1,4-Dichlorobenzene 2 4/29/2010 1,4-Dichlorobenzene 3 4/29/2010 Dichlorodifluoromethane 1 4/29/2010 Dichlorodifluoromethane 2 4/29/2010 Dichlorodifluoromethane 3 4/29/2010 1,1-Dichloroethane 1 4/29/2010 1,1-Dichloroethane 2 4/29/2010 1,1-Dichloroethane 3 4/29/2010 1,2-Dichloroethane 1 4/29/2010 1,2-Dichloroethane 2 4/29/2010 1,2-Dichloroethane 3 4/29/2010 cis-1,2-Dichloroethene 1 4/29/2010 cis-1,2-Dichloroethene 2 4/29/2010 cis-1,2-Dichloroethene 3 4/29/2010 trans-1,2-Dichloroethene 1 4/29/2010 trans-1,2-Dichloroethene 2 4/29/2010 trans-1,2-Dichloroethene 3 4/29/2010 1,1-Dichloroethene 1 4/29/2010 1,1-Dichloroethene 2 4/29/2010 1,1-Dichloroethene 3 4/29/2010 1,2-Dichloropropane 1 4/29/2010 1,2-Dichloropropane 2 4/29/2010 1,2-Dichloropropane 3 4/29/20101,3-Dichloropropane 1 4/29/2010

1,3-Dichloropropane 2 4/29/2010 1,3-Dichloropropane 3 4/29/2010 2,2-Dichloropropane 1 4/29/2010 2,2-Dichloropropane 2 4/29/2010 2,2-Dichloropropane 3 4/29/2010 cis-1,3-Dichloropropene 1 4/29/2010 cis-1,3-Dichloropropene 2 4/29/2010 cis-1,3-Dichloropropene 3 4/29/2010 trans-1,3-Dichloropropene 1 4/29/2010 trans-1,3-Dichloropropene 2 4/29/2010 trans-1,3-Dichloropropene 3 4/29/2010 1,1-Dichloropropene 1 4/29/2010 1,1-Dichloropropene 2 4/29/2010 1,1-Dichloropropene 3 4/29/2010 Ethylbenzene 1 4/29/2010 Ethylbenzene 2 4/29/2010 Ethylbenzene 3 4/29/2010 Hexachlorobutadiene 1 4/29/2010 Hexachlorobutadiene 2 4/29/2010 Hexachlorobutadiene 3 4/29/2010 2-Hexanone 1 4/29/2010 2-Hexanone 2 4/29/2010 2-Hexanone 3 4/29/2010 Isopropylbenzene 1 4/29/2010 Isopropylbenzene 2 4/29/2010 Isopropylbenzene 3 4/29/2010 p-isopropyltoluene 1 4/29/2010 p-isopropyltoluene 2 4/29/2010 p-isopropyltoluene 3 4/29/2010 Methylene chloride 1 4/29/2010 Methylene chloride 2 4/29/2010 Methylene chloride 3 4/29/2010 4-Methyl-2-pentanone (MIBK) 1 4/29/2010 4-Methyl-2-pentanone (MIBK) 2 4/29/2010 4-Methyl-2-pentanone (MIBK) 3 4/29/2010 Naphthalene 1 4/29/2010 Naphthalene 2 4/29/2010 Naphthalene 3 4/29/2010 n-Propylbenzene 1 4/29/2010 n-Propylbenzene 2 4/29/2010 n-Propylbenzene 3 4/29/2010 Styrene 1 4/29/2010 Styrene 2 4/29/2010 Styrene 3 4/29/2010 1,1,1,2-Tetrachloroethane 1 4/29/2010 1,1,1,2-Tetrachloroethane 2 4/29/2010 1,1,1,2-Tetrachloroethane 3 4/29/2010 1,1,2,2-Tetrachloroethane 1 4/29/2010 1,1,2,2-Tetrachloroethane 2 4/29/2010 1,1,2,2-Tetrachloroethane 3 4/29/2010 Tetrachloroethene 1 4/29/2010 Tetrachloroethene 2 4/29/2010 Tetrachloroethene 3 4/29/2010 Toluene 1 4/29/2010Toluene 2 4/29/2010

Toluene 3 4/29/2010 1,2,3-Trichlorobenzene 1 4/29/2010 1,2,3-Trichlorobenzene 2 4/29/2010 1,2,3-Trichlorobenzene 3 4/29/2010 1,2,4-Trichlorobenzene 1 4/29/2010 1,2,4-Trichlorobenzene 2 4/29/2010 1,2,4-Trichlorobenzene 3 4/29/2010 1,1,1-Trichloroethane 1 4/29/2010 1,1,1-Trichloroethane 2 4/29/2010 1,1,1-Trichloroethane 3 4/29/2010 1,1,2-Trichloroethane 1 4/29/2010 1,1,2-Trichloroethane 2 4/29/2010 1,1,2-Trichloroethane 3 4/29/2010 Trichloroethene 1 4/29/2010 Trichloroethene 2 4/29/2010 Trichloroethene 3 4/29/2010 Trichlorofluoromethane 1 4/29/2010 Trichlorofluoromethane 2 4/29/2010 Trichlorofluoromethane 3 4/29/2010 1,2,3-Trichloropropane 1 4/29/2010 1,2,3-Trichloropropane 2 4/29/2010 1,2,3-Trichloropropane 3 4/29/2010 1,1,2-Trichloro-1,2,2-trifluoroethane 1 4/29/2010 1,1,2-Trichloro-1,2,2-trifluoroethane 2 4/29/2010 1,1,2-Trichloro-1,2,2-trifluoroethane 3 4/29/2010 1,3,5-Trimethylbenzene 1 4/29/2010 1,3,5-Trimethylbenzene 2 4/29/2010 1,3,5-Trimethylbenzene 3 4/29/2010 Vinyl chloride 1 4/29/2010 Vinyl chloride 2 4/29/2010 Vinyl chloride 3 4/29/2010 m-Xylene & p-Xylene 1 4/29/2010 m-Xylene & p-Xylene 2 4/29/2010 m-Xylene & p-Xylene 3 4/29/2010 o-Xylene 1 4/29/2010 o-Xylene 2 4/29/2010 o-Xylene 3 4/29/2010Measured Value (μg/m3) 8:09 AM 4/29/2010 10:54 AM 191.291 11:50 AM 4/29/2010 2:35 PM 45.566 3:40 PM 4/29/2010 6:35 PM 192.650 8:09 AM 4/29/2010 10:54 AM 217.832 11:50 AM 4/29/2010 2:35 PM 187.227 3:40 PM 4/29/2010 6:35 PM 182.639 8:09 AM 4/29/2010 10:54 AM 0.208 11:50 AM 4/29/2010 2:35 PM 0.213 3:40 PM 4/29/2010 6:35 PM 0.209 8:09 AM 4/29/2010 10:54 AM 0.358 11:50 AM 4/29/2010 2:35 PM 0.298 3:40 PM 4/29/2010 6:35 PM 0.293 8:09 AM 4/29/2010 10:54 AM 0.135 11:50 AM 4/29/2010 2:35 PM 0.138 3:40 PM 4/29/2010 6:35 PM 0.136 8:09 AM 4/29/2010 10:54 AM 0.129 11:50 AM 4/29/2010 2:35 PM 0.000 3:40 PM 4/29/2010 6:35 PM 0.000 8:09 AM 4/29/2010 10:54 AM 1.041 11:50 AM 4/29/2010 2:35 PM 1.063 3:40 PM 4/29/2010 6:35 PM 1.045 8:09 AM 4/29/2010 10:54 AM 0.615 11:50 AM 4/29/2010 2:35 PM 0.634 3:40 PM 4/29/2010 6:35 PM 0.543 8:09 AM 4/29/2010 10:54 AM 7.960 11:50 AM 4/29/2010 2:35 PM 10.627 3:40 PM 4/29/2010 6:35 PM 10.454 8:09 AM 4/29/2010 10:54 AM 1.797 11:50 AM 4/29/2010 2:35 PM 0.117 3:40 PM 4/29/2010 6:35 PM 0.178 8:09 AM 4/29/2010 10:54 AM 0.104 11:50 AM 4/29/2010 2:35 PM 0.106 3:40 PM 4/29/2010 6:35 PM 0.105 8:09 AM 4/29/2010 10:54 AM 0.115 11:50 AM 4/29/2010 2:35 PM 0.117 3:40 PM 4/29/2010 6:35 PM 0.115 8:09 AM 4/29/2010 10:54 AM 0.326 11:50 AM 4/29/2010 2:35 PM 0.179 3:40 PM 4/29/2010 6:35 PM 0.178 8:09 AM 4/29/2010 10:54 AM 0.650 11:50 AM 4/29/2010 2:35 PM 0.571 3:40 PM 4/29/2010 6:35 PM 0.419 8:09 AM 4/29/2010 10:54 AM 2.561 11:50 AM 4/29/2010 2:35 PM 0.398 3:40 PM 4/29/2010 6:35 PM 0.290 8:09 AM 4/29/2010 10:54 AM 0.208 11:50 AM 4/29/2010 2:35 PM 0.213 Test Start Time Test End Date Test End Time3:40 PM 4/29/2010 6:35 PM 0.209 8:09 AM 4/29/2010 10:54 AM 1.561 11:50 AM 4/29/2010 2:35 PM 0.586 3:40 PM 4/29/2010 6:35 PM 0.595 8:09 AM 4/29/2010 10:54 AM 0.139 11:50 AM 4/29/2010 2:35 PM 0.117 3:40 PM 4/29/2010 6:35 PM 0.108 8:09 AM 4/29/2010 10:54 AM 28.680 11:50 AM 4/29/2010 2:35 PM 7.902 3:40 PM 4/29/2010 6:35 PM 10.879 8:09 AM 4/29/2010 10:54 AM 0.125 11:50 AM 4/29/2010 2:35 PM 0.128 3:40 PM 4/29/2010 6:35 PM 0.125 8:09 AM 4/29/2010 10:54 AM 0.146 11:50 AM 4/29/2010 2:35 PM 0.149 3:40 PM 4/29/2010 6:35 PM 0.146 8:09 AM 4/29/2010 10:54 AM 1.354 11:50 AM 4/29/2010 2:35 PM 1.382 3:40 PM 4/29/2010 6:35 PM 1.359 8:09 AM 4/29/2010 10:54 AM 0.146 11:50 AM 4/29/2010 2:35 PM 0.149 3:40 PM 4/29/2010 6:35 PM 0.146 8:09 AM 4/29/2010 10:54 AM 0.219 11:50 AM 4/29/2010 2:35 PM 0.223 3:40 PM 4/29/2010 6:35 PM 0.220 8:09 AM 4/29/2010 10:54 AM 0.239 11:50 AM 4/29/2010 2:35 PM 0.191 3:40 PM 4/29/2010 6:35 PM 0.188 8:09 AM 4/29/2010 10:54 AM 0.206 11:50 AM 4/29/2010 2:35 PM 0.149 3:40 PM 4/29/2010 6:35 PM 0.146 8:09 AM 4/29/2010 10:54 AM 0.157 11:50 AM 4/29/2010 2:35 PM 0.159 3:40 PM 4/29/2010 6:35 PM 0.157 8:09 AM 4/29/2010 10:54 AM 2.818 11:50 AM 4/29/2010 2:35 PM 2.991 3:40 PM 4/29/2010 6:35 PM 2.390 8:09 AM 4/29/2010 10:54 AM 0.104 11:50 AM 4/29/2010 2:35 PM 0.106 3:40 PM 4/29/2010 6:35 PM 0.105 8:09 AM 4/29/2010 10:54 AM 0.177 11:50 AM 4/29/2010 2:35 PM 0.181 3:40 PM 4/29/2010 6:35 PM 0.178 8:09 AM 4/29/2010 10:54 AM 0.104 11:50 AM 4/29/2010 2:35 PM 0.106 3:40 PM 4/29/2010 6:35 PM 0.105 8:09 AM 4/29/2010 10:54 AM 0.208 11:50 AM 4/29/2010 2:35 PM 0.213 3:40 PM 4/29/2010 6:35 PM 0.209 8:09 AM 4/29/2010 10:54 AM 0.156 11:50 AM 4/29/2010 2:35 PM 0.159 3:40 PM 4/29/2010 6:35 PM 0.157 8:09 AM 4/29/2010 10:54 AM 0.177 11:50 AM 4/29/2010 2:35 PM 0.181 3:40 PM 4/29/2010 6:35 PM 0.1788:09 AM 4/29/2010 10:54 AM 0.146 11:50 AM 4/29/2010 2:35 PM 0.149 3:40 PM 4/29/2010 6:35 PM 0.146 8:09 AM 4/29/2010 10:54 AM 0.104 11:50 AM 4/29/2010 2:35 PM 0.106 3:40 PM 4/29/2010 6:35 PM 0.105 8:09 AM 4/29/2010 10:54 AM 0.177 11:50 AM 4/29/2010 2:35 PM 0.181 3:40 PM 4/29/2010 6:35 PM 0.178 8:09 AM 4/29/2010 10:54 AM 0.126 11:50 AM 4/29/2010 2:35 PM 0.128 3:40 PM 4/29/2010 6:35 PM 0.125 8:09 AM 4/29/2010 10:54 AM 0.104 11:50 AM 4/29/2010 2:35 PM 0.106 3:40 PM 4/29/2010 6:35 PM 0.105 8:09 AM 4/29/2010 10:54 AM 2.455 11:50 AM 4/29/2010 2:35 PM 0.323 3:40 PM 4/29/2010 6:35 PM 0.231 8:09 AM 4/29/2010 10:54 AM 0.260 11:50 AM 4/29/2010 2:35 PM 0.266 3:40 PM 4/29/2010 6:35 PM 0.261 8:09 AM 4/29/2010 10:54 AM 3.975 11:50 AM 4/29/2010 2:35 PM 1.501 3:40 PM 4/29/2010 6:35 PM 1.122 8:09 AM 4/29/2010 10:54 AM 0.161 11:50 AM 4/29/2010 2:35 PM 0.106 3:40 PM 4/29/2010 6:35 PM 0.094 8:09 AM 4/29/2010 10:54 AM 0.112 11:50 AM 4/29/2010 2:35 PM 0.106 3:40 PM 4/29/2010 6:35 PM 0.105 8:09 AM 4/29/2010 10:54 AM 220.559 11:50 AM 4/29/2010 2:35 PM 44.734 3:40 PM 4/29/2010 6:35 PM 14.942 8:09 AM 4/29/2010 10:54 AM 10.412 11:50 AM 4/29/2010 2:35 PM 10.627 3:40 PM 4/29/2010 6:35 PM 10.454 8:09 AM 4/29/2010 10:54 AM 5.194 11:50 AM 4/29/2010 2:35 PM 1.063 3:40 PM 4/29/2010 6:35 PM 1.477 8:09 AM 4/29/2010 10:54 AM 1.437 11:50 AM 4/29/2010 2:35 PM 0.169 3:40 PM 4/29/2010 6:35 PM 0.129 8:09 AM 4/29/2010 10:54 AM 16.976 11:50 AM 4/29/2010 2:35 PM 2.191 3:40 PM 4/29/2010 6:35 PM 1.704 8:09 AM 4/29/2010 10:54 AM 0.115 11:50 AM 4/29/2010 2:35 PM 0.117 3:40 PM 4/29/2010 6:35 PM 0.115 8:09 AM 4/29/2010 10:54 AM 0.302 11:50 AM 4/29/2010 2:35 PM 0.308 3:40 PM 4/29/2010 6:35 PM 0.303 8:09 AM 4/29/2010 10:54 AM 0.150 11:50 AM 4/29/2010 2:35 PM 0.094 3:40 PM 4/29/2010 6:35 PM 0.109 8:09 AM 4/29/2010 10:54 AM 43.80011:50 AM 4/29/2010 2:35 PM 17.867 3:40 PM 4/29/2010 6:35 PM 7.423 8:09 AM 4/29/2010 10:54 AM 0.129 11:50 AM 4/29/2010 2:35 PM 0.106 3:40 PM 4/29/2010 6:35 PM 0.105 8:09 AM 4/29/2010 10:54 AM 0.167 11:50 AM 4/29/2010 2:35 PM 0.170 3:40 PM 4/29/2010 6:35 PM 0.167 8:09 AM 4/29/2010 10:54 AM 0.104 11:50 AM 4/29/2010 2:35 PM 0.085 3:40 PM 4/29/2010 6:35 PM 0.094 8:09 AM 4/29/2010 10:54 AM 1.041 11:50 AM 4/29/2010 2:35 PM 1.063 3:40 PM 4/29/2010 6:35 PM 1.045 8:09 AM 4/29/2010 10:54 AM 0.250 11:50 AM 4/29/2010 2:35 PM 0.234 3:40 PM 4/29/2010 6:35 PM 0.230 8:09 AM 4/29/2010 10:54 AM 1.243 11:50 AM 4/29/2010 2:35 PM 1.285 3:40 PM 4/29/2010 6:35 PM 1.043 8:09 AM 4/29/2010 10:54 AM 2.603 11:50 AM 4/29/2010 2:35 PM 2.657 3:40 PM 4/29/2010 6:35 PM 2.613 8:09 AM 4/29/2010 10:54 AM 0.500 11:50 AM 4/29/2010 2:35 PM 0.162 3:40 PM 4/29/2010 6:35 PM 0.140 8:09 AM 4/29/2010 10:54 AM 0.186 11:50 AM 4/29/2010 2:35 PM 0.191 3:40 PM 4/29/2010 6:35 PM 0.188 8:09 AM 4/29/2010 10:54 AM 0.256 11:50 AM 4/29/2010 2:35 PM 0.223 3:40 PM 4/29/2010 6:35 PM 0.220 8:09 AM 4/29/2010 10:54 AM 2.671 11:50 AM 4/29/2010 2:35 PM 0.624 3:40 PM 4/29/2010 6:35 PM 0.502 8:09 AM 4/29/2010 10:54 AM 1.211 11:50 AM 4/29/2010 2:35 PM 0.209 3:40 PM 4/29/2010 6:35 PM 0.160Footnotes:

* Front half fraction contains filter, cyclone, and cartridge ** Back half fraction contains condensate, solvent, impingers

Basis Test Method Used Data Flag (ADL, BDL, DDL) Front Half Mass (ng)

Dry U.S. EPA Method 0031 with SW -846 Method 8260B ADL ADL ADL ADL ADL ADL BDL BDL BDL BDL BDL BDL BDL BDL BDL ADL ADL ADL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL ADL ADL ADL BDL BDL BDL BDL BDLBDL BDL BDL BDL BDL BDL BDL ADL ADL ADL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL ADL ADL ADL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDLBDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL ADL ADL ADL BDL BDL BDL ADL ADL ADL BDL BDL BDL BDL BDL BDL ADL ADL ADL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL ADLADL ADL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL ADL ADL ADL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL BDL ADL ADL ADL ADL ADL ADLBack Half Mass (ng) Total Mass (ng) Test Method Comments lb/mmBtu

Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 1.47E-04 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 3.46E-05 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 1.46E-04 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 1.67E-04 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 1.42E-04 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 1.39E-04 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.60E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.61E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.59E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.75E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.26E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.22E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.04E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.05E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.03E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 9.90E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 0.00E+00 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 0.00E+00 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.99E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <4.72E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <4.81E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <4.13E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <6.11E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.38E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.87E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.35E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.99E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.79E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.88E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.73E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.50E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.36E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.35E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 4.99E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 4.34E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 3.18E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.97E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <3.02E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.20E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.60E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.61E-07 Calculated Emission RateSpreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.59E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.20E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <4.45E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <4.52E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.07E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.88E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.24E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 2.20E-05 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 6.00E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 8.26E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <9.59E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <9.69E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <9.53E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.12E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.13E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.11E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.04E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.05E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.03E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.12E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.13E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.11E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.68E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.70E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.67E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.83E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.45E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.43E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.58E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.13E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.11E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.21E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.21E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.19E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 2.16E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 2.27E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 1.82E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.99E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.36E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.37E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.35E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.99E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.60E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.61E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.59E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.20E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.21E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.19E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.36E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.37E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.35E-07Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.12E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.13E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.11E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.99E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.36E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.37E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.35E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <9.64E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <9.69E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <9.53E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.99E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 1.89E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 2.45E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 1.75E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.00E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.02E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.99E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 3.05E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 1.14E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 8.52E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.23E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.15E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.59E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 1.69E-04 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 3.40E-05 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 1.13E-05 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.99E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <3.99E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.12E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.10E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.28E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <9.82E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.30E-05 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.66E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.29E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.79E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.88E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.73E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.32E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.34E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.30E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.15E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.16E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.24E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 3.36E-05Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 1.36E-05 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 5.64E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <9.87E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.28E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.29E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.27E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.99E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <6.46E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.15E-08 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.99E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <8.07E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <7.94E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.92E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.78E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.75E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 9.54E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 9.76E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 7.92E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.00E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <2.02E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.99E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <3.84E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.23E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.06E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.43E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.45E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.43E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.97E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.70E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <1.67E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 2.05E-06 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 4.74E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 3.81E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 9.30E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 1.58E-07 Spreadsheet does not allow entry of individual fractions for four sets of three tubes. MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. This compound is a common contaminant in VOST analyses therefore any positive reading is subject to having resulted from contamination in the field or the laboratory

. 1.22E-07ug/dscm @ 7% O2

159.985 539 808 7.47 37.701 536 793 7.13 159.395 532 793 7.49 182.182 539 808 7.47 154.908 536 793 7.13 151.112 532 793 7.49 0.174 539 808 7.47 0.176 536 793 7.13 0.173 532 793 7.49 0.300 539 808 7.47 0.246 536 793 7.13 0.242 532 793 7.49 0.113 539 808 7.47 0.114 536 793 7.13 0.112 532 793 7.49 0.108 539 808 7.47 0.000 536 793 7.13 0.000 532 793 7.49 0.871 539 808 7.47 0.879 536 793 7.13 0.865 532 793 7.49 0.515 539 808 7.47 0.524 536 793 7.13 0.450 532 793 7.49 6.657 539 808 7.47 8.793 536 793 7.13 8.649 532 793 7.49 1.503 539 808 7.47 0.097 536 793 7.13 0.147 532 793 7.49 0.087 539 808 7.47 0.088 536 793 7.13 0.086 532 793 7.49 0.096 539 808 7.47 0.097 536 793 7.13 0.095 532 793 7.49 0.272 539 808 7.47 0.148 536 793 7.13 0.147 532 793 7.49 0.544 539 808 7.47 0.473 536 793 7.13 0.347 532 793 7.49 2.142 539 808 7.47 0.329 536 793 7.13 0.240 532 793 7.49 0.174 539 808 7.47 0.176 536 793 7.13 Calculated Emission Rate Steam Output (1000 lb/hr) Total Heat Input (mmBtu/hr) Flue Gas Moisture (%)0.173 532 793 7.49 1.305 539 808 7.47 0.485 536 793 7.13 0.492 532 793 7.49 0.116 539 808 7.47 0.097 536 793 7.13 0.090 532 793 7.49 23.986 539 808 7.47 6.538 536 793 7.13 9.001 532 793 7.49 0.104 539 808 7.47 0.106 536 793 7.13 0.104 532 793 7.49 0.122 539 808 7.47 0.123 536 793 7.13 0.121 532 793 7.49 1.132 539 808 7.47 1.143 536 793 7.13 1.124 532 793 7.49 0.122 539 808 7.47 0.123 536 793 7.13 0.121 532 793 7.49 0.183 539 808 7.47 0.185 536 793 7.13 0.182 532 793 7.49 0.200 539 808 7.47 0.158 536 793 7.13 0.156 532 793 7.49 0.173 539 808 7.47 0.123 536 793 7.13 0.121 532 793 7.49 0.132 539 808 7.47 0.132 536 793 7.13 0.130 532 793 7.49 2.357 539 808 7.47 2.475 536 793 7.13 1.977 532 793 7.49 0.087 539 808 7.47 0.088 536 793 7.13 0.086 532 793 7.49 0.148 539 808 7.47 0.149 536 793 7.13 0.147 532 793 7.49 0.087 539 808 7.47 0.088 536 793 7.13 0.086 532 793 7.49 0.174 539 808 7.47 0.176 536 793 7.13 0.173 532 793 7.49 0.131 539 808 7.47 0.132 536 793 7.13 0.130 532 793 7.49 0.148 539 808 7.47 0.149 536 793 7.13 0.147 532 793 7.490.122 539 808 7.47 0.123 536 793 7.13 0.121 532 793 7.49 0.087 539 808 7.47 0.088 536 793 7.13 0.086 532 793 7.49 0.148 539 808 7.47 0.149 536 793 7.13 0.147 532 793 7.49 0.105 539 808 7.47 0.106 536 793 7.13 0.104 532 793 7.49 0.087 539 808 7.47 0.088 536 793 7.13 0.086 532 793 7.49 2.053 539 808 7.47 0.267 536 793 7.13 0.191 532 793 7.49 0.218 539 808 7.47 0.220 536 793 7.13 0.216 532 793 7.49 3.325 539 808 7.47 1.242 536 793 7.13 0.928 532 793 7.49 0.134 539 808 7.47 0.088 536 793 7.13 0.078 532 793 7.49 0.094 539 808 7.47 0.088 536 793 7.13 0.086 532 793 7.49 184.463 539 808 7.47 37.012 536 793 7.13 12.363 532 793 7.49 8.708 539 808 7.47 8.793 536 793 7.13 8.649 532 793 7.49 4.344 539 808 7.47 0.879 536 793 7.13 1.222 532 793 7.49 1.202 539 808 7.47 0.140 536 793 7.13 0.107 532 793 7.49 14.197 539 808 7.47 1.812 536 793 7.13 1.410 532 793 7.49 0.096 539 808 7.47 0.097 536 793 7.13 0.095 532 793 7.49 0.253 539 808 7.47 0.255 536 793 7.13 0.251 532 793 7.49 0.125 539 808 7.47 0.078 536 793 7.13 0.090 532 793 7.49 36.632 539 808 7.4714.783 536 793 7.13 6.142 532 793 7.49 0.108 539 808 7.47 0.088 536 793 7.13 0.086 532 793 7.49 0.139 539 808 7.47 0.141 536 793 7.13 0.138 532 793 7.49 0.087 539 808 7.47 0.070 536 793 7.13 0.078 532 793 7.49 0.871 539 808 7.47 0.879 536 793 7.13 0.865 532 793 7.49 0.209 539 808 7.47 0.193 536 793 7.13 0.190 532 793 7.49 1.039 539 808 7.47 1.063 536 793 7.13 0.863 532 793 7.49 2.177 539 808 7.47 2.198 536 793 7.13 2.162 532 793 7.49 0.419 539 808 7.47 0.134 536 793 7.13 0.116 532 793 7.49 0.156 539 808 7.47 0.158 536 793 7.13 0.156 532 793 7.49 0.214 539 808 7.47 0.185 536 793 7.13 0.182 532 793 7.49 2.234 539 808 7.47 0.516 536 793 7.13 0.415 532 793 7.49 1.013 539 808 7.47 0.173 536 793 7.13 0.133 532 793 7.4914.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417

Flue Gas O 2(%) Flue Gas Flow Rate (scfm) Flue Gas Temperature (F) Flue Gas CO 2(%)14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 41714.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 41414.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417 14.72 4.28 163426 414 14.79 4.1 163351 417 14.77 4.1 160792 417Fuel Input Rate Fuel Type Units of Measure Measurement Method

59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous Fuel #159800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inous 59800 bitum inousFuel Input Rate Fuel Type Units of Measure Measurement Method Fuel #2Fuel Input Rate Fuel Type Units of Measure Measurement Method Fuel #3Fuel Input Rate Fuel Type Units of Measure Measurement Method Fuel #4Other Supporting

InformationEIA

Facility Code Facility Name

10743 Morgantown Energy Facility

Speciated Semi-Volatile Organic HAP Emission Data

Phenol 1 Phenol 2 Phenol 3 Acetophenone 1 Acetophenone 2 Acetophenone 3 Aniline 1 Aniline 2 Aniline 3 Benzidine 1 Benzidine 2 Benzidine 3 Carbazole 1 Carbazole 2 Carbazole 3 1,2-Diphenylhydrazine 1 1,2-Diphenylhydrazine 2 1,2-Diphenylhydrazine 3 N-Nitrosodimethylam ine 1 N-Nitrosodimethylam ine 2 N-Nitrosodimethylam ine 3 Pentachlorobenzene 1 Pentachlorobenzene 2 Pentachlorobenzene 3 Pentachloronitrobenzene 1 Pentachloronitrobenzene 2 Pentachloronitrobenzene 3 Pyridine 1 Pyridine 2 Pyridine 3 bis(2-Chloroethyl)ether 1 bis(2-Chloroethyl)ether 2 bis(2-Chloroethyl)ether 3 2-Chlorophenol 1 2-Chlorophenol 2 2-Chlorophenol 3 1,3-Dichlorobenzene 1 1,3-Dichlorobenzene 2 1,3-Dichlorobenzene 3 1,4-Dichlorobenzene 1 1,4-Dichlorobenzene 2 1,4-Dichlorobenzene 3 1,2-Dichlorobenzene 1 1,2-Dichlorobenzene 2 1,2-Dichlorobenzene 3 2,2'-oxybis(1-Chloropropane) 1 2,2'-oxybis(1-Chloropropane) 2

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

needed) Run Number2,2'-oxybis(1-Chloropropane) 3

Benzyl alcohol 1 Benzyl alcohol 2 Benzyl alcohol 3 2-Methylphenol 1 2-Methylphenol 2 2-Methylphenol 3 3/4-Methylphenol 1 3/4-Methylphenol 2 3/4-Methylphenol 3 N-Nitroso-di-n-propylam ine 1 N-Nitroso-di-n-propylam ine 2 N-Nitroso-di-n-propylam ine 3 Hexachloroethane 1 Hexachloroethane 2 Hexachloroethane 3 Nitrobenzene 1 Nitrobenzene 2 Nitrobenzene 3 Isophorone 1 Isophorone 2 Isophorone 3 2-Nitrophenol 1 2-Nitrophenol 2 2-Nitrophenol 3 2,4-Dimethylphenol 1 2,4-Dimethylphenol 2 2,4-Dimethylphenol 3 bis(2-Chloroethoxy)methane 1 bis(2-Chloroethoxy)methane 2 bis(2-Chloroethoxy)methane 3 Benzoic acid 1 Benzoic acid 2 Benzoic acid 3 2,4-Dichlorophenol 1 2,4-Dichlorophenol 2 2,4-Dichlorophenol 3 1,2,4-Trichlorobenzene 1 1,2,4-Trichlorobenzene 2 1,2,4-Trichlorobenzene 3 Naphthalene 1 Naphthalene 2 Naphthalene 3 4-Chloroaniline 1 4-Chloroaniline 2 4-Chloroaniline 3 Hexachlorobutadiene 1 Hexachlorobutadiene 2 Hexachlorobutadiene 3 4-Chloro-3-methylphenol 1 4-Chloro-3-methylphenol 2 4-Chloro-3-methylphenol 3 2-Methylnaphthalene 1 2-Methylnaphthalene 2 2-Methylnaphthalene 3Hexachlorocyclopentadiene 1

Hexachlorocyclopentadiene 2 Hexachlorocyclopentadiene 3 2,4,6-Trichlorophenol 1 2,4,6-Trichlorophenol 2 2,4,6-Trichlorophenol 3 2,4,5-Trichlorophenol 1 2,4,5-Trichlorophenol 2 2,4,5-Trichlorophenol 3 2-Chloronaphthalene 1 2-Chloronaphthalene 2 2-Chloronaphthalene 3 2-Nitroaniline 1 2-Nitroaniline 2 2-Nitroaniline 3 Dim ethylphthalate 1 Dim ethylphthalate 2 Dim ethylphthalate 3 2,6-Dinitrotoluene 1 2,6-Dinitrotoluene 2 2,6-Dinitrotoluene 3 2,4-Dinitrotoluene 1 2,4-Dinitrotoluene 2 2,4-Dinitrotoluene 3 Acenaphthylene 1 Acenaphthylene 2 Acenaphthylene 3 3-Nitroaniline 1 3-Nitroaniline 2 3-Nitroaniline 3 Acenaphthene 1 Acenaphthene 2 Acenaphthene 3 2,4-Dinitrophenol 1 2,4-Dinitrophenol 2 2,4-Dinitrophenol 3 4-Nitrophenol 1 4-Nitrophenol 2 4-Nitrophenol 3 Dibenzofuran 1 Dibenzofuran 2 Dibenzofuran 3 Diethylphthalate 1 Diethylphthalate 2 Diethylphthalate 3 4-Chlorophenyl-phenylether 1 4-Chlorophenyl-phenylether 2 4-Chlorophenyl-phenylether 3 Fluorene 1 Fluorene 2 Fluorene 3 4-Nitroaniline 1 4-Nitroaniline 2 4-Nitroaniline 3 4,6-Dinitro-2-methylphenol 14,6-Dinitro-2-methylphenol 2

4,6-Dinitro-2-methylphenol 3 N-Nitrosodiphenylam ine 1 N-Nitrosodiphenylam ine 2 N-Nitrosodiphenylam ine 3 4-Bromophenyl-phenylether 1 4-Bromophenyl-phenylether 2 4-Bromophenyl-phenylether 3 Hexachlorobenzene 1 Hexachlorobenzene 2 Hexachlorobenzene 3 Pentachlorophenol 1 Pentachlorophenol 2 Pentachlorophenol 3 Phenanthrene 1 Phenanthrene 2 Phenanthrene 3 Anthracene 1 Anthracene 2 Anthracene 3 Di-n-butylphthalate 1 Di-n-butylphthalate 2 Di-n-butylphthalate 3 Fluoranthene 1 Fluoranthene 2 Fluoranthene 3 Pyrene 1 Pyrene 2 Pyrene 3 Butylbenzylphthalate 1 Butylbenzylphthalate 2 Butylbenzylphthalate 3 3,3'-Dichlorobenzidine 1 3,3'-Dichlorobenzidine 2 3,3'-Dichlorobenzidine 3 bis(2-Ethylhexyl)phthalate 1 bis(2-Ethylhexyl)phthalate 2 bis(2-Ethylhexyl)phthalate 3 Benzo(a)anthracene 1 Benzo(a)anthracene 2 Benzo(a)anthracene 3 Chrysene 1 Chrysene 2 Chrysene 3 Di-n-octylphthalate 1 Di-n-octylphthalate 2 Di-n-octylphthalate 3 Benzo(b)fluoranthene 1 Benzo(b)fluoranthene 2 Benzo(b)fluoranthene 3 Benzo(k)fluoranthene 1 Benzo(k)fluoranthene 2 Benzo(k)fluoranthene 3 Benzo(a)pyrene 1 Benzo(a)pyrene 2Benzo(a)pyrene 3

Indeno(1,2,3-cd)pyrene 1 Indeno(1,2,3-cd)pyrene 2 Indeno(1,2,3-cd)pyrene 3 Dibenz(a,h)anthracene 1 Dibenz(a,h)anthracene 2 Dibenz(a,h)anthracene 3 Benzo(g,h,i)perylene 1 Benzo(g,h,i)perylene 2 Benzo(g,h,i)perylene 3Boiler ID

CFB 1 & 2

4/28/2010 8:28 AM 4/28/2010

4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 Test Start Date Test Start Time Test End Date4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/20104/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/20104/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/20104/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010 4/28/2010 8:28 AM 4/28/2010 4/30/2010 8:13 AM 4/30/2010 4/30/2010 12:19 PM 4/30/2010Footnotes: * 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

Measured Value (μg/m3) Basis (Wet or Dry)

11:45 AM 1.612 Dry 11:32 AM 1.753 Dry 3:24 PM 2.025 Dry 11:45 AM 1.300 Dry 11:32 AM 1.619 Dry 3:24 PM 1.969 Dry 11:45 AM 4.471 Dry 11:32 AM 4.640 Dry 3:24 PM 4.770 Dry 11:45 AM 30.883 Dry 11:32 AM 32.048 Dry 3:24 PM 32.949 Dry 11:45 AM 1.560 Dry 11:32 AM 1.619 Dry 3:24 PM 1.664 Dry 11:45 AM 1.456 Dry 11:32 AM 1.511 Dry 3:24 PM 1.553 Dry 11:45 AM 1.638 Dry 11:32 AM 1.700 Dry 3:24 PM 1.747 Dry 11:45 AM 1.638 Dry 11:32 AM 1.700 Dry 3:24 PM 1.747 Dry 11:45 AM 3.483 Dry 11:32 AM 3.615 Dry 3:24 PM 3.716 Dry 11:45 AM 4.471 Dry 11:32 AM 4.640 Dry 3:24 PM 4.770 Dry 11:45 AM 1.690 Dry 11:32 AM 1.753 Dry 3:24 PM 1.803 Dry 11:45 AM 1.586 Dry 11:32 AM 1.646 Dry 3:24 PM 1.692 Dry 11:45 AM 1.716 Dry 11:32 AM 1.780 Dry 3:24 PM 1.830 Dry 11:45 AM 1.638 Dry 11:32 AM 1.700 Dry 3:24 PM 1.747 Dry 11:45 AM 1.768 Dry 11:32 AM 1.834 Dry 3:24 PM 1.886 Dry 11:45 AM 1.768 Dry 11:32 AM 1.834 Dry Test End Time3:24 PM 1.886 Dry 11:45 AM 2.912 Dry 11:32 AM 3.021 Dry 3:24 PM 3.106 Dry 11:45 AM 1.378 Dry 11:32 AM 1.430 Dry 3:24 PM 1.470 Dry 11:45 AM 2.860 Dry 11:32 AM 2.967 Dry 3:24 PM 3.051 Dry 11:45 AM 1.638 Dry 11:32 AM 1.700 Dry 3:24 PM 1.747 Dry 11:45 AM 1.534 Dry 11:32 AM 1.592 Dry 3:24 PM 1.636 Dry 11:45 AM 1.482 Dry 11:32 AM 1.538 Dry 3:24 PM 1.581 Dry 11:45 AM 1.482 Dry 11:32 AM 1.538 Dry 3:24 PM 1.581 Dry 11:45 AM 2.132 Dry 11:32 AM 2.212 Dry 3:24 PM 2.274 Dry 11:45 AM 3.431 Dry 11:32 AM 3.561 Dry 3:24 PM 3.661 Dry 11:45 AM 1.300 Dry 11:32 AM 1.349 Dry 3:24 PM 1.387 Dry 11:45 AM 30.675 Dry 11:32 AM 33.721 Dry 3:24 PM 35.500 Dry 11:45 AM 1.534 Dry 11:32 AM 1.592 Dry 3:24 PM 1.636 Dry 11:45 AM 1.716 Dry 11:32 AM 1.780 Dry 3:24 PM 1.830 Dry 11:45 AM 1.586 Dry 11:32 AM 1.646 Dry 3:24 PM 1.692 Dry 11:45 AM 3.795 Dry 11:32 AM 3.939 Dry 3:24 PM 4.049 Dry 11:45 AM 1.430 Dry 11:32 AM 1.484 Dry 3:24 PM 1.525 Dry 11:45 AM 2.080 Dry 11:32 AM 2.158 Dry 3:24 PM 2.219 Dry 11:45 AM 1.482 Dry 11:32 AM 1.538 Dry 3:24 PM 1.581 Dry11:45 AM 12.478 Dry 11:32 AM 12.949 Dry 3:24 PM 13.313 Dry 11:45 AM 1.482 Dry 11:32 AM 1.538 Dry 3:24 PM 1.581 Dry 11:45 AM 1.404 Dry 11:32 AM 1.457 Dry 3:24 PM 1.498 Dry 11:45 AM 1.612 Dry 11:32 AM 1.673 Dry 3:24 PM 1.720 Dry 11:45 AM 2.132 Dry 11:32 AM 2.212 Dry 3:24 PM 2.274 Dry 11:45 AM 1.534 Dry 11:32 AM 1.592 Dry 3:24 PM 1.636 Dry 11:45 AM 3.431 Dry 11:32 AM 3.561 Dry 3:24 PM 3.661 Dry 11:45 AM 3.379 Dry 11:32 AM 3.507 Dry 3:24 PM 3.605 Dry 11:45 AM 1.456 Dry 11:32 AM 1.511 Dry 3:24 PM 1.553 Dry 11:45 AM 8.163 Dry 11:32 AM 8.471 Dry 3:24 PM 8.709 Dry 11:45 AM 1.404 Dry 11:32 AM 1.457 Dry 3:24 PM 1.498 Dry 11:45 AM 22.357 Dry 11:32 AM 23.200 Dry 3:24 PM 23.852 Dry 11:45 AM 9.359 Dry 11:32 AM 9.712 Dry 3:24 PM 9.984 Dry 11:45 AM 1.430 Dry 11:32 AM 1.484 Dry 3:24 PM 1.525 Dry 11:45 AM 1.690 Dry 11:32 AM 1.753 Dry 3:24 PM 1.803 Dry 11:45 AM 1.638 Dry 11:32 AM 1.700 Dry 3:24 PM 1.747 Dry 11:45 AM 1.586 Dry 11:32 AM 1.646 Dry 3:24 PM 1.692 Dry 11:45 AM 5.355 Dry 11:32 AM 5.557 Dry 3:24 PM 5.713 Dry 11:45 AM 5.095 Dry11:32 AM 5.287 Dry 3:24 PM 5.436 Dry 11:45 AM 1.846 Dry 11:32 AM 1.915 Dry 3:24 PM 1.969 Dry 11:45 AM 2.028 Dry 11:32 AM 2.104 Dry 3:24 PM 2.163 Dry 11:45 AM 1.716 Dry 11:32 AM 1.780 Dry 3:24 PM 1.830 Dry 11:45 AM 4.419 Dry 11:32 AM 4.586 Dry 3:24 PM 4.715 Dry 11:45 AM 1.586 Dry 11:32 AM 1.646 Dry 3:24 PM 1.692 Dry 11:45 AM 1.690 Dry 11:32 AM 1.753 Dry 3:24 PM 1.803 Dry 11:45 AM 2.444 Dry 11:32 AM 2.536 Dry 3:24 PM 2.607 Dry 11:45 AM 1.872 Dry 11:32 AM 1.942 Dry 3:24 PM 1.997 Dry 11:45 AM 1.794 Dry 11:32 AM 1.861 Dry 3:24 PM 1.914 Dry 11:45 AM 2.340 Dry 11:32 AM 2.428 Dry 3:24 PM 2.496 Dry 11:45 AM 4.315 Dry 11:32 AM 4.478 Dry 3:24 PM 4.604 Dry 11:45 AM 6.863 Dry 11:32 AM 7.122 Dry 3:24 PM 7.322 Dry 11:45 AM 1.586 Dry 11:32 AM 1.646 Dry 3:24 PM 1.692 Dry 11:45 AM 1.612 Dry 11:32 AM 1.673 Dry 3:24 PM 1.720 Dry 11:45 AM 2.392 Dry 11:32 AM 2.482 Dry 3:24 PM 2.552 Dry 11:45 AM 2.132 Dry 11:32 AM 2.212 Dry 3:24 PM 2.274 Dry 11:45 AM 2.548 Dry 11:32 AM 2.644 Dry 3:24 PM 2.718 Dry 11:45 AM 1.976 Dry 11:32 AM 2.050 Dry3:24 PM 2.108 Dry 11:45 AM 1.586 Dry 11:32 AM 1.646 Dry 3:24 PM 1.692 Dry 11:45 AM 1.586 Dry 11:32 AM 1.646 Dry 3:24 PM 1.692 Dry 11:45 AM 1.664 Dry 11:32 AM 1.726 Dry 3:24 PM 1.775 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 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.1 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.1 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.1 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 5.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 5.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 5.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.5 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.5 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.5 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 5.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 5.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 5.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6

Semi-Volatile Organic HAP Emission Test ResultsU.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 4.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 4.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 4.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 4.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 4.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 4.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.9 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.9 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.9 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.9 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.9 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 1.9 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 30 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 30 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 30 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4U.S. EPA Method 0010 with SW -846 Method 8270C BDL 20 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 20 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 20 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 10 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 10 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 10 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 14 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 14 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 14 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 15 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 15 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 15 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 10U.S. EPA Method 0010 with SW -846 Method 8270C BDL 10 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 10 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.8 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 8.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 8.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 8.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.2U.S. EPA Method 0010 with SW -846 Method 8270C BDL 3.2 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.4 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6 U.S. EPA Method 0010 with SW -846 Method 8270C BDL 2.6Back Half mass* (ng) Condensate Mass*** (ng) Total Composite (ng)

1.8 2 6.2 2.1 2 6.5 2.9 2 7.3 1.9 2 5 2.9 2 6 4 2 7.1 10 4 17.2 10 4 17.2 10 4 17.2 100 13 118.8 100 13 118.8 100 13 118.8 1 2.6 6 1 2.6 6 1 2.6 6 1.7 1.9 5.6 1.7 1.9 5.6 1.7 1.9 5.6 1.9 2.2 6.3 1.9 2.2 6.3 1.9 2.2 6.3 2.6 2.2 6.3 2.6 2.2 6.3 2.6 2.2 6.3 3.4 8 13.4 3.4 8 13.4 3.4 8 13.4 3.8 8 17.2 3.8 8 17.2 3.8 8 17.2 1.9 2.2 6.5 1.9 2.2 6.5 1.9 2.2 6.5 1.9 2 6.1 1.9 2 6.1 1.9 2 6.1 1.8 2.4 6.6 1.8 2.4 6.6 1.8 2.4 6.6 1.9 2 6.3 1.9 2 6.3 1.9 2 6.3 2.2 2.2 6.8 2.2 2.2 6.8 2.2 2.2 6.8 2 2.2 6.8 2 2.2 6.8 Semi-Volatile Organic HAP Emission Test Results2 2.2 6.8 4.4 2.2 11.2 4.4 2.2 11.2 4.4 2.2 11.2 1.7 1.4 5.3 1.7 1.4 5.3 1.7 1.4 5.3 3.4 3.2 11 3.4 3.2 11 3.4 3.2 11 1.8 1.9 6.3 1.8 1.9 6.3 1.8 1.9 6.3 2 2 5.9 2 2 5.9 2 2 5.9 1.7 2 5.7 1.7 2 5.7 1.7 2 5.7 1.5 1.6 5.7 1.5 1.6 5.7 1.5 1.6 5.7 2 4 8.2 2 4 8.2 2 4 8.2 7 2.8 13.2 7 2.8 13.2 7 2.8 13.2 1.5 1.6 5 1.5 1.6 5 1.5 1.6 5 38 50 118 45 50 125 48 50 128 1.7 1.6 5.9 1.7 1.6 5.9 1.7 1.6 5.9 2 2.2 6.6 2 2.2 6.6 2 2.2 6.6 1.9 2.2 6.1 1.9 2.2 6.1 1.9 2.2 6.1 8.6 3.4 14.6 8.6 3.4 14.6 8.6 3.4 14.6 1.6 1.9 5.5 1.6 1.9 5.5 1.6 1.9 5.5 1.4 4 8 1.4 4 8 1.4 4 8 1.6 1.7 5.7 1.6 1.7 5.7 1.6 1.7 5.720 8 48 20 8 48 20 8 48 1.9 1.4 5.7 1.9 1.4 5.7 1.9 1.4 5.7 1.4 1.4 5.4 1.4 1.4 5.4 1.4 1.4 5.4 1.8 2 6.2 1.8 2 6.2 1.8 2 6.2 2 4 8.2 2 4 8.2 2 4 8.2 1.4 1.7 5.9 1.4 1.7 5.9 1.4 1.7 5.9 2.4 8 13.2 2.4 8 13.2 2.4 8 13.2 2.2 8 13 2.2 8 13 2.2 8 13 1.7 1.5 5.6 1.7 1.5 5.6 1.7 1.5 5.6 20 1.4 31.4 20 1.4 31.4 20 1.4 31.4 1.5 1.7 5.4 1.5 1.7 5.4 1.5 1.7 5.4 22 50 86 22 50 86 22 50 86 10 11 36 10 11 36 10 11 36 1.6 1.5 5.5 1.6 1.5 5.5 1.6 1.5 5.5 1.5 2 6.5 1.5 2 6.5 1.5 2 6.5 1.8 1.7 6.3 1.8 1.7 6.3 1.8 1.7 6.3 1.6 1.9 6.1 1.6 1.9 6.1 1.6 1.9 6.1 10 8 20.6 10 8 20.6 10 8 20.6 2.2 7.4 19.62.2 7.4 19.6 2.2 7.4 19.6 1.7 2.4 7.1 1.7 2.4 7.1 1.7 2.4 7.1 2.2 2.4 7.8 2.2 2.4 7.8 2.2 2.4 7.8 2 2 6.6 2 2 6.6 2 2 6.6 3.2 11 17 3.2 11 17 3.2 11 17 1.5 2.2 6.1 1.5 2.2 6.1 1.5 2.2 6.1 1.7 2.2 6.5 1.7 2.2 6.5 1.7 2.2 6.5 2.2 3.8 9.4 2.2 3.8 9.4 2.2 3.8 9.4 1.4 2.8 7.2 1.4 2.8 7.2 1.4 2.8 7.2 1.9 2.6 6.9 1.9 2.6 6.9 1.9 2.6 6.9 2.6 3 9 2.6 3 9 2.6 3 9 12 1.8 16.6 12 1.8 16.6 12 1.8 16.6 15 3.2 26.4 15 3.2 26.4 15 3.2 26.4 1.3 2.2 6.1 1.3 2.2 6.1 1.3 2.2 6.1 1.4 2.6 6.2 1.4 2.6 6.2 1.4 2.6 6.2 3.6 2.2 9.2 3.6 2.2 9.2 3.6 2.2 9.2 1.8 2.8 8.2 1.8 2.8 8.2 1.8 2.8 8.2 3.2 3.2 9.8 3.2 3.2 9.8 3.2 3.2 9.8 2.4 2 7.6 2.4 2 7.62.4 2 7.6 1.1 2.4 6.1 1.1 2.4 6.1 1.1 2.4 6.1 1.1 2.6 6.1 1.1 2.6 6.1 1.1 2.6 6.1 1 2.8 6.4 1 2.8 6.4 1 2.8 6.4Test Method Comments lb/mmBtu ug/dscm @ 7% O2

MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.23E-6 1.342 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.32E-6 1.442 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.53E-6 1.665 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<9.93E-7 1.082 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.22E-6 1.331 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.49E-6 1.620 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.42E-6 3.722 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.5E-6 3.816 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.6E-6 3.924 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.36E-5 25.705 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.42E-5 26.359 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.49E-5 27.100 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.19E-6 1.298 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.22E-6 1.331 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.26E-6 1.369 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.11E-6 1.212 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.14E-6 1.243 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.17E-6 1.277 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.25E-6 1.363 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.398 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.32E-6 1.437 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.25E-6 1.363 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.398 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.32E-6 1.437 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.66E-6 2.899 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.73E-6 2.973 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.81E-6 3.057 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.42E-6 3.722 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.5E-6 3.816 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.6E-6 3.924 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.29E-6 1.406 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.32E-6 1.442 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.36E-6 1.483 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.21E-6 1.320 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.24E-6 1.353 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.391 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.31E-6 1.428 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.34E-6 1.464 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.38E-6 1.506 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.25E-6 1.363 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.398 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.32E-6 1.437 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.35E-6 1.471 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.39E-6 1.509 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.42E-6 1.551 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.35E-6 1.471 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.39E-6 1.509 Calculated Emission RateMDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.42E-6 1.551 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.22E-6 2.423 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.28E-6 2.485 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.35E-6 2.555 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.05E-6 1.147 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.08E-6 1.176 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.11E-6 1.209 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.18E-6 2.380 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.24E-6 2.441 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.3E-6 2.509 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.25E-6 1.363 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.398 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.32E-6 1.437 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.17E-6 1.277 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.2E-6 1.309 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.24E-6 1.346 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.13E-6 1.233 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.16E-6 1.265 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.19E-6 1.300 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.13E-6 1.233 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.16E-6 1.265 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.19E-6 1.300 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.63E-6 1.774 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.67E-6 1.819 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.72E-6 1.871 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.62E-6 2.856 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.69E-6 2.929 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.76E-6 3.011 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<9.93E-7 1.082 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.02E-6 1.109 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.05E-6 1.141 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.34E-5 25.532 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.55E-5 27.735 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.68E-5 29.198 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.17E-6 1.277 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.2E-6 1.309 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.24E-6 1.346 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.31E-6 1.428 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.34E-6 1.464 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.38E-6 1.506 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.21E-6 1.320 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.24E-6 1.353 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.391 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.9E-6 3.159 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.97E-6 3.239 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.06E-6 3.330 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.09E-6 1.190 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.12E-6 1.220 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.15E-6 1.255 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.59E-6 1.731 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.63E-6 1.775 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.68E-6 1.825 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.13E-6 1.233 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.16E-6 1.265 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.19E-6 1.300MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<9.53E-6 10.386 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<9.78E-6 10.650 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.01E-5 10.949 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.13E-6 1.233 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.16E-6 1.265 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.19E-6 1.300 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.07E-6 1.168 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.1E-6 1.198 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.13E-6 1.232 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.23E-6 1.342 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.26E-6 1.376 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.3E-6 1.414 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.63E-6 1.774 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.67E-6 1.819 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.72E-6 1.871 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.17E-6 1.277 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.2E-6 1.309 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.24E-6 1.346 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.62E-6 2.856 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.69E-6 2.929 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.76E-6 3.011 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.58E-6 2.813 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.65E-6 2.884 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.72E-6 2.965 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.11E-6 1.212 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.14E-6 1.243 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.17E-6 1.277 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<6.24E-6 6.794 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<6.4E-6 6.967 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<6.58E-6 7.163 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.07E-6 1.168 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.1E-6 1.198 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.13E-6 1.232 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.71E-5 18.608 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.75E-5 19.081 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.8E-5 19.618 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<7.15E-6 7.789 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<7.33E-6 7.988 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<7.54E-6 8.212 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.09E-6 1.190 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.12E-6 1.220 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.15E-6 1.255 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.29E-6 1.406 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.32E-6 1.442 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.36E-6 1.483 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.25E-6 1.363 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.398 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.32E-6 1.437 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.21E-6 1.320 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.24E-6 1.353 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.391 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<4.09E-6 4.457 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<4.2E-6 4.571 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<4.31E-6 4.699 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.89E-6 4.241MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.99E-6 4.349 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<4.1E-6 4.471 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.41E-6 1.536 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.45E-6 1.575 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.49E-6 1.620 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.55E-6 1.688 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.59E-6 1.731 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.63E-6 1.779 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.31E-6 1.428 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.34E-6 1.464 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.38E-6 1.506 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.38E-6 3.678 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.46E-6 3.772 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.56E-6 3.878 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.21E-6 1.320 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.24E-6 1.353 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.391 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.29E-6 1.406 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.32E-6 1.442 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.36E-6 1.483 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.87E-6 2.034 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.91E-6 2.086 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.97E-6 2.144 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.43E-6 1.558 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.47E-6 1.598 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.51E-6 1.642 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.37E-6 1.493 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.41E-6 1.531 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.44E-6 1.574 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.79E-6 1.947 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.83E-6 1.997 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.88E-6 2.053 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.3E-6 3.592 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.38E-6 3.683 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<3.48E-6 3.787 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<5.24E-6 5.712 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<5.38E-6 5.858 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<5.53E-6 6.022 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.21E-6 1.320 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.24E-6 1.353 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.391 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.23E-6 1.342 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.26E-6 1.376 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.3E-6 1.414 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.83E-6 1.991 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.87E-6 2.041 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.93E-6 2.099 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.63E-6 1.774 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.67E-6 1.819 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.72E-6 1.871 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.95E-6 2.120 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.E-6 2.174 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<2.05E-6 2.235 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.51E-6 1.644 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.55E-6 1.686MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.59E-6 1.734 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.21E-6 1.320 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.24E-6 1.353 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.391 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.21E-6 1.320 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.24E-6 1.353 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.28E-6 1.391 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.27E-6 1.385 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.3E-6 1.420 MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection.

<1.34E-6 1.460545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 Steam Output (1000 lb/hr) Total Heat Input (mmBtu/hr) Flue Gas Moisture (%)528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.6 545 834 7 534 810 7.5 528 767 7.615.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748

Flue Gas O 2(%) Flue Gas Flow Rate (scfm) Flue Gas CO 2(%)15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 16045915.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 16636615.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 16174815.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459 15.1 4.2 166366 15.2 4 161748 15.1 4 160459Fuel Input Rate Fuel Type

413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous Flue Gas Temperature (F) Fuel #1420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inous 413 59400 bitum inous 416 55500 bitum inous 420 55500 bitum inousUnits of Measure Measurement Method Fuel Input Rate

lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other Fuel #1lb/hour Other

lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Otherlb/hour Other

lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Otherlb/hour Other

lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Otherlb/hour Other

lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour Other lb/hour OtherFuel Type Units of Measure Measurement Method Fuel #2Fuel Input Rate Fuel Type Units of Measure Fuel #3Measurement Method Fuel Input Rate Fuel Type Fuel #4Units of Measure Measurement Method Fuel #4 Other Supporting InformationEIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

1 4/29/2010 7:21 4/29/2010 2 4/29/2010 11:17 4/29/2010 3 4/29/2010 15:25 4/29/2010 Run Number Test Start Date Test Start Time Test End DateMeasured Value (ppm) Basis (Wet or Dry) Test Method Used

9:21 1.77 Dry U.S. EPA Conditional Test Method 033 (CTM-033) 13:17 1.79 Dry U.S. EPA Conditional Test Method 033 (CTM-033) 17:25 1.43 Dry U.S. EPA Conditional Test Method 033 (CTM-033) Hydrogen Cyanide Emission Test Results Test End TimeData Flag (ADL,

BDL, DDL) Test Method

Comments ADL MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 1.53E-03 539 808 7.47 14.7 ADL MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 1.53E-03 536 793 7.13 14.81 ADL MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. 1.53E-03 532 793 7.49 14.77

Steam Output (1000 lb/hr) Total Heat

Input (mmBtu/hr) Calculated Emission Rate (lb/mmBtu) Flue Gas Moisture (%) Flue Gas CO 2(%)Fuel Input Rate Fuel Type Units of Measure Measurement

Method Fuel Input

Rate 4.36 163426 414 59800 bitum inous lb/hour Other 3.97 163351 417 59800 bitum inous lb/hour Other 4.09 160792 417 59800 subbituminous lb/hour Other Flue Gas Flow Rate (dscfm) Flue Gas

Temperature (F) Fuel #1 Flue Gas O 2(%)Fuel Type Units of Measure Measurement

Method Fuel Input Rate Fuel Type Units of Measure Measurement

Method Fuel Input

Rate Fuel #2 Fuel #3Fuel Type Units of Measure Measurement

Method Fuel #4 Other Supporting InformationEIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

1 4/29/2010 7:21 4/29/2010 2 4/29/2010 11:17 4/29/2010 3 4/29/2010 15:25 4/29/2010 Run Number Test Start Date Test Start Time Test End DateMeasured Value (ppm) Basis (Wet or Dry) Test Method Used

9:21 6.56 Dry U.S. EPA Method 26 13:17 6.39 Dry U.S. EPA Method 26 17:25 6.05 Dry U.S. EPA Method 26 Test End Time Hydrogen Chloride Emission Test ResultsData Flag (ADL,

BDL, DDL) Test Method

Comments ADL 26A 7.63E-03 539 808 7.47 14.7 ADL 26A 7.31E-03 536 793 7.13 14.81 ADL 26A 6.96E-03 532 793 7.49 14.77 Calculated Emission Rate (lb/mmBtu) Flue Gas Moisture (%) Flue Gas CO 2(%) Hydrogen Chloride Emission Test Results Steam Output (1000 lb/hr) Total Heat

Input (mmBtu/hr)Fuel Input Rate Fuel Type Units of Measure Measurement

Method Fuel Input

Rate 4.36 163426 414 59800 bitum inous lb/hour Other 3.97 163351 417 59800 bitum inous lb/hour Other 4.09 160792 417 59800 subbituminous lb/hour Other Flue Gas Temperature (F) Fuel #1 Flue Gas O 2(%) Flue Gas

Flow Rate (dscfm)Fuel Type Units of Measure Measurement

Method Fuel Input Rate Fuel Type Units of Measure Measurement

Method Fuel Input

Rate Fuel #2 Fuel #3Fuel Type Units of Measure Measurement

Method Fuel #4 Other Supporting InformationEIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

1 4/29/2010 7:21 4/29/2010 2 4/29/2010 11:17 4/29/2010 3 4/29/2010 15:25 4/29/2010 Run Number Test Start Date Test Start Time Test End DateMeasured Value (ppm) Basis (Wet or Dry) Test Method Used

9:21 0.083 Dry U.S. EPA Method 26 13:17 0.083 Dry U.S. EPA Method 26 17:25 0.082 Dry U.S. EPA Method 26 Hydrogen Flouride Emission Test Results Test End TimeData Flag (ADL,

BDL, DDL) Test Method

Comments BDL MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <5.35E-05 539 808 7.47 BDL MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <5.28E-05 536 793 7.13 BDL MDL established per 40CFR136B by standard deviation times "T"factor of replicate analyzes near instrument limit of detection. <5.16E-05 532 793 7.49 Hydrogen Flouride Emission Test Results Steam Output (1000 lb/hr) Total Heat

Input (mmBtu/hr) Calculated Emission Rate (lb/mmBtu) Flue Gas Moisture (%)Fuel Input Rate Fuel Type Units of Measure Measurement

Method 14.7 4.36 163426 414 59800 bitum inous lb/hour Other 14.81 3.97 163351 417 59800 bitum inous lb/hour Other 14.77 4.09 160792 417 59800 subbituminous lb/hour Other Flue Gas Flow Rate (dscfm) Flue Gas

Temperature (F) Fuel #1 Flue Gas CO 2(%) Flue Gas

O 2(%)Fuel Input

Rate Fuel Type Units of Measure Measurement

Method Fuel Input Rate Fuel Type Units of Measure Measurement

Method Fuel #2 Fuel #3Fuel Input

Rate Fuel Type Units of Measure Measurement

Method Fuel #4 Other Supporting InformationEIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

1 4/29/2010 7:21 2 4/29/2010 11:17 3 4/29/2010 15:25 Run Number Test Start Date Test Start TimeMeasured NO (ppm)

4/29/2010 9:21 205.4 4/29/2010 13:17 203.7 4/29/2010 17:25 200.9

Test End Time Test End DateMeasured NO 2(ppm) Basis (Wet or Dry) Test Method Used

Dry Dry Dry Dry Dry Dry NOXEmission Test ResultsData Flag (ADL, BDL, DDL) Test Method Comments (lb/mmBtu)

ADL Method 7E 0.303 ADL Method 7E 0.296 ADL Method 7E 0.292 Total NOXCalculated Emission Rateppmdv @ 7% O 2

172.6 539 808 7.47 14.7 4.36 168.3 536 793 7.13 14.81 3.97 166.1 532 793 7.49 14.77 4.09 Flue Gas O 2(%) Calculated Emission Rate Steam Output (1000 lb/hr) Total Heat Input

(mmBtu/hr) Flue Gas

Moisture (%) Flue Gas

CO 2(%)Fuel Input Rate Fuel Type Units of Measure Measurement

Method Fuel Input

Rate 163426 414 59800 bitum inous lb/hour Other 163351 417 59800 bitum inous lb/hour Other 160792 417 59800 subbituminous lb/hour Other Flue Gas Flow Rate (dscfm) Flue Gas

Temperature (F) Fuel #1Fuel Type Units of Measure Measurement

Method Fuel Input

Rate Fuel Type Units of Measure Measurement

Method Fuel Input

Rate Fuel #2 Fuel #3Fuel Type Units of Measure Measurement

Method Fuel #4 Other Supporting InformationEIA

Facility Code Facility Name Boiler ID

10743 Morgantown Energy Facility CFB 1 & 2

Run Number Test Start Date Test Start TimeTotal Dissolved Solids (mg solids/liter) Total Suspended Solids (mg solids/liter) Test End Time Test End DateTest Method Used Data Flag (ADL, BDL, DDL) Constisuent Emission Test ResultsTest Method Comments Fuel Input Rate Flue Gas Temperat ure (F) Flue Gas Flow Rate (dscfm) Steam Output (1000 lb/hr) Total Heat Input

(mmBtu/hr)Fuel Type Units of Measure Measurement

Method Fuel Input Rate Fuel Type Units of Measure Measurement

Method Fuel Input Rate Fuel #1 Fuel #2Fuel Type Units of Measure Measurement

Method Fuel Input

Rate Fuel Type Units of

Measure Measurement

Method Fuel #3 Fuel #4Other Supporting Information