Blast Furnace Ethanol Reaches Commercial Scale. What the Data Shows

The Jingtang Phase II facility in Hebei produced 99.9% purity bioethanol from blast furnace gas in June 2026, and the same quarter delivered ISCC EU certification, making this the first commercially demonstrated, market-certified recycled-carbon fuel from steel-mill waste gas in the world.
By Muflih Hidayat -
Blast furnace off-gas fermentation yields 99.9% anhydrous bioethanol at Shougang Jingtang steel mill, Hebei 2026
  • The Jingtang Phase II facility produced 99.9% anhydrous purity bioethanol from blast furnace gas in June 2026, the first time fuel-grade ethanol has been made at commercial demonstration scale through biological synthesis of steel-mill waste gas.
  • A Beijing Shougang LanzaTech subsidiary secured ISCC EU certification on 14 September 2026 via SCS Global Services, the first certification of its kind globally in the recycled carbon fuel sector, opening legal access to European transport and SAF markets under RED III.
  • Phase II is designed to deliver three revenue streams from a single waste-gas feed: 15,000 tonnes of anhydrous ethanol, 750 tonnes of microbial feed protein, and 2 million cubic metres of biogas per year, a circular output structure that permanent carbon storage cannot replicate.
  • Two independently operated blast-furnace-gas fermentation plants now produce commercial output on two continents (Jingtang in China and Steelanol at ArcelorMittal Ghent in Belgium), establishing gas fermentation as a replicable platform rather than a one-off demonstration.
  • The IEA revised its steel-sector CCUS capture projection down 40% between 2021 and 2023, from 670 Mt/yr to roughly 399 Mt/yr, signalling that gas fermentation and utilisation pathways occupy a real but bounded role of approximately 15% of sector reductions, not a dominant decarbonisation backbone.
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In June 2026, a steel mill in Hebei Province produced anhydrous ethanol at 99.9% purity directly from its own waste gases. Not from corn. Not from sugarcane. From the coke-oven and converter off-gas that pours out of a blast furnace.

This is the first time fuel-grade ethanol has been produced at commercial demonstration scale through biological synthesis of blast furnace and converter gas, rather than crop fermentation or fossil-fuel processing. For anyone who assumed blast furnace steelmaking was a stranded asset in a decarbonising world, that fact deserves a second look.

The Shougang LanzaTech Jingtang facility sits at an unusual intersection: a profitable, operating steel mill on one side, and a certified, revenue-generating carbon-utilisation product on the other. Two things that rarely meet at scale. The wider decarbonisation conversation usually presents hydrogen-based direct reduction and scrap maximisation as the only credible routes forward, yet Phase II trial production and ISCC EU certification (granted 14 September 2026) both landed in the same quarter, sharpening the commercial signal considerably.

Here is what the Jingtang data actually tells you about where this technology sits on the maturity curve, and whether gas fermentation is a genuine near-term pathway for hard-to-abate steel emissions or a well-certified detour from deeper structural change.

From waste gas to fuel-grade ethanol: what the Jingtang Phase II result actually means

Start with the process chain, because the result stands or falls on it. CO2-rich coke-oven and converter gas is pretreated, then fed to proprietary microbes that ferment it into ethanol. That output is distilled to roughly 95% concentration, then passed through a molecular sieve for dehydration, stripping the remaining water to reach 99.9% anhydrous purity.

That final purity figure is not a cosmetic detail. It is the specification threshold for transport-fuel blending, sustainable aviation fuel (SAF) feedstock, and industrial chemical applications. Lower-purity hydrous ethanol causes phase separation in gasoline blends, corrodes equipment, and fails downstream petrochemical processes. Anhydrous grade clears all of that.

Phase II is designed to deliver three output streams from a single waste-gas feed:

  • 15,000 tonnes of anhydrous ethanol per year
  • 750 tonnes of microbial feed protein per year
  • 2 million m3 of biogas per year

Company-wide ethanol production had already reached 52,762 tonnes across the first half of 2026, showing the platform is producing volume, not just running a demonstration line.

Jingtang Phase II Process & Output Breakdown

The purity result matters most when read alongside the certification. On 14 September 2026, a Beijing Shougang LanzaTech subsidiary secured ISCC EU certification via SCS Global Services, the first globally in the recycled carbon fuel sector. Under RED III, certified recycled-carbon fuels must demonstrate mandated emissions savings against fossil comparators to qualify for European transport and aviation markets.

The ISCC EU greenhouse gas methodology for recycled carbon fuels sets out the lifecycle accounting framework that certified products must satisfy, requiring demonstrated emissions savings against fossil comparators before qualifying for European transport and aviation markets under RED III.

The carbon math Shougang cites Producing 1 tonne of ethanol consumes approximately 0.5 tonnes of CO2. This is the figure the company uses to align the project with China’s dual-carbon policy goals.

Put the two together and the significance sharpens. The 99.9% purity result is what makes the ethanol technically usable in regulated fuel markets, and the ISCC EU certification is what makes it legally saleable into them. For an investor weighing the commercial maturity of gas fermentation, that combination moves the technology from promising pilot to market-accessible product. The three-output model of fuel, protein, and biogas also points to a circular revenue structure that permanent carbon storage, which generates no saleable product, simply cannot match.

Gas fermentation at commercial scale: how the technology reached this point

The Jingtang result did not arrive in isolation. It sits at the end of an eight-year deployment arc, and the pattern of that arc is more persuasive than any single milestone.

Phase I launched commercially at the Jingtang steel mill in May 2018, operating at a 10,000-tonne scale on steel-mill off-gas. Three years later, in April 2021, LanzaTech’s platform expanded beyond conventional steelmaking with the Shoulang Jiyuan plant in Ningxia, which uses ferroalloy off-gas as feedstock. Then came Phase II trial production in June 2026, targeting 15,000 tonnes per year of anhydrous ethanol at the same Jingtang site.

That is a coherent scale-up progression at a single location, and it is corroborated on a separate continent.

The Steelanol project at ArcelorMittal’s Ghent site in Belgium shipped its first commercial barge of ethanol on 11 December 2024, following a commercial ramp-up through 2023 and 2024. Its design capacity of roughly 80 million litres (around 63,000 tonnes) per year makes it the largest blast-furnace-gas fermentation deployment outside China. Reported capital cost sits at approximately 150 million euros, though this figure has not been independently confirmed.

Facility Location Feedstock Operational milestone
Jingtang (Phase I) Caofeidian, Hebei, China Steel-mill off-gas (blast furnace, converter) Commercial launch May 2018
Jingtang (Phase II) Caofeidian, Hebei, China CO2-rich industrial tail gas Trial production June 2026
Shoulang Jiyuan Ningxia, China Ferroalloy off-gas Operations began April 2021
Steelanol Ghent, Belgium (ArcelorMittal) Blast-furnace gas First commercial barge December 2024

The same timeline that proves replicability also reveals the friction. Multi-year gaps separate groundbreaking from commercial output. Capital requirements run into nine figures. Operations depend on stable waste-gas supply and complex integration with an existing mill. LanzaTech’s platform reports cumulative CO2 reductions of roughly 380,000 tonnes since commercial operations began, a meaningful number that took years and substantial investment to accumulate.

Two independently operated blast-furnace-gas fermentation plants, on two continents, both producing commercial output, clears the minimum bar for treating this as a platform rather than a one-off. What it tells you is that gas fermentation is commercially replicable, but neither fast nor cheap, and any timeline assumption about its wider role in steel decarbonisation should carry that weight.

Carbon utilisation versus permanent storage: the honest case for and against gas fermentation

Here is where the analysis gets genuinely contested, and it is worth holding both sides in view rather than resolving the tension prematurely.

The proponent case

Advocates including LanzaTech and Shougang make a clean argument. Gas fermentation converts waste gases into saleable products, generating revenue that permanent carbon capture and storage (CCS) cannot. It retrofits existing plant without replacing the core ironmaking process. It produces certified lower-carbon fuels that displace more carbon-intensive alternatives under regulatory lifecycle accounting. And it adapts to changing gas compositions, including the hydrogen-rich streams that steelmaking may shift toward over time.

The proponent position rests on a specific claim:

CCUS implementation economics vary significantly depending on whether the chosen pathway generates saleable product or requires permanent storage infrastructure, a distinction that determines both the capital structure and the operating revenue profile of competing decarbonisation routes at the facility level.

  • Waste gases are emitted anyway, so converting them into fuels that displace fossil alternatives delivers real near-term reductions
  • ISCC EU and RED III frameworks only recognise pathways that achieve mandated savings against fossil comparators, meaning certified fuels demonstrably cut emissions within the applicable accounting system
  • Revenue-generating utilisation can fund progress while structural solutions scale

The critical case

The Institute for Energy Economics and Financial Analysis (IEEFA) pushes back hard, and its April 2024 report on steel decarbonisation sets out why:

  • Utilisation pathways that yield fuels eventually re-emit their stored carbon when those fuels are burned
  • They do not eliminate the fossil inputs at the source of ironmaking
  • They risk locking in existing high-emissions infrastructure while diverting capital from hydrogen-DRI and scrap maximisation, which IEEFA views as more robust routes

IEEFA’s broader contention is that CCUS in steel, including utilisation, is unlikely to play a major role given high costs, energy intensity, and a thin record of large-scale success.

Neither side gets full comfort from the institutional numbers, and one figure captures the discomfort better than any other.

The chemistry underpinning blast furnace operations is central to why gas fermentation occupies the role it does: steel decarbonisation physics constrains every retrofit pathway, because the reduction of iron ore requires carbon at temperatures and reaction conditions that no current low-carbon substitute fully replicates at comparable cost.

The number neither side finds comfortable The IEA cut its projection for steel-sector CCUS capture from 670 Mt/yr (2021 Net Zero scenario) to about 399 Mt/yr in its 2023 update, a 40% downward revision.

That revision does not vindicate either camp. It does not kill the utilisation case, and it does not confirm CCUS as a decarbonisation backbone. What it signals is recalibration: institutions are trimming the expected role of these technologies, which matters directly for anyone modelling long-term steel pathways.

The IEA still assigns CCUS a real role, roughly 15% of steel-sector emissions reductions in its Clean Technology Scenario, with cumulative capture near 10 Gt CO2 by 2060. The World Economic Forum’s 2024 tracker estimates CCUS on the BF-BOF route could cut plant-level CO2-equivalent by up to 90%, while contributing around 13% of global steel emissions reductions by 2050.

CCUS Institutional Projections Dashboard

For the investment thesis, the read is this: the strongest version of the gas fermentation case is as a near-term, revenue-generating bridge for mills that will keep running blast furnace routes regardless, not as a permanent decarbonisation end-state. The analytical work that separates an informed position from a headline reaction is understanding exactly where those boundary conditions hold, and where they do not.

What the Jingtang milestone signals for investors in hard-to-abate sectors

So what should a serious investor or analyst now be watching, given everything the evidence has established?

Start with the commercial unlock that matters most. The ISCC EU certification connects Jingtang’s output directly to European transport and SAF fuel markets under RED III. That is not merely technical feasibility, it is a policy-reinforced revenue pathway. In a sector where most CCUS technologies are not expected to reach commercial availability until after 2028, according to the WEF, a certified, market-accessible product in 2026 is a genuine first-mover position.

The forward variables are not interchangeable. They matter in sequence:

  1. Whether Phase II reaches its 15,000 t/yr design throughput in sustained commercial operation, not just trial production, which was confirmed in June 2026 but is not yet proven at continuous scale
  2. Whether additional steel mills adopt the model, which would move gas fermentation from two-site platform toward genuine sector option
  3. Whether the policy environment in key markets, EU RED III and China’s dual-carbon framework, continues to support recycled-carbon fuel demand

There is a structural point worth sitting with. No commercial industrial waste-gas fermentation projects outside LanzaTech’s portfolio have been identified in accessible sources. That absence of competition is both a strength and a risk.

On the one hand, it hands LanzaTech’s platform a real near-term market window with no rival at scale. On the other, technology that has not faced competitive pressure has not been tested by market discipline either. The transition from trial to sustained commercial throughput at Phase II is the next hard data point that will tell you whether the window is being converted into durable position.

For mining and energy investors mapping decarbonisation exposure, this development does not displace the hydrogen-DRI thesis. It offers a different kind of optionality: revenue-generating rather than cost-absorbing, and specifically applicable to blast furnace assets that are not disappearing in the near term. That is a distinct exposure worth understanding on its own terms.

The hydrogen-DRI pathway represents the structural alternative most analysts cite as the deeper solution, but its commercial deployment timeline extends well beyond the near-term window in which blast furnace assets will continue operating across most major steel economies.

What the Jingtang result changes, and what it does not

The central finding is calibrated, not enthusiastic. Gas fermentation from blast furnace gas is now commercially demonstrated on two continents, certified for European fuel markets, and generating revenue. That changes its status from experimental pathway to validated near-term option for mills running existing blast furnace routes. Its arrival at the 2026 China Metallurgical Exhibition in late September marked its move into mainstream industry visibility.

Steel decarbonisation investment pathways diverge sharply by geography: North American mills face a different capital allocation calculus than their Chinese or European counterparts, with scrap availability, energy mix, and carbon pricing regimes producing materially different technology adoption sequences across the same global decarbonisation timeline.

What has not changed is just as important. The technology does not eliminate fossil inputs, does not permanently sequester carbon, and cannot make blast furnace steelmaking net-zero compatible on its own. It is a bridge, not a destination.

The IEA’s framing holds the whole thing in place: CCUS and utilisation are assigned a real but bounded role, roughly 15% of steel-sector reductions in the Clean Technology Scenario, and gas fermentation lives inside that bounded space.

The usable takeaway is a specific one. Treat this as one data point in a multi-pathway decarbonisation landscape, relevant precisely where blast furnace operations are medium-term fixtures and certified fuel markets are within reach. The sophistication of the view depends on holding both truths at once.

This article is for informational purposes only and should not be considered financial advice. Investors should conduct their own research and consult with financial professionals before making investment decisions. Past performance does not guarantee future results, and financial projections are subject to market conditions and various risk factors.

Frequently Asked Questions

What is bioethanol from blast furnace gas and how is it produced?

Bioethanol from blast furnace gas is fuel-grade ethanol made by feeding CO2-rich coke-oven and converter off-gas to proprietary microbes that ferment it into ethanol, which is then distilled and dehydrated to 99.9% anhydrous purity. Unlike conventional bioethanol, no crops are used; the feedstock is industrial waste gas that would otherwise be vented or flared.

What does ISCC EU certification mean for steel-mill gas fermentation ethanol?

ISCC EU certification confirms that the ethanol meets the greenhouse gas savings thresholds required under RED III, making it legally saleable into European transport and sustainable aviation fuel markets as a recycled-carbon fuel. The Jingtang subsidiary that received this certification on 14 September 2026 was the first in the recycled carbon fuel sector globally to do so.

How much ethanol is the Jingtang Phase II facility designed to produce?

Phase II targets 15,000 tonnes of anhydrous ethanol per year from a single waste-gas feed, alongside 750 tonnes of microbial feed protein and 2 million cubic metres of biogas annually. Company-wide ethanol production had already reached 52,762 tonnes across the first half of 2026, showing the broader platform is generating commercial volume.

Does gas fermentation from blast furnace gas make steelmaking net-zero compatible?

No. Gas fermentation converts waste emissions into saleable fuels but does not eliminate the fossil inputs at the core of blast furnace ironmaking, and the carbon is re-emitted when the fuel is burned. The IEA assigns CCUS and utilisation pathways roughly 15% of steel-sector emissions reductions in its Clean Technology Scenario, positioning gas fermentation as a near-term bridge rather than a structural end-state.

Which other facilities have commercially demonstrated blast furnace gas fermentation at scale?

The Steelanol project at ArcelorMittal's Ghent site in Belgium shipped its first commercial barge of ethanol on 11 December 2024, with a design capacity of roughly 80 million litres (around 63,000 tonnes) per year, making it the largest deployment outside China. Together with Jingtang, these two independently operated plants on two continents establish the technology as commercially replicable, though capital costs run into nine figures and multi-year gaps separate groundbreaking from commercial output.

Muflih Hidayat
By Muflih Hidayat
Mining & Energy Journalist
Muflih Hidayat is a Mining and Energy Journalist at Discovery Alert with over nine years in mining journalism and strategic communications. Winner of the 2025 Champion of Journalism award (PT Agincourt Resources, ASTRA Group) and the 2022 Subroto Award in Energy Journalism from Indonesia's Ministry of Energy and Mineral Resources, he is a member of the Association of Indonesian Mining Professionals (PERHAPI).
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