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2026-rc.1 (Release Candidate)

Release note · Release date: October 27, 2026

What changed

Cornerstone EEIO 2026 combines USEEIO’s detailed picture of the US economy with CEDA’s global coverage and trade modeling, representing a step change improvement to both models.

Three groups of improvements sit behind the changes.

  1. A more current picture of the US economy that accounts for imports. US input-output tables are rebuilt for every year from 2017 to 2024, manufacturing uses facility-reported emissions, and imports are modeled where they are made.

  2. Newer data for Europe, the UK and China, and better gap-filling for the rest. Europe moves from the OECD’s ICIO tables to Eurostat’s FIGARO (through 2023). China moves to the latest National Bureau of Statistics tables (through 2023), with more sectors. Countries without data are filled with the auto-balanced structural reflection method.

  3. A validation process that feeds back into the model. Third-party benchmarks review the sectors behind about 50% of global emissions. Gaps are traced and fixed in the data or the method and documented when unresolved.

Together these make the 2017–2026 time series possible.

Why do these improvements matter?

They translate real world changes to corporate footprints. Three examples show how:

New data for China

Cornerstone adopts the most recent economic data released by the Chinese National Bureau of Statistics (2023 vs. 2020), which reflects methodology changes, changes in the economic structure, and sector-specific decarbonization.

For example, China’s battery factor rises by ~30% driven by a change in the composition of battery production in China. From 2020 to 2023, battery production more than tripled, but more importantly it shifted to require more Lithium-ion and less Lead-acid as inputs. This is because the majority of the market growth in batteries are in EVs and grid storage that require lithium-ion. Lithium-ion needs lithium chemicals and power-hungry cell factories, being more carbon intensive per dollar than lead-acid batteries, driving the emission factor up.

Stacked bar chart of China battery production. In 2020, output was 382 GWh, mostly lead-acid. In 2023, output was 1,183 GWh, mostly lithium-ion.

Figure 1:China battery production, 2020 and 2023. Output in GWh. The split by battery type is approximate. Sources: NBS input-output tables 2020 and 2023; MIIT; China lead-acid battery industry statistics.

New data for Europe

Cornerstone adopts the most recent release of FIGARO, Eurostat’s official input-output and emissions dataset. FIGARO is more granular than the OECD dataset for Europe, is available as a time series through 2023, and is updated every year, matching Cornerstone’s release cadence.

This data update lowers European factors by about 4% in median. The most significant change is in electricity factors, which fall in every EU country. This change is driven by an increase in renewable energy and by an increase in energy prices due to the gas-supply shocks the Ukraine war has caused in Europe. For example, Germany’s power factor fell by 60%, as renewables grew from 35% to over 50% of generation and wholesale power prices more than doubled.

Bar showing that about 25% of the fall in Germany's power emission factor comes from a cleaner grid and about 75% from higher prices.

Figure 2:Germany’s power emission factor falls by 60%. About 25% of the change comes from a cleaner grid, as renewables grew from 35% to over 50% of generation, and about 75% from higher prices, as wholesale power prices more than doubled, from about €44 to €95 per MWh. Sources: Ember, Öko-Institut, SMARD, Vattenfall.

Incorporation of imports in the US

USEEIO treated the US as a closed economy: every product used in the US was assumed to be made in the US. Cornerstone uses trade data to model each import in the country that produced it. Many imports come from more emissions-intensive economies such as China and India, so US factors tend to rise by 10 to 30% on average. This is the main upward pressure and the main reason for the change for USEEIO users. One example is light trucks and utility vehicles. The US factor rises by ~24%, mostly because many of their components are now modeled as imports from the countries that make them. Public data suggests that about 60% of the components of a US-assembled light truck are imported, with Mexico the largest source, followed by Europe and Canada (see Figure 3).

One horizontal stacked bar showing the estimated origin of light-truck components. Made in the US 41%. Imported: Mexico 24%, Europe 7%, Canada 6%, China 5%, Japan 5%, ASEAN 4%, South Korea 4%, other 4%.

Figure 3:Estimated origin of the components of a US-assembled light truck. Sources: NHTSA AALA parts content data; International Trade Administration data as reported by MNI (March 2025).

How do the emission factors change?

The charts compare the new factors with each model they replace.

Two waterfall charts. Against CEDA 2025, the factor goes from 0.6942 to 0.5324 (23.3% lower), with data updates adding 5.8% and methodology changes removing 27.5%. Against USEEIO v1.4 for the US, it goes from 0.2474 to 0.2454 (0.8% lower), with data updates adding 0.4% and methodology changes removing 1.2%.

Figure 4:Emission factors fall 23.3% against CEDA 2025 and 0.8% against USEEIO v1.4 (US). Production-weighted totals in kg CO₂e per 2024 USD, split into data updates and methodology changes.

For a more detailed summary of the changes against USEEIO or CEDA, please refer to Summary of changes vs. USEEIO and Summary of changes vs. CEDA. The full list of data and methodology changes is in the Change log. For even additional details or custom support on how to navigate the changes in your footprint, sign up for a demo of the enterprise product here.

Applies to: 2026-rc.1 · Last reviewed: 2026-rc.1