Atomfair Brainwave Hub: Hydrogen Science and Research Primer / Environmental Impact and Sustainability / Life Cycle Assessment (LCA) of Hydrogen Systems
The transition to hydrogen as a decarbonization tool in heavy industries such as steel and ammonia production presents a significant opportunity to reduce greenhouse gas emissions. However, the environmental benefits depend heavily on the production method, supply chain efficiency, and end-use applications. A life cycle assessment (LCA) approach is essential to evaluate the true sustainability of hydrogen-based alternatives compared to conventional processes.

### Steel Production: Conventional vs. Hydrogen-Based

Traditional steel manufacturing relies on the blast furnace-basic oxygen furnace (BF-BOF) route, which uses coking coal as both a reducing agent and energy source. This process emits approximately 1.8 to 2.2 metric tons of CO₂ per ton of steel produced. Direct reduced iron (DRI) using natural gas emits less, around 0.9 to 1.3 metric tons of CO₂ per ton of steel, but still contributes significantly to carbon emissions.

Hydrogen-based steelmaking, primarily through hydrogen-DRI or electrolytic reduction, eliminates CO₂ emissions at the point of production if green hydrogen (produced via electrolysis using renewable electricity) is used. However, the LCA must account for upstream emissions from hydrogen production.

- **Gray Hydrogen (SMR):** If hydrogen is produced via steam methane reforming without carbon capture, the emissions range from 9 to 12 kg CO₂ per kg of hydrogen. Using this in steelmaking reduces direct emissions but results in only marginal lifecycle benefits compared to natural gas-based DRI.
- **Green Hydrogen (Electrolysis):** With renewable electricity, electrolysis emits close to zero CO₂ during hydrogen production. The LCA shows a reduction of up to 95% in lifecycle emissions compared to BF-BOF routes. However, the energy intensity of electrolysis requires substantial renewable capacity.

Resource trade-offs include high water consumption for electrolysis (~9 liters per kg of hydrogen) and land use for renewable energy infrastructure. Mining for critical minerals (e.g., iridium for PEM electrolyzers) also introduces environmental burdens.

### Ammonia Production: Conventional vs. Hydrogen-Based

Ammonia is predominantly synthesized via the Haber-Bosch process, which consumes natural gas as both feedstock and energy source, emitting 1.6 to 2.4 metric tons of CO₂ per ton of ammonia. Hydrogen is a key input, and its production method dictates the lifecycle emissions.

- **Gray Hydrogen (SMR):** Conventional ammonia plants using SMR-derived hydrogen contribute heavily to emissions, with over 80% of the carbon footprint tied to hydrogen production.
- **Green Hydrogen (Electrolysis):** Switching to renewable-based hydrogen can reduce emissions by up to 90%. However, the Haber-Bosch process remains energy-intensive, requiring ~30 GJ per ton of ammonia even with clean hydrogen.

Alternative pathways, such as electrochemical ammonia synthesis, are in development but currently lack scalability. The LCA of green ammonia must also consider nitrogen sourcing—whether from air separation (energy-intensive) or alternative methods.

### Emission Reductions and Trade-Offs

The table below summarizes key LCA metrics for hydrogen-based steel and ammonia compared to conventional methods:

| Metric | Conventional Steel (BF-BOF) | H₂-Based Steel (Green H₂) | Conventional Ammonia (SMR) | H₂-Based Ammonia (Green H₂) |
|----------------------|----------------------------|---------------------------|---------------------------|-----------------------------|
| CO₂ Emissions (t/t) | 1.8 - 2.2 | 0.1 - 0.3 | 1.6 - 2.4 | 0.2 - 0.4 |
| Energy Input (GJ/t) | 20 - 25 | 25 - 30 | 28 - 35 | 30 - 40 |
| Water Use (kl/t) | 2 - 4 | 3 - 6 | 1 - 3 | 5 - 8 |

While hydrogen decarbonization drastically cuts CO₂ emissions, it increases energy and water demands. Renewable energy availability is critical—regions with low renewable penetration may see limited benefits if grid electricity powers electrolysis.

### Resource and Infrastructure Challenges

The scalability of hydrogen-based industries depends on:
- **Renewable Energy Supply:** Green hydrogen requires 50-55 kWh per kg, necessitating vast wind or solar farms.
- **Hydrogen Storage and Transport:** Compression or liquefaction adds energy penalties (10-30% loss). Ammonia and LOHCs as carriers introduce additional conversion losses.
- **Material Requirements:** Electrolyzers and fuel cells need platinum-group metals and rare earths, raising concerns over supply chain sustainability.

### Conclusion

Hydrogen can decarbonize steel and ammonia production effectively, but only if the hydrogen is produced renewably. The LCA reveals substantial emission reductions with green hydrogen, albeit with higher energy and water footprints. Transitioning at scale demands integrated renewable infrastructure, efficient storage solutions, and careful resource management to avoid shifting environmental burdens. Policymakers and industries must prioritize holistic lifecycle planning to ensure hydrogen’s role in decarbonization is both effective and sustainable.
Back to Life Cycle Assessment (LCA) of Hydrogen Systems