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Article

USA Carbon Footprints of Grills, by Fuel & Grill Type, 2022–27

1
Atlantic Consulting, Obstgartenstrasse 14, 8136 Thalwil, Switzerland
2
Charbroil LLC, Columbus, GA 31904, USA
*
Author to whom correspondence should be addressed.
Fuels 2022, 3(3), 475-485; https://doi.org/10.3390/fuels3030029
Submission received: 25 May 2022 / Revised: 13 July 2022 / Accepted: 28 July 2022 / Published: 3 August 2022

Abstract

:
Grill-specific footprints for common fuel/grill types in the USA have been estimated from public information and data from a major grill manufacturer. In 2022, grill-specific footprints vary by a ratio of 9:1. A typical gas grill has the highest footprint; a wood-pellet grill is lowest; charcoal briquettes, electricity and super-efficient gas grills come in-between those two. Efficiency varies greatly for gas (natural gas or propane) grills: a typical gas grill has twice the footprint of a super-efficient one. In 2027, the footprint rankings could change considerably from 2022. With biofuel substitution, the super-efficient gas grill would move ahead of pellets. Electricity and charcoal could improve but would still place fifth and sixth. The range of grill-specific footprints could fall to 4.5:1, and within a much-lower range. The highest footprint in 2027 is almost 60% lower than 2022′s highest.

1. Introduction

Outdoor grilling, or barbequing, is a popular means of cooking in the USA. According to a biannual survey of the Hearth, Patio & Barbeque Association (https://bit.ly/3AfuA1v (accessed on 20 May 2022)), the majority of American consumers, 70% of households, own at least one grill. Of those, nearly half own two grills. The authors estimate the total ‘grill park’ at around 160 million. Grills fired by gas (natural gas or propane) are found in two-thirds of grill-owning households, charcoal in about half, electric in 10–15% and wood pellets in about 10%.
Significant numbers of consumers are trying to live more sustainably. A 2021 opinion poll (https://bwnews.pr/3R4udgf (accessed on 20 May 2022)) reports that 22% of US consumers have made major behavior changes and 55% have made modest behavior changes in their life patterns to become more sustainable. Sixty percent of the same consumers say that sustainability is an important criterion in their purchasing—presumably including that of grills.
Carbon footprints are a popular measure of sustainability. Peer-reviewed footprints of grilling have been published for the United Kingdom [1], and a non-peer-reviewed study by the University of Sheffield was published in 2019 (https://bit.ly/3bJeN0r (accessed on 20 May 2022)). For the US, a non-peer-reviewed comparison of charcoal briquettes and gas was done in 2008 by Tristram O West of the Environmental Sciences Division at Oak Ridge National Laboratory in the USA. Other, informal investigations appear from time to time in the popular media: such as https://www.theatlantic.com/science/archive/2021/07/grilling-emissions-environment/619394/, https://grist.org/article/greenguide-grilling/, https://blog.constellation.com/2019/06/06/energy-efficient-gas-vs-electric-grills/, https://www.starenergypartners.com/blog/energy-efficiency/ecofriendly-grilling-gas-charcoal/, https://www.pointclickswitch.com/blog/energy-saving-bbq-tips/, https://justenergy.com/blog/green-grilling-eco-friendly-summer-bbq/, https://www.quora.com/What-type-of-BBQ-grill-is-the-most-efficient (accessed on 20 May 2022)). Inspection of these suggests some are biased, most are non-quantitative, and they do not draw common conclusions.
This paper is believed to be the first peer-reviewed, comprehensive footprint for grilling in the US.

2. Materials and Methods

This study has estimated a ‘grill-specific’ footprint in 2022 that is a function of:
  • A fuel footprint: carbon-dioxide-equivalents emitted per unit of fuel energy consumed; and
  • A cooking footprint: the time required and efficiency of heat delivery by each grill type.
Inputs for 2022 are presented in the following two subsections. A third subsection presents a possible scenario for fuel footprints in five years’ time, in 2027. A section thereafter presents the results, which is followed by discussion.

2.1. Fuel Footprints 2022

The fuels are presented in alphabetical order: charcoal, electricity, hydrogen, natural gas, propane and wood.

2.1.1. Charcoal Briquettes

Kingsford charcoal briquettes are the leading seller in the USA, according to several sources, accounting for well over 50% of total physical volume. Therefore, this has been used as proxy for all charcoal briquettes. Their composition (Table 1) has been estimated from several sources: a video from 2001 of a Kingsford factory (https://bit.ly/3bInhVO (accessed on 20 May 2022)) that appears to be located on or next to an open-pit coal mine; correspondence of Kingsford with members of the California BBQ Association from around 2001 (https://www.virtualweberbullet.com/all-about-charcoal/ (accessed on 20 May 2022)) reproduces the information, which was originally posted by Kingsford. This original was verified by the authors at https://archive.org/web/ (accessed on 20 May 2022)); a Kingsford safety data sheet from 2016 (https://bit.ly/3y8EGOV (accessed on 20 May 2022)); and a material analysis of 74 brands of briquettes, including 3 samples from Kingsford, by [2]. Eric Johnson also corresponded with the Dr A Drobniak, corresponding author of [2], who now works for the Indiana Geological & Water Survey. Based on all that, the weighted lower heating value (LHV) of a briquette (Table 1) was used to iteratively estimate composition, which came out identically to Kingsford’s reported LHV of 22.6 MJ/kg, or 9700 BTU/lb (https://bit.ly/3R2zQLJ (accessed on 20 May 2022)). After the initial version of this paper was submitted to review on 25 May 2022, the authors identified a patent from Kingsford [3] that was published only one day earlier, on 24 May 2022. This patent confirmed the authors’ estimated composition.
About 85% of the pre-combustion footprint (Table 2) comes from the production of charcoal, which includes the briquetting process. This does not include the emissions of the charcoal pyrolysis itself, but of the various operations around that (as shown in the Kingsford video). As briquettes are made from waste wood, that wood is considered carbon-neutral at its point of collection.
The footprint comes out at 0.902 kg CO2e/kg briquette, or 0.093 lb CO2e/kBTU or 93 lb CO2e/mmBTU briquette.
About 85% of the combustion footprint (Table 3) comes from burning of the fossil coal component, with the remainder coming from burning of the limestone. The charcoal and wood are assumed to be carbon neutral.
The footprint comes out at 0.396 kg CO2e/kg briquette, or 0.041 lb CO2e/kBTU or 41 lb CO2e/mmBTU briquette.

2.1.2. Electricity

Electricity is assumed to be ‘at the plug’ closest to a residential grill. Electricity is defined as the average supplied in the US. According to the US Energy Information Administration (https://bit.ly/2kyD53l (accessed on 20 May 2022)), the fuel mix for this is approximately: 40% gas; and 20% each for coal, nuclear and renewables.
According to the current fuel mix, the pre-combustion footprint (Table 4) comes out at 0.025 lb CO2e/kBTU or 25 lb CO2e/mmBTU.
Using the same fuel mix and the US-average GHG factors published by the US Environmental Protection Agency (EPA) on 15 September 2021 at https://www.epa.gov/climateleadership/ghg-emission-factors-hub (accessed on 20 May 2022), the footprint of American electricity is 403 g CO2e/kWh, which converts to 0.261 lb CO2e/kBTU or 261 lb CO2e/mmBTU.
This figure can vary considerably by region. In the southeastern SERC grid that has the highest footprint in the continental US, the electricity footprint is 724 g CO2e/kWh, which converts to 0.468 lb CO2e/kBTU or 468 lb CO2e/mmBTU. In the upstate New York NPCC grid that has the lowest footprint in the US, the electricity footprint is 106 g CO2e/kWh, which converts to 0.068 lb CO2e/kBTU or 68 lb CO2e/mmBTU.
National footprints of electricity are often used in carbon footprints of products. However, many product footprints assume electricity is supplied by a specific grid or even a specific generating plant (this is supported by the practice of selling ‘green electricity’. Customers can buy low-carbon power, which is delivered in the form of a carbon credit, not in actual ‘green’ electrons.). There is no set rule or convention as to which should be used.
For electricity, a 10% loss—a typical value in footprint models—has been assumed for transport and distribution to the point of use.

2.1.3. (Green) Hydrogen

Green hydrogen is presumed to be made from electrolysis of water powered by renewable electricity. Hydrogen grilling is not yet commercial. Given its minor role and the uncertainty surrounding its eventual, commercial footprint, the authors have simply taken the working definition of the European Union (https://bit.ly/3bGeWSq (accessed on 20 May 2022)), which is that to be classified as ‘green’, hydrogen must have a footprint of 85 lb CO2e/mmBTU or less.

2.1.4. Natural Gas

Natural gas in the US is typically around 95% methane plus some ethane, carbon dioxide and traces of other hydrocarbons and nitrogen.
The US-national average pre-combustion footprint for natural gas is 0.042 lb CO2e/kBTU or 42 lb CO2e/mmBTU LHV [5]. Natural gas pre-combustion footprints have surfaced in the mainstream media in recent years, particularly with respect to (1) emissions from fracking and (2) fugitive emissions of methane throughout the supply chain. The NETL data [5] take full, state-of-the-art account for this. The stoichiometric output of carbon dioxide from burning of methane was applied: 0.136 lb CO2e/kBTU or 136 lb CO2e/mmBTU LHV. A GHG factor published by the US Environmental Protection Agency (EPA) on 15 September 2021 at https://www.epa.gov/climateleadership/ghg-emission-factors-hub (accessed on 20 May 2022) was not applied, because it is nearly 15% lower—which does not seem physically plausible.

2.1.5. Propane

Propane in the US consists mainly of, not surprisingly, propane, plus small amounts of other hydrocarbons and carbon dioxide. It is produced both as a byproduct of oil refining and as a byproduct of natural-gas processing. (Propane and butane must be removed from natural gas, before the gas is charged to a high-pressure pipeline, because under high pressure they will condense. Those liquids would cause problems in pipeline operations. Most butane in the USA ends up in gasoline or petrochemicals). Internationally, propane is usually designated as liquified petroleum gas (LPG), which can be mainly propane, mainly butane or some mix of the two.
The most recent, authoritative report of propane’s US footprint comes from California’s Air Resources Board as part of its Low Carbon Fuels Standard (https://bit.ly/3OSPuaH (accessed on 20 May 2022): 194 lb CO2e/mmBTU. The stoichiometric output of carbon dioxide from burning of propane was applied as the combustion footprint: 0.151 lb CO2e/kBTU or 151 lb CO2e/mmBTU. The remainder is the pre-combustion footprint of 0.043 lb CO2e/kBTU or 43 lb CO2e/mmBTU.

2.1.6. Wood Pellets and Wood Logs

Wood comes from countless species of trees. Therefore, do wood pellets, which can also come from ‘woody biomass’. Those used in grilling come from waste/residue wood, not from stem wood. Lower heating values of 19.6 and 20 MJ/kg are used for pellets and air-dried wood [6]. Combustion emissions are 202 lb CO2e/mmBTU [1]. Pre-combustion footprints are taken from ecoinvent: pellets from the process ‘Wood pellets, u = 10%, at storehouse/RER U’; and logs from ‘Logs, hardwood, at forest/RER U’. European datasets were used, because no equivalent US datasets are readily available. From inspection of the data, it is believed that European and US figures would be very similar.

2.2. Cooking Footprints 2022

Non-confidential efficiencies and time periods of fire-up and cooking were supplied through Alex Gafford by a leading manufacturer of grills (Table 5).
From these, heat fluxes for a grill session were derived (method is shown for gas/electric grills in Figure 1 as an example, fluxes for all grills are shown in Table 6).

2.3. Grill Footprints in 2027

Therefore, how might fuel footprints be reduced in the coming five years? Plausible scenarios for each of the fuels were estimated, based on best efforts analysis and best-available data.

2.3.1. No-Coal Charcoal?

The only obvious reduction possibility for briquettes is a reformulation of its current composition by the removal of fossil coal and its replacement with charcoal from wood. This is not an obvious possibility—it could be that fossil coal is critical to customer acceptance or production cost or some other requirement.

2.3.2. Electricity Decarbonized

US power has steadily shifted to renewable fuels for years past and will do for years to come. According to the US Energy Information Administration (https://bit.ly/3OAbibu (accessed on 20 May 2022)), the renewables share of electricity was: 10% in 2010; is now 24%; and by 2027 will reach 32%. The average footprint of American power, USEIA projects, will drop in 2022–2027 by 23%. (US-average power footprints published by the USEIA are about 10% lower than those published by US EPA For these kinds of statistics, that means they are effectively equal).

2.3.3. Green Hydrogen

As there are so many uncertainties about green hydrogen, an alternative case for 2027 has not been projected. The main alternative is: will green hydrogen happen or not? If it does, the best estimate for 2027 is the same as for 2022.

2.3.4. Renewable Gas

From reports in the media, renewable gas—i.e., biogas—is booming. Indeed it is, but from a very low base globally and in the USA. According to interpolation of data from [7], biogas accounts for 0.07% of all gas in the world’s grids. The IEA projects this to climb to 0.5% by 2030 [7] (also see https://bit.ly/3ybgefV (accessed on 20 May 2022)). Therefore, steep growth (mainly in Asia), but still a small presence overall. Moreover, only about 10% of biogas is upgraded to biomethane and injected to the natural gas grid—the rest is used for heating or electricity generation by the biogas producer. The plausible scenario, therefore, is that the footprint of gas-grilling in the US will not change by 2027.

2.3.5. rPropane

Renewable propane has been available for about 6–7 years now. Its typical footprint is about 80% less than that of fossil propane [8,9]. Several propane (LPG) distributors in Europe (for example, https://bit.ly/3AfwLSJ (accessed on 20 May 2022)) offer rPropane in cylinders that can be used for grilling. There is considerable production of rPropane in the USA. Some 250 million tons/year will be made in 2022, and this will probably break 1 million tons/year by 2025 [10]. That could be enough to justify an effort to divert some of it into grilling. A prime target would be California distributors, who already sell it into the Autogas market [9].

2.3.6. Wood

The rules of carbon accounting can be confused, when it comes to wood burning. A decade or two ago, wood was commonly considered to be carbon neutral. “You burn the tree; the tree grows back” [11]. Increasingly, this view is challenged, because it suggests that if someone cut down all the world’s forests and burned them, overnight, this would cause zero carbon emission. Therefore, there have been challenges. One of the most prominent was the Manomet Project (https://bit.ly/3aa9LKb (accessed on 20 May 2022)) in Massachusetts that blocked construction of a pellet-fired power plant. ‘Pellet Wars’ have also raged in Europe; nonetheless, pellet imports for European power generation are growing dramatically. In the past year, the International Energy Conservation Code (IECC), a building code created by the International Code Council in 2000, was amended to exclude wood from its previous classification as a ‘renewable’ fuel. (If it’s not renewable, what is it? The revised code does not say, other than it is not renewable). Thus far, this has been only for commercial buildings: a similar proposal for residential buildings is still in debate. Nonetheless, a ‘carbon-neutral presumption’ has been and is being challenged. Therefore, there is some possibility of a public backlash against pellets. Or even wood. However, the footprint impact is difficult or impossible to quantify, and it is even more difficult to project a difference from today to 2027—so it is assumed that accounting rules will not change by then.

3. Results

Grill-specific footprints for 2022 were calculated by: multiplying (1) the fuel footprint (carbon emission per energy unit of a given fuel) times (2) the required energy flux of a given grill type. These are presented from lowest to highest (Figure 2), and for reference, the fuel-only footprints are presented alongside. Fuel-only footprints were also broken out by life-cycle stage (Figure 3).
Using the same method as for 2022, possible footprints were calculated for 2027 (Table 7). They are presented alongside the 2022 ones for comparison.

4. Discussion

The variation of grill-specific footprints is broad, and rankings could change considerably from 2022 to 2027 (Table 7). These are discussed in subsequent subsections. One reviewer asked that pre-2022 footprints be addressed. It can be said that: (1) footprints of electric grills have likely declined over the past decade, as US power has steadily decarbonized; (2) manufacturers of high-quality grills have worked for a decade or more to improve efficiency; and (3) the carbon-emission factors of charcoal, natural gas, propane and wood have likely not changed significantly over the past decade.
Another remarkable finding is that both fuel footprints (which are well known) and cooking footprints (less well known) are critical. The importance of efficiency—the key to the cooking footprint—is seen obviously in gas grills. A super-efficient gas grill’s footprint is less than half that of a typical one’s (Figure 2), despite using the exact same fuel. The low-efficiency electric grill has a footprint four times that of a high-efficiency, again, using the same fuel.

4.1. Footprints 2022

Today in 2022, grill-specific footprints for US grills vary by a factor of 9:1. A typical gas grill’s footprint is highest; its 3.6 lb CO2e/grill session is nine times that of a pellet grill, which comes in lowest at 0.4 lb. Charcoal briquettes and electricity and super-efficient grills come in-between.
Pellets are a clear winner, with a footprint one-third that of second-place electricity. This is because they are made from wood considered to be carbon neutral, and their production footprint is modest. Electricity has the highest fuel footprint, yet the second-lowest grill-specific footprint, thanks to the high efficiency of its grill. Perhaps surprisingly, charcoal briquettes come in fourth, even though they are composed mostly of wood that is considered carbon neutral. Their production involves use of fossil gas, and they contain some fossil coal, which of course is not carbon neutral. Grill efficiency also makes a big difference for gas (either natural gas or propane): a typical gas grill has twice the footprint of a super-efficient one.
The wild card here is electricity. Generating footprints of regional grids in the continental US vary by a factor of four, from high in the coal-dominated southeast to low in hydro-heavy upstate New York. The US average is about halfway in-between. At its low, electricity’s footprint is 0.43 lb CO2e/grill session, almost equal to that of pellets (Figure 4). At its high of 1.82 lb CO2e/grill session, electricity’s footprint is about equal to briquettes’. The other fuels have some variation, but not nearly that of electricity, and not enough to significantly change rankings.

4.2. Footprints 2027

Five years from now, three significant differences could ensue (Figure 5):
(1)
rankings could change considerably;
(2)
footprint variation could narrow from 9:1 today to about 4.5:1; and that
(3)
within a much-lower range, the highest footprint of in 2027 of 1.5 lb CO2e/grill session coming in almost 60% lower than 2022′s highest of 3.6 lb.
If biopropane were substituted for today’s fossil propane, the super-efficient gas grill would move slightly ahead of pellets, with its two less-efficient incarnations coming in third and fourth (similar results would come from substitution of natural gas with biomethane, but this is less available to grills, so the biopropane case has been presented). Electricity lowers its footprint 20%, but still is relegated to fifth. Charcoal also makes a 20% improvement but comes in last.
The 2027 case is only a scenario, of course, but the possibilities are plausible. That said, the rankings could stay relatively similar to today’s. Only electricity is almost certainly destined to lower its footprint; for its competitors, improvement is a choice that suppliers can make (or not). Despite improvement, electricity will still in 2027 have the kind of variation it has today: its high will be in the range of a briquette footprint; its low will be competitive with the footprints of pellets and biopropane.

Author Contributions

Concept, E.J. and A.G.; method, E.J.; validation, E.J.; formal analysis, E.J.; investigation, E.J.; data curation, E.J. and A.G.; writing—original draft preparation, E.J.; writing—review and editing, A.G.; visualization, A.G.; supervision, E.J. and A.G. All authors have read and agreed to the published version of the manuscript.

Funding

No external funding was received.

Institutional Review Board Statement

No experimentation was involved.

Informed Consent Statement

All data used are public information, except the grill efficiencies supplied by Charbroil. Readers may of course request such data from Charbroil, but it is Charbroil’s choice whether or not to provide them.

Data Availability Statement

Data used in the study are referenced in the above paper.

Conflicts of Interest

The authors have no conflict to declare.

References

  1. Johnson, E. Charcoal versus LPG Grilling: A Carbon-Footprint Comparison. Environ. Impact Assess. Rev. 2009, 29, 370–378. [Google Scholar] [CrossRef]
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  3. Fisher, S.S.; Maier, G.; Wang, M.; El-Sayed, T.M.; Claudnic, M.E.; Gregg, A.; Thuerk, J. Flavor Briquet. U.S. Patent 11,339,340 B2, 24 May 2022. [Google Scholar]
  4. Atima, D.; Suthirat, K. Estimated Greenhouse Gases Emissions from Mobile and Stationary Sources in the Limestone and Basalt Rock Mining in Thailand. Am. J. Environ. Sci. 2016, 12, 334–340. [Google Scholar] [CrossRef] [Green Version]
  5. National Energy Technology Laboratory; Skone, T.J. Life Cycle Analysis of Natural Gas Extraction and Power Generation; National Energy Technology Laboratory: Pittsburgh, PA, USA, 2019.
  6. U.S. Department of Energy. Lower and Higher Heating Values of Fuels; U.S. Department of Energy: Washington, DC, USA, 2010.
  7. International Energy Agency. World Energy Outlook 2021; International Energy Agency: Paris, France, 2021. [Google Scholar]
  8. Johnson, E. A Carbon Footprint of HVO Biopropane. Biofuels Bioprod. Biorefining 2017, 11, 887–896. [Google Scholar] [CrossRef] [Green Version]
  9. Atlantic Consulting; Stonedown Limited. The Value of HVO Biopropane in Production and in the Market; Atlantic Consulting: Gattikon, Switzerland; Stonedown Limited: London, UK, 2021. [Google Scholar]
  10. World LP Gas Association. Renewable LPG the Decarbonised Future; World LP Gas Association: Paris, France, 2022. [Google Scholar]
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Figure 1. Gas/electric heat flux.
Figure 1. Gas/electric heat flux.
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Figure 2. Carbon footprints for grills, grill-specific and fuel-only, USA 2022.
Figure 2. Carbon footprints for grills, grill-specific and fuel-only, USA 2022.
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Figure 3. Carbon footprints for grills, fuel-only by life-cycle stage, USA 2022.
Figure 3. Carbon footprints for grills, fuel-only by life-cycle stage, USA 2022.
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Figure 4. Grill-specific carbon footprints for grills, with high-low-average electricity, USA 2022.
Figure 4. Grill-specific carbon footprints for grills, with high-low-average electricity, USA 2022.
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Figure 5. Grill-specific carbon footprints for grills, USA 2022 and alternate 2027.
Figure 5. Grill-specific carbon footprints for grills, USA 2022 and alternate 2027.
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Table 1. Composition of Kingsford charcoal briquettes.
Table 1. Composition of Kingsford charcoal briquettes.
ComponentWeight %LHV, MJ/kgWeighted LHV
Charcoal70%2819.6
Brown coal9%171.53
Limestone15%3.20.48
Sawdust5%190.95
NaBorate1%00
Briquette100% 22.6
Table 2. Pre-combustion footprint of Kingsford charcoal briquettes.
Table 2. Pre-combustion footprint of Kingsford charcoal briquettes.
ComponentGHG Factor kg CO2/kg FuelWeight kgWeighted Footprint kg CO2/kgFootprint Sources
Charcoal1.230.700.861ecoinvent: charcoal, at plant, Base Case
Brown coal0.340.090.031ecoinvent: Hard coal mix, at regional storage/UCTE U
Limestone0.010.150.002Average of ecoinvent and [4]
Sawdust0.170.050.008Wood pellets, u = 10%, at storehouse/RER U
NaBorate 0.010NA
Briquette 1.000.902
Table 3. Combustion footprint of Kingsford charcoal briquettes.
Table 3. Combustion footprint of Kingsford charcoal briquettes.
ComponentGHG Factor kg CO2/kg FuelWeight kgWeighted Footprint kg CO2/kgNotes
Charcoal00.700Assumed carbon neutral
Brown coal3.670.090.33100% carbon to CO2
Limestone0.440.150.066100 CaCO3 + Heat > 56 CaO + 44 CO2
Sawdust00.050Assumed carbon neutral
NaBorate00.010NA
Briquette 1.000.396
Table 4. Pre-combustion footprints, US electricity (lb CO2e/mmBTU).
Table 4. Pre-combustion footprints, US electricity (lb CO2e/mmBTU).
FuelWeighted Average FootprintSource
Coal7.07ecoinvent
Nuclear0.72UN Economic Commission for Europe
Gas16.71National Energy Technology Laboratory (US)
Renewables0.72UN Economic Commission for Europe
Sum25.23
Table 5. Grill efficiencies and fire-up/cook times.
Table 5. Grill efficiencies and fire-up/cook times.
Grill TypeBTU/hr MaxBTU/hr MinBTU/hr sq inFuelIgnition MinWarm up MinCook MinNotes
Electric high heat5975N/A20001530
Electric low heat5975N/A20001530
Electric average heat5975N/A20Electricity01530300 sq in, thermostatic control, assume operating rate at 2/3 max
Typical convective gas grill at 30,000 BTU/hr.30,00013,500100Propane01530300 sq in, assume operating rate at avg of max rate and min rate
Improved IR gas grill at 22,500 BTU/hr.22,50013,50075Propane01530300 sq in, assume operating rate at avg of max rate and min rate
Super efficient IR gas grill at 15,000 BTU/hr15,000900050Propane01030300 sq in, assume operating rate at avg of max and min
Pellet Smoker/Grill40,000N/A157Pellets101040254 sq in, thermostatic control, assume opeating rate at 1/2 max
Charcoal GrillN/AN/AN/ACharcoal briquettes01575254 sq in, no control; assume 2.2 lb @ 9700 BTU/lb, i.e., 1 kg charcoal, consumed over 90 min
Table 6. Heat fluxes, by grill type.
Table 6. Heat fluxes, by grill type.
Grill TypeBTUh MaxBTU/Cycle Aka Q TotalkBtu/Cycle
Electric high597534853.5
Electric low597534853.5
Electric average597534853.5
Typical gas grill30,00018,37518.4
Improved gas grill22,50014,62514.6
Super-efficient gas grill15,00085008.5
Pellet40,00020,00020.0
CharcoalN/A14,22714.2
Table 7. Carbon footprint rankings, by fuel, 2022 base case vs. alternative 2027 case.
Table 7. Carbon footprint rankings, by fuel, 2022 base case vs. alternative 2027 case.
Base Case 2022Possible Case 2027
Grill Fuellb CO2e/mmBTU LHVGrill Fuellb CO2e/mmBTU LHV
Wood logs4Wood logs4
Wood pellets20Wood pellets20
Green hydrogen85Renewable propane39
Charcoal briquettes134Biomethane (gas)44
Natural gas177Green hydrogen85
Propane194Charcoal briquettes107
Electricity314Electricity255
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Johnson, E.; Gafford, A. USA Carbon Footprints of Grills, by Fuel & Grill Type, 2022–27. Fuels 2022, 3, 475-485. https://doi.org/10.3390/fuels3030029

AMA Style

Johnson E, Gafford A. USA Carbon Footprints of Grills, by Fuel & Grill Type, 2022–27. Fuels. 2022; 3(3):475-485. https://doi.org/10.3390/fuels3030029

Chicago/Turabian Style

Johnson, Eric, and Alex Gafford. 2022. "USA Carbon Footprints of Grills, by Fuel & Grill Type, 2022–27" Fuels 3, no. 3: 475-485. https://doi.org/10.3390/fuels3030029

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