ML16053A210

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Northwest Medical Isotopes, LLC - NWMI-2016-RAI-001, Revision 0, Engineering Design File, Appendix E, EDF-3124-0009, Off-Road Emissions During Construction
ML16053A210
Person / Time
Site: Northwest Medical Isotopes
Issue date: 07/31/2015
From: Mcmanus G
Northwest Medical Isotopes, Portage
To:
Office of Nuclear Reactor Regulation
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ML16053A221 List:
References
NWMI-LTR-2016-002 EDF-3124-0009, NWMI-2016-RAI-001, Rev. 0
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Text

NWMI-201 6-RAI-001 Rev. 0 E CAL,*S I* SOTO*

Appendix E -

EDF-3124-0009, Off-Road Emissions During Construction E-i

Document ID: EDF-3124-0009 Revision ID: 1 Effective Date: July 31, 2015 Engineering Design File Off-Road Emissions During Construction Portage Project No.: 3124 Project

Title:

NWMI Environmental Report 4Portage TEM-9002 09129/09 Rev. 0

TEM-9002 ENGINEERING DESIGN FILE EDF-3124-0009 09/29109 Rev. I Rev. 0 Page 1 of 9

1. Portage Project No.: 3124 2. Project/Task: NWML Environmental Report
3. DCN#

4.

Title:

Off-Road Emissions During Construction

5. NPH PC or SDC: N/A
6. SSC Safety Category: N/A 7 Suini: This EDF documents the assumptions and calculations used to determine the emissions from non-road construction vehicles during the construction phase of the Northwest Medical Isotopes, LLC (NWMI)

Radioisotope Production Facility. The emission factors were obtained from the EPA NONROAD model. The results for NOR, CO, PM-10, PM-2.5, CO 2, and SOx are presented.

8. Distribution: (Portage, Inc.)

9: Review.(R) andApprove (A) Signatures: .,* ,, , ..... , , , .,-

(Identify minimum 'reviews and approvals. Additio~nal reviews/approvals may be added.) __....._____

' ,"* :* *.o ' * °1 Printed Name! * ,'['  ; * ,, : ..

  • S .... . .. "R/A ,* Organization -. . ,Signature *.:Date Author/Design agent A Gary McManus .i* .1/*7 1(((,, 1/21/16 Independent Review R Dave Thome *,/-1/21/16 Independent Review R Project Manager R/A John Belier 1/21/16 Registered Professional Engineer's Stamp (if required) [] N/A

TEM-9002 09129109 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. 1 Rev. 0 Page 2of 9 Introduction and Purpose During the construction phase, non-road air emissions would result from the activities of the construction equipment during operation. Off-road vehicle emissions were estimated for diesel-fueled construction equipment used for moving, grading, and compacting earthen materials, using emission factors for off-road construction based on values from the U.S. Environmental Protection Agency (EPA) NONROAD) model (EPA, 2008). Model emission factors were based on grams per horsepower hour. These values were combined with the number of pieces of equipment and hours of operation to estimate the total pounds released for each activity.

Assumptions On-road vehicle emissions were calculated using emission rate in grams(g)/horsepower-hour (hp-hr).

Average horsepower ratings for similar types of equipment were found in vendor data and used for the calculation. The number of pieces of equipment used and hours are the same used for the fugitive dust calculations (EDF-3 124-0004, Calculationfor DeterminationofFugitive Dust During ConstructionActivities from ConstructionEquipment), with the addition of a paver and asphalt roller. Emission factors (EF) are shown in Table 1. The assumed hours of operation for each piece of equipment are provided in Table 2.

Table 1. Emission Factors from NONROAD and AP-42 Compactor 232 5.58 0.748 !0.252 !0.189 521 0.931

'Ecaaor 15___ 5.65 2 -0.867 ,:, 0.280. LO ,,,.210 ...

' 521 - , : 0.93,1 ,...

Front loaders 100 , 5.65 0.867 i0.280 0.210 ~' 521 i 0.931

-! Graders! .,* 145 , "!°5.65: 0;,O867-;' 0.280 0):

.210,; ,':521 -,:> ..0.931': ...-

Paver -, 142 5.65 0 867 !0 280 0.210 521 ,, 0.931 S' l~ttoroller.. ... 232, 5.58

  • 0.748, 0...0252 ... 0.189 , 521 0.....0931...

a Emission factors from EPA Report NR-009d, Exhaust and CrankcaseEmission Factorsfor Nonroad Engine Modeling-Compression-Ignition,Table D-l, July 2010 (see Attachment 1).

b Assumes aPM-2.5 to PM-10 ration of 0.75.

eFrom Table 3.3.1 of EPA AP-42, Compilation of Air PollutantEmission Factors (see Attachment 2)

CO =carbon monoxide. PM-2.5 = particulate matter 2.5 jIm or less diameter.

CO2 = carbon dioxide. PM-10 = particulate matter 10 ju or less diameter.

NOx = mttrogen oxides. SO, = sulfur dioxide.

Total emissions were calculated using the following equation (EPA Report NR-009d, Exhaust and Crankcase Emission Factorsfor NonroadEngine Modeling-Compression-Ignition):

Emissions = EF

  • hp
  • hr where:

EF = emission factor (Table 1) lhp = average rated horse power of type of equipment used (Table 1) hr = hours of operation (Table 2)

Example calculation:

Emissions NO* EF x hap x hr

- 5.58 g/hp-hr x 250 hp x 100 hr

= 140 kilograms (kg) (310 pounds [lb])

TEM-9002 ENGINEERING DESIGN FILE EDF-31 24-0009 09129109 Rev. I Rev. 0 Page 3 of 9 The total emission for each type of the equipment in Table 1 was calculated and is shown in Table 2.

Table 2. Off-Road Vehicle Emissions (During 17 Months of Construction)

I. ._ I I ,IUU 1'4U [ IU 'IY 0..) 1U 1.):,UUU LYUUU Excavators 1 ;60 ,49 110 7.5 17; 2.4 5.4 ,1.8 4.0 ,4,500 10,000 8.1 18

  • 1 .- 120 r. 68 ;.,150 -. 10 , ' *5.6 -[6,200- 14,000* ::11 , '25 Lloaderso Graers 1 80 '66 150 i10 22 3.2 7.2 ,2.4 S5.4 6,000 i13,000 '11 24 Paver - 1 ","d*: 80 *64 1i40" 10*i' ...22 ' 32.
  • :-7:0-:. 72.4 *5.3Y" 5,900 i13,6000 Asphalt.... 1i.. 80- 100 2°d 30 '4-1 77 9.'

,700 21,000~i roller

.Total .....-
647 ,:-1430 7i91.:5 , 202 . ..30.-27 66.0, 7 22.6i Si 50, 6 -**,

0  !-30 0 ,:13 0 107;1 "236-CO =carbon monoxide. PM-2.5 =particulate matter 2.5 jrm or less diameter.

CO2 = carbon dioxide. PM-10 = particulate matter 10 pgm or less diameter.

NO* =mntrogen oxides. SOx = sulfur dioxide.

References AP-42, Compilationof Air PollutantEmission Factors, Volume I, Chapter 3, "Stationary Internal Combustion Sources," Fifth Edition, U.S. Environmental Protection Agency, Office of Air and Radiation, Washington, D.C., 2000.

EDF-3 124-0004, Calculationfor Determination of Fugitive Dust During Construction Activities from Construction Equipment, Rev. 1, Portage, Inc., Idaho Falls, Idaho, February 3, 2015.

EPA, 2008, <"NONROAD Model (nonroad engines, equipment, and vehicles)," U.S. Environmental Protection Agency, http://www3.epa.gov/otaq/nonrdmdl.htm, Washington, D.C., 2008.

NR-009d, Exhaust and Crankcase Emission Factorsfor Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 ENGINEERING DESIGN FILE EDF-31 24-0009 09/29109 Rev. 1 Rev. 0 Page 4 of 9 Attachment 1 Emission Table D-1 from EPA Report NR-009d (4 pages)

Table D1. Summary of Certiflcation Data for Nonroad Compression Ignition Engines*

.>Otol1l*hp'*:

g/hip-hr HO NOx HC+NOx CO PM HC frac HO calc NOx calc 2000 0.692103 5.170337 5.966223 4.051366 0.452858 0.113196 0.675351 5.290871 2001 0.628378 5.073763 6.018891 4. 174066 0.44201 0.141247 0.850153 5.168735 average 0.760241 5.12205 5.992557 4.1127 0.4474 0.7628 5.2298 sample size HO NOx HC+NOx CO PM 2000 4 6 20 20 20 2001 5 5 19 19 19 total 9 11 39" 39 39 glhp-hr HO NOx HC+NOx CO PM HC frac HC calc NOx calc 2000 0.489983 3.749647 4.9489 2.207041 0.289982 0.081156 0.401631 4.547269 2001 0.447831 4.,109521 4.80692 2.114884 0.242992 0.09869 0.474395 4.332525 average 0.468907 3.929584 4,87791 2.1610 0.2665 0.4380 4.4399 sample size HO NOx HC+NOx CO PM 2000 9 10 40. 39 40 2001 16 16 43 43 43 total 25 26 83 82 83

>25,to 50 lip :

glhp-hr HO NOx HC+NOx CO PM HO frac HO caic NOx caic 1999 0.496458 4.558405 4.983359 1.54213 0,35614 0.047095 0.23469 4.748669 2000 0.452946 4.893606 5.083919 1,522782 0.331 337 0.056039 0.284899 4.79902 2001 0.472917 4.469647 4.952901 1.532028 0.329222 0,064006 0.31 7014 4.635887 average 0.4741 07 4.640553 5.006726 1.5323 0.3389 0.2789 4.7279 sample size HC NOx HC+NOx CO PM 1999 11 15 72 72 72 2000 14 22 95 96 96 2001 25 35 103 104 104 total 50 72 270 272 272 Source: NR-009d, Exhaust and CrankcaseEmission Factorsfor NonroadEngine Modeling, Compression-ignition,U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 ENGINEERING DESIGN FILE EDF-3124-0009 09129/09 Rev. 1 Rev. 0 Page 5 of 9 Table Dl. Summary of Cextification Data for Nonroad Compression Ignition Engines (cont)*

,50 :toi 100 hp:,i g/hp-hr HG NOx HC+NOx CO PM 1998 0.528845 5.682411 4.235576 2.753546 0.472055 1999 0.517642 5.61 3376 6.569501 2.34687 0.452553 2000 0.46289 5.494892 4.235576 2.047055 0.460428 2001 0.575867 5.604515 5.976957 2.314372 0.506824 average 0.5213 5.5988 5.254402 2.36655 0.4730 sample size HC NOx HC+NOx CO PM 1998 18 71 1 21 19 1999 27 91 3 33 31 2000 35 104 1 38 36 2001 40 127 3 47 43 total 120 393 8 139 129

>100 to 175 hp':

g/hp-hr HG NOx HC+NOx CO PM 1997 0.297479 5.599201 0.745072 0.281 314 1998 0.355336 5.743938 0.961288 0.276378 1999 0.35159 5.749792 0.93731 0.270345 2000 0.33246 5.593736 0.68581 0.282059 2001 0.3551 07 5.574714 1.003922 0.28934 average 0.3384 5.6523 0.8667 0.2799 sample size HC NOx HO+NOx CO PM 1997 29 43 0 29 25 1998 25 52 0. 27 24 1999 25 59 0 27 25 2000 27 61 0 29 28 2001 34 69 0 37 36 total 140 284 0 149 138

>1!75 to 300 hpl g/hp-hr HC NOx HC+NOx CO PM 1996 0.331633

  • 5.667602 0.834876 0.239994 1997 0.307044 5.723983 0.819777 0.24542 1998 0.31 6321 5.574079 0.722968 0.262486 1999 0.314974 5.549376 0.695869 0.257528 2000 0.26631 5.441729 4.54 0.666725 0.240685 2001 0.314765 5.506545 4.203295 0.744633 0.266622 average 0.3085 5.5772 4.371 648 0.7475 0.2521 sample size HO NOx HO+NOx CO PM 1996 44 44 0 44 44 1997 43 43 0 43 43 1998 72 72 0. 72 72 1999 71 71 0 71 71 2000 64 64 2 64 64 2001 86 86 6 88 88 total 380 380 8 382 382 D3 Source: NR-009d, Exhaust and Crankcase Emission Factorsfor Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 09129109 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. 1 Rev. 0 Page 6 of 9 Table D1. Summary of Certification Data for Nonroad Compression Ignition Engines (cont)*

>300:10:tO !600 g/hp-hr HC NOx HC+NOx CO PM~

1996 0.260521 6.264393* 1.353145 0.195978 1997 0.1553 5.865363 1.431343 0.213156 1998 0.209071 6.126551 1.289223 0.198893 1999 0.201521 6.04976 1.201752 0.192703 2000 0.186024 5.77026 5.24 1.254546 0.203148 average 0.2025 6.0153 5.24 t1.3060 0.2008 200lTier 2 0.1t669 4.3351 4.345348 0,8425 0.1t316 sample size HC NOx . HC+NOx CO PM 1996 40 40 0 40 40 1997 35 35 0 35 35 1998 48 48 0 48 48 1999 55 55 0 55 55 2000 51 51 1 51 51 2001 14 14 35 35 35 total ' 243 243 36 264 264

  • g/hp-hr HC NOx HC+NOx CO PM 1996 0.174804 6.063537 1.502117 0.242149 1997 0.135125 5.872338 1.571034 0.236991 1998 0.190719 *5.866023 1,277422 0.205116 1999 0.118392 5.723896 1.361031 0.227162 2000 0.126821 5.790567 1.368105 0.225632 2001 0.138065 5.612418 3.975047 0.883305 0.183773 average 0.1473 5.8215 3.975047 1.3272 0.2201 samPle size HO NOx HC+NOx CO PM 1996 11 11 0 11 11 1997 10 10 0 10 10 1998 12 12 0 12 12 1999 13 13 0 13 13 2000 15 15 0 15 15 2001 16 16 3 17 17 total 77 77 3 78 78 Source: NR-009d, Exhaust and CrankcaseEmission Factorsfor Nonroad Engine Modeling, Compression-Ignition,U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 ENGINEERING DESIGN FILE EDF-31 24-0009 09/29/09 Rev. 1 Rev. 0 Page 7 of 9 Table D1. Summary of Certification Data for Nonroad Compression Ignition Engines (cont)*

>750 hD5:.i;:i g/hp-hr HC NOx HC+NOx CO PMI 2000 0.25906 6.252638 0.727419 0,183308 2001 0.31 3093 6,052394. 0.800887 0.203589 average 0.2861 6.1525 0.7642 0.1934 sample size HC NOx HC+NOx CO PM 2000 16 16 0 16 16 2001 18 18 0 . 18 18 total 34 34 0 34 34
  • Values in bold are used in NONROAD. All are Tier 1 emission factors, with the exception that both Tier 1 and Tier 2 emission factors are provided for the >300 to 600 hp category.

Source: NR-009d, Exhaust and CrankcaseEmission Factorsfor NonroadEngine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 09129109 ENGINEERING DESIGN FILE EDF-31 24-0009 Rev. 1 Rev. 0 Page 8 of 9 Attachment 2 EPA AIP-42 Volume 1, Table 3.3.1 Table 3.3-1. EMISSION FACTORLS FOR UNCONTROLLED GASOLINE AND DIESEL INDUSTRIAL ENGINESa Gasoline Fuel Diesel Fuel (5CC 2-02-003-01,.2-03-003-01) (SCC 2--02_-001-02, 2-03-001-01)

Emission Factor Emission Factor Emission Factor Emission Factor EMVISSION (lb/hp-br) (lb!IMLMBm) (lb/hp-hr) (lbi/MMBt) FACTOR Pollutant (power output) (fuel input) (power output) (fuel ienput) RATING NOx 0.011 1.63 0.031 4.41 D CO 6.96 E-03d 0 .9 9 dt 6.68 E£-03 0.95 D SOR 5.91 E-04 0_0S4 2.05 E,-03 0_29 D PM-10b 7.21EF_-04 0.10 2.20E,-03 0.31 D CO~c 1.08 154 1.15 164 B Aldehydes 4.85 E-04 0.07 4.63 E-04 0.07 D TO(G Exhaust 0.015 2.10 2.47 E-03 0.35 D Evaporative 6.61 FE-)4 0.09 0.00 0.00 B Crankcase 4.85 E_-03 0.69 4.'41 B-05 0.01 B Refueling 1.08 E-03 0.15 0.00 0.00 B References 7,000 B~n/hp-hr2,5-6,9-14.

was used When necessatry, to conv:ert fro6man average brake-specific lb/MMBtu to lb/h*p-hr. Tofiuel consumption convert (BSFC) from lb/hp-hr to of kg/kw-,

lir, mufltiply by 0.603. To conv*ert fr'om lbbqvIMBtu to ng!!J, multiply by 430. SCC = Source Classification Code. TOC = total organic compounds.

b PM-i10 = particulate matter less than or equal to 10 jgm aerodynamic diameter. All particulate is assumed to be _<1 jim in size.

Assumes 99% conversion of carbon in fueol to CO, with 87 weight % carbon in diesel, 86 weight %

carbon in gasoline, average BSFC of 7,000 Btu/hp*-hr, diesel heating value of 19,300 BtuIlb, and gasoline heatincx value of'20,300 Btu/lb.

d Instead of 0.439' lb/ p-hr (power output) and 62.7 lb/mmBtu (fueol input), the correct emissions factors values are 6.96 E-(03 lb/hp-hr (power output) and 0.99 lb/mmnitu (fuel input), respectiv~ely.

This is an editorial correction. March 24, 2009 Source:

Sources,"AP-42, Compilation Fifth Edition, of Air PollutantEmission Factors, Volume I, Chapter 3, "Stationary Internal Combustion U.S. Environmental Protection Agency, Office of Air and Radiation, Washington, D.C., 2000.

TEM-9002 09129109 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. I Rev. 0 Page 9 of 9 Attachment 3 Excel Spreadsheet of Calculations E~~oi~meel lip Woe- I Co- P,0"1 Ip .,5 l 0o2" I FEilssion Fader (gthr-hp)' ___ ___

s' Reldazer 250 5.5OE+60 7.482-01 2.52E-01 1.892-01 521 9.31E-0L Compacter 232 5.50E+00 7.402-01 2.52E-01 1.892-01 521 4.9.31E-01 Exc~avators 145 5.05E+00 8.872'-01 2.89E-01 2.102-01 521 9.1E0 4 9.512-01 Front Loaders Graders Paver 122 145 142 5.652+00 5.652+65 5.65E+60 8.67E-21 8.6"/E-01 8,."/E-01 2.652-01 2.802-01 2.86E-01 2.10E-01 2.10E-01 2.10E-01 525 521 521 f.9.51E-01 9.512-01 Asphalt Roller 232 5.582+65 7.48E-01 2.522-01 1.88E-01 521 9.s1E-oo a.Emission factnor from EPA ReporINo. E*R-G009d,July 2010, "Exirnst and Crankcase Emission Factors for Nonroad Ergire, Mc~elir.-Cnnmressinr-T~ltiiin" Annoendix D Tables NR-009d Reference Location

b. Assumes a PM2.5 to PM.10 rati on of 0.75 - I
c. From EPA 2000, AP-42, Voilsos I Table 3.3.1 ittp www.epa. ov etaq/models h________________________ nanrdmdlnaonrdmdl20OlO420r102001.p

________ ________ Pollutaet~s) _ ________

Equipmeet Nejaber Soees NOn COl P0018 PM-2.5 C02 SOs (k*g) (Ik) (kg) (Ik) (ha) (1ke) (kg) OIli) (kg) (Ike) (lie (Its)

Belldozer 1 160 139 507 19 41 6 14 5 10 15,925 29,715 21 51 Comipeetor 1 129 035 542 21 46 7 13 2 12 14,505 31,975 26 57 E2eavatoles 1 60 49 165 0 17 2 5 2 4 4,113 9,993 0 10 letn 1 120 65 150 10 23 1 7 5 6 6,252 15,781 11 25 Grader, 1 80 66 145 10 22 1 7 2 5 6,044 13,324 11 24 Paver 1 88 64 142 10 22 5 7 2 5 5,919 15,040 11 21 Asphalt 1 89 104 223 14 31 5 19 4 2 9,679 21,319 17 50 Reller ____ ________

Tetal 646 1,422 91 281 30 67 23 59 65,672 152,159 187 236

NWMI-201 6-RAI-001 Rev. 0 E CAL,*S I* SOTO*

Appendix E -

EDF-3124-0009, Off-Road Emissions During Construction E-i

Document ID: EDF-3124-0009 Revision ID: 1 Effective Date: July 31, 2015 Engineering Design File Off-Road Emissions During Construction Portage Project No.: 3124 Project

Title:

NWMI Environmental Report 4Portage TEM-9002 09129/09 Rev. 0

TEM-9002 ENGINEERING DESIGN FILE EDF-3124-0009 09/29109 Rev. I Rev. 0 Page 1 of 9

1. Portage Project No.: 3124 2. Project/Task: NWML Environmental Report
3. DCN#

4.

Title:

Off-Road Emissions During Construction

5. NPH PC or SDC: N/A
6. SSC Safety Category: N/A 7 Suini: This EDF documents the assumptions and calculations used to determine the emissions from non-road construction vehicles during the construction phase of the Northwest Medical Isotopes, LLC (NWMI)

Radioisotope Production Facility. The emission factors were obtained from the EPA NONROAD model. The results for NOR, CO, PM-10, PM-2.5, CO 2, and SOx are presented.

8. Distribution: (Portage, Inc.)

9: Review.(R) andApprove (A) Signatures: .,* ,, , ..... , , , .,-

(Identify minimum 'reviews and approvals. Additio~nal reviews/approvals may be added.) __....._____

' ,"* :* *.o ' * °1 Printed Name! * ,'['  ; * ,, : ..

  • S .... . .. "R/A ,* Organization -. . ,Signature *.:Date Author/Design agent A Gary McManus .i* .1/*7 1(((,, 1/21/16 Independent Review R Dave Thome *,/-1/21/16 Independent Review R Project Manager R/A John Belier 1/21/16 Registered Professional Engineer's Stamp (if required) [] N/A

TEM-9002 09129109 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. 1 Rev. 0 Page 2of 9 Introduction and Purpose During the construction phase, non-road air emissions would result from the activities of the construction equipment during operation. Off-road vehicle emissions were estimated for diesel-fueled construction equipment used for moving, grading, and compacting earthen materials, using emission factors for off-road construction based on values from the U.S. Environmental Protection Agency (EPA) NONROAD) model (EPA, 2008). Model emission factors were based on grams per horsepower hour. These values were combined with the number of pieces of equipment and hours of operation to estimate the total pounds released for each activity.

Assumptions On-road vehicle emissions were calculated using emission rate in grams(g)/horsepower-hour (hp-hr).

Average horsepower ratings for similar types of equipment were found in vendor data and used for the calculation. The number of pieces of equipment used and hours are the same used for the fugitive dust calculations (EDF-3 124-0004, Calculationfor DeterminationofFugitive Dust During ConstructionActivities from ConstructionEquipment), with the addition of a paver and asphalt roller. Emission factors (EF) are shown in Table 1. The assumed hours of operation for each piece of equipment are provided in Table 2.

Table 1. Emission Factors from NONROAD and AP-42 Compactor 232 5.58 0.748 !0.252 !0.189 521 0.931

'Ecaaor 15___ 5.65 2 -0.867 ,:, 0.280. LO ,,,.210 ...

' 521 - , : 0.93,1 ,...

Front loaders 100 , 5.65 0.867 i0.280 0.210 ~' 521 i 0.931

-! Graders! .,* 145 , "!°5.65: 0;,O867-;' 0.280 0):

.210,; ,':521 -,:> ..0.931': ...-

Paver -, 142 5.65 0 867 !0 280 0.210 521 ,, 0.931 S' l~ttoroller.. ... 232, 5.58

  • 0.748, 0...0252 ... 0.189 , 521 0.....0931...

a Emission factors from EPA Report NR-009d, Exhaust and CrankcaseEmission Factorsfor Nonroad Engine Modeling-Compression-Ignition,Table D-l, July 2010 (see Attachment 1).

b Assumes aPM-2.5 to PM-10 ration of 0.75.

eFrom Table 3.3.1 of EPA AP-42, Compilation of Air PollutantEmission Factors (see Attachment 2)

CO =carbon monoxide. PM-2.5 = particulate matter 2.5 jIm or less diameter.

CO2 = carbon dioxide. PM-10 = particulate matter 10 ju or less diameter.

NOx = mttrogen oxides. SO, = sulfur dioxide.

Total emissions were calculated using the following equation (EPA Report NR-009d, Exhaust and Crankcase Emission Factorsfor NonroadEngine Modeling-Compression-Ignition):

Emissions = EF

  • hp
  • hr where:

EF = emission factor (Table 1) lhp = average rated horse power of type of equipment used (Table 1) hr = hours of operation (Table 2)

Example calculation:

Emissions NO* EF x hap x hr

- 5.58 g/hp-hr x 250 hp x 100 hr

= 140 kilograms (kg) (310 pounds [lb])

TEM-9002 ENGINEERING DESIGN FILE EDF-31 24-0009 09129109 Rev. I Rev. 0 Page 3 of 9 The total emission for each type of the equipment in Table 1 was calculated and is shown in Table 2.

Table 2. Off-Road Vehicle Emissions (During 17 Months of Construction)

I. ._ I I ,IUU 1'4U [ IU 'IY 0..) 1U 1.):,UUU LYUUU Excavators 1 ;60 ,49 110 7.5 17; 2.4 5.4 ,1.8 4.0 ,4,500 10,000 8.1 18

  • 1 .- 120 r. 68 ;.,150 -. 10 , ' *5.6 -[6,200- 14,000* ::11 , '25 Lloaderso Graers 1 80 '66 150 i10 22 3.2 7.2 ,2.4 S5.4 6,000 i13,000 '11 24 Paver - 1 ","d*: 80 *64 1i40" 10*i' ...22 ' 32.
  • :-7:0-:. 72.4 *5.3Y" 5,900 i13,6000 Asphalt.... 1i.. 80- 100 2°d 30 '4-1 77 9.'

,700 21,000~i roller

.Total .....-
647 ,:-1430 7i91.:5 , 202 . ..30.-27 66.0, 7 22.6i Si 50, 6 -**,

0  !-30 0 ,:13 0 107;1 "236-CO =carbon monoxide. PM-2.5 =particulate matter 2.5 jrm or less diameter.

CO2 = carbon dioxide. PM-10 = particulate matter 10 pgm or less diameter.

NO* =mntrogen oxides. SOx = sulfur dioxide.

References AP-42, Compilationof Air PollutantEmission Factors, Volume I, Chapter 3, "Stationary Internal Combustion Sources," Fifth Edition, U.S. Environmental Protection Agency, Office of Air and Radiation, Washington, D.C., 2000.

EDF-3 124-0004, Calculationfor Determination of Fugitive Dust During Construction Activities from Construction Equipment, Rev. 1, Portage, Inc., Idaho Falls, Idaho, February 3, 2015.

EPA, 2008, <"NONROAD Model (nonroad engines, equipment, and vehicles)," U.S. Environmental Protection Agency, http://www3.epa.gov/otaq/nonrdmdl.htm, Washington, D.C., 2008.

NR-009d, Exhaust and Crankcase Emission Factorsfor Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 ENGINEERING DESIGN FILE EDF-31 24-0009 09/29109 Rev. 1 Rev. 0 Page 4 of 9 Attachment 1 Emission Table D-1 from EPA Report NR-009d (4 pages)

Table D1. Summary of Certiflcation Data for Nonroad Compression Ignition Engines*

.>Otol1l*hp'*:

g/hip-hr HO NOx HC+NOx CO PM HC frac HO calc NOx calc 2000 0.692103 5.170337 5.966223 4.051366 0.452858 0.113196 0.675351 5.290871 2001 0.628378 5.073763 6.018891 4. 174066 0.44201 0.141247 0.850153 5.168735 average 0.760241 5.12205 5.992557 4.1127 0.4474 0.7628 5.2298 sample size HO NOx HC+NOx CO PM 2000 4 6 20 20 20 2001 5 5 19 19 19 total 9 11 39" 39 39 glhp-hr HO NOx HC+NOx CO PM HC frac HC calc NOx calc 2000 0.489983 3.749647 4.9489 2.207041 0.289982 0.081156 0.401631 4.547269 2001 0.447831 4.,109521 4.80692 2.114884 0.242992 0.09869 0.474395 4.332525 average 0.468907 3.929584 4,87791 2.1610 0.2665 0.4380 4.4399 sample size HO NOx HC+NOx CO PM 2000 9 10 40. 39 40 2001 16 16 43 43 43 total 25 26 83 82 83

>25,to 50 lip :

glhp-hr HO NOx HC+NOx CO PM HO frac HO caic NOx caic 1999 0.496458 4.558405 4.983359 1.54213 0,35614 0.047095 0.23469 4.748669 2000 0.452946 4.893606 5.083919 1,522782 0.331 337 0.056039 0.284899 4.79902 2001 0.472917 4.469647 4.952901 1.532028 0.329222 0,064006 0.31 7014 4.635887 average 0.4741 07 4.640553 5.006726 1.5323 0.3389 0.2789 4.7279 sample size HC NOx HC+NOx CO PM 1999 11 15 72 72 72 2000 14 22 95 96 96 2001 25 35 103 104 104 total 50 72 270 272 272 Source: NR-009d, Exhaust and CrankcaseEmission Factorsfor NonroadEngine Modeling, Compression-ignition,U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 ENGINEERING DESIGN FILE EDF-3124-0009 09129/09 Rev. 1 Rev. 0 Page 5 of 9 Table Dl. Summary of Cextification Data for Nonroad Compression Ignition Engines (cont)*

,50 :toi 100 hp:,i g/hp-hr HG NOx HC+NOx CO PM 1998 0.528845 5.682411 4.235576 2.753546 0.472055 1999 0.517642 5.61 3376 6.569501 2.34687 0.452553 2000 0.46289 5.494892 4.235576 2.047055 0.460428 2001 0.575867 5.604515 5.976957 2.314372 0.506824 average 0.5213 5.5988 5.254402 2.36655 0.4730 sample size HC NOx HC+NOx CO PM 1998 18 71 1 21 19 1999 27 91 3 33 31 2000 35 104 1 38 36 2001 40 127 3 47 43 total 120 393 8 139 129

>100 to 175 hp':

g/hp-hr HG NOx HC+NOx CO PM 1997 0.297479 5.599201 0.745072 0.281 314 1998 0.355336 5.743938 0.961288 0.276378 1999 0.35159 5.749792 0.93731 0.270345 2000 0.33246 5.593736 0.68581 0.282059 2001 0.3551 07 5.574714 1.003922 0.28934 average 0.3384 5.6523 0.8667 0.2799 sample size HC NOx HO+NOx CO PM 1997 29 43 0 29 25 1998 25 52 0. 27 24 1999 25 59 0 27 25 2000 27 61 0 29 28 2001 34 69 0 37 36 total 140 284 0 149 138

>1!75 to 300 hpl g/hp-hr HC NOx HC+NOx CO PM 1996 0.331633

  • 5.667602 0.834876 0.239994 1997 0.307044 5.723983 0.819777 0.24542 1998 0.31 6321 5.574079 0.722968 0.262486 1999 0.314974 5.549376 0.695869 0.257528 2000 0.26631 5.441729 4.54 0.666725 0.240685 2001 0.314765 5.506545 4.203295 0.744633 0.266622 average 0.3085 5.5772 4.371 648 0.7475 0.2521 sample size HO NOx HO+NOx CO PM 1996 44 44 0 44 44 1997 43 43 0 43 43 1998 72 72 0. 72 72 1999 71 71 0 71 71 2000 64 64 2 64 64 2001 86 86 6 88 88 total 380 380 8 382 382 D3 Source: NR-009d, Exhaust and Crankcase Emission Factorsfor Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 09129109 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. 1 Rev. 0 Page 6 of 9 Table D1. Summary of Certification Data for Nonroad Compression Ignition Engines (cont)*

>300:10:tO !600 g/hp-hr HC NOx HC+NOx CO PM~

1996 0.260521 6.264393* 1.353145 0.195978 1997 0.1553 5.865363 1.431343 0.213156 1998 0.209071 6.126551 1.289223 0.198893 1999 0.201521 6.04976 1.201752 0.192703 2000 0.186024 5.77026 5.24 1.254546 0.203148 average 0.2025 6.0153 5.24 t1.3060 0.2008 200lTier 2 0.1t669 4.3351 4.345348 0,8425 0.1t316 sample size HC NOx . HC+NOx CO PM 1996 40 40 0 40 40 1997 35 35 0 35 35 1998 48 48 0 48 48 1999 55 55 0 55 55 2000 51 51 1 51 51 2001 14 14 35 35 35 total ' 243 243 36 264 264

  • g/hp-hr HC NOx HC+NOx CO PM 1996 0.174804 6.063537 1.502117 0.242149 1997 0.135125 5.872338 1.571034 0.236991 1998 0.190719 *5.866023 1,277422 0.205116 1999 0.118392 5.723896 1.361031 0.227162 2000 0.126821 5.790567 1.368105 0.225632 2001 0.138065 5.612418 3.975047 0.883305 0.183773 average 0.1473 5.8215 3.975047 1.3272 0.2201 samPle size HO NOx HC+NOx CO PM 1996 11 11 0 11 11 1997 10 10 0 10 10 1998 12 12 0 12 12 1999 13 13 0 13 13 2000 15 15 0 15 15 2001 16 16 3 17 17 total 77 77 3 78 78 Source: NR-009d, Exhaust and CrankcaseEmission Factorsfor Nonroad Engine Modeling, Compression-Ignition,U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 ENGINEERING DESIGN FILE EDF-31 24-0009 09/29/09 Rev. 1 Rev. 0 Page 7 of 9 Table D1. Summary of Certification Data for Nonroad Compression Ignition Engines (cont)*

>750 hD5:.i;:i g/hp-hr HC NOx HC+NOx CO PMI 2000 0.25906 6.252638 0.727419 0,183308 2001 0.31 3093 6,052394. 0.800887 0.203589 average 0.2861 6.1525 0.7642 0.1934 sample size HC NOx HC+NOx CO PM 2000 16 16 0 16 16 2001 18 18 0 . 18 18 total 34 34 0 34 34
  • Values in bold are used in NONROAD. All are Tier 1 emission factors, with the exception that both Tier 1 and Tier 2 emission factors are provided for the >300 to 600 hp category.

Source: NR-009d, Exhaust and CrankcaseEmission Factorsfor NonroadEngine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 09129109 ENGINEERING DESIGN FILE EDF-31 24-0009 Rev. 1 Rev. 0 Page 8 of 9 Attachment 2 EPA AIP-42 Volume 1, Table 3.3.1 Table 3.3-1. EMISSION FACTORLS FOR UNCONTROLLED GASOLINE AND DIESEL INDUSTRIAL ENGINESa Gasoline Fuel Diesel Fuel (5CC 2-02-003-01,.2-03-003-01) (SCC 2--02_-001-02, 2-03-001-01)

Emission Factor Emission Factor Emission Factor Emission Factor EMVISSION (lb/hp-br) (lb!IMLMBm) (lb/hp-hr) (lbi/MMBt) FACTOR Pollutant (power output) (fuel input) (power output) (fuel ienput) RATING NOx 0.011 1.63 0.031 4.41 D CO 6.96 E-03d 0 .9 9 dt 6.68 E£-03 0.95 D SOR 5.91 E-04 0_0S4 2.05 E,-03 0_29 D PM-10b 7.21EF_-04 0.10 2.20E,-03 0.31 D CO~c 1.08 154 1.15 164 B Aldehydes 4.85 E-04 0.07 4.63 E-04 0.07 D TO(G Exhaust 0.015 2.10 2.47 E-03 0.35 D Evaporative 6.61 FE-)4 0.09 0.00 0.00 B Crankcase 4.85 E_-03 0.69 4.'41 B-05 0.01 B Refueling 1.08 E-03 0.15 0.00 0.00 B References 7,000 B~n/hp-hr2,5-6,9-14.

was used When necessatry, to conv:ert fro6man average brake-specific lb/MMBtu to lb/h*p-hr. Tofiuel consumption convert (BSFC) from lb/hp-hr to of kg/kw-,

lir, mufltiply by 0.603. To conv*ert fr'om lbbqvIMBtu to ng!!J, multiply by 430. SCC = Source Classification Code. TOC = total organic compounds.

b PM-i10 = particulate matter less than or equal to 10 jgm aerodynamic diameter. All particulate is assumed to be _<1 jim in size.

Assumes 99% conversion of carbon in fueol to CO, with 87 weight % carbon in diesel, 86 weight %

carbon in gasoline, average BSFC of 7,000 Btu/hp*-hr, diesel heating value of 19,300 BtuIlb, and gasoline heatincx value of'20,300 Btu/lb.

d Instead of 0.439' lb/ p-hr (power output) and 62.7 lb/mmBtu (fueol input), the correct emissions factors values are 6.96 E-(03 lb/hp-hr (power output) and 0.99 lb/mmnitu (fuel input), respectiv~ely.

This is an editorial correction. March 24, 2009 Source:

Sources,"AP-42, Compilation Fifth Edition, of Air PollutantEmission Factors, Volume I, Chapter 3, "Stationary Internal Combustion U.S. Environmental Protection Agency, Office of Air and Radiation, Washington, D.C., 2000.

TEM-9002 09129109 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. I Rev. 0 Page 9 of 9 Attachment 3 Excel Spreadsheet of Calculations E~~oi~meel lip Woe- I Co- P,0"1 Ip .,5 l 0o2" I FEilssion Fader (gthr-hp)' ___ ___

s' Reldazer 250 5.5OE+60 7.482-01 2.52E-01 1.892-01 521 9.31E-0L Compacter 232 5.50E+00 7.402-01 2.52E-01 1.892-01 521 4.9.31E-01 Exc~avators 145 5.05E+00 8.872'-01 2.89E-01 2.102-01 521 9.1E0 4 9.512-01 Front Loaders Graders Paver 122 145 142 5.652+00 5.652+65 5.65E+60 8.67E-21 8.6"/E-01 8,."/E-01 2.652-01 2.802-01 2.86E-01 2.10E-01 2.10E-01 2.10E-01 525 521 521 f.9.51E-01 9.512-01 Asphalt Roller 232 5.582+65 7.48E-01 2.522-01 1.88E-01 521 9.s1E-oo a.Emission factnor from EPA ReporINo. E*R-G009d,July 2010, "Exirnst and Crankcase Emission Factors for Nonroad Ergire, Mc~elir.-Cnnmressinr-T~ltiiin" Annoendix D Tables NR-009d Reference Location

b. Assumes a PM2.5 to PM.10 rati on of 0.75 - I
c. From EPA 2000, AP-42, Voilsos I Table 3.3.1 ittp www.epa. ov etaq/models h________________________ nanrdmdlnaonrdmdl20OlO420r102001.p

________ ________ Pollutaet~s) _ ________

Equipmeet Nejaber Soees NOn COl P0018 PM-2.5 C02 SOs (k*g) (Ik) (kg) (Ik) (ha) (1ke) (kg) OIli) (kg) (Ike) (lie (Its)

Belldozer 1 160 139 507 19 41 6 14 5 10 15,925 29,715 21 51 Comipeetor 1 129 035 542 21 46 7 13 2 12 14,505 31,975 26 57 E2eavatoles 1 60 49 165 0 17 2 5 2 4 4,113 9,993 0 10 letn 1 120 65 150 10 23 1 7 5 6 6,252 15,781 11 25 Grader, 1 80 66 145 10 22 1 7 2 5 6,044 13,324 11 24 Paver 1 88 64 142 10 22 5 7 2 5 5,919 15,040 11 21 Asphalt 1 89 104 223 14 31 5 19 4 2 9,679 21,319 17 50 Reller ____ ________

Tetal 646 1,422 91 281 30 67 23 59 65,672 152,159 187 236

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