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2020 National Emissions Inventory Technical
Support Document: Miscellaneous Non-
Industrial NEC: Residential Charcoal Grilling


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EP A-454/R-23 -001 dd
March 2023

2020 National Emissions Inventory Technical Support Document: Miscellaneous Non-Industrial

NEC: Residential Charcoal Grilling

U.S. Environmental Protection Agency
Office of Air Quality Planning and Standards
Air Quality Assessment Division
Research Triangle Park, NC


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Contents

List of Tables	i

30	Miscellaneous Non-Industrial NEC: Residential Charcoal Grilling	30-1

30.1	Sector Descriptions and Overview	30-1

30.2	EPA-developed estimates	30-1

30.2.1	Activity data	30-1

30.2.2	Allocation procedure	30-2

30.2.3	Emission factors	30-4

30.2.4	Controls	30-5

30.2.5	Emissions	30-5

30.2.6	Example calculations	30-6

30.2.7	Improvements/Changes in the 2020 NEI	30-7

30.2.8	Puerto Rico and U.S. Virgin Islands	30-7

30.3	References	30-8

List of Tables

Table 30-1: Emissions Factors for Residential Grilling (2810025000)	30-4

Table 30-2: Sample calculations for VOC emissions from residential grilling in Ada County, Idaho	30-6

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30 Miscellaneous Non-Industrial NEC: Residential Charcoal Grilling

30.1	Sector Descriptions and Overview

Residential barbecue grilling emissions include emissions from the burning of charcoal (including the use
of lighter fluid) and emissions from all types of meat cooked on charcoal, gas, and electric grills.
Combustion emissions from gas barbecue grills are not included. This source category
(SCC=2810025000) is one of many components in the Miscellaneous Non-Industrial sector. The SCC
description is "Miscellaneous Area Sources; Other Combustion; Charcoal Grilling - Residential (see 23-
02-002-xxx for Commercial); Total".

A list of agencies that submitted residential charcoal grilling emissions is provided in Section 6.2.3.

30.2	EPA-developed estimates

Emissions from this source category include criteria pollutants, (CO, NOx, PM10-PRI, PM25-PRI and VOC)
and HAP emissions from residential barbecue grilling. Sources of emissions include burning charcoal and
using lighter fluid in charcoal grills, and cooking meat on charcoal, gas, and electric grills. To perform the
relevant calculations data are needed on activities and emissions factors for those activities. Activity
data includes information about total charcoal sold, total meat cooked, and total amount of lighter fluid
used.

30.2.1 Activity data

There are three types of activity data for this source category: (1) amount of meat cooked on charcoal
grills; (2) amount of meat cooked on gas and electric grills; and (3) number of grilling events using lighter
fluid. Each of these types of activity data is discussed in the subsections below.

Meat cooked on charcoal grills

This source category includes emissions from the amount of charcoal burned and the amount of meat
cooked.

The total amount of charcoal sold in the United States is based on data from the Heath, Patio, and
Barbecue Association (HPBA) [ref 1], which is distributed to each county based on the proportion of 1-4
unit homes in each county, from the U.S. Census Bureau [ref 2], This distribution procedure is discussed
in more detail in Section . We assume that all charcoal sold is burned.

The amount of meat cooked is determined based on assumptions about the amount of meat cooked per
pound of charcoal sold. This calculation assumes 17.64 charcoal briquettes per pound of charcoal sold
[ref 3] and 0.033 pounds of meat cooked per briquette fref 4], These numbers are multiplied together to
calculate a value of 0.588 pounds of meat cooked per pound of charcoal sold.

0.588 lb. meat cooked per lb. charcoal sold

= 17.64 briquettes per lb. charcoal
x 0.033 lb. meat cooked per briquette

30-1


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Meat cooked on gas and electric grills

The amount of meat cooked on gas grills is calculated based on assumptions about the ratio of gas
grilling to charcoal grilling, including that charcoal grills represent 41% of grills and gas/electric grills
represent 59% [ref 4], and that charcoal grills are used 27 times per year and gas/electric grills are used
45 times per year [ref 5], This calculation results in an estimated ratio of 2.398, meaning that for every
pound of meat cooked on a charcoal grill an additional 2.398 pounds of meat are cooked on a gas or
electric grill.

2.398 gas or electric grilling ratio

45 times per year(gas or electric) x 59% gas or electric grills	^)

27 times per year(charocal) x 41% charcoal grills

The values from equations 1 and 2 are used with national data on the amount of charcoal sold from the
HPBA [ref 1] to estimate the total amount of meat cooked on charcoal, gas, and electric grills. This
national charcoal sales data is distributed to the counties based on the number of homes in each county,
as described in the following section.

Grilling events using lighter fluid

This calculation is based on the percentage of homes that have a grill (80%) [ref 6], the percentage of
grills that are charcoal grills (41%) [ref 5], the percentage of charcoal grills that use lighter fluid (37%)
[ref 7], and the number of times per year that charcoal grills are used (27) [ref 6], This results in a value
of approximately 3.28 grilling events per household per year where lighter fluid is used.

3.28 grilling events with lighter fluid

= 80% homes with a grill x 41% grills that are charcoal
x 37% charcoal grills that use lighter fluid
x 27 times per year charcoal grills are used

This number is multiplied by the number of occupied homes in each county to determine the total
number of grilling events in each county where lighter fluid is used. Seen Section on allocation
procedure for information on calculating the number of occupied 1-4-unit households.

,c Hc,0 X 3.28	^4j

Where:

nLF.c = Number of grilling events in county c where lighter fluid is used

Hc,o = Total occupied households of 1-4 units in county c

3.28 = Number of grilling events with lighter fluid per home, from equation 3

30.2.2 Allocation procedure

National data on the amount of charcoal sold is distributed to the counties based on the proportion of
occupied 1-4-unit homes in each county. It is assumed that households in larger apartment buildings
would not have the space to have or use an outdoor grill. The data on the number of occupied 1-4 unit
homes in each county is from the U.S. Census Bureau American Community Survey [ref 2], Occupied

30-2


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households between 1 and 4 units are estimated using the sum of total 1-4-unit households and the
fraction of total occupied households in the US.

units=4

Hn

Hm= ) HrtX	(5)

,o	Hc t

Hr	(6)

1US,o

		7	I—I	Y —

' '	nUS,t

umts=l

HRC = c'°



Where:



Hc,o

= Total

HClt

= Total

Hus,o

= Total

Hus,t

= Total

HRC

= Ratio

in United States

The national-level data on charcoal sales is distributed to the counties using the ratio from equation 6.

Charcoalc = HRC x Charcoalus x 2000 lbs. per ton	(7)

Where:

Charcoalc = Amount of charcoal sold in county c, in pounds

HRc	= Ratio of households of 1-4 units in county c to total households of 1-4 units in United

States

Charcoalus = Amount of charcoal sold in the United States, in tons

The amount of charcoal sold in each county (from equation 7) is multiplied by the amount of meat
cooked per pound of charcoal (from equation 1) to estimate the amount of meat cooked on charcoal
grills in each county.

Meatcharcoai c Charcoalc ^ 0.588

Where:

Meatcharcoai,c = Amount of meat cooked on charcoal grills in county c, in pounds

Charcoalc = Amount of charcoal sold in county c, in pounds

0.588	= Pounds of meat cooked per pound of charcoal, from equation 1

The amount of meat cooked on charcoal grills is used with the ratio from equation 2 to estimate the
amount of meat cooked on gas or electric grills.

Meatgas/elec c W6?&tc/jarcoa; c x 2.398

Where:

Meatgas/eiec,c = Amount of meat cooked on gas or electric grills in county c, in pounds

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Meatcharcoai,c = Amount of meat cooked on charcoal grills in county c, in pounds
2.398 = Ratio of meat cooked on gas or electric grills to charcoal grills, from equation 2

The amount of meat cooked on charcoal and on gas or electric grills is added together to determine the
total amount of meat cooked on grills in each county.

Meattc MeCLtgas/elec,c M 6 at char coal,c	(10)

Where:

Meatt,c = Total amount of meat cooked on grills in county c, in pounds
Meotgas/eiec,c = Amount of meat cooked on gas or electric grills in county c, in pounds
Meatcharcoai,c = Amount of meat cooked on charcoal grills in county c, in pounds

30.2.3 Emission factors

The emissions factors are shown in Table 30-1, including the actual emissions factor used in the
calculations, and the original emissions factor from the reference if it is different from the actual factor.
These emission factors for CAPs are also provided in the "Wagon Wheel Emission Factor Compendium"
on the 2020 NEI Supporting Data and Summaries site. The emissions factors for CO, NOX, PM10-PRI,
PM25-PRI, and VOC are from EPA's report, Emissions from Street Vendor Cooking Devices (Charcoal
Grilling) [ref 8], There is also a separate emissions factor for VOC from lighter fluid, from the South Coast
Air Quality Management District, Rule 1174 [ref 9], The HAP emission factors (also available in the zip
file "HAPAugmentation_Nonpoint_28jan2023", on the 2020 NEI Supplemental data FTP site) are
speciation factors from the EPA SPECIATE database [ref 10], which are speciation factors for charbroiling
meat.

	Table 30-1: Emissions Factors for Residential Grilling (2810025000)	

Pollutant

Pollutant
Code

Emissions

Factor
(original)

Emissions
Factor Units
(original)

Emissions
Factor
(actual)

Emissions
Factor Units
(actual)

Emissions

Factor
Reference

CO

CO

162.97a

g/kg meat

325.93

Ibs./ton
meat

6, Table E-2

NOX

NOX

3.37a

6.74

PM10-PRI

PM10-PRI

9.10a

18.19

PM25-PRI

PM25-PRI

n/a

14.56b

VOC

VOC

0.94a

1.88





0.02

Ibs./grilling
event

6, section
(c)(1)

1,3-Butadiene

106990





1.04E-02

Ibs./lb. VOC

6

2,2,4-

Trimethylpentan
e

540841





1.12E-03

Acetaldehyde

75070





1.09E-01

Anthracene

120127





1.09E-05

Benzene

71432





8.26E-03

Ethyl Benzene

100414





1.09E-03

Fluoranthene

206440





3.98E-05

Formaldehyde

50000





1.38E-01

30-4


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Pollutant
Code

Emissions

Emissions

Emissions

Emissions

Emissions

Pollutant

Factor

Factor Units

Factor

Factor Units

Factor



(original)

(original)

(actual)

(actual)

Reference

Hexane

110543





4.38E-03





m-Xylene

108383





5.97E-04





Naphthalene

91203





8.94E-04





o-Xylene

95476





1.09E-03





Phenanthrene

85018





1.20E-04





Propionaldehyde

123386





5.01E-02





p-Xylene

106423





5.97E-04





Pyrene

129000





5.67E-05





Toluene

108883





3.98E-03





a.	Based on average of test numbers MCI, MC2, MC3, MC6, MC7, and MC8from the table showing
emissions factors for emissions per kg meat cooked. See Table E-2 in Reference 9.

b.	PM25-PRI emission factor is based on assumption that PM25-PRI = PM10-PRI x 0.8.

30.2.4	Controls

There are no controls assumed for this category.

30.2.5	Emissions

The emissions of PM10-PRI, PM25-PRI, and VOC for residential barbecue grilling are calculated by
multiplying the amount of meat grilled in each county (from equation 10) by the emissions factors from
Table 30-1.

Meatt r

P — 	L±	 v fF

p'c 2000 lbs. per ton p'meat

(11)

Where:

EP,c =

Meatt,c =

EFpfmeat ~

Emissions of pollutant p from grilling meat in county c, in pounds
Total amount of meat cooked on grills in county c, in pounds
Emissions factor for pollutant p from grilling meat

It is assumed that CO and NOX emissions are from charcoal combustion, and there are no significant
emissions of these pollutants from gas or electric grills. Therefore, to estimate CO and NOX emissions,
the emissions factors for these pollutants are multiplied by the amount of meat cooked on charcoal
(from equation 8), rather than the total amount of meat cooked.

j-,	MeCLttfuiTccicil^	/ii_\

ico/wox'c - 2000 Ibs.per ton X ttc°/N0X	(lla)

Where:

Eco/nox,c = Emissions of pollutant CO or NOX from grilling meat in county c, in pounds
Meatcharcoai,c = Total amount of meat cooked on charcoal grills in county c, in pounds
EFCo/nox= Emissions factor for CO or NOX from grilling meat

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For VOC, there is a separate calculation to account for emissions from lighter fluid use, in which the
number of grilling events per year where lighter fluid is used (from equation 4) is multiplied by an
emissions factor of 0.02 lbs. VOC/grilling event (Table 30-1).

EvOC,LF,c = nLF,c X EFvOC,LF	(12)

Where:

Evoc,lf,c	=	Emissions of VOC from lighter fluid use in county c, in pounds

nLF.c	=	Number of grilling events in county c where lighter fluid is used

EFvoqlf	=	Emissions factor for VOC from lighter fluid use

These VOC emissions are added to the VOC emissions from grilling meat to determine the total VOC
emissions from residential grilling.

Evoc.c = EvOC,LF,c + EvOC,meat,c	(13)

Where:

Evoqc	= Total emissions of VOC from residential grilling in county c, in pounds

Evoc,lf,c	= Emissions of VOC from lighter fluid use in county c, in pounds

Evoc,meat,c	= Emissions of VOC from grilling meat in county c, in pounds

Emissions of HAPs are calculated by multiplying the total VOC emissions by the speciation factors in
Table 30-1.

Eh,c ~ Evoc,c * EFh	(14)

Where:

Eh,c	=	Emissions of HAP h in county c, in pounds

Evoqc	=	Total emissions of VOC from residential grilling in county c, in pounds

EFh	=	Emissions factor for HAP h

30.2.6 Example calculations

Sample calculations for estimating VOC emissions from residential grilling in Ada County, ID, are shown
in Table 30-2. Note that equations 1, 2, and 3 result in constant values for each county, so these
calculations are not repeated here. See Section 30.2.1 for more information about these equations.

Table 30-2: Sample calculations for VOC emissions from residential grilling in Ada County, Idaho

Eq.#

Equation

Values for Ada County, ID

Result

5

units=4

Hc,o= ^ HCit
units=1

Hus,o
X	:-

Hus,t

138,929 1

— 4 unit homes in Ada County
x (154,408 occupied homes in Ada County)
/(162,766 Total homes in Ada County)

131,795 occupied
homes in Ada
County, ID

30-6


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Eq.#

Equation

Values for Ada County, ID

Result

4

^LF,c HC/o ^ 3.28

131,795 occupied homes in Ada County
x 3.28 grilling events per home

432,287 grilling
events in Ada
County, ID

6

Hco

IW —

131,795 occupied homes in Ada County

0.00148 ratio of
homes in Ada
County, ID

c Y.cH0

89,010,502 homes in U. S.

7

Charcoalc = HRC x
Charcoalus x
2000 lbs. per ton

0.00148 x 890,910 tons charcoal x
2000 lbs. per ton

2,638,284.3
pounds charcoal
in Ada County, ID

8

M6CLtcflarcoaic

= Charcoalc x 0.588

2,638,284.3 lbs. charcoal x 0.588

1,551,311 lbs.
meat grilled on
charcoal grills in
Ada County, ID

9

MecLtgas/eiec,c

M6CLtcflarcoaic

X 2.398

1,551,311 lbs. meat x 2.398

3,720,044 lbs.
meat grilled on
gas or electric
grills in Ada
County, ID

10

Meattc

Meatgas/eiecc

+ M6CLtcflarcoaic

1,551,311 lbs. meat + 3,720,044 lbs. meat

5,271,355 lbs.
meat grilled in
Ada County, ID

11

_ Meattr

n — x

P'c 2000 Ibs.per ton
EFp,meat

5,271,355 lbs. meat

			x 1.88 lbs. per ton

2000 lbs. per ton

4,955 lbs. VOC
from grilling meat
in Ada County, ID

12

Evoc,lf,c

= nLF,c X EFv0C,Lp

432,287 grilling events

x 0.02 lb. per grilling event

8,645 lbs. VOC
from lighter fluid
in Ada County, ID

13

Evoc,c

= EvOC,LF,c + EVoc,meat,c

4,955 lbs. VOC + 8,645 lbs. VOC

13,601 lbs. VOC
from residential
grilling in Ada
County, ID

30.2.7 Improvements/Changes in the 2020 NEI

There are no significant changes from the methodology used to calculate the 2020 NEI emissions.

30.2.8 Puerto Rico and U.S. Virgin Islands

Emissions from Puerto Rico are calculated using the same method described above. Insufficient data
exists to calculate emissions for the counties in the US Virgin Islands, so emissions are based on a proxy
county in Florida: 12087, Monroe County. The total emissions in lbs. for this Florida County is divided by
its population creating a Ibs.-per-capita emission factor. For each US Virgin Island County, the lbs. per
capita emission factor is multiplied by the county population (from the same year as the inventory's
activity data) which serves as the activity data. In these cases, the throughput (activity data) unit and the
emissions factor denominator unit are "EACH".

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30.3 References

1.	Hearth, Patio and Barbecue Association (HPBA), Statistics/Barbecue Statistics/Charcoal
Shipments for 2013. accessed April 2015.

2.	U.S. Census Bureau. Community Facts, Housing, Selected Housing Characteristics. Table DP04,
American Community Survey 5-Year Estimates, 2020.

3.	Kingsford email on the weight of their charcoal briquettes 4/11/2015.

4.	Hearth, Patio and Barbecue Association (HPBA), Statistics. BBQ Grill Shipments, accessed April
2015.

5.	Hearth, Patio & Barbecue Association (HPBA), 2011 State of the Barbecue Industry Report.
accessed April 2015.

6.	Hearth, Patio & Barbecue Association (HPBA), 2014 State of the Barbecue Industry Report.

7.	Hearth, Patio and Barbecue Association (HPBA) 3/23/2015 email from Jessica Boothe on how
many people with charcoal grills use lighter fluid.

8.	U.S. Environmental Protection Agency. 1999. Emissions from Street Vendor Cooking Devices
(Charcoal Grilling). EPA/600/SR-99/048.

9.	South Coast Air Quality Management District. October 5, 1990. "Rule 1174. "Control of Volatile
Organic Compound Emissions from the Ignition of Barbecue Charcoal" accessed May 2015.

10.	U.S. Environmental Protection Agency. 2014. SPECIATE Database, version 4.4. Speciation profile
4553, meat charbroiling. Speciation profile was adjusted to be based on VOC, rather than total
organic gases (TOG), by removing methane from the profile.

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United States	Office of Air Quality Planning and Standards	Publication No. EPA-454/R-23-001dd

Environmental Protection	Air Quality Assessment Division	March 2023

Agency	Research Triangle Park, NC


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