Information Collection Request 

Boiler MACT Emissions Report 

We Energies 

Valley Power Plant 

Boiler 3 Outlet Duct 

Milwaukee, Wisconsin 

April 20 through 22, 2010 
1520 Kensington Road, Suite 204 

Oak Brook, IL 60523-2141 

630-521-9400 

630-521-9494 fax

Information Collection Request 

Boiler MACT Emissions Report 

We Energies 

Valley Power Plant 

Boiler 3 Outlet Duct 

Milwaukee, Wisconsin 

April 20 through 22, 2010 

Report Submittal Date 

June 24, 2010 

Prepared By 

Platt Environmental Services 

Report No. M101602 
Table of Contents 

1.0 INTRODUCTION.............................................................................................................................. 1

2.0 EXECUTIVE SUMMARY................................................................................................................. 2

3.0 TEST METHODOLOGY .................................................................................................................. 3

Method 1 Sample and Velocity Traverse Determination .............................................................3

Method 2 Volumetric Flow Rate Determination ...........................................................................3

Method 3A Oxygen (O2)/Carbon Dioxide (CO2) Determination..................................................4

OTM27 Filterable Particulate Determination................................................................................4

OTM 028 Condensable Particulate Determination ......................................................................4

Method 29 Trace Metals Determination.......................................................................................5

Mercury Determination by Method 30B (Sorbent Trap Method)..................................................5

4.0 TEST RESULTS SUMMARIES....................................................................................................... 6

5.0 CONCLUSION AND CERTIFICATION......................................................................................... 10

APPENDIX 

Test Section Diagrams...............................................................................................................12 

Sample Train Diagrams .............................................................................................................14 

Calculation Nomenclature and Formulas...................................................................................20 

Sample Analysis Data................................................................................................................36 

Reference Method Test Data (Computerized Sheets)...............................................................75 

Calibration Data .......................................................................................................................104 

Gas Certification Sheets ..........................................................................................................139 

Field Data Sheets.....................................................................................................................141 
ICR Boiler MACT Emissions Report PES Report No.: M101602 

We Energies-Valley Power Plant Boiler 3 Outlet Duct April 20 through 22, 2010 

1 

1.0 Introduction 

PLATT ENVIRONMENTAL SERVICES (PES) conducted an information 

collection request (ICR) boiler maximum achievable control technology (MACT) 

emissions test program for We Energies at the Valley Power Plant on the Boiler 3 

Outlet Duct on April 20 through 22, 2010. This report summarizes the results of 

the test program and test methods used. 

The test location, test dates, and test parameters are summarized below, in 

Table 1. 

Table 1 

Test Overview 

Test 

Location Test Dates Test Method Test Parameters 

USEPA Method 3A Oxygen (O2), Carbon Dioxide (CO2) 

Other Test Method 

27 (OTM27) 

<PM2.5 Filterable Particulate, 

Total Filterable Particulate 

Other Test Method 

28 (OTM 28) Condensable Particulate 

USEPA Method 5/29 

Antimony (Sb), Arsenic (As), Beryllium 

(Be), Cadmium (Cd), Chromium (Cr), 

Cobalt (Co), Lead (Pb), Manganese (Mn), 

Nickel (Ni), Selenium (Se) 

and Filterable Particulate 

Boiler 3 

Outlet Duct 

April 20 

through 22, 

2010 

USEPA Method 30B Mercury (Hg) 

The identification of individuals associated with the test program is summarized 

below in Table 2. 

Table 2 

Test Personnel 

Location Address Contact 

Test Facility We Energies 

Valley Power Plant 

Milwaukee, Wisconsin 

Ms. Brenda Bergemann 

(414) 221-2459 (phone) 

Brenda.bergemann@we-energies.com 

Testing 

Company 

Representative 

Platt Environmental Services, Inc.

1520 Kensington Road, Suite 204

Oak Brook, Illinois 60523 

Mr. Mark E. Peterson 

Senior Project Manager 

(630) 521-9400 (phone) 

mpeterson@plattenv.com 

The test crew consisted of Messrs. J. Howe, J. Zeiss, A. Sczygielski, Rich 

Sollars, Rod Sollars, D. Quedens, B. Hendricks, M. Platt, and M. Peterson of 

PES. The purpose of the test program was to evaluate the emissions of the 

constituents listed in Table 1 to satisfy the USEPA information request. 
ICR Boiler MACT Emissions Report PES Report No.: M101602 

We Energies-Valley Power Plant Boiler 3 Outlet Duct April 20 through 22, 2010 

2 

2.0 Executive Summary 

Selected results of the test program are summarized below, in Table 3. A 

complete summary of emission test results follows the narrative portion of this 

report. 

Table 3 

Test Results 

Test Location Test Parameter 

Emission 

Rate 

<PM2.5, filterable, lb/mmBtu 0.0010 

>PM2.5, filterable, lb/mmBtu 0.0012 

PM, condensable 0.0118 

<PM2.5, total, lb/mmBtu 0.0129 

Total PM, lb/mmBtu 0.0141 

Filterable PM (from M29), lb/mmBtu 0.0025 

Sb, lb/mmBtu < 6.09 E-07 

As, lb/mmBtu <6.11 E-07 

Be, lb/mmBtu < 1.53 E-08 

Cd, lb/mmBtu < 1.53 E-08 

Cr, lb/mmBtu 5.27 E-04 

Co, lb/mmBtu 5.18 E-06 

Pb, lbs/mmBtu 1.20 E-06 

Mn, lbs/mmBtu 6.75 E-05 

Ni, lb/mmBtu 3.08 E-04 

Se, lb/mmBtu < 3.95 E-06 

Boiler 3 Outlet 

Duct

Hg, lb/mmBtu 2.08 E-08 

A standard F-Factor of 9780 dscf/mmBtu for Bituminous Coal was used in the 

calculation of the emissions on a lb/mmBtu basis. Compounds expressed above 

as less than or equal to values had a fraction or fractions that were below 

detection limits. Detection limits for each fraction were used to determine the 

emission rate for these compounds. 
ICR Boiler MACT Emissions Report PES Report No.: M101602 

We Energies-Valley Power Plant Boiler 3 Outlet Duct April 20 through 22, 2010 

3 

3.0 Test Methodology 

Emissions testing were conducted following the methods specified in 40 CFR, 

Part 60, Appendix A and 40CFR63, Appendix A. Schematics of the sampling 

trains used and copies of field data sheets for each test run are included in the 

Appendix. 

The following methodologies were used during the test program: 

Method 1 Sample and Velocity Traverse Determination 

Test measurement points were selected in accordance with Method 1, 40 CFR, 

Part 60, Appendix A. The characteristics of the measurement location are 

summarized below, in Table 4. 

Table 4 

Sample Point Selection 

Test Location 

Upstream 

Distance 

Downstream 

Distance Test Parameters 

Number of 

Sampling Points 

Filterable Particulate, 

Condensable Particulate, Total 

Particulate, Sb, As, Be, Cd, Cr, 

Co, Pb, Mn, Ni, and Se 

24 

Boiler 3 Outlet 

Duct >0.5 >2.0 

Hg 3 

Method 2 Volumetric Flow Rate Determination 

Gas velocity was measured following Method 2, 40 CFR, Part 60, Appendix A, 

for purposes of calculating stack gas volumetric flow rate. An S-type pitot tube, 

differential pressure gauge, thermocouple and temperature readout were used to 

determine gas velocity at each sample point. All of the equipment used was 

calibrated in accordance with the specifications of the Method. Calibration data is 

presented in the Appendix. 
ICR Boiler MACT Emissions Report PES Report No.: M101602 

We Energies-Valley Power Plant Boiler 3 Outlet Duct April 20 through 22, 2010 

4 

Method 3A Oxygen (O2)/Carbon Dioxide (CO2) Determination 

A Servomex analyzer was used to determine stack gas oxygen (O2) and carbon 

dioxide content and, by difference, nitrogen content in accordance with Method 

3A, 40 CFR, Part 60, Appendix A for purposes of calculating stack gas molecular 

weight as well as for calculating emissions on a lb/mmBtu basis. The O2

instrument has a nondispersive infrared-based detector and operates in a range 

of 0-25%, the CO2 instrument also uses a nondispersive infrared-based detector 

and operates in the range of 0-20%. All of the equipment used was calibrated in 

accordance with the specifications of the Method. 

OTM27 Filterable Particulate Determination

Stack gas filterable particulate concentrations and emission rates were 

determined in accordance with Other Test Method 27 (OTM27) for determination 

of particulate matter less than 2.5 microns. An Environmental Supply Company, 

Inc. sampling train was used to sample stack gas at a constant rate, as specified 

in the Method. Filterable particulate matter was separated into two fractions; one 

containing less than PM2.5, the other greater than PM2.5. 

OTM 028 Condensable Particulate Determination 

Stack gas condensable particulate concentrations and emission rates were 

determined in accordance with the dry draft impinger method, in conjunction with 

Method OTM27 filterable particulate sampling. Condensable particulate matter 

was collected in the impinger portion of the Method OTM027 sampling train. 

The condensable particulate matter (CPM) was collected in impingers after 

filterable particulate material was collected utilizing Method OTM27. The organic 

and aqueous fractions were then taken to dryness and weighed. The total of all 

fractions represents the CPM. Compared to the December 17, 1991 promulgated 

Method 202, this Method includes the addition of a condenser, followed by a 

water dropout impinger immediately after the final heated filter. One modified 

Greenburg Smith impinger and an ambient temperature filter follow the water 

dropout impinger. A schematic of the sampling train configured with these 

changes is found in the Appendix. 

CPM was collected in the water dropout, modified Greenburg Smith impinger and 

ambient filter portion of the sampling train as described in this Method. The 

impinger contents were purged with nitrogen (N2) immediately after sample 

collection to remove dissolved sulfur dioxide (SO2) gases from the impingers. 

The impinger solution was then extracted with acetone and methylene chloride 

(MeCl2). The organic and aqueous fractions were dried and the residues 

weighed. The total of the aqueous and organic fractions represents the CPM. 

The samples were analyzed by PES personnel in Des Plaines, Illinois. 
ICR Boiler MACT Emissions Report PES Report No.: M101602 

We Energies-Valley Power Plant Boiler 3 Outlet Duct April 20 through 22, 2010 

5 

Method 29 Trace Metals Determination

Stack gas metals concentrations and emission rates were determined in 

accordance with Method 29. An Environmental Supply Company, Inc. sampling 

train was used to sample stack gas, in the manner specified in the Method. 

Analyses of the samples collected were conducted by Maxxam Analytics, Inc. 

Samples were analyzed for the following metals, using Inductively Coupled 

Argon Plasma emission spectroscopy (ICP): Antimony, Arsenic, Beryllium, 

Cadmium, Chromium, Cobalt, Lead, Manganese, Nickel, and Selenium. All of the 

equipment used was calibrated in accordance with the specifications of the 

Method. Calibration data is presented in the Appendix. 

Mercury Determination by Method 30B (Sorbent Trap Method) 

Paired trains were utilized using three (3) test points at the Boiler 3 Outlet Duct. 

Per Method 30B sampling, each sample was collected on the paired in-situ 

sorbent traps. A tube of silica was used to capture remaining moisture prior to the 

sample reaching the gas metering system. 

The sample train used for this test program was designed by APEX, Inc. and 

meet all requirements for Method 30B sampling. Samples were analyzed onsite 

utilizing an Ohio Lumex, Inc. analyzer for total gaseous mercury. 
ICR Boiler MACT Emissions Report PES Report No.: M101602 

We Energies-Valley Power Plant Boiler 3 Outlet Duct April 20 through 22, 2010 

6 

4.0 Test Results Summaries 

Client:

Facility:

Test Location:

Test Method:

Normal Normal Normal

4/20/10 4/21/10 4/22/10

8:00 8:00 8:15

14:03 13:59 14:17

Run 1 Run 2 Run 3 Average

308.4 306.5 306.6 307.2

7.5% 7.8% 7.4% 7.6%

28.32 28.12 28.14 28.19

123.776 134.068 127.101 128.315

43.066 44.802 44.749 44.206

310,944 323,477 323,096 319,172

187,133 193,166 193,818 191,372

12.8 12.5 12.6 12.6

5.9 6.0 5.9 5.9

101.7 107.2 100.5 103.1

0.0004 0.0003 0.0003 0.0003

0.0007 0.0005 0.0005 0.0006

1.080 0.762 0.807 0.883

0.0013 0.0009 0.0009 0.0010

0.0007 0.0003 0.0002 0.0004

0.0012 0.0004 0.0003 0.0006

1.915 0.709 0.536 1.053

0.0023 0.0008 0.0006 0.0012

0.0037 0.0035 0.0037 0.0036

0.0062 0.0058 0.0062 0.0061

9.938 9.566 10.366 9.957

0.0121 0.0113 0.0121 0.0118

0.0041 0.0038 0.0040 0.0040

0.0069 0.0063 0.0067 0.0066

11.0180 10.3280 11.1730 10.840

0.0134 0.0122 0.0130 0.0129

0.0048 0.0041 0.0042 0.0044

0.0081 0.0067 0.0070 0.0073

12.9330 11.0370 11.7090 11.893

0.0157 0.0130 0.0136 0.0141

grains/dscf

Stack Conditions

End Time

Average %CO2 by volume, dry basis

Average %O2 by volume, dry basis

Gas Volumetric Flow Rate, acfm

Gas Volumetric Flow Rate, dscfm

Average Flue Pressure, in. Hg

Isokinetic Variance

lb/hr

lb/mmBtu (Standard Fd Factor)

We Energies

Valley Power Plant

Boiler 3 Outlet Duct

Average Gas Velocity, ft/sec

Source Condition

Date

Start Time

Average Gas Temperature, °F

grains/acf

grains/dscf

lb/hr

lb/mmBtu (Standard Fd Factor)

Condensable PM (OTM28)

grains/acf

grains/dscf

lb/hr

lb/mmBtu (Standard Fd Factor)

lb/mmBtu (Standard Fd Factor)

grains/acf

Total PM

Filterable >PM2.5 (OTM27)

OTM27/OTM28

grains/dscf

Filterable <PM2.5 (OTM27)

lb/hr

grains/acf

Gas Sample Volume, dscf

Flue Gas Moisture, percent by volume

Total PM<2.5

grains/acf

grains/dscf

lb/hr

lb/mmBtu (Standard Fd Factor)
ICR Boiler MACT Emissions Report PES Report No.: M101602 

We Energies-Valley Power Plant Boiler 3 Outlet Duct April 20 through 22, 2010 

7 

Client:

Facility:

Test Location:

Test Method:

Normal Normal Normal

4/20/10 4/21/10 4/22/10

8:00 8:00 8:16

12:09 12:07 12:26

Run 1 Run 2 Run 3 Average

307.9 306.9 306.2 307.0

8.3% 8.0% 7.8% 8.0%

28.32 28.12 28.14 28.19

122.211 147.658 147.529 139.133

39.864 42.140 41.965 41.323

287,824 304,257 302,995 298,359

171,726 181,078 181,080 177,961

12.8 12.5 12.6 12.6

5.9 6.0 5.9 5.9

92.5 98.5 98.4 96.5

0.0005 0.0009 0.0008 0.0007

0.0009 0.0016 0.0013 0.0013

1.282 2.449 2.094 1.942

0.0017 0.0031 0.0026 0.0025

Method 5 from M29 Train

grains/dscf

Filterable PM (Method 29)

lb/hr

grains/acf

lb/mmBtu (Standard Fd Factor)

We Energies

Valley Power Plant

Boiler 3 Outlet Duct

Average Gas Velocity, ft/sec

Source Condition

Date

Start Time

Average Gas Temperature, °F

Gas Sample Volume, dscf

Flue Gas Moisture, percent by volume

Stack Conditions

End Time

Average %CO2 by volume, dry basis

Average %O2 by volume, dry basis

Gas Volumetric Flow Rate, acfm

Gas Volumetric Flow Rate, dscfm

Average Flue Pressure, in. Hg

Isokinetic Variance
ICR Boiler MACT Emissions Report PES Report No.: M101602 

We Energies-Valley Power Plant Boiler 3 Outlet Duct April 20 through 22, 2010 

8 

Client:

Facility:

Test Location:

Test Method:

Normal Normal Normal

4/20/10 4/21/10 4/22/10

8:00 8:00 8:16

12:09 12:07 12:26

Run 1 Run 2 Run 3 Average

307.9 306.9 306.2 307.0

8.3% 8.0% 7.8% 8.0%

28.32 28.12 28.14 28.19

122.211 147.658 147.529 139.133

39.864 42.140 41.965 41.323

287,824 304,257 302,995 298,359

171,726 181,078 181,080 177,961

12.8 12.5 12.6 12.6

5.9 6.0 5.9 5.9

92.5 98.5 98.4 96.5

< 0.160 < 0.132 < 0.132 < 0.141

< 0.809 < 0.670 < 0.670 < 0.716

< 5.20E-04 < 4.54E-04 < 4.55E-04 < 4.76E-04

< 6.88E-07 < 5.70E-07 < 5.70E-07 < 6.09E-07

< 0.260 < 0.215 < 0.215 < 0.230

< 0.809 < 0.670 < 0.670 < 0.716

< 5.20E-04 < 4.54E-04 < 4.55E-04 < 4.76E-04

< 6.88E-07 < 5.74E-07 < 5.70E-07 < 6.11E-07

< 0.540 < 0.447 < 0.447 < 0.478

< 0.202 < 0.167 < 0.168 < 0.179

< 1.30E-04 < 1.14E-04 < 1.14E-04 < 1.19E-04

< 1.72E-07 < 1.43E-07 < 1.43E-07 < 1.53E-07

< 0.043 < 0.036 < 0.036 < 0.038

< 0.202 < 0.167 < 0.168 < 0.179

< 1.30E-04 < 1.14E-04 < 1.14E-04 < 1.19E-04

< 1.72E-07 < 1.43E-07 < 1.43E-07 < 1.53E-07

164.529 479.974 212.108 285.537

355.900 1038.251 458.818 617.656

2.29E-01 7.04E-01 3.11E-01 4.15E-01

3.03E-04 8.89E-04 3.90E-04 5.27E-04

1.645 4.207 1.565 2.472

4.034 10.315 3.837 6.062

2.59E-03 7.00E-03 2.60E-03 4.06E-03

3.43E-06 8.83E-06 3.26E-06 5.18E-06

0.214 0.107 0.167 0.163

1.841 0.926 1.443 1.403

1.18E-03 6.28E-04 9.79E-04 9.30E-04

1.57E-06 7.93E-07 1.23E-06 1.20E-06

20.002 34.154 49.713 34.623

45.723 78.071 113.638 79.144

2.94E-02 5.30E-02 7.71E-02 5.31E-02

3.89E-05 6.69E-05 9.67E-05 6.75E-05

110.606 251.068 81.443 147.706

270.181 613.292 198.944 360.806

1.74E-01 4.16E-01 1.35E-01 2.42E-01

2.30E-04 5.25E-04 1.69E-04 3.08E-04

2.269 < 1.150 0.809 < 1.409

7.455 < 3.779 2.657 < 4.630

4.80E-03 < 2.56E-03 1.80E-03 < 3.05E-03

6.34E-06 < 3.24E-06 2.26E-06 < 3.95E-06

We Energies

Valley Power Plant

Boiler 3 Outlet Duct

Source Condition

29

End Time

Average Gas Temperature, °F

Average Flue Pressure, in. Hg

Date

ug/dscm

Gas Sample Volume, dscf

Average %O2 by volume, dry basis

Start Time

Stack Conditions

Flue Gas Moisture, percent by volume

Antimony (Sb) Emissions

Isokinetic Variance

Gas Volumetric Flow Rate, dscfm

Average %CO2 by volume, dry basis

Cadmium (Cd) Emissions

ppb

lb/hr

lb/mmBtu

ug/dscm

lb/mmBtu

Beryllium (Be) Emissions

ug/dscm

ppb

ug/dscm

ppb

lb/mmBtu

ppm

lb/hr

ppb

lb/hr

lb/mmBtu

ppb

Chromium (Cr) Emissions

Average Gas Velocity, ft/sec

Gas Volumetric Flow Rate, acfm

ug/dscm

Arsenic (As) Emissions

lb/hr

ug/dscm

Cobalt (Co) Emissions

lb/hr

ppb

lb/hr

lb/mmBtu

ppb

ug/dscm

Lead (Pb) Emissions

lb/mmBtu

ug/dscm

Nickel (Ni) Emissions

lb/hr

lb/hr

lb/mmBtu

lb/mmBtu

ppb

ug/dscm

Manganese (Mn) Emissions

lb/hr

lb/mmBtu

lb/mmBtu

Selenium (Se) Emissions

ppb

ug/dscm

lb/hr
ICR Boiler MACT Emissions Report PES Report No.: M101602 

We Energies-Valley Power Plant Boiler 3 Outlet Duct April 20 through 22, 2010 

9 

Test No. Date Start Time End Time

Vm 

(standard L) ng detected ppb ug/dscm ug/wscm

lbs/mmBtu 

(Fd Factor)

1A 4/20/2010 8:05 12:05 542.620 19.00 4.20E-03 0.04 0.03 2.98E-08

1B 4/20/2010 8:05 12:05 531.498 20.00 4.51E-03 0.04 0.03 3.20E-08

19.50 4.35E-03 0.04 0.03 3.09E-08

2A 4/21/2010 8:00 12:00 457.657 10.00 2.62E-03 0.02 0.02 1.87E-08

2B 4/21/2010 8:00 12:00 447.071 10.00 2.68E-03 0.02 0.02 1.92E-08

10.00 2.65E-03 0.02 0.02 1.89E-08

3A 4/22/2010 8:20 12:20 456.941 6.50 1.71E-03 0.01 0.01 1.21E-08

3B 4/22/2010 8:20 12:20 446.902 7.00 1.88E-03 0.02 0.01 1.33E-08

6.75 1.79E-03 0.01 0.01 1.27E-08

12.08 2.93E-03 0.02 0.02 2.08E-08

Method 30B (Sorbent Trap) Mercury Test Results Summary

We Energies

Valley Power Plant

Unit 3 Duct

Overall Average

Run 3 Average

Run 1 Average

Run 2 Average

 
ICR Boiler MACT Emissions Report PES Report No.: M101602 

We Energies-Valley Power Plant Boiler 3 Outlet Duct April 20 through 22, 2010 

10 

5.0 Conclusion and Certification 

PLATT ENVIRONMENTAL SERVICES is pleased to have been of service to We 

Energies. If you have any questions regarding this test report, please do not 

hesitate to contact us at 630-521-9400. 

CERTIFICATION 

As project manager, I hereby certify that this test report represents a true and 

accurate summary of emissions test results and the methodologies employed to 

obtain those results, and the test program was performed in accordance with the 

methods specified in this test report. 

PLATT ENVIRONMENTAL SERVICES 

__________________________________ Program Manager 

Mark E. Peterson 

__________________________________ Quality Assurance 

Jeffrey M. Crivlare 
APPENDIX
M101602 12 Platt Environmental
M101602 13 Platt Environmental
M101602 14 Platt Environmental
M101602 15 Platt Environmental
M101602 16 Platt Environmental
M101602 17 Platt Environmental
M101602 18 Platt Environmental
M101602 19 Platt Environmental
M101602 20 Platt Environmental
M101602 21 Platt Environmental
M101602 22 Platt Environmental
M101602 23 Platt Environmental
M101602 24 Platt Environmental
M101602 25 Platt Environmental
M101602 26 Platt Environmental
M101602 27 Platt Environmental
M101602 28 Platt Environmental
M101602 29 Platt Environmental
M101602 30 Platt Environmental
M101602 31 Platt Environmental
M101602 32 Platt Environmental
M101602 33 Platt Environmental
M101602 34 Platt Environmental
M101602 35 Platt Environmental
M101602 36 Platt Environmental
M101602 37 Platt Environmental
M101602 38 Platt Environmental
M101602 39 Platt Environmental
M101602 40 Platt Environmental
M101602 41 Platt Environmental
M101602 42 Platt Environmental
M101602 43 Platt Environmental
M101602 44 Platt Environmental
M101602 45 Platt Environmental
M101602 46 Platt Environmental
M101602 47 Platt Environmental
M101602 48 Platt Environmental
M101602 49 Platt Environmental
M101602 50 Platt Environmental
M101602 51 Platt Environmental
M101602 52 Platt Environmental
M101602 53 Platt Environmental
M101602 54 Platt Environmental
M101602 55 Platt Environmental
M101602 56 Platt Environmental
M101602 57 Platt Environmental
M101602 58 Platt Environmental
M101602 59 Platt Environmental
M101602 60 Platt Environmental
M101602 61 Platt Environmental
M101602 62 Platt Environmental
M101602 63 Platt Environmental
M101602 64 Platt Environmental
M101602 65 Platt Environmental
M101602 66 Platt Environmental
M101602 67 Platt Environmental
M101602 68 Platt Environmental
M101602 69 Platt Environmental
M101602 70 Platt Environmental
M101602 71 Platt Environmental
M101602 72 Platt Environmental
M101602 73 Platt Environmental
M101602 74 Platt Environmental
M101602 75 Platt Environmental
M101602 76 Platt Environmental
M101602 77 Platt Environmental
M101602 78 Platt Environmental
M101602 79 Platt Environmental
M101602 80 Platt Environmental
M101602 81 Platt Environmental
M101602 82 Platt Environmental
M101602 83 Platt Environmental
M101602 84 Platt Environmental
M101602 85 Platt Environmental