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v1.0Last reviewed July 2026
Authored by Jeremiah Say

Lead Systems Architect at GreenCalculus. Translates GHG Protocol methodology into high-precision JavaScript calculation engines. Architect of the MasterBrain data layer covering 1,000+ environmental tools, aligned with IPCC AR6 and the GHG Protocol Corporate Standard (2026 revision).

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Fuel, Distance and Energy Conversion — Methodology and Calculation Approach

Fuel, distance and energy conversion: 500 litres of diesel on a net calorific basis is 418.75 kg, 5,480 kWh and 1.292 tCO₂e, using DEFRA 2026 fuel properties and factor 2.58354 kgCO₂e per litre. Pick net not gross calorific value, and pair a per-litre factor with a volume.
MB v2026.62 · updated 24 Jul 2026

Citation-grade reference for converting between the three interchangeable representations of a fuel event — volume or mass, energy content, and distance travelled — and the CO₂e that follows. Defines the physical links that connect them (density, calorific value and fuel economy), isolates the gross-versus-net calorific value trap that swings energy totals by roughly a tenth and the gallon and factor-basis traps that can distort a footprint by a fifth, works three audit-record examples, and fixes the provenance discipline that keeps a conversion chain reconcilable. Emission factors and fuel properties resolve live from the GreenCalculus MasterBrain; pure unit conversions are hardcoded as exact definitional constants.

The Conversion Triangle

⚐ The central tension this page resolves

A single physical quantity of fuel wears three interchangeable numeric faces — a volume or mass (litres, tonnes), an energy content (kWh, GJ), and, once burned in a vehicle, a distance (kilometres, miles) — and each converts to the others through a physical property. The emissions follow from whichever face you start with, via the matching emission factor. The danger is that the same fuel gives different numbers depending on which basis you use, and mixing bases silently corrupts the result. The same litre of diesel is 0.8375 kg, about 10.96 kWh of usable energy, and roughly 2.58 kgCO₂e — but only if you pick net calorific value, not gross, and only if you pair a per-litre factor with a volume, not with an energy figure. Choose gross calorific value where net is required and the energy total is off by a tenth; read a US “40 mpg” as if it were a UK one and the per-kilometre figure is off by a fifth. This page maps the conversion triangle, names each trap with its magnitude, and enforces the provenance discipline that keeps a fuel-distance-energy chain auditable end to end.

Figure 1.1 — The conversion triangle: three faces of one fuel event, one emissions output

Volume / mass

litres, m³, tonnes
what you buy and meter

Energy

kWh, MJ, GJ
usable heat content

Distance

km, miles
vehicle output

Emissions output

CO₂e = (any face) × matching emission factor — per-litre, per-tonne, or per-kWh. Pair the factor basis to the activity basis.

Every fuel calculation is a walk around this triangle. A fleet manager starts with litres purchased; an energy manager starts with metered kWh; a vehicle analyst starts with distance and fuel economy. All three arrive at the same physical fuel and the same emissions — provided the conversions between the faces use the right physical property and the emission factor is drawn on the matching basis. The rest of this page defines the links, isolates the three basis traps, and works the chains end to end.

Named concept · Citable definition

The three conversion properties

The three faces of a fuel event are connected by three physical properties. Density (kg per litre) converts volume to mass. Calorific value (kWh or MJ per litre or per kg) converts volume or mass to energy content — and comes in two forms, gross and net, that differ by roughly a tenth. Fuel economy (litres per 100 km, or miles per gallon) converts distance travelled to fuel consumed. Density and calorific value are fuel properties that resolve live from the DEFRA dataset; fuel economy is a vehicle property supplied by the analyst. Getting any of the three wrong propagates directly into the emissions total.

Density converts between the volume a fuel occupies and the mass it carries: mass = volume × density. Diesel is about 0.8375 kg per litre, petrol about 0.7475, so a litre of diesel weighs more and carries more energy than a litre of petrol. Density matters wherever an emission factor is published on a mass basis (per tonne) but the fuel is metered by volume, or vice versa — coal and petroleum coke factors are per tonne, liquid road fuels per litre, and converting between them requires the density. The [gc_fuel] shortcode exposes density directly via its density_kg_litre field, so the value resolves live and stays current with each DEFRA release.

Calorific value (also heating value) converts a quantity of fuel to its usable energy content: energy = volume × calorific value. It is the property that lets a litre of diesel be expressed as roughly 10.96 kWh, or a cubic metre of natural gas as its kWh equivalent. Calorific value is why the same fuel can be reported on a volume basis or an energy basis and reconcile — and it is the site of the single most consequential trap on this page, because it comes in two forms that differ materially. The [gc_fuel] shortcode exposes it via cv_kwh_litre, and the emission factor itself is published on both a volume basis (per_litre) and two energy bases (per_kwh_gcv, per_kwh_ncv) so the analyst can work from whichever face the activity data uses.

Fuel economy converts distance travelled to fuel consumed: fuel = distance × consumption rate. It is expressed as litres per 100 km (the SI-adjacent convention) or miles per gallon (the imperial and US convention), and unlike density and calorific value it is a property of the vehicle, not the fuel — so it is supplied by the analyst, not looked up in the fuel dataset. Fuel economy is the bridge that lets a distance-based activity figure (odometer readings, telematics) become a fuel quantity and then an emissions figure, and it carries the second major trap of this page: mpg is ambiguous between US and imperial gallons. For a more direct distance-to-emissions route that skips the fuel-quantity step, the per-kilometre vehicle factors used in business-travel car accounting and fleet emissions apply the fuel economy and factor in one combined coefficient.

Gross vs Net Calorific Value

Named concept · Citable definition

The gross/net calorific value distinction

Calorific value is published two ways. Gross calorific value (GCV, or higher heating value) counts the energy recovered if the water vapour produced by combustion is condensed back to liquid; net calorific value (NCV, or lower heating value) does not, because most equipment vents that vapour as hot exhaust. NCV is lower than GCV by roughly 10% for gaseous fuels and 5–7% for liquid fuels. The two are not interchangeable: an energy figure, a calorific value, and an emission factor must all be on the same basis, or the emissions total is wrong by the gross-net gap.

The distinction matters because emission factors and energy figures both come in gross and net flavours, and combining a gross energy figure with a net factor (or the reverse) introduces a silent error of several percent. DEFRA publishes UK natural gas and grid-gas figures on the gross basis by convention, while IPCC and much international energy accounting use net; the [gc_fuel] factor exposes both energy-basis factors (per_kwh_gcv and per_kwh_ncv) precisely so the analyst can match the basis of their metered energy data. The rule is simple and absolute: identify whether the energy figure is gross or net, then use the calorific value and the emission factor on the same basis. The volume-basis route (per-litre, per-tonne) sidesteps the question entirely, which is one reason it is the safer default when the fuel is metered by volume.

Table 3.1 Indicative gross vs net calorific value and the gap (DEFRA conventions; illustrative, verify live via [gc_fuel])
Fuel Net CV (approx) Gross CV (approx) Net/gross gap Emission-factor bases available
Natural gas ~9.8 kWh/m³ ~10.9 kWh/m³ ~10% per_kwh_gcv · per_kwh_ncv (live)
Diesel ~10.96 kWh/L ~11.75 kWh/L ~7% per_litre · per_kwh_gcv · per_kwh_ncv (live)
Petrol ~9.6 kWh/L ~10.3 kWh/L ~7% per_litre · per_kwh_gcv · per_kwh_ncv (live)
LPG ~6.6 kWh/L ~7.1 kWh/L ~7% per_litre · per_kwh_gcv · per_kwh_ncv (live)

The calorific values in the table are indicative and rounded for illustration; the authoritative current values resolve live through the [gc_fuel] cv_kwh_litre field and the two energy-basis factor fields. The point of the table is the gap column: for gaseous fuels the gross-net gap is around a tenth, large enough that a basis mismatch is a material error rather than a rounding nuance.

The Unit Traps: Gallons, Miles, and Energy Units

Beyond the gross-net distinction, three unit ambiguities routinely corrupt fuel conversions. Two are pure-definition traps (gallons and energy units) that carry exact answers once the definition is fixed; the third is a factor-basis pairing error. Unlike fuel properties, the definitional conversions never change — they are fixed by the SI and imperial systems — so this page hardcodes them as exact constants rather than resolving them from a dataset.

US vs imperial gallon (and mpg)

The gallon is not one unit. A US gallon is 3.78541 litres; an imperial (UK) gallon is 4.54609 litres — about 20% larger. Because miles-per-gallon divides distance by gallons, a US mpg and a UK mpg for the identical vehicle are different numbers, and a fuel economy quoted in “mpg” without its gallon is ambiguous by 20%. This is the most common cross-border fuel-conversion error: a US-sourced “40 mpg” figure read as a UK one, or vice versa, distorts the resulting per-kilometre emissions by a fifth. Example C works both readings of the same “40 mpg” to show the gap explicitly. The safe practice is to convert fuel economy to litres per 100 km — an unambiguous SI-adjacent unit — before any emissions calculation.

Distance and energy unit definitions

Distance and energy carry their own definitional conversions, all exact: one mile is 1.60934 kilometres; one kilowatt-hour is exactly 3.6 megajoules; one gigajoule is 277.778 kilowatt-hours. These are fixed constants, not measured data, so they never drift and are hardcoded with their definitions. The only error they produce is arithmetic — dropping a factor of 1,000 between kWh and MWh, or between MJ and GJ — which is why a conversion chain should carry its units through every step rather than tracking bare numbers.

Volume-basis vs energy-basis emission factors

The third trap is a pairing error rather than a definition. Every fuel emission factor is published on multiple bases — per litre, per tonne, per kWh gross, per kWh net — and the factor must match the basis of the activity data. Multiplying litres of diesel by a per-kWh factor, or metered kWh by a per-litre factor, produces a number that is wrong by the calorific value. The pairing rule is mechanical: volume activity data takes a per-volume factor, mass data takes a per-mass factor, energy data takes a per-energy factor on the matching gross/net basis. The [gc_fuel] shortcode carries all bases for exactly this reason, and the correct discipline is to read the factor field that matches the activity unit rather than converting the activity to fit a single factor.

The Conversion and Emissions Calculation

The conversions are a chain of multiplications, each applying one physical property, terminating in the emissions factor on the matching basis.

Mass = Volume × Density Energy = Volume × Calorific value (gross OR net — match the factor) Fuel = Distance × Fuel economy (in consistent volume units) Emissions = (Volume | Mass | Energy) × EFmatching basis
Every step carries a unit. The emissions line takes whichever face the activity data provides — litres × per-litre factor, tonnes × per-tonne factor, or kWh × per-kWh factor on the correct gross/net basis. Never cross bases: a per-litre factor multiplies litres, never kWh. Fuel economy must be resolved to a single unambiguous unit (litres per 100 km) before use, to eliminate the gallon ambiguity of §4.

The chains compose: distance becomes fuel via economy, fuel becomes energy via calorific value, and any face becomes emissions via the matching factor. Because each link is a documented physical property, a conversion chain is fully auditable — a reviewer can reconstruct the emissions from the activity data and the stated properties. That auditability is the whole value of doing the conversion transparently rather than reaching for a single opaque per-kilometre coefficient, and it is why every worked example below states its density, calorific value and factor basis explicitly.

Worked Examples — Audit Records

Three audit-record snapshots. Emission factors and fuel properties are cross-checked against the live [gc_fuel] values at this page’s review date; unit-conversion constants are the exact definitional values. All inputs are stated so each example reconciles independently.

Example A Litres of diesel to mass, energy and CO₂e Volume → all faces
Inputs
Fictional fleet fuel record · review-date snapshot 2026-07-01
Fuel purchased: 500 litres diesel (average biofuel blend)
Density: 0.8375 kg/L (DEFRA fuel properties, [gc_fuel field=”density_kg_litre”])
Net calorific value: 10.96 kWh/L (DEFRA, net basis)
Emission factor: 2.58354 kgCO₂e/L (DEFRA 2026, AR5, matches 2.58354) The base case — one volume figure expressed as all three faces plus emissions, each via its property.
Mass = 500 × 0.8375= 418.75 kg
Energy (net) = 500 × 10.96= 5,480 kWh = 19.73 GJ
Emissions = 500 × 2.58354= 1,291.8 kgCO₂e
= tCO₂e= 1.292 tCO₂e
500 L = 418.75 kg = 5,480 kWh = 1.292 tCO₂e volume basis · DEFRA 2026
Reading: the same 500 litres is simultaneously 418.75 kg, 5,480 kWh (19.73 GJ) and 1.292 tCO₂e — three faces of one fuel event, each reached by one property. The emissions were computed on the volume basis (litres × per-litre factor), the safest route when the fuel is metered by volume because it never touches the gross/net question. Had the analyst instead started from the energy figure, they would have needed the per-kWh factor on the net basis to match the net energy — pairing net energy with a gross factor would misstate the result. The energy figure uses net CV; a gross-CV energy figure would be about 7% higher (~5,875 kWh) and would require the gross per-kWh factor to reconcile.
Example B Distance and fuel economy to fuel and CO₂e Distance → fuel → emissions
Inputs
Fictional vehicle telematics record · review-date snapshot 2026-07-01
Distance: 10,000 km (odometer)
Fuel economy: 7.0 L/100 km diesel (resolved to L/100 km — no gallon ambiguity)
Emission factor: 2.58354 kgCO₂e/L (DEFRA 2026, matches 2.58354) The distance route — economy converts distance to fuel, then the factor converts fuel to emissions.
Fuel = 10,000 × 7.0 ÷ 100= 700 L
Emissions = 700 × 2.58354= 1,808.5 kgCO₂e
÷ 1000 → tCO₂e= 1.808 tCO₂e
Per-km intensity= 180.8 gCO₂e/km
1.808 tCO₂e · 180.8 gCO₂e/km 7.0 L/100km · DEFRA 2026
Reading: starting from distance, fuel economy converts 10,000 km to 700 litres, and the per-litre factor converts that to 1.808 tCO₂e, or 180.8 gCO₂e/km. Because the fuel economy was already expressed in litres per 100 km, there is no gallon ambiguity to resolve — the number is unconditional. Had it been supplied as “40 mpg” instead, the analyst would first have to establish which gallon (Example C), and the per-kilometre result would differ by up to a fifth depending on the answer. This is why resolving fuel economy to a metric unit before calculating is a discipline, not a preference.
Example C mpg to gCO₂/km — the gallon trap Unit trap
Inputs
The same “40 mpg”, two gallons · review-date snapshot 2026-07-01
Fuel economy: 40 mpg (petrol) — gallon unspecified
Imperial gallon: 4.54609 L (exact) · US gallon: 3.78541 L (exact)
Mile: 1.60934 km (exact)
Emission factor: 2.075 kgCO₂e/L petrol (DEFRA 2026, matches 2.075) The failure case. An unlabelled mpg yields two different per-km figures — a 20% spread from the gallon alone.
km per gallon (both) = 40 × 1.60934= 64.374 km
Imperial: L/100km = 4.54609 ÷ 64.374 × 100= 7.062 L/100km
Imperial: gCO₂e/km = 7.062 × 2.075 × 10= 182.5 gCO₂e/km
US: L/100km = 3.78541 ÷ 64.374 × 100= 5.880 L/100km
US: gCO₂e/km = 5.880 × 2.075 × 10= 151.9 gCO₂e/km
Spread from the gallon alone182.5 vs 151.9 = +20%
40 mpg = 182.5 (UK) or 151.9 (US) gCO₂e/km same number · 20% spread by gallon
Reading: the identical “40 mpg” produces 182.5 gCO₂e/km read as imperial and 151.9 read as US — a 20% spread with nothing changed but the gallon. The imperial figure is higher because an imperial gallon is larger, so “40 miles per imperial gallon” means more fuel per mile than “40 miles per US gallon.” An mpg quoted without its gallon is unusable for emissions accounting, and a cross-border dataset that mixes the two silently biases every affected vehicle. The fix is unconditional: convert every mpg to litres per 100 km, stating the gallon used, before any emissions step. The gallon and mile constants here are exact definitions, not dataset values — they never change.

Sensitivity: Which Basis Choice Moves the Number Most

The conversion traps differ in magnitude, and ranking them tells the analyst where to concentrate care. The table shows the error introduced by each basis mistake, referenced to a correct baseline.

Table 7.1 Error introduced by each basis mistake, ranked by magnitude
Basis mistake Correct Mistaken Error Where it bites
US mpg read as imperial (or reverse) correct gallon wrong gallon ±20% Cross-border fleet / vehicle-spec data
Gross CV used where net required (gas) net basis gross basis ~10% Gaseous-fuel energy totals
Gross/net mismatch (liquid fuels) matched basis crossed basis ~7% Energy-basis liquid-fuel totals
Diesel vs petrol density confusion 0.8375 (diesel) 0.7475 (petrol) ~11% Volume ↔ mass conversions
Factor-basis mismatch (per-litre vs per-kWh) matched crossed order-of-magnitude Any face-to-emissions step

Two points. First, the factor-basis mismatch (last row) is not a percentage error but an order-of-magnitude one — multiplying litres by a per-kWh factor produces a nonsensical result off by roughly the calorific value, so it is usually caught by a sanity check, unlike the subtler gallon and gross-net errors that produce plausible-looking wrong numbers. Second, the gallon trap tops the percentage ranking at ±20%, which is why it earns its own worked example: it is both the largest common error and the easiest to make silently, because an mpg figure looks complete even when its gallon is unstated.

Conversion Reference

The constants and properties used across the page, with their render basis. Fuel emission factors and physical properties resolve live from the MasterBrain and re-baseline with each DEFRA release. Pure unit conversions are exact definitional constants — fixed by the SI and imperial systems, never drifting — and are hardcoded as such; they are not a data gap.

Table 8.1 Conversion constants and fuel properties — value, use, and render basis
Quantity Value Converts Render
US gallon 3.78541 L gallon → litre (US) ◆ exact definition
Imperial gallon 4.54609 L gallon → litre (UK) ◆ exact definition
Mile 1.60934 km mile → km ◆ exact definition
Kilowatt-hour 3.6 MJ kWh → MJ ◆ exact definition
Gigajoule 277.778 kWh GJ → kWh ◆ exact definition
Diesel density ~0.8375 kg/L volume → mass ● live [gc_fuel density_kg_litre]
Diesel net CV ~10.96 kWh/L volume → energy (net) ● live [gc_fuel cv_kwh_litre]
Diesel emission factor 2.58354 kgCO₂e/L volume → CO₂e ● live 2.58354
Petrol emission factor 2.075 kgCO₂e/L volume → CO₂e ● live 2.075
Natural gas emission factor 0.18231 kgCO₂e/kWh energy (gross) → CO₂e ● live 2.02633

The two render bases are not interchangeable in maintenance terms: the definitional constants are cited to the SI and imperial standards and never need updating, while the live fuel properties and factors flush automatically on each MasterBrain release. Presenting them together, clearly labelled, is what lets a reader know which numbers to trust as permanent and which to re-verify against the current dataset.

Governance: Every Conversion Carries a Basis

Named concept · Citable definition

The basis-provenance rule

A fuel conversion is only auditable if every step declares its basis: the gross or net flavour of any calorific value and energy figure, the US or imperial flavour of any gallon or mpg, the unit of every activity figure, and the matching basis of every emission factor. A conversion chain that reaches an emissions total without stating these cannot be verified and cannot be reproduced — and because the errors they hide (gross-net, gallon, factor-basis) produce plausible-looking wrong numbers, an unstated basis is not a cosmetic omission but a defect.

The discipline is procedural, not calculative, and it is what separates a defensible fuel inventory from an unreproducible one. Two provenance notes recur. First, the DEFRA emission factors this page draws on are published on the IPCC AR5 GWP-100 basis by DEFRA convention — that is part of their definition, and they should not be mixed with AR6-basis totals within a single inventory, nor “corrected” to AR6. Second, the CO₂e itself is formed from the underlying gases via their global warming potentials, defined in the global warming potential glossary and the IPCC AR6 GWP dataset; the fuel factors already embed this conversion at AR5, so the analyst applying a per-litre diesel factor does not re-apply a GWP. The converted quantities feed directly into the diesel, natural gas and LPG combustion methodologies as Scope 1 activity, and the upstream fuel supply is handled separately in the well-to-tank methodology — keeping combustion and upstream on their own factors, never double-counted.

Failure Modes

Five recurring ways a fuel-distance-energy conversion goes wrong, each with the signature that lets a reviewer detect it.

10.1 Unlabelled mpg
A fuel economy quoted as “mpg” with no gallon, then used directly for emissions. US and imperial gallons differ by ~20%, so the result is ambiguous by a fifth (Example C). Detection: any mpg figure without an explicit US/imperial label, especially in cross-border datasets. Fix: convert every mpg to litres per 100 km, stating the gallon, before calculating (§4).
10.2 Gross/net calorific-value mismatch
Combining a gross energy figure with a net calorific value or emission factor, or the reverse — a ~10% error for gas, ~7% for liquids. Detection: an energy total whose basis is not stated, or a per-kWh factor whose gross/net flavour does not match the energy figure. Fix: identify the basis of the energy data and use the calorific value and factor on the same basis (§3).
10.3 Factor-basis mismatch
Multiplying activity data by an emission factor on the wrong basis — litres by a per-kWh factor, kWh by a per-litre factor. Produces a result off by roughly the calorific value. Detection: an emissions figure that fails a sanity check by an order of magnitude, or a factor field whose unit does not match the activity unit. Fix: read the factor field that matches the activity unit; never convert the activity to fit a single factor (§4).
10.4 Wrong-fuel density or CV
Applying diesel’s density or calorific value to petrol, or a generic constant to a specific fuel — an error of several to eleven percent. Detection: a volume-to-mass or volume-to-energy conversion using a property that does not match the named fuel. Fix: read the property for the specific fuel via [gc_fuel], not a generic constant.
10.5 Mixed GWP basis
Treating the DEFRA AR5-basis fuel factors as AR6, or blending them with AR6-basis totals in one inventory. The DEFRA factors carry AR5 by definition. Detection: a total that mixes DEFRA fuel factors with AR6-basis figures without segregation. Fix: keep one GWP basis per inventory; DEFRA factors stay on AR5 (§9).

Implementation Workflow

Six steps to a reproducible fuel-distance-energy conversion
  1. 01
    Identify the starting face. Volume, mass, energy or distance — the form the activity data actually arrives in (litres purchased, kWh metered, km driven).
  2. 02
    Resolve every ambiguous unit. Convert mpg to litres per 100 km stating the gallon; label every energy figure gross or net; carry units through each step.
  3. 03
    Source fuel properties live. Read density (density_kg_litre) and calorific value (cv_kwh_litre) for the specific fuel via [gc_fuel]; use exact definitional constants for pure unit conversions.
  4. 04
    Convert to the emissions face. Apply the physical properties in a documented chain, keeping every intermediate value and its unit.
  5. 05
    Apply the matching factor. Multiply by the emission factor on the basis that matches the activity unit — per-litre for volume, per-tonne for mass, per-kWh (gross or net) for energy. Never cross bases.
  6. 06
    Record the provenance. Document every basis (gross/net, US/imperial, factor basis, AR5 GWP) so the chain reconciles and a reviewer can reproduce it.

Converting fuel for a fleet or combustion inventory? The converted quantities feed the diesel and natural gas combustion methodologies, and the DEFRA emission factor dataset supplies the underlying factors and properties.

Standards Alignment

Standard Role for fuel-distance-energy conversion
UK DEFRA 2025 Source of the fuel emission factors (per-litre, per-tonne, per-kWh gross/net), densities and calorific values that drive every conversion. AR5 GWP-100 basis.
IPCC AR6 The GWP-100 values behind the CO₂e conversion, and the gross/net calorific-value conventions the international energy accounting community follows.
GHG Protocol Corporate Standard Defines the Scope 1 combustion boundary the converted fuel quantities feed, and the requirement for transparent, reproducible calculation methods.

Methodology Metadata — for GHG Inventory Documentation

Copy into the methodology notes accompanying a fuel conversion. Adjust the fuel, basis and unit lines to match the conversion performed.

Methodology GreenCalculus Fuel, Distance and Energy Conversion Methodology v1.0 (July 2026). greencalculus.com/methodology/fuel-distance-energy-conversion-methodology/.
Conversions Mass = volume × density; Energy = volume × calorific value (state gross or net); Fuel = distance × fuel economy (in L/100km). Emissions = activity × EF on the matching basis.
Fuel properties Density [gc_fuel field="density_kg_litre"], calorific value [gc_fuel field="cv_kwh_litre"] (live, DEFRA). CV basis: [gross | net] stated. Diesel ~0.8375 kg/L, ~10.96 kWh/L net at review date.
Emission factors Per-litre 2.58354, per-kWh gross/net per_kwh_gcv/per_kwh_ncv, per-tonne per_tonne (live, DEFRA 2026, AR5 GWP-100). Factor basis matched to activity unit.
Unit constants US gallon 3.78541 L, imperial gallon 4.54609 L, mile 1.60934 km, kWh 3.6 MJ, GJ 277.778 kWh — exact definitional constants (SI / imperial), hardcoded. Gallon flavour stated for any mpg.
GWP basis DEFRA fuel factors carry IPCC AR5 GWP-100 by convention; not mixed with AR6-basis totals. CO₂e conversion per IPCC AR6 GWP values is already embedded in the factors.
Downstream use Converted fuel quantities feed Scope 1 combustion (diesel, natural gas, LPG); upstream fuel via well-to-tank, never double-counted.
Fuel, distance and energy conversion methodology — 500 L diesel = 418.75 kg, 5,480 kWh and 1.292 tCO2e on a net calorific basis.
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Frequently Asked Questions

Two separate conversions, each via its own property. For energy, multiply litres by the calorific value: a litre of diesel is about 10.96 kWh on the net basis, so 500 litres is about 5,480 kWh (19.73 GJ) — but state whether you are using net or gross calorific value, because gross is about 7% higher for diesel. For emissions, multiply litres by the per-litre emission factor: at 2.58354 kgCO₂e/L, 500 litres is 1,291.8 kgCO₂e (Example A). The two conversions are independent — you do not go through kWh to reach CO₂e when you have a per-litre factor. Use the calorific value only if you actually need the energy figure, or if your emission factor is on a per-kWh basis, in which case match the gross/net flavour.

Gross calorific value (higher heating value) counts the energy recovered if the water vapour from combustion is condensed; net calorific value (lower heating value) does not, because most equipment vents that vapour. Net is lower — about 10% lower for gaseous fuels, 5–7% for liquids. Which to use depends on your data and factor: the rule is that the energy figure, the calorific value and the emission factor must all be on the same basis. DEFRA publishes UK gas on the gross basis; IPCC and much international accounting use net. The [gc_fuel] factor carries both energy-basis factors (per_kwh_gcv and per_kwh_ncv) so you can match. If your fuel is metered by volume, the per-litre route sidesteps the question entirely and is the safer default.

Because a US gallon (3.78541 L) and an imperial gallon (4.54609 L) are different volumes, about 20% apart. Miles per gallon divides distance by gallons, so “40 miles per US gallon” and “40 miles per imperial gallon” describe different fuel consumption — the imperial figure uses more fuel per mile because the gallon is bigger. In Example C the same “40 mpg” gives 182.5 gCO₂e/km read as imperial and 151.9 read as US, a 20% spread from the gallon alone. An mpg quoted without stating its gallon is unusable for emissions accounting, and cross-border datasets that mix the two silently bias every affected vehicle. Always convert mpg to litres per 100 km, stating the gallon, before calculating.

Two categories, and the distinction matters for maintenance. Fuel properties and emission factors — density, calorific value, and the per-litre/per-tonne/per-kWh factors — are DEFRA data that re-baseline with each annual release, so they resolve live via the [gc_fuel] shortcode and flush automatically when the dataset updates. Pure unit conversions — a US gallon is 3.78541 litres, a mile is 1.60934 km, a kWh is exactly 3.6 MJ — are exact definitional constants fixed by the SI and imperial systems; they never change, so they are hardcoded with their definitions rather than pulled from a dataset. Treating a definitional constant as if it needed updating, or a live factor as if it were fixed, are both errors — the reference table (§8) labels each so you know which to re-verify.

No — that is a factor-basis mismatch and produces a result off by roughly the calorific value (failure mode 10.3). The emission factor must match the basis of the activity data: litres take a per-litre factor, tonnes take a per-tonne factor, kWh take a per-kWh factor on the matching gross/net basis. Multiplying litres by a per-kWh factor mixes a volume with an energy coefficient, giving a number that is nonsensical by about a factor of ten — usually caught by a sanity check, but a real error nonetheless. The [gc_fuel] shortcode publishes the factor on every basis precisely so you can read the field that matches your activity unit. Read the matching factor rather than converting your activity data to fit a single factor.

Multiply the litres-per-100km figure by the per-litre emission factor, then divide by 100 to get per-kilometre, and convert kg to grams. For diesel at 7.0 L/100km and 2.58354 kgCO₂e/L: 7.0 × 2.58354 = 18.08 kgCO₂e per 100 km, which is 180.8 gCO₂e/km (Example B). If your fuel economy is in mpg, first resolve the gallon and convert to L/100km (Example C) — otherwise the result is ambiguous by up to 20%. For a route that combines fuel economy and factor into a single per-kilometre coefficient, the business-travel car and fleet methodologies use DEFRA per-km vehicle factors directly, which is convenient when you have distance but not a measured fuel economy.

Not separately — the DEFRA fuel emission factors already embed the global-warming-potential conversion. A per-litre diesel factor of 2.58354 kgCO₂e/L is a CO₂-equivalent figure: it has already combined the fuel’s CO₂, methane and nitrous oxide emissions using their GWP-100 values (on the AR5 basis, by DEFRA convention). So when you multiply litres by that factor you get CO₂e directly, with no further GWP step. You would only apply a GWP yourself if you were working from raw per-gas masses rather than a pre-aggregated CO₂e factor. One provenance note: because the DEFRA factors carry AR5, do not mix them with AR6-basis totals in one inventory, and do not “correct” them to AR6 — the AR5 basis is part of their definition (§9).

Both are valid; the transparent chain is more auditable. A single per-kilometre vehicle factor (distance × combined coefficient) is convenient and correct when you have only distance and want a quick figure — the fleet methodology uses exactly this. But it hides the density, calorific value and fuel economy inside one number, so a reviewer cannot see how it was built or check the basis assumptions. Converting through the explicit chain — distance to fuel via economy, fuel to emissions via the per-litre factor — keeps every property visible and every basis stated, so the result can be reconstructed and verified. Use the combined coefficient for speed when only distance is available; use the transparent chain when the calculation must be audited or when you hold measured fuel data.

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