Compliance · Carbon accounting

Carbon Accounting, Measurement and Methodology in Australia: The Complete GHG Protocol and AASB S2 Alignment Guide.

Carbon accounting is the systematic process of measuring, recording, and reporting an organisation’s greenhouse gas (GHG) emissions across its operations and value chain. For Australian entities subject to AASB S2 mandatory climate disclosure obligations, rigorous carbon accounting is not optional. It is the quantitative foundation on which compliant, credible, and assurance-ready disclosure depends.

This guide provides a definitive reference on carbon accounting methodology for Australian organisations. It covers the GHG Protocol framework, Scope 1, 2, and 3 measurement approaches, data collection and estimation methods, baseline setting, and the data governance practices required to meet assurance requirements under AASB S2.

carbon accounting at a glance

framework

GHG Protocol Corporate Standard

primary

gases

CO2, CH4, N2O, HFCs, PFCs, SF6, NF3

seven

scopes

direct, energy, value chain

1 · 2 · 3

boundary

operational control or equity share

disclosed

factors

National Greenhouse Accounts Factors

DCCEEW

unit

metric tonnes CO2 equivalent

tCO2-e

Emissions = Activity Data x Emissions Factor

The basics

What is Carbon Accounting?

Carbon accounting is the process of identifying, quantifying, and reporting greenhouse gas emissions in a systematic and standardised way. In corporate practice, carbon accounting follows established international methodologies, primarily the GHG Protocol Corporate Accounting and Reporting Standard, to produce emissions inventories that are comparable, consistent, and verifiable over time.

Under AASB S2, Australian entities are required to disclose their Scope 1, Scope 2, and Scope 3 GHG emissions, measured in metric tonnes of carbon dioxide equivalent (tCO2-e). The emissions intensity, boundaries, and calculation methodologies applied must be disclosed alongside the quantitative data to allow users to assess the quality and reliability of the information.

The framework

The GHG Protocol: Australia's Primary Carbon Accounting Framework

The GHG Protocol Corporate Accounting and Reporting Standard, published by the World Resources Institute and the World Business Council for Sustainable Development, is the primary international framework for corporate carbon accounting. AASB S2 explicitly references the GHG Protocol as the preferred methodology for emissions measurement.

The GHG Protocol framework defines

Seven greenhouse gases: the gases that must be included in corporate inventories: CO2, CH4, N2O, HFCs, PFCs, SF6, and NF3
Three emission scopes: Scope 1, Scope 2, and Scope 3, and the boundaries that determine which emissions fall within each scope
Organisational boundary approaches: equity share and operational control, which determine which operations an entity must account for
Base year protocol: for establishing a historical reference point from which emissions trends are measured
Quality criteria: completeness, consistency, accuracy, transparency, and relevance, which underpin credible carbon accounting

Emission scopes

Understanding Emission Scopes: Scope 1, 2, and 3

The three emission scopes are the foundation of every AASB S2 disclosure. Each is defined and treated differently under the GHG Protocol, and each requires distinct measurement methods and data sources. For a focused, plain-English breakdown of all three, including the full 15 Scope 3 categories and how each scope is disclosed under AASB S2, read our complete guide to Scope 1, 2 and 3 emissions.

Scope 1 Emissions: Direct Emissions

Owned or controlled sources

Scope 1 emissions are direct greenhouse gas emissions from sources owned or controlled by the reporting entity. They arise from physical or chemical processes where GHGs are released directly into the atmosphere. Common Scope 1 sources for Australian organisations include:

Stationary combustion: emissions from burning fuels in boilers, furnaces, and generators on-site
Mobile combustion: emissions from fuel combustion in vehicles, aircraft, ships, and other mobile equipment owned or controlled by the entity
Fugitive emissions: intentional or unintentional releases of GHGs, including refrigerant leakage, coal mine methane, and oil and gas system leaks
Process emissions: GHGs released as a result of industrial processes, such as cement calcination, steel production, and chemical manufacturing

Scope 1 emissions are typically the most straightforward to measure directly, using fuel consumption data multiplied by GHG Protocol or Australian Government emissions factors. They are also the focus of first-year mandatory assurance requirements under AASB S2.

Scope 2 Emissions: Indirect Energy Emissions

Purchased energy

Scope 2 emissions are indirect greenhouse gas emissions from the generation of purchased or acquired energy (primarily electricity, steam, heat, or cooling) consumed by the reporting entity but produced by a third party. Scope 2 is an accounting convenience: the entity does not directly control the source of the emissions but is responsible for the demand that drives them.

AASB S2 and the GHG Protocol require entities to report Scope 2 using two methods:

Location-based method: uses the average emissions intensity of the electricity grid in the region where the entity operates, applying national or regional grid emissions factors
Market-based method: uses emissions factors specific to the electricity the entity has contractually procured, including from renewable energy certificates (RECs), Power Purchase Agreements (PPAs), or supplier-specific emissions rates

In Australia, location-based Scope 2 calculations use the National Electricity Market (NEM) emissions intensity factors published by the Clean Energy Regulator under the NGER scheme. Market-based calculations must account for the retirement of relevant GreenPower or Large-scale Generation Certificate (LGC) instruments.

Scope 3 Emissions: Value Chain Emissions

Upstream and downstream

Scope 3 emissions are all indirect emissions (not included in Scope 2) that occur in the value chain of the reporting entity, both upstream and downstream. The GHG Protocol Scope 3 Standard organises these into fifteen categories across two groups, listed below.

For most Australian entities, purchased goods and services (Category 1), use of sold products (Category 11), and investments (Category 15, particularly relevant for financial institutions) will be the most material Scope 3 categories. A Scope 3 materiality screening should be conducted to identify priority categories for measurement before committing to full inventory development.

Upstream Scope 3 categories

Categories 1 to 8

Cat.

Downstream Scope 3 categories

Categories 9 to 15

Cat.

Organisational Boundaries: Defining What You Must Account For

Before measuring emissions, an entity must define its organisational boundary: the set of operations for which it will account in its GHG inventory. The GHG Protocol provides two approaches:

Operational Control

Most common in Australia

The entity accounts for 100% of emissions from operations over which it has operational control, meaning the authority to introduce and implement operating policies. Emissions from operations in which the entity has an equity interest but not operational control are excluded.

Equity Share

Proportional

The entity accounts for emissions in proportion to its equity share in each operation. A 60% equity stake in a joint venture, for example, means accounting for 60% of that venture’s emissions.

AASB S2

AASB S2 does not prescribe a boundary method but requires the chosen method to be disclosed and applied consistently across reporting periods. Operational control is the most commonly adopted approach for Australian entities, as it aligns most closely with the scope of management responsibility.

Calculation

Emissions Calculation Methods

Activity Data and Emissions Factors

The fundamental carbon accounting equation is: Emissions = Activity Data x Emissions Factor. Activity data is a quantitative measure of an activity that generates GHG emissions, for example litres of diesel consumed, kilowatt-hours of electricity used, or kilometres travelled. Emissions factors convert that activity data into an equivalent quantity of GHG emissions, expressed in tCO2-e.

Australian emissions factors for key energy and fuel types are published by the Australian Government’s Department of Climate Change, Energy, the Environment and Water (DCCEEW) through the National Greenhouse Accounts Factors publication. These are updated annually and represent the primary reference for NGER-aligned Scope 1 and Scope 2 calculations.

Emissions = Activity Data x Emissions Factor

The fundamental carbon accounting equation

Estimation Methods for Scope 3

Direct measurement of Scope 3 emissions is rarely achievable across all categories. Accepted estimation methods include:

Spend-based

Multiplying supplier spend data by emissions intensity factors derived from economy-wide input-output databases such as the Australian Industrial Ecology Virtual Laboratory

Physical activity-based

Multiplying quantities of goods or services purchased by product-level emissions factors from life cycle assessment databases

Supplier-specific

Using product carbon footprint data provided directly by suppliers, validated against recognised methodologies

Hybrid

Combining activity-based data where available with spend-based estimates for categories where activity data cannot be obtained

Entities should disclose the methods applied for each Scope 3 category and note where estimates involve significant uncertainty.

Baseline

Setting and Using a GHG Emissions Baseline

A baseline year is a historical reference point against which an entity tracks emissions performance over time. Establishing a meaningful baseline is foundational to demonstrating progress against climate targets and is required under AASB S2 when disclosing emissions reduction commitments.

A valid baseline year should be the earliest year for which reliable and complete emissions data is available. Where an entity has undergone significant structural changes (acquisitions, divestitures, or changes in organisational boundary), the base year inventory should be recalculated to ensure like-for-like comparability.

The GHG Protocol base year recalculation protocol specifies the triggers and methods for recalculating baseline emissions. Triggers include mergers and acquisitions, divestiture of significant operations, changes in calculation methodology, and the identification of significant errors in prior-year data.

Data quality

Data Quality, Audit Readiness, and Assurance Preparation

The quality of carbon accounting data determines whether disclosures are credible to investors and auditable by assurance providers. AASB S2’s phased assurance requirements (limited assurance from year two for Group 1, reasonable assurance from year four) mean that entities must design their data governance infrastructure with auditability in mind from the first year of reporting.

Key data quality principles for AASB S2-aligned carbon accounting include:

Principle

What it means

Completeness

All emission sources within the defined boundary are included, with any exclusions documented and justified

Consistency

Emissions are calculated using the same methodology across periods to enable meaningful trend analysis

Transparency

Data sources, emissions factors, calculation methods, and any assumptions or estimates are fully documented and available for review

Accuracy

Systematic errors are minimised through data validation procedures, cross-checks against NGER submissions, and use of current emissions factors

Relevance

The inventory reflects the GHG sources most significant to the entity’s operations and value chain

FAQ

Frequently Asked Questions: Carbon Accounting

What is the GHG Protocol and why does it matter for Australian entities?

The GHG Protocol Corporate Accounting and Reporting Standard is the globally recognised methodology for corporate greenhouse gas accounting. AASB S2 identifies the GHG Protocol as the primary framework for emissions measurement, meaning Australian entities subject to mandatory climate disclosure must apply GHG Protocol principles and definitions when preparing their emissions inventories. Entities may also reference the NGER Technical Guidelines for Australian-specific emissions factors, which are consistent with GHG Protocol methodology.

What is the difference between location-based and market-based Scope 2 reporting?

Location-based Scope 2 reporting uses the average emissions intensity of the electricity grid where the entity operates. In Australia, this is typically the NEM regional grid factor. Market-based Scope 2 reporting uses the emissions factor associated with the specific electricity supply contractually arranged by the entity, including renewable energy products. Entities that have purchased renewable energy through PPAs or GreenPower should disclose both figures, as AASB S2 requires both the location-based and market-based Scope 2 figures to be disclosed.

Are all fifteen Scope 3 categories required to be reported under AASB S2?

AASB S2 requires disclosure of Scope 3 emissions across all material categories. Entities are not required to disclose categories where emissions are immaterial or where the entity can demonstrate that the category is not applicable to its business model. However, a documented materiality screening process must be conducted and disclosed, explaining why excluded categories were determined to be immaterial. Entities cannot omit Scope 3 disclosures without documented justification.

What emissions factors should Australian entities use for Scope 1 calculations?

For Scope 1 calculations, Australian entities should use the National Greenhouse Accounts Factors published annually by DCCEEW. These factors cover stationary combustion, mobile combustion, and fugitive emission sources across the major fuel types used in Australian industry. NGER-registered entities will already be using these factors for their NGER submissions and can use the same data as a foundation for AASB S2 Scope 1 disclosures.

How should an entity handle data gaps in its Scope 3 inventory?

Data gaps are common in Scope 3 inventories, particularly for purchased goods and services and upstream supplier emissions. The GHG Protocol recommends using spend-based estimation methods as a starting point where supplier-specific data is unavailable. Entities should disclose the proportion of their Scope 3 inventory estimated using spend-based versus activity-based methods, and note categories where significant uncertainty exists. The expectation under AASB S2 is progressive improvement in data quality over time rather than complete data coverage in year one.

What is a base year recalculation and when is it required?

A base year recalculation is required when a significant structural or methodological change makes the base year inventory non-comparable with current-year data. Triggers include mergers, acquisitions, and divestitures that materially change the organisational boundary; changes in calculation methodology; and correction of significant errors in prior-year data. AASB S2 requires entities to disclose the reason for any base year recalculation and to restate prior-year data to ensure comparability across the time series presented.

How do carbon accounting requirements under AASB S2 differ from NGER reporting?

NGER reporting covers Scope 1 and Scope 2 emissions from large facility-level emitters and is submitted to the Clean Energy Regulator for regulatory compliance purposes. AASB S2 carbon accounting covers a broader scope, including Scope 3 value chain emissions, and is disclosed in annual reports for use by investors, lenders, and other financial statement users. NGER data provides a useful and auditable starting point for AASB S2 Scope 1 and Scope 2 disclosures but does not satisfy the full AASB S2 reporting requirement on its own.

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