Low-carbon fuel life-cycle evaluation for shipping
Shipping can use several fuels types, and the industry is exploring alternatives to conventional heavy fuels that can help the sector decarbonise. The assessment method of fuels significantly impacts whether they are considered “low carbon”. Life-cycle assessment accounts for greenhouse gas (GHG) emissions at all stages of the fuels’ production and consumption, including the emissions of the energy used to produce and deliver the fuel, in addition to the direct emissions from the vehicle or vessel and end-of-life disposal.
Comparing fuels based solely on direct CO2 emissions - currently the norm - can lead to misleading conclusions about the climate impacts of fuels. Fuels such as Liquefied Natural Gas (LNG) or methanol produced using fossil fuels have lower direct CO2 emissions than conventional maritime fuel. However, a life-cycle-based evaluation that includes other greenhouse gases like methane and upstream fuel production emissions suggests their GHG benefits are marginal at best.
Equally, the life-cycle approach highlights that several new alternatives can only be considered low-carbon if they are produced sustainably. Some new fuels, if produced using fossil-fuels or fossil-based energy, are in fact worse than what they are intended to replace. Fuels that can have low life-cycle emissions when produced sustainably are: biofuels, hydrogen, synthetic hydrocarbons, ammonia and electricity.
Biofuels are primarily produced from biomass. They can be blended into petroleum-based shipping fuels and used in existing infrastructure. There are three main production pathways: biochemical, oleochemical/lipid, and thermochemical (see ITF, 2020 for a detailed explanation).
Hydrogen has potential appeal for shipping, either as hydrogen fuel cells to power electric motors or as a liquid fuel in combustion engines (alone or in a dual fuel combination). However, hydrogen produced from fossil fuels has a significant upstream GHG footprint. So on a life-cycle basis, hydrogen can only be considered low-carbon if generated using more sustainable processes. Water electrolysis is the most promising of these as, if renewable electricity is used, almost all GHG could be eliminated from the process. But it is more expensive. Applying carbon capture and storage (CCS) to fossil fuel-based hydrogen can reduce the life-cycle emission intensity by 60-70%. Methane pyrolysis (anaerobic decomposition of natural gas) is in the early stages of investigation, but could theoretically reduce GHG emissions by 90% compared to conventional methane reformation based hydrogen.
Synthetic hydrocarbons (or electrofuels where the hydrogen is derived from the electrolysis of water) are produced by combining hydrogen with carbon building blocks. They can be produced as a gaseous or liquid and blended with petroleum-based fuels or used in substitution. The carbon footprint inherent in producing the hydrogen and carbon elements used dictates the carbon intensity of the resulting synthetic fuel. These fuels become more attractive as the cost of renewable electricity used in production falls.
Ammonia, like hydrogen, has zero direct CO2 emissions. It has some advantages over hydrogen, including easier storage, greater energy density, and it is not explosive. Safety protections are needed, however, as it is toxic. Ammonia is also more difficult to ignite than pure hydrogen. It needs to be used in conjunction with a starter (pilot) fuel. If a fossil fuel (such as diesel) is used, it reduces the emission-reduction potential of ammonia. However, sustainably produced hydrogen, biofuels or synthetic fuels could be used as the starter fuel to keep emissions low. Whichever method of hydrogen production is used impacts the life-cycle emissions of the ammonia and the energy efficiency of the ammonia production itself. Currently, most ammonia is produced using fossil fuel-based hydrogen.
Electricity also has zero direct emissions. The way electricity is generated impacts its life-cycle emissions. For it to be considered low-carbon, it must be produced from low carbon energy sources. Life-cycle emissions from the use of electricity in ships are also affected by batteries and other component manufacture emissions, which must be reduced.
The GHG impacts of this measure will be dependent on the extent to which the industry adopts low-, or zero-life-cycle carbon fuels.
Life-cycle GHG emissions of different fuel options (conventional and alternative) per kWh of shaft work are listed below, drawn from ITF analysis based on Balcombe et al. (2019); Parkinson et al. (2019); Kortsari et al. (2020); Pavlenko et al. (2020):
- Ammonia (methane pyrolysis): 341.6 gCO2e/kWh to 743 gCO2e/kWh
- Ammonia (renewables): 44.3 gCO2e/kWh to 252 gCO2e/kWh
- Ammonia (SMR): 820.5 gCO2e/kWh to 1400 gCO2e/kWh
- Ammonia (SMR+CCS): 241.5 gCO2e/kWh to 745 gCO2e/kWh
- Biochemical ethanol (Advanced): 90 gCO2e/kWh to 160 gCO2e/kWh
- Biochemical ethanol (sugar based): 190 gCO2e/kWh to 300 gCO2e/kWh
- Bio-methane: 220 gCO2e/kWh to 460 gCO2e/kWh
- Bio-methanol & DME: 40 gCO2e/kWh to 290 gCO2e/kWh
- Electricity (nordic region): 43 gCO2e/kWh to 327 gCO2e/kWh
- Heavy fuel oil (HFO): 680 gCO2e/kWh to 769 gCO2e/kWh
- Hydrogen (methane pyrolysis): 347.5 gCO2e/kWh to 939 gCO2e/kWh
- Hydrogen (renewables): 66.7 gCO2e/kWh to 439 gCO2e/kWh
- Hydrogen (SMR): 759.4 gCO2e/kWh to 1295 gCO2e/kWh
- Hydrogen (SMR+CCS): 223.5 gCO2e/kWh to 689 gCO2e/kWh
- Liquefied natural gas (LNG): 547 gCO2e/kWh to 769 gCO2e/kWh
- Marine diesel oil (MDO): 643 gCO2e/kWh to 727 gCO2e/kWh
- Methanol (from fossil fuels): 700 gCO2e/kWh to 970 gCO2e/kWh
- Oleochemical biofuel (FAME): 90 gCO2e/kWh to 450 gCO2e/kWh
- Oleochemical biofuel (HVO): 220 gCO2e/kWh to 410 gCO2e/kWh
- Thermochemical FT-diesel: 32 gCO2e/kWh to 49 gCO2e/kWh
- Thermochemical pyrolysis oil: 241 gCO2e/kWh to 342 gCO2e/kWh
A set of life-cycle criteria need to be defined and adopted for this measure to take effect. The current International Maritime Organization (IMO) Energy Efficiency Design Index (EEDI) for ships uses only direct CO2 emissions in its calculations. As part of the European Green Deal, a proposal is being developed to establish a common EU regulatory framework to limit the yearly GHG intensity of the energy used on-board by a ship and increase the share of renewable and low-carbon fuels in the fuel mix of international maritime transport. The proposed approach would establish the methodology and the formula that should apply to calculate the yearly average GHG intensity of the energy used on-board, impose limits and a verification and monitoring process.
Almost all low-carbon fuels have lower energy density, so more is needed to achieve the same energy release. This can require larger tanks, impacting a vessel’s overall capacity. Additionally, there is the cost of retrofitting existing vessels or infrastructure or developing dedicated infrastructure.
Currently, sustainably producing hydrogen, ammonia and synthetic hydrocarbons costs more than production by fossil fuels, and this is expected to remain the case in the medium term. The International Energy Agency (IEA) estimates production costs for ammonia at USD 140/MWh (when electricity is USD 50/MWh, at 3 000 hours for the hydrogen electrolysers), and USD 70/MWh (when electricity is priced at USD 25/MWh). IHS Markit estimate the cost of current ammonia production (steam methane reforming (SMR)) at roughly USD 50/MWh.
Adopting life-cycle based evaluation for low- and zero-carbon fuels in shipping can encourage similar fuel evaluations in other sectors, thereby encouraging more widespread use of truly low-carbon fuels across the economy.
There are concerns around the sustainability impacts of biofuels, including land use and land use change. For example, clearing natural carbon sinks, such as forests, to cultivate biomass for biofuel production would likely increase the life-cycle GHG emissions. To be truly low carbon on a life-cycle basis, feedstocks for biofuels would have to be sustainably sourced.
Some alternative fuels have higher NOx emissions or pose safety and toxicity risks, which need to be managed.
Regulatory approaches, such as energy efficiency standards for new ships (EEDI) and existing ships (EEXI), carbon intensity indicators, and fuel blending mandates, can be used to encourage the uptake of these fuels, as can economic measures such as low-carbon fuel standards, financial measures and abolishing subsidies for fossil fuels and engine standards for short-lived climate pollutants.
ITF (2021) Transport Climate Action Directory – Life-cycle evaluation of low-carbon shipping fuels
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