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

CAL,*S E

I* SOTO*

NWMI-201 6-RAI-001 Rev. 0 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 09/29109 Rev. 0 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. I 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, CO2, 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 ENGINEERING DESIGN FILE EDF-3124-0009 09129109 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, Calculation for Determination of Fugitive Dust During Construction Activities from Construction Equipment), 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 Crankcase Emission Factors for 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 Pollutant Emission 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 Factors for Nonroad Engine 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 09129109 Rev. 0 ENGINEERING DESIGN FILE EDF-31 24-0009 Rev. I 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 Excavators Lloaderso Graers Paver -

Asphalt....

roller I

,IUU 1'4U [

IU 'IY 1

60

,49 110 7.5

  • 1

.- 120 r. 68 ;.,150 -. 10 1

80

'66 150 i10 1 ","d*:

80

  • 64 1i 40" 10*i' 1i..80-100 2°d 30 1

'4-17; 22 22 '

0..)

2.4 3.2

32.

5.4

,1.8 7.2

,2.4

-7:0-:. 72.4 1U 1.):,UUU LYUUU 4.0

,4,500 10,000

' *5.6 -[6,200-14,000*

S5.4 6,000 i13,000

  • 5.3 Y" 5,900 i13,6000 77 9.'

,700 21,000~i 8.1 18

11

, '25

'11 24

.Total 647,:-1430 7 i91.:5, 202...30.-27 66.0, 7 22.6i 50, Si 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, Compilation of Air Pollutant Emission 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, Calculation for 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 Factors for Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 09/29109 Rev. 0 ENGINEERING DESIGN FILE EDF-31 24-0009 Rev. 1 Page 4 of 9 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 2000 0.692103 2001 0.628378 average 0.760241 sample size 2000 2001 total glhp-hr 2000 2001 average sample size 2000 2001 total HO 4

5 9

HO 0.489983 0.447831 0.468907 NOx 5.170337 5.073763 5.12205 NOx 6

5 11 NOx 3.749647 4.,109521 3.929584 HC+NOx 5.966223 6.018891 5.992557 HC+NOx 20 19 39" HC+NOx 4.9489 4.80692 4,87791 CO 4.051366

4. 174066 4.1127 CO 20 19 39 CO 2.207041 2.114884 2.1610 PM HC frac 0.452858 0.113196 0.44201 0.141247 0.4474 PM 20 19 39 PM HC frac 0.289982 0.081156 0.242992 0.09869 0.2665 HO calc 0.675351 0.850153 0.7628 NOx calc 5.290871 5.168735 5.2298 HC calc 0.401631 0.474395 0.4380 NOx calc 4.547269 4.332525 4.4399 HO NOx HC+NOx CO 9

10

40.

39 16 16 43 43 25 26 83 82 PM 40 43 83

>25,to 50 lip :

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

TEM-9002 09129/09 Rev. 0 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. 1 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 1998 0.528845 1999 0.517642 2000 0.46289 2001 0.575867 average 0.5213 sample size HC 1998 18 1999 27 2000 35 2001 40 total 120

>100 to 175 hp':

g/hp-hr HG 1997 0.297479 1998 0.355336 1999 0.35159 2000 0.33246 2001 0.3551 07 average 0.3384 sample size HC 1997 29 1998 25 1999 25 2000 27 2001 34 total 140 NOx 5.682411 5.61 3376 5.494892 5.604515 5.5988 NOx 71 91 104 127 393 NOx 5.599201 5.743938 5.749792 5.593736 5.574714 5.6523 NOx 43 52 59 61 69 284 HC+NOx 4.235576 6.569501 4.235576 5.976957 5.254402 HC+NOx 1

3 1

3 8

HC+NOx HO+NOx 0

0.

0 0

0 0

HC+NOx 4.54 4.203295 4.371 648 HO+NOx 0

0 0.

0 2

6 8

CO 2.753546 2.34687 2.047055 2.314372 2.36655 CO 21 33 38 47 139 CO 0.745072 0.961288 0.93731 0.68581 1.003922 0.8667 CO 29 27 27 29 37 149 CO 0.834876 0.819777 0.722968 0.695869 0.666725 0.744633 0.7475 CO 44 43 72 71 64 88 382 PM 0.472055 0.452553 0.460428 0.506824 0.4730 PM 19 31 36 43 129 PM 0.281 314 0.276378 0.270345 0.282059 0.28934 0.2799 PM 25 24 25 28 36 138 PM 0.239994 0.24542 0.262486 0.257528 0.240685 0.266622 0.2521 PM 44 43 72 71 64 88 382

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

  • 5.667602 1997 0.307044 5.723983 1998 0.31 6321 5.574079 1999 0.314974 5.549376 2000 0.26631 5.441729 2001 0.314765 5.506545 average 0.3085 5.5772 sample size HO NOx 1996 44 44 1997 43 43 1998 72 72 1999 71 71 2000 64 64 2001 86 86 total 380 380 D3 Source: NR-009d, Exhaust and Crankcase Emission Factors for Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 ENGINEERING DESIGN FILE EDF-3124-0009 09129109 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 t 1.3060 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 Crankcase Emission Factors for Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 09/29/09 Rev. 0 ENGINEERING DESIGN FILE EDF-31 24-0009 Rev. 1 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 Crankcase Emission Factors for Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 09129109 Rev. 0 ENGINEERING DESIGN FILE EDF-31 24-0009 Rev. 1 Page 8 of 9 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 9dt 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

b d

References 2,5-6,9-14. When necessatry, an average brake-specific fiuel consumption (BSFC) of 7,000 B~n/hp-hr was used to conv:ert fro6m lb/MMBtu to lb/h*p-hr. To convert from lb/hp-hr to 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.

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.

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: AP-42, Compilation of Air Pollutant Emission 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.

TEM-9002 09129109 Rev. 0 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. I Page 9 of 9 Excel Spreadsheet of Calculations Woe-I Co-P,0"1 Ip

.,5 l 0o2" I s'

E~~oi~meel lip FEilssion Fader (gthr-hp)'

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 Front Loaders 122 5.652+00 8.67E-21 2.652-01 2.10E-01 525 4 9.512-01 Graders 145 5.652+65 8.6"/E-01 2.802-01 2.10E-01 521 f.9.51E-01 Paver 142 5.65E+60 8,."/E-01 2.86E-01 2.10E-01 521 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 h________________________

ittp www.epa. ov etaq/models 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

CAL,*S E

I* SOTO*

NWMI-201 6-RAI-001 Rev. 0 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 09/29109 Rev. 0 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. I 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, CO2, 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 ENGINEERING DESIGN FILE EDF-3124-0009 09129109 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, Calculation for Determination of Fugitive Dust During Construction Activities from Construction Equipment), 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 Crankcase Emission Factors for 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 Pollutant Emission 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 Factors for Nonroad Engine 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 09129109 Rev. 0 ENGINEERING DESIGN FILE EDF-31 24-0009 Rev. I 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 Excavators Lloaderso Graers Paver -

Asphalt....

roller I

,IUU 1'4U [

IU 'IY 1

60

,49 110 7.5

  • 1

.- 120 r. 68 ;.,150 -. 10 1

80

'66 150 i10 1 ","d*:

80

  • 64 1i 40" 10*i' 1i..80-100 2°d 30 1

'4-17; 22 22 '

0..)

2.4 3.2

32.

5.4

,1.8 7.2

,2.4

-7:0-:. 72.4 1U 1.):,UUU LYUUU 4.0

,4,500 10,000

' *5.6 -[6,200-14,000*

S5.4 6,000 i13,000

  • 5.3 Y" 5,900 i13,6000 77 9.'

,700 21,000~i 8.1 18

11

, '25

'11 24

.Total 647,:-1430 7 i91.:5, 202...30.-27 66.0, 7 22.6i 50, Si 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, Compilation of Air Pollutant Emission 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, Calculation for 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 Factors for Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 09/29109 Rev. 0 ENGINEERING DESIGN FILE EDF-31 24-0009 Rev. 1 Page 4 of 9 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 2000 0.692103 2001 0.628378 average 0.760241 sample size 2000 2001 total glhp-hr 2000 2001 average sample size 2000 2001 total HO 4

5 9

HO 0.489983 0.447831 0.468907 NOx 5.170337 5.073763 5.12205 NOx 6

5 11 NOx 3.749647 4.,109521 3.929584 HC+NOx 5.966223 6.018891 5.992557 HC+NOx 20 19 39" HC+NOx 4.9489 4.80692 4,87791 CO 4.051366

4. 174066 4.1127 CO 20 19 39 CO 2.207041 2.114884 2.1610 PM HC frac 0.452858 0.113196 0.44201 0.141247 0.4474 PM 20 19 39 PM HC frac 0.289982 0.081156 0.242992 0.09869 0.2665 HO calc 0.675351 0.850153 0.7628 NOx calc 5.290871 5.168735 5.2298 HC calc 0.401631 0.474395 0.4380 NOx calc 4.547269 4.332525 4.4399 HO NOx HC+NOx CO 9

10

40.

39 16 16 43 43 25 26 83 82 PM 40 43 83

>25,to 50 lip :

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

TEM-9002 09129/09 Rev. 0 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. 1 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 1998 0.528845 1999 0.517642 2000 0.46289 2001 0.575867 average 0.5213 sample size HC 1998 18 1999 27 2000 35 2001 40 total 120

>100 to 175 hp':

g/hp-hr HG 1997 0.297479 1998 0.355336 1999 0.35159 2000 0.33246 2001 0.3551 07 average 0.3384 sample size HC 1997 29 1998 25 1999 25 2000 27 2001 34 total 140 NOx 5.682411 5.61 3376 5.494892 5.604515 5.5988 NOx 71 91 104 127 393 NOx 5.599201 5.743938 5.749792 5.593736 5.574714 5.6523 NOx 43 52 59 61 69 284 HC+NOx 4.235576 6.569501 4.235576 5.976957 5.254402 HC+NOx 1

3 1

3 8

HC+NOx HO+NOx 0

0.

0 0

0 0

HC+NOx 4.54 4.203295 4.371 648 HO+NOx 0

0 0.

0 2

6 8

CO 2.753546 2.34687 2.047055 2.314372 2.36655 CO 21 33 38 47 139 CO 0.745072 0.961288 0.93731 0.68581 1.003922 0.8667 CO 29 27 27 29 37 149 CO 0.834876 0.819777 0.722968 0.695869 0.666725 0.744633 0.7475 CO 44 43 72 71 64 88 382 PM 0.472055 0.452553 0.460428 0.506824 0.4730 PM 19 31 36 43 129 PM 0.281 314 0.276378 0.270345 0.282059 0.28934 0.2799 PM 25 24 25 28 36 138 PM 0.239994 0.24542 0.262486 0.257528 0.240685 0.266622 0.2521 PM 44 43 72 71 64 88 382

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

  • 5.667602 1997 0.307044 5.723983 1998 0.31 6321 5.574079 1999 0.314974 5.549376 2000 0.26631 5.441729 2001 0.314765 5.506545 average 0.3085 5.5772 sample size HO NOx 1996 44 44 1997 43 43 1998 72 72 1999 71 71 2000 64 64 2001 86 86 total 380 380 D3 Source: NR-009d, Exhaust and Crankcase Emission Factors for Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 ENGINEERING DESIGN FILE EDF-3124-0009 09129109 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 t 1.3060 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 Crankcase Emission Factors for Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 09/29/09 Rev. 0 ENGINEERING DESIGN FILE EDF-31 24-0009 Rev. 1 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 Crankcase Emission Factors for Nonroad Engine Modeling, Compression-Ignition, U.S. Environmental Protection Agency, Washington, D.C., July 2010.

TEM-9002 09129109 Rev. 0 ENGINEERING DESIGN FILE EDF-31 24-0009 Rev. 1 Page 8 of 9 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 9dt 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

b d

References 2,5-6,9-14. When necessatry, an average brake-specific fiuel consumption (BSFC) of 7,000 B~n/hp-hr was used to conv:ert fro6m lb/MMBtu to lb/h*p-hr. To convert from lb/hp-hr to 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.

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.

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: AP-42, Compilation of Air Pollutant Emission 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.

TEM-9002 09129109 Rev. 0 ENGINEERING DESIGN FILE EDF-3124-0009 Rev. I Page 9 of 9 Excel Spreadsheet of Calculations Woe-I Co-P,0"1 Ip

.,5 l 0o2" I s'

E~~oi~meel lip FEilssion Fader (gthr-hp)'

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 Front Loaders 122 5.652+00 8.67E-21 2.652-01 2.10E-01 525 4 9.512-01 Graders 145 5.652+65 8.6"/E-01 2.802-01 2.10E-01 521 f.9.51E-01 Paver 142 5.65E+60 8,."/E-01 2.86E-01 2.10E-01 521 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 h________________________

ittp www.epa. ov etaq/models 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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