A FPA Protection ^\xSmartWay

M lkAgency	U.S. Environmental Protection agency"'

2023 SmartWay
Rail Carrier Partner Tool:

Technical
Documentation

U.S. Version 1.0
(Data Year 2022)

EPA-420-B-23-025 i April 2023 i SmartWay Transport Partnership i epa.gov/smartway


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^CPA Envlronmemal Protection	^^\XSmartWay

* mAgency	U.S. Environmental Protection Agency^

2023 SmartWay
Rail Carrier Partner Tool:

Technical
Documentation

U.S. Version 1.0
(Data Year 2022)

Transportation and Climate Division
Office of Transportation and Air Quality
U.S. Environmental Protection Agency

EPA-420-B-23-025
April 2023


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Table of Contents

1.0 DATA SOURCES	3

2.0 EMISSION ESTIMATION	4

2.1 PubLic DiscLosure Reports	12

3.0 ACTIVITY INPUT VALIDATION	13

REFERENCES	15

APPENDIX A: LOCOMOTIVE EMISSION FACTORS	A-l

APPENDIX B: SURROGATE LOCOMOTIVE DATA	B-l

APPENDIX C: DERIVATION OF NATIONAL AVERAGE G/KW-HR EMISSION FACTORS	C-l

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List of Tables

Table l. Example Operation Hour Allocation by Tier Level	5

Table 2. Emission Factors by Tier Level and Unit Type	5

Table 3. Emission Factors by Engine Tier Only	7

Table 4. National Average Railcar Volume Data (Tool Defaults)	9

Table 5. 2011 Ri Activity Data and Rail Tool Validation Ranges	14

Table A-i. Line Haul Locomotive Emission Factors (grams per gal)	A-i

Table A-2. Small Line-haul Locomotive Emission Factors (grams per gal)	A-i

Table A-3. Yard Locomotive Emission Factors (grams per gal)	A-i

Table B-i. Fuel Usage Surrogates	B-i

Table B-2. Surrogates for Estimating Annual Miles and Ton-Miles	B-2

Table C-i. Electric Generation Mix	C-i

Table C-2. Power Plant Emissions in Grams per kWh of Electricity Available at Power Plant Gate	C-i

Table C-3. Power Plant Emissions Grams per kWh of Electricity Available at User Sites (wall outlets)	C-2

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Data Sources

The technical approach recommended for the SmartWay railroad model was developed to encourage
railroad participation by providing methods to calculate emissions, fuel consumption, and comparison
metrics based, to the extent possible, based on data the participating railroad companies have on hand and
provide annually to the Department of Transportation's Federal Railroad Administration (FRA). For example,
the approach presented uses data elements that Class l railway companies submit in their annual R-i
reports. Class I Railroad companies can use their most recent R-i data for this SmartWay Tool. The relevant
data reported annually to the FRA's R-i forms include:

Power Unit Information - Form 710
Locomotive Unit Miles - Form 755, lines 8-14
^ Railcar Miles - Form 755, line 30

Fuel Consumption by Fuel Type and Unit Type - Form 750, lines 1-3
Ton-Mile Data - Form 755, lines 104,110,113

As Class 2 and 3 railroads do not need to provide detailed information to the FRA, in order for them to
participate in the SmartWay Program they need to develop and submit the required data specific for their
operations. Where a Class 2 or 3 railroad company does not have all of the required information, surrogate
data are provided in the Appendix B of this report that may be useful to develop some of the basic data
required for the Tool.

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S Emission Estimation

Regardless of the Locomotive class, the SmartWay Rail Tool was designed to calculate C02 performance
metrics based on fuel consumption estimates, and NOx and PM emissions based on tier-specific engine
operation information.

In the SmartWay Rail Tool, the data for line-haul (including short line-haul and passenger rail) and yard
operations are handled separately, even though many of the data elements are the same. Line-haul and yard
operations are sufficiently different that they require separate emission factors associated with the different
duty cycles. If operational surrogates are needed, then these should be compiled specific to either line-haul
or yard operations.

The specific Rail Tool calculation outputs include:

^ total mass emissions (C02, NOx, PMi0 and PM2,5)
g/ton-mile (gross, revenue, non-revenue)
g/railcar-mile (just total miles)

^ g/truck-equivalent-mile (just total miles)

The following presents the calculation procedures used to estimate these performance metrics.

l Calculating mass emissions (total grams)

a. C021

i.	Diesel fuel: grams of C02 = total gallons diesel (freight + passenger + switching) x 10,180 g
C02/gallon.

ii.	Biodiesel: The Tool uses the biodiesel blend percentage to interpolate between regular diesel
and 100% biodiesel fuel factors, with 100% biodiesel = 9,460 g/gallon. Therefore 20% biodiesel
(B20) has a fuel factor of 10,180 - (10,180 - 9,460) x (20/100) = 10,036 g C02/gallon

iii.	LNG: grams of C02 = total gallons LNG (freight + passenger + switching) x 4,394 g C02/gallon.

iv.	CNG: If input in cubic feet, grams of C02 = total cubic feet (freight + passenger + switching) x 57.8.
If CNG input is in equivalent gallons, the Tool multiplies total gallons by 7,030 g C02/gallon.

v.	Electric: grams of C02 = total kWh x 607 g C02/kWhr. See Appendix C for details.

1 With the exception of the electricity factors, the source of the fuel-based C02 factors are discussed in the SmartWay Truck Tool Technical Documentation.

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X-

b. NOx, PM and Black Carbon (BC)

i. Diesel - Data Input Methods 2 and 4 (inputs differentiated by line haul and switcher)
1) The Tool first calculates the proportion of hrs/units by Tier level,
a) The following provides an example for line haul units:

Table 1. Example Operation Hour
Allocation by Tier Level

Tier Level	Hrs	Fraction

Non-Tier -

3,000

0.15

0

0

0

0+

1,000

0.05

1

2,000

0.1

i*

5,000

0.25

2

0

0

z*

4,000

0.2

3

5,000

0.25

4

0

0

Total

20,000

1.00

b)	The Tool repeats this calculation for the switcher distribution

c)	The Tool then calculates weighted average fuel factors for NOx and PM, using the
following table.2

d)	BC is calculated by multiplying PM2,5 values by 0.6767.3

Table 2. Emission Factors by Tier Level and Unit Type





g/gal

Engine Tier

Unit Type

z

0

X

PM10

PM2.5

Non-tier

Line-Haul/Passenger

270.40

6.66

6.46

Switcher

264.48

6.69

6.49

Tier o

Line-Haul/Passenger

178.88

6.66

6.46

Switcher

191.52

6.69

6.49

Tier o +

Line-Haul/Passenger

14976

4.16

4.04

2	EPA 2009, Emission Factors for Locomotives.

https://nepis.epa.aov/Exe/ZvN ET.exe/Pi00500B.TXT?ZvActionD=ZvDocument&Client=EPA&lndex=2006+Thru+20i0&Docs=&Querv=&Time=&EndTime=&Se
archMethod=i&TocRestrict=n&Toc=&TocEntrv=&QFieLd=&QFieLdYear=&QFieLdMonth=&QFieLdDav=&lntQFieLdOp=0&ExtQFieLdOp=0&XmLQuerv=&FiLe=D%?A%
5CzvfiLes%5Clndex%20Data%5Co6thruio%5CTxt%5Cooooooio%5CPioo50QB.txt&User=ANONYMOUS&Password=anonvmous&SortMethod=h%7C-
&MaximumDQCuments=l&FuzzvDegree=0&lmageQuaLitv=r7fig8/r7fig8/xlfi0vlfi0gl6/i42fi&DispLav=hpfr&DefSeekPage=x&SearchBack=ZvActionL&Back=Zv
ActionS&BackDesc=ResuLts%20paae&MaximumPaaes=i&ZvEntrv=i&SeekPaae=x&ZvPURL. Accessed 3-29-23.

3	Commission for Environmental Cooperation 2015. North American Black Carbon Emissions Estimation Guidelines - Methods for Estimating Black Carbon
Emissions, http://www.cec.ora/north-american-black-carbon-emissions-estimation-auidelines-i/. Accessed 3-29-2023.

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Table 2. Emission Factors by Tier Level and Unit Type

g/gal

Engine Tier

Unit Type

z

0

X

PM10

PM2.5



Switcher

161.12

350

340

Tier 1

Line-Haul/Passenger

139.36

6.66

6.46

Switcher

150.48

6.54

6.34

Tier 1 +

Line-Haul/Passenger

139.36

4.16

4.04

Switcher

150.48

350

340

Tier 2

Line-Haul/Passenger

102.96

374

363

Switcher

110.96

2.89

2.80

Tier 2*

Line-Haul/Passenger

102.96

1.66

1.61

Switcher

110.96

1.67

1.62

Tier 3

Line-Haul/Passenger

102.96

1.66

1.61

Switcher

68.40

1.22

1.18

Tier 4

Line-Haul/Passenger

20.80

0.31

0.30

Switcher

15.20

0.23

0.22

i)	Example calculation for the weighted NOx factor for line-haul case above:

Weighted average = 270.4 x 0.15 +178.88 x 0.0 +149.76 x 0.05 +139.36 x 0.1 +
139.36 x 0.25 +102.96 x 0.0 +102.96 x 0.1 +102.96 x 0.25 = 132.86 g/gal NOx

ii)	The Tool repeats these calculations for PMio/2,5

iii)	All calculations are then repeated for switchers

2)	The Tool multiplies gallons of (freight + passenger) diesel by weighted average fuel
factors for line-haul/passenger category.

3)	The Tool multiplies gallons of switcher diesel by weighted average fuel factors for
switchers.

4)	The Tool sums grams for line-haul/passenger and switchers to obtain total tons for NOx,
PM10, PM2i5 and BC.

ii. Diesel - Data Input Methods 1 and 3 (inputs NOT differentiated by line haul and switcher)
1) The Tool uses Table 2 to calculate the weighted average fuel factors4

4 The factors in Table 2 are calculated by weighting the Line haul/passenger and switcher values from Table 1 by the national average relative fuel
consumption levels for these categories (0.925 and 0.075, respectively). National average values were obtained from 2010 R-i reports.

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Table 3. Emission Factors by Engine Tier Only





g/gal



Engine Tier

z

0

X

PM10

PM2.5

Non-Tier

269.96

6.66

6.46

Tier 0

179.83

6.66

6.46

Tier 0+

150.61

4.11

399

Tier 1

140.19

6.65

6.45

Tier 1*

140.19

4.11

399

Tier 2

103.56

368

357

Tier 2*

103.56

1.66

1.61

Tier 3

100.37

1.63

1.58

Tier 4

20.38

O.31

0.30

2) The Tool follows the same process as for Data Input Methods 2 and 4, but there is no
need to sum across unit types (step 4 above).

iii.	Biodiesel -

1)	Biodiesel NOx, PMi0/2,5and BC emissions are calculated by applying an adjustment factor
to diesel emissions. Therefore, the first is to multiply the biodiesel gallons by the diesel
fuel factors as described above to calculate an unadjusted estimate for grams of NOx,
PM10, PM2i5 and BC.

2)	Next the Tool calculates adjustment factors based on % biodiesel blend specified - see
Truck Tool Technical Documentation for references.

a)	% change in emissions = (exp[a * (vol% biodiesel)] -1} * 100%

Where a = 0.0009794 for NOx, and a = -0.006384 for PM10/25 and BC

b)	The Tool applies the adjustment factor to the unadjusted grams of NOx, PM10/25 and
BC calculated above. In general PM/BC emissions are somewhat lower than diesel
emissions, while NOx emissions increase slightly.

iv.	LNG - 5

1)	The Tool first sums total gallons of LNG across line-haul, passenger, and switchers

2)	The Tool then multiplies total gallons by 20.3 g/gal to obtain grams NOx; and by 1.35
g/gal to obtain PMi0. The Tool multiplies the gallons value by 1.31 to obtain PM2i5. See
Appendix A regarding the source of these fuel-based factors.

3)	The Tool estimates BC emissions by multiplying the PM2,5 value by 0.059, the fraction of
PM2.5 emissions attributable to elemental carbon as estimated by the MOVES3 model for
Class 8b onroad natural gas trucks.

5 LNG, CNG, and Electricity factors do not vary with engine tier. Therefore the Tool does not calculate weighted averages based on tier Level distributions,
but simply uses the gallons and/or kWh amounts from the Operations screen.

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v. CNG -

1)	The Tool converts cubic feet of CNG to gallons if necessary with l standard cubic foot of
CNT = 0.00823 equivalent gallons.

2)	The Tool sums total gallons of CNG across line-haul, passenger, and switchers

3)	The Tool multiplies total gallons by 20.3 g/gal to obtain grams NOx; and by 1.35 g/gal to
obtain PM10. The Tool multiplies the gallons value by 1.31 to obtain PM2.5. See Appendix A
regarding the source of these fuel-based factors.

4)	The Tool estimates BC emissions by multiplying the PM25 value by 0.059, the fraction of
PM2.5 emissions attributable to elemental carbon as estimated by the MOVES3 model for
Class 8b onroad natural gas trucks.

2	Calculate g/ton-mile for each pollutant (three types of "ton-miles")

a.	Grams per gross ton-mile: the Tool divides the grams of each pollutant (fleet total) by gross ton-
miles entered on Operations screen.

b.	Grams per revenue ton-mile: the Tool divides the grams of each pollutant (fleet total) by revenue
ton-miles entered on Operations screen.6

c.	Grams per non-revenue ton-mile: the Tool divides the grams of each pollutant (fleet total) by
non-revenue ton-miles entered on Operations screen.

3	Calculate g/railcar-mile for each pollutant7

a. The Tool divides the grams of each pollutant by total railcar-miles entered.

4	Calculate g/truck-equivalent-mile

a.	Since rail operators do not provide railcar type/volume information, a national default value of
6,091 cubic feet per car is assumed for all carriers - see the Shipper Tool Technical
Documentation for details.

b.	Calculate the "truckload equivalents" factor (TE): divide the national average railcar volume by
3,780 cubic feet.8

c.	g/truck-equivalent-mile = g/railcar-mile / TE, and is calculated for each pollutant.

6	Value reported in SmartWay Public Bin Export Report.

7	Ibid.

8	Truck industry average freight volume is 2.78 TEU = 3,780 cubic feet (see Shipper Tool Technical Documentation).

vi. Electricity -

1)	The Tool sums total kWh of electricity across line-haul, passenger, and switchers

2)	The Tool then multiplies total kWh by 0.220 to obtain grams NOx; by 0.059 for grams
PMi0; by 0.028 for grams PM25, and by 0.0026 for BC. See Appendix C for details.

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Table 4. National Average Railcar Volume Data (Tool Defaults)

Type in Tool

Railcar Type

Cubic
Feet

Sou rce/Assum ptio n

Key: Norfolk Southern (NS), Union Pacific (UP), Burlington
Northern Santa Fe (BNSF), CSX Transportation (CSX), Guide
to Railcars (GTRC), Chicago Rail Car Leasing (CRCL), Union
Tank Car Company (UTCC), U.S Department of Agriculture
(USDA)

Box-Plain 50' +
Box Equipped

Boxcar 50 ft
and longer
including
equipped
boxcars

7,177

Based on the average of the following boxcar types:
50 ft assumed to be 5.6Q4 freflectina the averaae of 5.^55
(NS), 5,431 (UP), 5,238 (CSX), 6,175 (BSNF), 6,269 (GTRC)].
60 ft assumed to be 6.648 freflectina the averaae of 6.618
(NS), 6,389 (UP), 6,085 (CSX), 7,500 (BNSF)].

50 ft hiah cube assumed to be 6.^04 freflectina the averaae
of 6,339 (NS) and 6,269 (CSX)].

60 ft hiah cube assumed to be 6.Q17 freflectina the averaae
of 7,499 (NS), 6,646 (CSX), and 6,607 (GTRC)].

86 ft assumed to be q.qqq (NS).

Autooarts assumed to be 7.4QQ (NS).

Box-Plain 40'

Boxcar 40ft

4,555

Based on estimate of 50 ft boxcar volume described above.
Assumed 40 ft length would result in 20% reduction in
volume.

Flat TOFC/COFC
Flat General
Service
Flat all other

Flat car - all
types except
for multi-level

6,395

Based on the average of the following flat car types:
60 ft assumed to be 6.73Q (BNSF).

8q ft assumed to be Q.^72 (BNSF).

Coil assumed to be 3,387 (NS).

Covered coil assumed to be 5.2Q4 freflectina the averaae of
8,328 (NS) and 2,260 (BNSF)].

Centerbeam assumed to be 6.546 freflectina the averaae of
5,857 (UP) and 7,236 (BNSF)].

Bulkhead assumed to be 7.0^0 (BNSF).

Flat Multi level

Multi-level flat
car

13,625

Based on the average of the following multi-level flat car
types:

Unilevel (that carrv verv larae carao. such as
vehicles/tractors) assumed to be 12.183 (NS).

Bi-level assumed to be 14.38i(NS).

Tri-level assumed to be 14.313 (based on averaae of 15.287
(NS) and 13,339 (BNSF).



Flat Car - all
types-
including
multi-level

7,428

Based on the average volumes of the flatcar types described
above including multi-level as a single flat car type.

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Table 4. National Average Railcar Volume Data (Tool Defaults)

Type in Tool

Railcar Type

Cubic
Feet

Sou rce/Assum ptio n

Key: Norfolk Southern (NS), Union Pacific (UP), Burlington
Northern Santa Fe (BNSF), CSX Transportation (CSX), Guide
to Railcars (GTRC), Chicago Rail Car Leasing (CRCL), Union
Tank Car Company (UTCC), U.S Department of Agriculture
(USDA)

Gondola Plain

Gondola

Equipped

Gondola - all
types
Including
equipped

5,190

Based on the average of the following gondola car types:
^2-^ ft assumed to be 2.626 [based on averaae of 2.66^
(NS), 2,743 (CSX), 2,400 (BNSF), and 2,697 (CRLC)].

60-66 ft assumed to be ^72 fbased on averaae of ^.281
(NS), 3.242 (CSX), 3.350 (BNSF), CRCL-3,670, and 3.366
(GTRC)].

Municipal Waste assumed to be 7.QQQ (NS).

Woodchip assumed to be 7.781 fbased on averaae of 7.862

(NS) and 7.700 (CRCL)].

Coal assumed to be 4.170 fbased on averaae of ^.78^ (NS)
and 4.556 (BNSF)].

Refrigerator
Mechanical
Refrigerated
non-mechanical

Refrigerated -
Mechanical
/non-
Mechanical

6,202

Based on the average of the following refrigerated car types:
48-72 ft assumed to be 6.Q63 [based on averaae of 6.043
(UP) and 7.883 (BNSF)].
fiO ft assumed to be ^.i67(GTRC).

40-Q0 ft assumed to be 6.476 [based on averaae of 6.0^2
(UP) and 6,000 (BNSF)].

Hopper Open

Top-General

Service

Open Top
Hopper

4,220

Based on the average of the following open top hopper car
types:

42 ft assumed to be 3,000 (UP).

54 ft assumed to be 3,700 (UP).

60 ft assumed to be ^.188 [based on averaae of R.12R (UP)
and 5,250 (GTRC)].

ar ft+ assumed to be 4.10c; [based on averaae of 4.^00 (UP)
and 3,710 (BNSF).

Woodchip assumed to be 707^ [based on averaae of 7^2^
(NS), 5999 (UP), and 7700 (CRCL)].

Small Aaareaate assumed to be 2.2^2 [based on averaae of
2,150 (NS), 2,106 (BNSF), and 2,500 (CRCL)].

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Table 4. National Average Railcar Volume Data (Tool Defaults)

Type in Tool

Railcar Type

Cubic
Feet

Sou rce/Assum ptio n

Key: Norfolk Southern (NS), Union Pacific (UP), Burlington
Northern Santa Fe (BNSF), CSX Transportation (CSX), Guide
to Railcars (GTRC), Chicago Rail Car Leasing (CRCL), Union
Tank Car Company (UTCC), U.S Department of Agriculture
(USDA)

Hopper Covered

Covered Top
Hopper

4,188

Based on the average of the following covered top hopper
car types:

45 ft assumed to be 5,250 (GTRC).

Aaareaate assumed to be 2.^7^ fbased on averaae of 2.1^0
(NS) and 3.000 (CRCL)].

Small Cube Gravel assumed to be 2.cm fbased on averaae

of 2,655 (NS), 3.100 (CSX), and 3.063 (BNSF).

Med-Larae Cube Ores and Sand assumed to be 416Q fbased

on average of 3,750 (NS) and 4,589 (BNSF)].

Jumbo assumed to be R1A7 fbased on averaae of 4.87c; (NS).

4,462 (CSX), 5.175 (BNSF), and 6,075 (CRCL)].

Pressure Differential (flour) assumed to be roro fbased on

average of 5,124 (NS) and 4,975 (CRCL)].

Tank under
22,000 gallons

Tank Cars
under 22,000
gallons

2,314

Assumes 1 gallon=0.i337 cubic foot (USDA).

Based on small tank car average volume of 17,304 gallons,
which is the average of the following currently manufactured
tank car volume design capacities of 13,470,13,710,15,100,
15,960,16,410,17.300,19,900, 20,000, 20,590, and 20,610
gallons (GTRC).

Tank over 22,000
gallons

Tank Cars
over 22,000
gallons

3,857

Assumes 1 gallon = 0.1337 (USDA).

Based on large tank car volume of 28,851 gallons, which is
the average of the following currently manufactured tank car
volume design capacities of 23,470, 25,790, 27,200, 28,700,
30,000, 33,000, and 33,800 gallons (GTRC).

All other cars
Work Equip &
company Freight
No payment car-
miles

All Other Cars

5.014

Based on average volume presented above for each of the
nine railcar types (all flatcars are represented by the line item
that includes multi-level flatcars - 7,428).

References

Burlington Northern Santa Fe Railway (BNSF), Available at: http://www.bnsf.com/customers/how-can-i-
ship/individual-railcar/#%23subtabs-3. Accessed 3-29-23.

CSX Transportation (CSXT), Customer Equipment. Available at:

https://www.csx.com/index.cfm/customers/resources/equipment/. Accessed 3-29-23.

Norfolk Southern Railway Company (NS), Customer Equipment. Available at:
http://www.nscorp.com/content/nscorp/en/shippina-tools/equipment-auide/merchandise-
equipment.html. Accessed 3-29-23.

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Union Pacific Railroad (UP), Customer Equipment, Car Types. Available at:
http://www.uprr.com/customers/equip-resources/cartvpes/index.shtml. Accessed 3-29-23.

Chicago Rail Car Leasing (CRCL), Rail Car Types. Available at: https://chicaaofreiahtcar.com/railcars/.
Accessed 3-29-23.

Surface Transportation Board (STB), Industry Data, Economic Data and Statistical Reports, Class 1 Annual
Report Financial Form R-i Available at https://www.stb.aov/reports-data/economic-data/annual-report-
financial-data/. Accessed 3-29-23.

United States Department of Agriculture, Economic Research Service,20005-4788, June 1992, Agricultural
Handbook Number 697, Washington, DC. Available at: https://www.ers.usda.aov/publications/pub-
details/?pubid=4i88i. Accessed 3-29-23.

Union Tank Car Company, Chicago, IL, Basic Design Specifications. Available at: https://www.utlx.com/.
Accessed 3-29-23.

The Rail Tool provides a report summarizing Scope 1 and Scope 2 emissions for public disclosure purposes.
Mass emissions are presented in metric tons for C02 (biogenic and non-biogenic), N0X, and PM9 for all fleets.
Biogenic C02 emissions estimates are assumed to equal 2 percent of total C02 emissions, as per U.S.
requirements for biomass-based diesel from the EPA Renewable Fuel Standard program final volume
requirements.10

C02 equivalent (C02e) emissions are also provided in the tool's Public Disclosure report and are calculated by
multiplying C02 values by a scaling factor of 1.0142. The scaling factor was based on data from Table 2-13 in
the most recent EPA Emissions and Sinks Report. The factor was derived by dividing the Rail emissions for
each greenhouse gas excluding C02 (CH4, N20, and HFCs) by the total emissions including C02, and then
summing the ratios to obtain the total scaling factor.

9	Emissions from CH4, N20, HFC's, PFC's, SF6 and NF3 have been deemed immaterial, comprising Less than 5% of overall GHG emissions and are therefore
excluded for reporting purposes.

10	As stated in the Final Rule (Table I.B.7-1 - see https://www.aovinfo.aov/content/pka/FR-2020-02-06/pdf/2020-004?i.pdf. accessed 3-29-23), the
volume requirements for biomass-based diesel in 2020 is 2.10%, rounded to equal 2% for calculation purposes. The percentage will be updated annually in
the Tool.

2.1 PUBLIC DISCLOSURE REPORTS

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Q Activity Input Validation

SmartWay has developed general validation criteria based on 2011 R-i report data in order to perform range
checks on Partner activity inputs. These range checks are simply intended to identify unreasonable data
entries only. Table 4 summarizes the R-i data used for each Class 1 Rail Line, as well as the range check
values derived from the carrier-specific data. Range check values are displayed in bold.

Maximum acceptable values for fuel use, ton-miles, car-miles, and unit miles for Class 1 operators were set
equal to three times the rail-line specific maximum shown in the table. Similarly, minimum acceptable values
for Class 1 operators were set equal to one tenth for fuel use, ton-miles, car-miles, and unit miles. Maximum
acceptable values for Class 2 and 3 operators were set at one tenth of the Class 1 maximum value.

The tool also uses the fuel consumption, gross ton-mile and revenue ton-mile entries to calculate tons of
CO2 per ton-mile. If the resulting values are outside of expected ranges (less than 10 or greater than 90 tons
per gross ton-mile, or less than 10 or greater than 60 tons per revenue ton-mile), the user must either change
the fuel and/or ton-mile entries or enter an explanation for the unexpected values.

SmartWay will re-evaluate validation ranges to make them more precise, comprehensive, and consistent as
Rail Partner data is collected in the future.

SmartWay Technical. Documentation | Section 3 13


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U.S. Environmental Protection Agency J

Table 5. 2011 Ri Activity Data and Rail Tool Validation Ranges

Rail Line

Total Fuel Use
(gallons diesel
oil)

Gross ton
miles total
(thousands)

Revenue
Freight ton

miles
(thousands)

Non
revenue
Freight ton

miles
(thousands)

Total
freight car

miles
(thousands)

Total
Locomotive unit
miles

Locomotive

Train
switching
unit miles

Locomotive

Yard
switching
unit miles

BNSF

1,340,634.000

1,200,654,478

648,431.637

6,117,197

11,316,277

495.865,213

2,161,568

14,323.105

CSX

500,735.225

456,207,620

228,394.651

1,216,165

4.789.143

186,017,342

6,557.484

14.352,854

GTC

124,776,076

105.195.469

51,253.084

518,201

1,241,217

31.375.934

2,686,536

4.714.915

KCSR

64.833.378

55.889,957

30,485,863

1.338,343

628,431

23,846,725

516,654

26,504,929

NS

473.887,662

392,056,820

191,712,562

1,267,931

4,327.021

170,767,368

7,042,003

14,060,355

Soo

72,442,000

70,325,676

34.581,354

333.090

807.927

27.407.979

2,686,353

2,577.600

UP

1,117,851,152

1,072,705.764

544.397.317

5,485.720

11,012,608

424,786,444

12,635,406

19.169.964



















Class 1 max

4,021,902,000

3,601,963,434

1.945.294.911

18,351.591

33.948,831

1.487.595.639

37,906,218

79.514.787

Class 1 min

6,483,338

5,588,996

3,048,586

33.309

62,843

2,384.673

51.665

257.760



















Class 2/3
max

134,063,400

120,065,448

64,843,164

611,720

1,131,628

49.586,521

1,263,541

2,650,493

Class 2/3
min

> 0

> 0

> 0

> 0

> 0

> 0

> 0

> 0

SmartWay Technical. Documentation | Section 3 14


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\

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MENTAL PROTECTION AGENCY"'

U.S. Environmental Protection Agency

References

California Air Resource Board

Rail Yard Agreement, Sacramento California 2007.

U.S. Department of Transportation

Bureau of Transportation Statistics, Freight in America, January 2006.

U.S. Department of Transportation

Surface Transportation Board, Form R-i

United States Code of Federal Regulations

Title 40 Section Chapter 1, Subchapter Q, Part 600.113, Fuel Economy Calculations
U.S. Environmental Protection Agency

Regulatory Support Document: Locomotive Emission Standards Final Rule, 1997.

U.S. Environmental Protection Agency

2009 Locomotive Emission Factor Study, Ann Arbor, Ml.2009.

U.S. Environmental Protection Agency

MARKAL Input Data for non-Light Duty Vehicles, Research Triangle Park, NC 2009

SmartWay Technical. Documentation | References


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U.S. Environmental Protection Agency +

Appendix A: Locomotive Emission Factors

A-l. FUEL-BASED EMISSION FACTORS

Table A-l. Line Haul Locomotive Emission Factors (grams per gal)

Pollutant

Z

0

X

PM10

co2

Diesel

270.402

6.662

10,180

Biodiesel
(B-20)

1731

7.881

9.4604

CNG





7.0304

LNG

20.33

1.353

3.8654

1.	MARKAL data (2009)

2.	EPA Locomotive Emission Factors (2009)

3.	ARB Rail Yard Agreement (2007) in terms of diesel equivalents
4.40 CFR 600.113

Table A-2. Small Line-haul Locomotive Emission Factors (grams per gal)

Small Line

Emission Factor

Haul

g/gal

z

0

X

236.60

PM10

582

co2

10,180

Uncontrolled yard locomotive emission factors were obtained from EPA's Locomotive Emission Factors
(2009).

Table A-3. Yard Locomotive Emission Factors (grams per gal)



Emission Factor

Yard

g/gal

z

0

X

264.48

PM10

6.69

co2

10,180

Uncontrolled yard locomotive emission factors were obtained from EPA's Locomotive Emission Factors
(2009). All emission factors listed here reflect uncontrolled (i.e., pre-Tier 0) emission levels.

SmartWay Technical. Documentation | Appendix A A-l


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Appendix B: Surrogate Locomotive Data

SURROGATE DATA FOR EMISSION ESTIMATION

Data provided in the R-i reports have been compiled and evaluated to identify useful surrogates that may
help Partners gap-fill missing data. Because the data is from Class I operations, it may be biased to larger
operations.

SURROGATES FOR CALCULATING FUEL CONSUMPTION

The basic approach allows for emission calculations that roughly approximate emissions using reported total
annual fuel consumption. If annual fuel consumption data are unknown, surrogate data, such as locomotive
population, miles traveled, annual ton-miles or TEU-miles, can be used to provide an estimate for line-haul
locomotive fuel consumption, as noted in the following table.

Table B-i. Fuel Usage Surrogates

Line Haul Surrogate

Data Options in
Absence of Annual
Fuel Usage

Number of
Locomotives

Total Annual
Locomotive
Miles

Total Annual Ton
Miles Freight
Transported

Total Annual TEU
mile Equivalents

Multiplication Factor
for estimating
Annual Fuel Usage
(gal/yr)

132,800 (gal/yr per
locomotive)

2.44 (gal/

locomotive

miles)

0.002 (gal/ton
miles freight
transported)

0.053

(gal/TEU-mile
Equivalents)

Values used to develop the surrogates were derived from the Bureau of Transportation Statistics 2012
National Transportation Statistics Table 4-17.

When using the basic approach to estimate yard locomotive emissions, the number of locomotives can be
applied to the fuel consumption factors noted in the following equation to estimate annual fuel usage:

Yard Fuel Use (gal/yr) = 195,451 (gal/yr per yard locomotive) x Number of Yard Locomotives

SURROGATES FOR METRIC COMPARISONS

The railroad model is designed to apply calculated emissions to a variety of operational parameters. This
allows the derivation of metrics that can be used as a reference point to evaluate a Partner's environmental
performance relative to others.

In instances where the necessary information has not been provided, surrogate data presented in Table B-2,
may be used to estimate total miles traveled or the total annual ton-miles, based on the number of active
line-hail locomotives in the Partner's fleet.

SmartWay Technical. Documentation | Appendix B B-l


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Table B-2. Surrogates for Estimating Annual Miles and Ton-Miles

Metric for Which Surrogate
Data is Needed

Total Annual Train
Miles Traveled

Total Annual
Ton Miles

Multiplication Factor for
Estimating Train miles or ton-
miles based on the Number
of Locomotives

54,400 (miles/yr per
Locomotive)

63,744.000 (ton-
miles/yr per
Locomotive)

SmartWay Technical. Documentation | Appendix B B-


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U.S. Environmental Protection Agency +

Appendix C: Derivation of National Average
g/kW-hr Emission Factors

FROM ARGONNE GREET MODEL Version 201Q. http://areet.es.anl.gov/
l. Electric Generation Mix (eGRID U.S. Average 2018 Data (https://www.epa.gov/earid)

Table C-i. Electric Generation Mix



U.S. Mix

Residual oil

0.6%

Natural gas

35.1%

Coal

27.5%

Nuclear power

194%

Bio mass

1.6%

Hydro

6.9%

Wind

6.5%

Solar

1.5%

Geothermal

0.4%

Other

0.3%

2.	Electric Transmission and Distribution Loss = 4.87%

3.	Power Plant Emissions: in Grams per kWh of Electricity Available at Power Plant Gate

Table C-2. Power Plant Emissions in Grams per kWh of Electricity Available at

Power Plant Gate



GREET CaLcuLated Emission Factors



By Fuel Type Plants (Stationary and Transportation)

Oil Fired

NG Fired

Coal Fired

Biomass Fired

TOTAL based on US Mix

z

0

X

397

0.21

O.36

O.92

0.21

PM10

0.16

0.011

0.06l

2.09

O.O56

PM2.5

0.11

0.011

0.043

0.6l

0.026

BC

0.0073

0.0015

0.0018

0.0015

0.0025

co2

840

404

947

0

407

Assumes no emissions from nuclear power plants, hydro, wind, solar, geothermal, and "Other"

4. Power Plant Emissions: Grams per kWh of Electricity Available at User Sites (wall outlets)
Total power plant gate emissions/(i-electric transmission and distribution loss)

SmartWay Technical. Documentation | Appendix C C-l


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Table C-3. Power Plant Emissions Grams per kWh of Electricity Available at

User Sites (wall outlets)



Total delivered based on US electric generation mix

NOx

0.22

PM10

0.059

PM2.5

0.028

BC

0.0026

co2

428

SmartWay Technical. Documentation | Appendix C C-2


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U.S. Environmental Protection Agency»

X-

For more information:

U. S. Environmental Protection Agency
Office of Transportation and Air Quality
1200 Pennsylvania Ave. NW
Washington, DC 20460
(734)214-4333

www.epa.aov/transportation-air-pollution-and-
climate-chanae

U. S. Environmental Protection Agency
National Vehicle and Fuel Emissions Laboratory
2565 Plymouth Rd.

Ann Arbor, Ml 48105
(734) 214-4200

www.epa.gov/aboutepa/about-national-
vehicle-and-fuel-emissions-laboratorv-nvfel

EPA 420 B 23 025 | April 2023 | SmartWay Transport Partnership | epa.gov/smartway


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