Appendix 9 – Methods for Calculating Energy Use and Greenhouse Gas Emissions

Appendix 9 – Methods for Calculating Energy Use and Greenhouse Gas Emissions

by Contact on 30 October 2026

This Appendix details the methods for calculating energy use and greenhouse gas (GHG) emissions as required by Criterion 2.10. It also provides GHG targets to guide development of GHG management plans.

Section

9.1 Introduction

9.2 Scope and timeframe for calculating energy use and GHG emissions

9.3 On-site energy use (Indicator 2.10.1)

9.4 GHG emissions (Indicator 2.10.2)

9.5 Target-setting for GHG management plans (Indicator 2.10.3)

9.1 Introduction

Measurement, reporting, and management of on-site energy use and GHG emissions are data and calculation-intensive processes. ASC strongly recommends the use of the ASC Greenhouse Gas Calculator (https://ghg.asc-aqua.org) to assist in undertaking calculations; it ensures correct methods and provides results consistent with the required reporting format. Other tools or frameworks may be used if it can be demonstrated that they follow the methodological requirements outlined in this Appendix.

9.2 Scope and timeframe for calculating energy use and GHG emissions

Both energy use and GHG emissions are calculated relative to a quantity of production. This requires that production data and input data (feeds, energy inputs, etc.) relate to a consistent timeframe. Given the differences between production cycles of different culture systems and species, two timeframe options may be used for calculations:

Option A. Calculate values for the most recently completed production cycle.

Option B. Calculate values for the three most recent consecutive years of production.

If insufficient data are available for initial audits, the UoC shall demonstrate how they will collect and calculate values once production data are available (after first production cycle if using Option A or, on an interim basis, after one year of continuous production if using Option B).

All energy use and GHG data calculations may be undertaken at a site-specific or multi-site scale. If calculating values for multiple sites together, all sites included shall farm the same species, use the same production method, and be located in the same country.

9.3 On-site energy use (Indicator 2.10.1)

Energy use of production is calculated as megajoules of energy per tonne of net live weight production (MJ/t). The required scope of activities and inputs to include in energy use calculations is provided in Table 1.

Table 1 Energy inputs required in energy consumption calculations for Indicator 2.10.1.

Included

Excluded

Fuels used for heating, generators, equipment

Employees vehicles and travel

On-grid electricity used for production

Energy use by employees housing, offices and other non-production facilities

District heating and cooling used for production

Energy inputs to processing or other downstream (post-production) activities

Fuel inputs to vessels, owned or contracted, including barges, well boats and vessels servicing sites

Energy inputs to feed mills, hatcheries and other upstream (pre-production) activities

Fuel and electricity used during fallow period preceding production

On-site energy use shall be calculated using the following formula:

E=(Qi×Di)P E=frac{({Q}_{i}times {D}_{i})}{P}

Where:

  • E is the energy use in MJ/t.

  • Qi is the quantity of energy input i

  • Di is the energy density of input i as listed in Table 2.

  • P is the net live weight production in tonnes.

To facilitate calculations, energy densities are automatically calculated when submitting energy use data to ASC.

Table 2 Energy density values for calculation of energy consumption.

Energy input

Units

Energy density (MJ per unit)

Electricity

kWh

3.6

Diesel

L

38.2

Petrol/gasoline

L

34.4

Fuel oil

L

42.6

Natural gas (gaseous)

m3

39.8

Liquid natural gas

L

22.6

Liquid petroleum gas

L

26.1

Biomass

kg

15.2

Biodiesel

L

30.2

Biogas

kg

19.9

Source: DESNZ (2022)140140DESNZ (2022). Greenhouse gas reporting: Conversion factors 2022. United Kingdom Department for Energy Security and Net Zero. Available at https://www.gov.uk/government/publications/greenhouse-gas-reporting-conversion-factors-2022

9.4 GHG emissions (Indicator 2.10.2)

GHG emissions are calculated following an attributional life cycle assessment approach (Figure 1). Emissions are calculated and reported in units of kg carbon dioxide-equivalent (CO2e) per tonne of live weight production and then converted to kg CO2e per kg of edible product to inform target-setting and tracking the GHG Management Plan.

Figure 1 System boundaries for calculating GHG emissions of aquaculture products, showing included processes for feed (shaded) and farm stages.

Calculation of GHG emissions for ASC is categorised following the emission scopes defined by the Greenhouse Gas Protocol (WRI, 2004141141World Resources Institute (WRI). (2004). The Greenhouse Gas Protocol: A Corporate Accounting and Reporting Standard. Washington, D. C.: World Resources Institute.). To ensure comparability of GHG data between ASC-certified sites, a consistent application of these scopes is used, including activities and inputs listed for each in Table 3.

Table 3 Included inputs and activities for GHG emissions calculations according to Greenhouse Gas Protocol scope.

Scope 1

Fuels used for heating, generators, equipment, vessels (including owned or contracted, well boats, etc.)

Fuels used during fallow periods

Scope 2

Electricity and district heating/cooling used for production

Electricity and district heating and cooling used during fallow periods

Scope 3

Production of juveniles if transferred from another grow out facility (salmon only)

Production and processing of feeds and transport of feeds to site

Production and processing of fuels

Production of liquid oxygen (RAS systems only) and fertilisers (pond systems only)

ASC accepts two methods of handling co-product allocation in GHG accounting: mass allocation and economic allocation. This methodological choice affects GHG emission factors for feed ingredients as well as processing of fish products, if applicable. Farms may follow one or both allocation methods. Feed mills are required to provide farms GHG data specific to the allocation method requested. If farms are using the ASC GHG Calculator or another tool that supports both methods, and have data from their feed suppliers reflecting both methods, they shall subsequently report GHG values following both methods.

UoCs are highly encouraged to use the ASC GHG Calculator or another tool to support GHG calculations. If undertaking calculations manually, the following equations shall be used to calculate Scope 1 (Appendix 9 (9.4.1)), Scope 2 (Appendix 9 (9.4.2)) and Scope 3 (Appendix 9 (9.4.3)) emissions. Each calculation requires a combination of input quantities and their corresponding emission factors, which must be documented alongside calculations.

9.4.1 Scope 1 GHG Emissions

Scope 1 GHG emissions shall be calculated using the following formula:

S1=(Qi×Gi)P {S}_{1}=frac{({Q}_{i}times {G}_{i})}{P}

Where:

  • Qi is the quantity of fuel input i.

  • Gi is the Scope 1 emission factor of input i as listed in Table 4.

  • P is the net live weight of production in tonnes.

Table 4 Greenhouse gas intensity (kg CO2e/unit), according to Greenhouse Gas Protocol scope, for calculation of Scope 1 and Scope 3 emissions from on-site energy use.

Energy input

Units

Scope 1

Scope 3

Diesel

L

2.71

0.63

Petrol/gasoline

L

2.34

0.60

Fuel oil

L

3.18

0.70

Natural gas (gaseous)

m3

2.02

0.35

Liquid natural gas

L

1.16

0.40

Liquid petroleum gas

L

1.56

0.18

Biomass

kg

0.06

0.08

Biodiesel

L

0.17

0.39

Biogas

kg

0.01

0.13

Source: DESNZ (2022)140140DESNZ (2022). Greenhouse gas reporting: Conversion factors 2022. United Kingdom Department for Energy Security and Net Zero. Available at https://www.gov.uk/government/publications/greenhouse-gas-reporting-conversion-factors-2022

9.4.2 Scope 2 GHG Emissions

Scope 2 GHG emissions shall be calculated using the following formula:

S2=(Qi×Gi)P {S}_{2}=frac{({Q}_{i}times {G}_{i})}{P}

Where:

  • Qi is the quantity of electricity or district heating used.

  • Gi is the country-specific emission factor of electricity or district heating.

  • P is the net live weight of production in tonnes.

9.4.3 Scope 3 GHG Emissions

Scope 3 emissions associated with feed ingredients and milling shall be calculated using the following formula:

S3(Feed)=(Qf×Gf,a)P {S}_{3(Feed)}=frac{({Q}_{f}times {G}_{f,a})}{P}

Where:

  • Qf is the total quantity of feed f used.

  • Gf,a is the emissions, per tonne of feed f, for each ingredient group a (and milling) as provided by the feed supplier.

  • P is the net live weight of production in tonnes.

Scope 3 emissions from feed transportation to sites shall be calculated using the following formula:

S3(Feed transport)=(Qf×Tf,m×Gm)P {S}_{3(Feed transport)}=frac{({Q}_{f}times {T}_{f,m}times {G}_{m})}{P}

Where:

  • Qf is the quantity of feed f used.

  • Tf,m is the transportation distance in kilometres (km) by transport mode m (e.g., truck, sea).

  • Gm is the emission factor per tonne-km of transport by mode m.

  • P is the net live weight production in tonnes.

Scope 3 emissions associated with (production of) fuels and other inputs (e.g., liquid oxygen) shall be calculated using the following formula:

S3(Other)=(Qi×Gi)P {S}_{3(Other)}=frac{({Q}_{i}times {G}_{i})}{P}

Where:

  • Qi is the quantity of fuel or other input.

  • Gi is the scope 3 emission factor (Table 4 for fuels) for input i.

  • P is the net live weight production in tonnes.

9.5 Target-setting for GHG management plans (Indicator 2.10.3)

Species-specific targets serve as a basis for understanding the relative emissions of aquaculture production and guiding reduction efforts in GHG management plans (Table 5). These are based on average species-specific estimates of GHG intensity from Gephart et al. (2021)142142Gephart, J. A., Henriksson, P. J., Parker, R. W., Shepon, A., Gorospe, K. D., Bergman, K., … & Troell, M. (2021). Environmental performance of blue foods. Nature, 597(7876), 360-365.. They will be regularly updated based on data submitted to ASC to support target-setting and tracking relevant to different species and production systems. Farms are not required to meet these targets but they serve as guidance to inform reduction efforts in the GHG management plans.

Table 5 Species-specific GHG targets to incorporate into GHG management plans.

kg CO2e / kg edible

kg CO2e / tonne live

Species group

Mass

Economic

Mass

Economic

Abalone

3.2

3.2

650

650

Bivalves

3.2

3.2

650

650

Catfish

10.0

6.5

5,000

3,200

Cod

10.0

6.5

5,000

3,200

Crustaceans

9.5

7.8

5,400

4,400

Flatfish

10.0

6.5

5,000

3,200

Salmonids – freshwater

5.4

3.7

3,200

2,100

Pangasius

7.8

6.1

4,200

3,200

Pike-perch

10.0

6.5

5,000

3,200

Salmonids – marine

5.1

3.0

3,000

1,700

Seabass, seabream, meagre

10.0

6.5

5,000

3,200

Seriola and cobia

10.0

6.5

5,000

3,200

Tilapia

10.8

8.8

4,000

3,300

Tropical marine finfish

10.0

6.5

5,000

3,200