25
1 INTRODUCTION
With over 80 percent of world merchandize trade
carried by sea. Maritime transport is considered the
most attractive option for transferring commodities
[1]. Maritime transport is as essential component of
world economy is responsible for safe delivery of
grains, food, solid and energy raw materials and
consumer goods [2].
Climate change is becoming a growing global
challenge, so reducing greenhouse gas (GHG)
emissions is essential. At the same time, global energy
demand is projected to increase by 28 % between 2015
and 2040. The sea transport sector is the largest user of
fossil fuels. The fuel consumption of shipping is
dominated by three type of ships: oil tankers,
container ships and bulk carriers. Ships carry on-
board thousands of metric tons of fuel for
consumption, which is great source of strong
environmental pollutants such as CO
2, NOX, SOx,
ozone, benzene and particulate matter (PM). At the
same time, the fuel oil price is increasing and public is
becoming more concerned about the environmental
footprint of shipping. Global CO
2 emissions have
exhibited a rapid increase. According to the
International Energy Agency (IEA), CO
2 emissions
from the transportation sector represented 24 % of
global CO
2 emissions during the year 2016. Maritime
transportation is a significant source of anthropogenic
SO
x and NOx emissions, which account for 13% of
global SO
x emissions and 15% of global NOx
emissions. [3].
The contribution of global carbon dioxide emission
from various sources is shown in Figure 1.
Alternative Fuels – Prospects for the Shipping Industry
M. Popek
Gdynia Maritime University, Gdynia, Pola
nd
ABSTRACT: Emissions from the sea transport sector are one of the major contributors to the climate change due
to extreme dependency on fossil fuels. Environmental revolution has pushed shipping to focus significantly on
the potential application of different cleaner fuels and sustainable source of energy solutions. The global
shipping industry is considering alternative fuel options that meet economic feasibility and safety requirements.
There is a variety of alternative fuel types available for shipping, such as liquefied natural gas (LNG), methanol,
hydrogen, ethanol, ammonia and others. For many years, the advantages and disadvantages of using selected
alternative fuels have been analysed from the point of view of sea transport costs. This paper presents the basic
parameters for comparing different fuels, the characteristics needed to adopt alternative fuels in maritime
transport. In addition, it provides an overview of the main technical challenges and drivers for the adoption of
alternative marine fuels assessed through infrastructural, economic and environmental dimensions.
http://www.transnav.eu
the
International Journal
on Marine Navigat
ion
and Sa
fety of Sea Transportation
Volume 18
Number 1
March 2024
DOI: 10.12716/1001.18.01.
01
26
Figure 1. Shipping contribution to global CO2 emissions.
Source: [4]
If treated as a country, international shipping
would have been the sixth largest emitter of energy-
related CO
2, just above Germany, with total emissions
in the range of 900 million tons of CO
2 per year [5]. A
various parts of shipping industry are actively
examining a number of ways to reduce emissions,
which are primarily linked to reducing fuel
consumption. In the longer time, the ship industry is
also exploring a number of alternative fuel source. In
April 2018 Marine Environment Protection Committee
(MEPC) adopted a resolution on the IMO's Initial
Strategy for reducing greenhouse gas (GHG)
emissions from international shipping. To address
such concerns, the International Maritime
Organization has proposed measures to reduce
greenhouse gas (GHG) emissions by at least 50% by
2050 [6]. International shipping needs to reduce its
Carbon Footprint (CF) by 40 % by 2030, and by at least
70 % by 2050 compared to 2008. Reductions in carbon
intensity are to be achieved by ships by implementing
the next steps of the Energy Efficiency Design Index
(EEDI) for new ships. On June 17, 2021 the IMO
accepted amendments to MARPOL VI during MEPC
76, introducing provisions for the Energy Efficiency
Existing Vessel Index (EEXI) and a requirements to
reduce the carbon intensity of operations through the
carbon intensity indicator (CII). The vessel’s achieved
EEXI indicates its energy efficiency compared to the
baseline. The ships achieved EEXI index will be then
compared to the required energy efficiency index of
the existing ship based on the corresponding
reduction factor expressed as a percentage of the
baseline value of the Energy Efficiency Design Index
(EEDI. EEXI generally applies to any vessel of 400
gross tonnage and above, while CII applies to vessels
of 5000 gross tonnage and above. As of January 1
st
2023 all ships are required to calculate the achieved
EEXI to measure their energy efficiency and begin
collecting data for annual operational CII. This means
that the first annual reports will be completed in 2023,
and initial CII assessment will be granted in 2024. To
mitigate sulphur emissions, from January 1
st
2020, the
limit for sulphur in fuel oil used on-board ships
operating outside designed Emission Control Areas
(ECAs) was reduced to 0.50 percent in global seas [7].
This will significantly reduce the amount of sulphur
oxides emanating from ships and should have health
and environmental benefits for the world, particularly
for populations living close to ports and costs. There
is an even stricter limit of 0.10 percent already effect in
ECAs, which have been established by IMO. This 0.10
percent m/m limit applies in the four established
ECAs: the Baltic Sea area; the North Sea area, the
North American area (covering designated coastal
areas of the U. S. and Canada); and the Caribbean Sea
area (around Puerto Rico and the United States Virgin
Islands). Annex VI of the International Convention for
the Prevention of Pollution from Ships (MARPOL)
also establishes limits for NO
x emissions from marine
diesel engines. The IMO emissions standards are
commonly referred to as Tier I, II and III. The Tier I
standards were defined in the 1993 version of Annex
VI, while Tier II and III standards were introduced
Annex VI amendments adopted in 2008.
While the IMO has not entered into any binding
agreements on decarbonisation, the European Union
(EU) is pushing for stricter GHG reduction
regulations within its jurisdiction. For example, the
"Fit for 55" package launched in 2021 aims to
transition the EU maritime sector to decarbonisation
by reducing greenhouse gas emissions by at least 55%
by 2030 compared to 1990 levels. In 2020 The
European Parliament passed a resolution to include
shipping in the European Emissions Trading System
from 2023, with a goal of achieving a 40% reduction in
CO
2 emissions by 2030 [1]. An alternative to reducing
shipping emissions and meeting regulations is to
switch from fossil fuels to new propulsion
technologies, such as alternative fuels. A special topic
of IMO discussion is the needs and possibilities of
countries in the process of energy transformation
towards low/zero emission alternative fuels for
shipping. The discussion emphasizes that the
decarbonization of international shipping is a priority
for IMO. The IMO Initial Strategy on the reduction of
GHG emissions from shipping sets key ambitions. The
IMO has set two main goals. The first is to reduce
annual greenhouse gas emission from international
shipping by at least half by 2050 compared to 2008
levels, and work towards phasing out GHG emissions
from shipping entirely as soon as possible in this
century [8].The second goal includes The Initial
Strategy, which aims to reduce the carbon intensity of
international shipping (to reduce emissions per
transport work) by at least 40% on average in
international shipping by 2030, aiming to reach 70%
by 2050 compared to 2008. Policy recommendations
comprise of increasing the stringency of operational
carbon intensity standards to encourage the move to
low-carbon fuels; an evaluation of well-to-wake
emissions; the mandating of zero-emissions ships; and
an acceleration of research, design and development.
Activities are also focused on solutions to overcome
barriers to global access to low and zero-emission
marine fuels. Attention is drawn to the current
scarcity of renewable fuels such as hydrogen,
ammonia and methanol. The Initial Strategy will be
revised by 2023.
The paper presents the basic parameters for
comparing of the following alternative fuels: LNG,
hydrogen, ammonia and methanol, the characteristics
needed to adopt alternative fuels in maritime
transport. In addition, it provides an overview of the
main technical challenges and drivers for the adoption
of alternative marine fuels assessed through
infrastructural, economic and environmental
dimensions.
27
2 CHARACTERISTIC OF ANALYSED FUELS
Currently, the dominant fuel in international shipping
is Heavy Fuel Oil (HFO) (79% of total fuel
consumption by energy value in 2018, based on cruise
allocation). However, significant changes in the fuel
mix have been observed in recent years. It was found
that HFO consumption decreased by approximately
7% (absolute reduction of 3%), while marine diesel
(MDO) and liquid nitrogen (LNG) consumption
increased by 6 and 0.9% (absolute increase of 51 and
26 respectively %). It is estimated that methanol has
become the fourth largest fuel consumption [9].
Different scenarios for climate targets and support for
sustainable and smart mobility strategies assume that
renewable and low-emission fuels should account for
between 6% and 9% of all fuels in international
maritime transport in 2030 and between 86% and 88%
by 2050 to contribute to the achievement of EU-wide
greenhouse gas emissions reduction targets [10].
There is a variety of alternative fuel types available for
shipping, such as gaseous fuels such as LNG, LPG,
methanol, hydrogen and ammonia, biofuels, fuel cells,
among others. The industry must choose the future
marine fuels by evaluating factors such as
environmental impact, technical performance,
availability, cost and infrastructure [11]. Among the
proposed alternative fuels for shipping, IMO has
identified LNG, hydrogen, ammonia, and methanol as
a most promising solution.
2.1 LNG
Natural gas, in the form of Liquefied Natural Gas
(LNG), is the most frequently used alternative fuel in
shipping [12]. LNG has been used to power the diesel
propulsion systems since the delivery of the Provalys
vessel in 2006.
LNG is a colourless and non-toxic liquid, that is
formed when natural gas is cooled to -162°C. During
this process, the volume of gas is reduced 600 times,
facilitating safer storage and transportation. LNG is a
cryogenic liquid that rapidly evaporates, when
exposed to normal atmospheric conditions. Such a
rapid phase transition phenomenon can lead to
critical risks, and the ignition of this flammable gas
mixture can cause catastrophic events in particular
fire and explosion [13]. LNG combustion is as
operationally efficient as HFO. LNG is considered one
of the most viable solutions, because it is the cleanest
fossil fuel used in shipping. The use of LNG as a fuel
for marine transportation will result in environmental
benefits, including a reduction of carbon dioxide
(CO
2) emissions by 25%, nitrogen oxides (NOx) by
90%, sulphur dioxide (SO
2) and fine particles by 100%
[14]. Although LNG is the cleanest fossil fuel
available, but the slippage of methane may offset its
beneficial effect on GHG reduction [15]. In addition,
the global warming potential of natural gas is an
aspect that may reduce the attractiveness of natural
gas as a fuel. The Tables 1 provides an overview of
advantages and disadvantages of LNG.
Table 1. An overview of advantages and disadvantages of
LNG as an alternative fuel
________________________________________________
Advantages Disadvantages
________________________________________________
the fastest growing gas high flammability
supply source globally methane slip- reduction of CO2
technology of gas engines is limited
is mature 40% lower volumetric energy
the cleanest fossil fuel density than diesel
available today limited infrastructure-necessary
high energy density investment in LNG
approximately 18 % infrastructure
higher than that of HFO treated as a short-term solution,
measurable reduction of especially when the goal is
CO
2, SOx, NOx, and zero-emission shipping
particles emissions
________________________________________________
Source: [13-16]
In marine transportation, there are currently two
different options for operating engines with LNG:
engines that run solely on natural gas, and dual-fuel
engines that either run on a mixture of diesel and
natural gas, or switch between diesel and natural gas
operation.
2.2 Hydrogen
Hydrogen (H
2) is currently an energy option in the
context of decarbonisation in various sectors of the
industry, as it has the greatest potential for zero
emissions, especially when produced from renewable
resources. The use of hydrogen as ship fuel represents
a significant opportunity for clean energy production;
however, it comes with significant implementation
challenges. With the tightening of IMO regulations to
reduce greenhouse gas emissions from ships,
liquefied hydrogen has been recognized as an
alternative to marine fuels.
Hydrogen is a colourless, odourless, tasteless,
nontoxic, relatively unreactive and flammable gas
with a wide flammability range. Hydrogen is
commonly produced by converting natural gas or coal
into hydrogen gas and CO
2. For long-term
sustainability goals, it should be generated from
renewable energy through electrolysis [17]. To obtain
liquid hydrogen, the fuel must be stored at
temperatures below -253°C, which requires a large
input of energy. Hydrogen is flammable over a wide
mixing range with air, the flammability range is from
4 to 74% by volume [18]. Hydrogen (in the gaseous
phase) is lighter than air, which means that in the
event of a leak, the gas will quickly rise and be
diluted, reducing the risk of accidental ignition and
combustion.
Two types of hydrogen are currently being studied
as fuel options: compressed hydrogen and liquefied
hydrogen. These options have the advantage of an
uncomplicated fuel production process, as only one
additional step (liquefaction or compression) is
needed to produce the final fuel. However, the energy
density of these fuels is lower than alternative fuels.
The low energy density makes the use of hydrogen
make the most sense for short shipping application,
where the amount of fuel that needs to be stored on
board is the smallest. The advantage of hydrogen
options is that none of them require reforming or
cleaning on board before use. Some applications of
hydrogen are currently being considered, such as gas
28
turbines, fuel cells or internal combustion engines in
stand-alone operations [19]. The Tables 2 provides an
overview of advantages and disadvantages of
hydrogen.
Table 2. An overview of advantages and disadvantages of
hydrogen as an alternative fuel
________________________________________________
Advantages Disadvantages
________________________________________________
carbon and sulphur low volumetric energy
free-reduction of emission density efficient storage
electrolysis process is mature of fuel is high
and available low temperatures below -
very high gravimetric energy 253°C to liquefy
density a flammable gas with very
suitable for relatively short low activation and
distance ignition energy
lack of marine transport
experience
permeability material
challenges
high fuel cost
high cost of bunkering
infrastructure
lack of safety regulation for
bunkering
a lack of standardised design
and fuelling procedures
________________________________________________
Source:[17-19]
With properly advanced technology, there are not
principal limitations to production capacity that could
restrict the amount of available hydrogen to the
shipping industry.
2.3 Ammonia
In the Full Report of the Fourth IMO GHG Study
2020, it was assessed that ammonia is one of the
promising alternative fuels. Ammonia is an important
option for zero-carbon fuel, because it can be used
either directly as a fuel in internal combustion engines
or as a chemical carrier for hydrogen to be used in
fuel cells [20]. Around 80% of the world’s production
of ammonia is as a widely used chemical and its
production amounts to approximately 200 million
tons yearly and is used as feedstock for the
production of fertilizers [21]. Unfortunately, currently
most of the hydrogen used to produce ammonia is
produced using fossil fuels such as natural gas and
coal, and only a small portion is produced from other
sources such as electrolysis. Although large quantities
of anhydrous ammonia are now being sold and
handled around the world it is not considered one of
the most toxic cargoes handled in shipping. The risk
of fire and explosion is lower than with other fuels
due to its low flammability limit and strict ignition
conditions. Nonetheless, with the right conditions
there exists a potential for ammonia to ignite. Thus, in
principle ammonia is required to be isolated from any
ignition source on-board vessel, when used as a
marine fuel. Small fires involving ammonia can be
extinguished with dry chemicals or CO
2 and large
ammonia fires can be extinguished through water
spray, fog, or foam emissions [22]. The main risks
associated with ammonia are due to its toxic and
corrosive nature. Thus, liquid ammonia allows storing
more energy per cubic meter than liquid hydrogen,
and moreover, without the need for cryogenic
temperature storage - as is the case with liquid
hydrogen. Storing ammonia at -33.4°C is
technologically easier and cheaper than storing
hydrogen at -252.9°C [23]. There is therefore no need
for a cryogenic system to store ammonia. In principle,
therefore, ammonia storage is much less complicated
than hydrogen and LNG. Ammonia can be stored at
ambient temperature (20°C) at a pressure of just 10
bar. Liquid ammonia has a higher energy density
(12.7 GJ/m3) than both liquid and compressed
hydrogen, which benefits fuel storage [24]. Ammonia
can be decomposed to produce hydrogen, and can
also be burned directly [25]. Ammonia offers the
possibility of storing more hydrogen in liquid form
without the need for cryogenic storage (-33.4°C for
ammonia versus -252.9°C for hydrogen), thus NH3 is
a suitable hydrogen carrier [26]. This is an important
consideration because hydrogen is much more
expensive to store than ammonia, despite the fact that
the two fuels have similar energy densities. They have
already begun work on ammonia-powered marine
engines; the first ammonia-powered marine engine is
expected to enter service around 2024 [25]. The Tables
3 provides an overview of advantages and
disadvantages of ammonia.
Table 3. An overview of advantages and disadvantages of
ammonia as an alternative fuel
________________________________________________
Advantages Disadvantages
________________________________________________
carbon free fuel toxic properties-the need for
stored as a liquid at ambient a safety equipment
temperature NO
x and N2O are generated
low flammability-low risk of when burned
ignition slow flame propagation
commonly shipped around speed
the world corrosive nature-
available port loading incompatible with various
infrastructures-commonly industrial materials
traded commodity larger storage tanks
storage is easier and less lack of regulations issues of
expensive than H
2 toxicity, safety, and
experience in handling storage
established safe handling production reliant on natural
procedures gas
________________________________________________
Source:[20-26]
LNG, liquefied ammonia and liquefied hydrogen
have different physical properties. Analysis has
shown that liquefied ammonia and liquefied
hydrogen were disadvantageous as far as maritime
transportation cost is concerned due to calorific value
and density per unit. However, price competitiveness
of ammonia and liquefied hydrogen may vary in the
future based on policy support for carbon trading
schemes or subsidies [27]. On an equal volume basis,
LNG transports 22.88 MMBTU/m3 of energy, 14.53
MMBTU/m3 of liquefied ammonia, and 9.51
MMBTU/m3 of liquefied hydrogen. In order to
transport the same amount of energy, assuming that
the cargo hold size for LNG is 1.00, a cargo hold about
1.57 times larger and about 2.41 times larger is
required for liquefied ammonia and liquefied
hydrogen, respectively (Fig.2.).
29
*Volume: Require volume for transporting the same energy
Figure 2. Physical properties of gas fuels. Source: [27].
2.4 Methanol
Methanol (MeOH) is a substance commonly used in
the chemical industry to make consumer and
industrial products, but is also used as an alternative
marine fuel. Methanol is also well known as a fuel for
cars and similar engine applications. Every year over
70 million tons of methanol are produced globally.
Methanol is produced mainly via catalytic
conversion of synthesis gas (CO and H
2) from natural
gas reforming, coal gasification or synthesis from
biomass. Currently, many research and production
initiatives are being undertaken that treat solid and
liquid forms of forest biomass (such as pyrolysis
liquid, forest residues, black liquor, etc.) as raw
materials for methanol production [28]. Methanol can
also be produced by catalytic synthesis of carbon
dioxide (CO
2) and hydrogen obtained via electrolysis.
Methanol was classified, as per European
classification (modified 67/548/CEE and 1999/45/CE
directives), as an easily flammable fluid. Following
the European Classification (modified 1272/2008
Regulation), methanol is classified as a toxic substance
of category 3, and as a hazardous substance for health
of category 1.
There are also fewer challenges in adopting
methanol as a marine fuel compared to LNG or
hydrogen. Investigations shows that the handling and
installation of a liquid like methanol had clear
advantages over gas or cryogenic fuels regarding fuel
storage and bunkering. Because methanol is a liquid,
it is very similar to marine fuels such as heavy fuel oil
(HFO). This means that existing storage, distribution
and bunkering infrastructure could be used for
handling of methanol. Only minor modifications of
infrastructure are required [29]. From an
environmental perspective, methanol is readily
biodegradable in both aerobic and aquatic
environments.
Methanol requires larger storage volumes or more
frequent bunkering as compared to conventional fuel
oils. As with other fuels, methanol's future will be
determined not only by the upscaling of its
production, but also by its availability at various ports
and the future cost of the fuel. The Tables 4 provides
an overview of advantages and disadvantages of
methanol.
Table 4. An overview of advantages and disadvantages of
methanol as an alternative fuel
________________________________________________
Advantages Disadvantages
________________________________________________
liquid at ambient temperature lower volumetric energy
potential of widespread density than diesel
availability central nervous system toxic
retrofitting ships is not fuel
expensive highly flammable low flash
the same bunkering and safety point, require more
standards as conventional extensive monitoring
marine fuels
easier to store and handle than
hydrogen and ammonia
low investments and
bunkering infrastructure
________________________________________________
Source:[28-29]
3 POTENTIAL AND LIMITING FACTORS
Alternative fuels have great advantages as well as
their own problems. An important aspect of the use of
alternative fuels is the identification of barriers that
hinder their use in maritime transport. The possibility
of using alternative fuels in the maritime sector
strongly depends on the type of fleet, technical
parameters of ships, ship operation, investment costs,
environmental impact and geographical location,
which determines the availability of alternative fuels.
Several important criteria have been identified, which
are used in the selection of alternative fuels (Fig. 3.).
Figure 3. Main aspects important for evaluation of
alternative fuel solutions for shipping
30
It is recognized that the cost of fuel is the main
criterion for evaluating alternative marine fuels and
that significant increases in fuel costs will be borne by
ship owners, ship operators, shippers and,
consequently, end consumers. The total cost for a fuel
includes the production cost, transportation, storage
cost and possible regulatory costs in the future (such
as carbon tax). Compared to hydrogen and ammonia,
LNG currently has a lower cost, as among alternative
shipping fuels, it is widely available shipping fuel
today [30]. Alternative fuels not only vary in price
among themselves, but also independently vary
considerably from port to port around the world.
Therefore, fleet operators are making decisions not
only about what to bunker with, but also where to
bunker. Available data indicate that estimated prices
for fuels derived from natural gas, such as LNG and
methanol, trough 2030 are associated with less
uncertainty than fuels derived from renewable
sources, including hydrogen and ammonia [31].
Each type of alternative fuel requires specialized
infrastructure for its production, storage, delivery and
combustion at port, terminals and ships. Building and
testing alternative-fuel ships involves large capital
expenditures [32]. The development of alternative fuel
infrastructure is hampered by economic
consideration, as fleet operators choose not to make
the necessary retrofits to ship engines and fuelling
systems and build new vessels, fearing the high cost
of both upgrades and alternative fuel. They are also
concerned about the low availability of alternative
fuels in ports [33]. An important aspect of fuel
infrastructure construction, in addition to capital
investment, is the availability of standards for fuel
quality and production. To ensure the safe operation
of fuels, it is necessary to standardize them.
Parameters such as energy density and storage
volume are important in the selection of alternative
fuels for marine sector, because they affect the
endurance range of ship and the frequency of
bunkering. Alternative fuels with lower volumetric
energy density than HFO require a larger fuel volume
to provide the same cargo work, This either reduces
the volume of space available for cargo transport or
will reduce the vessel’s range between bunkering [34].
Increasing vessel fuel storage capacity is therefore
costly and reduces the amount of space available for
cargo transportation. Different solutions are currently
available or under development to carry out the
fuelling of LNG ships. These differ mainly due to the
availability of LNG supply infrastructures and the
ship type. The LNG bunkering methods currently in
use are truck-to-ship (TTS), ship-to-ship (STS) and
pipeline-to-ship (PTS) [12]. The most widely accepted
LNG bunkering method is to use pipelines to transfer
the fuel from an LNG depot to a receiving point on
ships, known as pipeline-to-ship (PTS). Unfortunately,
there is a lack of infrastructure in the terminals for this
type of bunkering and therefore alternative methods
are used. Hydrogen storage is one of the main
obstacles for its wider application in the marine
sector. It is estimated that new infrastructure would
cost over several billion dollars in the coming decade.
Ammonia is already a widely traded commodity with
established supply chains and availability at most
ports around the world. Compared to hydrogen, there
is an extensive ammonia distribution network, and
port infrastructure is available. At the same time,
possible accessibility problems are pointed out,
particularly in terms of geographic locations for
ammonia bunkering. Methanol as an alternative fuel
solution is a readily available fuel solution as there is
a global production infrastructure and the potential as
a fully renewable fuel of the future. Since methanol is
a well-known and widely used substance, distribution
infrastructure already exists, as well as experience in
handling it. Bunkering infrastructure is also available,
but may not be sufficient given the use of methanol as
a marine fuel.
The shipping industry faces the challenge of
choosing alternative fuels to decarbonize its
operations, while renewable fuels and related
infrastructure remain under development. Shipping
companies choose multiple fuels to diversify. The
most common scenario envisioned by 2050 is ships
simultaneously fuelled by variants of diesel/biodiesel,
methane, methanol and ammonia. This represents a
significant increase in complexity compared to today's
fleet, where simultaneous management of the
consumption of more than one fuel type within a fleet
is rare. Compliance with regulations and practical
needs affect the technological potential of alternative
fuel. Most metals corrode over time when in contact
with fuel. Uncertainty about current and future
marine fleet that may be susceptible to high levels of
corrosion when using alternatives fuels shrouds the
potential for adoption.
Developing a legal framework for the introduction
of alternatives fuels is a challenge and requires both
scientific knowledge and practical information. It is
essential for a systematic and consistent evaluation in
the selection of marine fuels. The ideal marine fuel
will the one with the best properties that coincide
with the concept of sustainable development (in terms
of economic, environmental and social aspects), that
contribute to the goals of decarbonisation of the
maritime transport, while recognizing the pace of
technological development. In addition, there is a
need for international harmonization of safety
standards, as well as national regulations, for both the
production of fuels and their operation on-board ship.
From the environmental perspective, the amount
of emissions generated by the use of a particular fuel
indicates environmental friendliness. The emissions
greenhouse gases and other emitted substances from
fuel production and use have a direct impact on
climate and thus are very important when comparing
the environmental impact of different fuels. However,
the emission associated with any fuel are not limited
to those generated in the process of consuming it. The
production of fuels contributes significantly to the
total gasses emissions and should be considered
together with fuel combustion. A significant portion
of the emissions generated along the entire value
chain of a given fuel is generated during the
transportation phase. Therefore, Life Cycle
Assessment (LCA), which considers environmental
aspects and potential environmental aspects
throughout their life cycle can be used to support
analysis for the whole life benefit of the fuels. There
are two primary factors that make LNG appear to be
an attractive alternative for meeting Annex VI fuel
sulphur content requirements. LNG enables ships to
meet MARPOL Annex VI requirements in global
trade, because LNG's sulphur content is significantly
31
lower than Annex VI requirements for ECAs areas, as
its sulphur content is significantly lower than Annex
VI requirements for ECAs. In addition, LNG reduces
NO
x emissions to a level that will meet MARPOL
Annex VI requirements. In some markets, natural gas
and LNG are cheaper than high-sulphur marine fuel
oils, based on heating value. Currently, ammonia
faces several barriers before it can be used as an
energy carrier on a global scale. As a result,
ammonia as a fuel still requires further research and
analysis that takes into account all the effects in both
the production and use of ammonia produced by
different methods. First, ammonia should be
produced cheaply. Current methods still rely on
hydrogen production contributes significantly to
climate change. Globally, about 420 million tons of
CO
2 are emitted into the atmosphere during ammonia
synthesis, and it is estimated that ammonia
production accounts for more than 1 % of total
energy-related CO
2 emissions [35. A significant
contribution of the marine sector is only possible with
ammonia produced by electrolysis from renewable
source. All changes in ammonia production and
operation technology must be cost-effective. Burning
ammonia leads to elevated levels of emissions of
nitrogen oxides, which are environmental pollutants,
and nitrous oxide, which is a greenhouse gas. As a
result, ammonia cannot be considered a “greenhouse
gas-free” or environmentally friendly energy source
unless steps are taken to reduce emissions. Ammonia
is also labelled as highly toxic to aquatic organisms
with long-lasting effects. Most liquid ammonia spilled
directly into water, dissolves forming a balance of
mostly ammonium hydroxide and a little ammonia
depending on the pH and temperature of the water.
Dissolved ammonia poses a serious threat to aquatic
organisms, killing most of them in close proximity, as
lethal concentrations can be easily exceeded. The
long-term effects of an ammonia spill are related to
the time required to restore the original state through
the nitrogen cycle [36]. Leaks or incomplete
combustion can contribute to ammonia emissions into
the atmosphere and, consequently, would contribute
to acid deposition and eutrophication, which could
harm soil and water quality. However, with careful
operation and control of the combustion system, these
emissions can be prevented. Currently, hydrogen
produced mainly by steam reforming of natural gas,
which is a fossil fuel. A by-product of this process is
CO2, which is a greenhouse gas. It is estimated that
hydrogen produced from fossil fuels contributes to
global warming at a similar rate to the direct burning
of fossil fuels. In contrast, hydrogen derived from
renewable energy, such as solar power, is
environmentally clean both in its generation and
combustion. The actual CO
2 emissions from burning
methanol result from the carbon content of the fuel as
well as depending on the purity of the fuel. CO
2 from
burning bio-methanol is considered climate neutral
and therefore not considered a GHG gas. CO
2 emitted
from biomass-based fuels is assumed to be removed
from the atmosphere when new biomass is grown to
replace the biomass used to produce the fuel.
Methanol has a much lower environmental impact
in the event of a spill or leak than conventional
hydrocarbon fuels. Methanol in case of spills into the
aquatic environment is fully soluble in water,
biodegradable and non-bioaccumulative. Only very
high concentrations in the environment pose a lethal
threat or affect local marine life. This means that a
methanol spill would cause limited damage to the
environment.
The impact of the use of alternative marine fuels
on human health and occupational safety is
important, as potential problems associated with
alternative marine fuels (e.g., toxicity, flammability,
explosiveness) can lead to occupational health risks
for ship crews and shore personnel. The hazards
posed by the properties of ammonia mean that safety
principles used in the ammonia industry should be
implemented on ships and the crew on board must be
equipped with appropriate chemical-resistant
protective clothing and breathing apparatuses.
There are a number of significant barriers that
need to be overcome before ammonia can be more
widely used in the shipping industry. Ammonia as a
fuel can compete with fertilizers in food production,
which can have serious socio-economic consequences.
The question remains to be resolved: Will ammonia
production be sufficient to meet the demands of
agriculture and the maritime economy? Globally,
ships in operation consume about 300 million tons of
fuel annually. In order for ammonia to completely
replace diesel fuel
its production would have to be
twice as large, or about 550 million tons. This is
because the energy density of ammonia is half that of
diesel fuel. Another important socio-economic issue in
the future may be the need to support the economic
transition after the reduction of coal mining and
exports in the some regions of the world.
4 CONCLUSIONS
Protection of environment and sustainable growth of
international sea transportation is the unquestioned
goal and a common understanding for the countries
as well as various stakeholders of shipping industry.
To achieve the ambitious emission reduction targets
set by IMO and the EU, alternative fuels within the
maritime industry are receiving attention over the
years from state administration, shipping company,
industrial partners and academic researchers. A
successful transition from fossil fuels to renewable
fuels in the maritime sector requires simultaneous
attention to regulation, production, distribution and
ships.
In the search cleaner fuels in shipping, several
solutions to find new alternative fuels that could
replace fossil fuels are currently being explored.
Alternative fuels such as ammonia, methanol and
especially hydrogen are currently being explored by
the maritime sector. Currently, the lack of
infrastructure for alternative fuels is the main obstacle
to the development of alternative fuel-powered
maritime transportation.
The use of LNG provides a readily available
transition fuel for the maritime industry. Of the
alternative fuels analysed, natural gas has the least
potential as a long-term solution. This is due to its
characteristics, as it is susceptible to constraints and
changing prices. It can be concluded that while LNG
32
allows for air pollution reduction, it is certainly not an
option for decarbonizing shipping.
Hydrogen is the most promising zero-emission
fuel of the future. However, there are still some
barriers and limitations that need to be addressed
before its global deployment. Among others, the need
to develop a production base and distribution
infrastructure, as well as to further improve hydrogen
storage technologies, remain among the key obstacles
at present. Hydrogen is being considered as part of an
intensive energy transition effort, which will only
become profitable when production and demand
increase significantly as costs fall. Methanol and
ammonia are fuels that are cheaper to produce and
easier to store then hydrogen and can be considered
as potential substitutes for it. Both hydrogen and
ammonia have promising potential to replace
conventional fuels, because only hydrogen and
ammonia have the potential for zero carbon
emissions. Moreover, of the alternative fuels,
methanol, hydrogen and ammonia can be produced
using renewable electricity. This is expected to
happen in the future due to increasing global energy
demand and the time required to develop supply
chain and the infrastructure for these alternative fuels.
REFERENCES
[1] K. Gore, P. Rigot-ller, J. Coughlan, 2022, “Cost
assessment of alternative fuels for maritime
transportation in Ireland”, Transp Res D, 110. Available:
https://doi.org/10.1016/j.trd.2022.103416
[2] OECD, “International transport forum”, Transport
outlook, Paris, 2021.
[3] IEA, “World Energy Outlook”, Paris, 2017.
[4] H. Ritchie, M. Roser, P. Rosado, “CO₂ and Greenhouse
Gas Emissions”, 2020. Published online at
OurWorldInData.org. Available:
https://ourworldindata.org/co2-and-greenhouse-gas-
emissions.
[5] L. Van Hoecke, L. Laffineur, R. Campe, P. Perreault, W.
Verbruggen, S. Lenaerts, 2021, “Challenges in the use of
hydrogen for maritime applications”, Energy Environ.
Sci., 14, 815843. Available:
https://doi.org/10.1039/D0EE01545H
[6] P. Balcobe, J. Staffel, I.G. Kerdan, J.F. Speirs, N.P.
Brandon, A.D. Hawkes, 2021, “How can LNG fuelled
ships meet decarbonisation targets? An environmental
and economic analysis”, Energy, 227, 120462. Available:
https://doi.org/10.1016/j.energy.2021.120462
[7] Y. Zhao, F. Fan, K. Fagerholt, J. Zhou, 2021, “Reducing
sulphur and nitrogen emissions in shipping
economically”, Transp. Res. Part d Transp. Environ. 90,
102641. Available:
https://doi.org/10.1016/j.trd.2020.102641
[8] J. D. Ampah, A. A. Yusuf, S. Afrane, C. Jin, H. Liu, 2021,
“Reviewing two decades of cleaner alternative marine
fuels: towards IMO’s decarbonisation of the maritime
transport sector”, J. Clean. 320. 128871. Available:
https://doi.org/10.1016/j.jclepro.2021.128871
[9] IMO, CCC 7/3/9, “Amendments to the IGF Code and
Development of Guidelines for Low-flashpoint Fuels”,
International Maritime Organization, UK, 2022.
[10] EU Monitor, “COM(2021)562 - Use of renewable and
low-carbon fuels in maritime transport”, 2021.
[11] M. Prussi, N. Scarlat, M. Acciaro, V. Kosmos, 2021,
“Potential and limiting factors in the use of alternative
fuels in the European maritime sector”, J. Clean. Prod.
291. Available:
https://doi.org/10.1016/j.jclepro.2021.125849
[12] B. Jeong, B.S. Lee, P. Zhou, S. Ha, 2018, “Determination
of safety exclusion zone for LNG bunkering at fuel-
supplying point”, Ocean Eng. 152, pp. 113-129.
Available: https://doi.org/10.1016/j.oceaneng.2018.01.066
[13] Guidelines for systems and installations for supply of
LNG as fuel to ships, ISO standard Geneva Switzerland,
2015.
[14] D. Gribi, A.A. Zerrouki, N. Chennpuf, “Liquefied
Natural Gas can be the alternative marine fuel with the
new regulation on sulphur emissions to protect the
environment”, J. Mater. Environ. Sci., 12(4), pp. 595-602,
2021.
[15] M. Al-Breiki, Y. Bicer, 2021, “Comparative life cycle
assessment of sustainable energy carriers including
production, storage, overseas transport and utilization”,
J. Clean. Prod. 279. Available:
https://doi.org/10.1016/j.jclepro.2020.123481.
[16] E. T. Iannaccone, G. Landucci, G.E. Scarponi, S.
Bonvivini, V. Cozzani, “Inherent safety assessment of
alternative technologies for LNG ship bunkering”,
Ocean Eng. 185, pp. 100-114, 2019.
[17] American Bureau of Shipping, “Sustainability
Whitepaper: Hydrogen as Marine Fuel”, Spring, USA,
2022.
[18] A.R. Nerheim, V. Ǣsøy, F. T. Holmeset, 2021,
Hydrogen as a Maritime Fuel-Can Experience with
LNG Be Transferred to Hydrogen Systems?J. Mar. Sci
Eng. 9, pp. 743-749. Available: https://doi.org/
10.3390/jmse9070743
[19] C. Acar, I. Dincer, 2019, Review and evaluation of
hydrogen production options for better environment”, J.
Clean Prod. 218, pp. 83549. Available:
https://doi.org/10.1016/j. jclepro.2019.02.046.
[20] J. Faber, S. Hanayama, S. Zhang, P. Pereda, B. Comer, E.
Hauerhof, W.S. van der Loeff, T. Smith, Y. Zhang, H.
Kosaka, et al. “Reduction of GHG Emissions from
ShipsFourth IMO GHG Study 2020Final Report”,
International Maritime Organization IMO, London, UK,
2020.
[21] A. Al-Enazi, E. Okonkwo, Y. Bicer, T. Al-Ausari, 2021,
“A review of cleaner alternative fuels for maritime
transport”, Energy Rep. 7, pp. 1962-1985. Available:
https://doi.org/10.1016/j.egyr. 2021.03.036.
[22] J. Camilo Gomez Trillos, D. Wilken, U. Brand, T. Vogt,
J.C. Trillos, U. Brand, T. Vogt, D. Wilken, “Life cycle
assessment of a hydrogen and fuel cell ropax ferry
prototype. In Progress in Life Cycle Assessment”,
Springer: Berlin, Germany, 2019.
[23] N. Ash, T. Scarbrough, “Sailing on solar: Could green
ammonia decarbonize international shipping?
Environmental Defence Fund, London, 2019.
[24] J.J. De-Troya, C. Álvarez, C. Fernández-Garrido, L.
Carral, “Analysing the possibilities of using fuel cells in
ships”, Int. J. Hydrog. Energy, 41, pp. 28532866, 2016.
[25] S. Ueda, K. Tsumura, Y. Watambe, H. Tamura, D."
Yamada, LNG as fuel" to "Ammonia as fuel (Ship's fuel
transition to achieve carbon neutrality)”, Mitsubishi
Heavy Ind Tech Rev , 599(2), June 2022.
[26] ITF, “Decarbonising Maritime Transport. Pathways to
Zero-Carbon Shipping by 2035”, International Transport
Forum: Paris, France, 2018.
[27] IMO, CCC 8/INF. 17. “A Study on the Transportation
Cost of a Liquefied Hydrogen Carrier Using Boil-off-gas
as a Fuel”, International Maritime Organization IMO,
London, UK, 2022.
[28] M., Svenberg, J. Ellis, J. Ludgren, I. Landälv,
“Renewable methanol as a fuel for the shipping
industry”, Renewable Sustainable Energy Rev. 94, pp.
1217-1228, 2018.
[29] K. Andersson, C. M. Salazar, “Methanol as a marine
fuel report” Methanol Institute, 2015.
[30] J. Metcalfe, L.R. Burger, J. Mackay, “Unlocking South
Africa
s hydrogen potential. PwC Network”, 2020.
33
Available:
htttps://www.pwc.co.za/en/assets/pdf/unlocking-south-
africa’s-hydrogen-potential. Pdf
[31] DNV GL, “Comparison of alternative marine fuels”, For
SEALNG, DNV GL. No 2019-0567,2019.
[32] C.J. McKinlay, S.R. Turnock, D.A. Hudson,A
Comparison of Hydrogen and Ammonia for Future
Long Distance Shipping Fuels”, The Royal Institution of
Naval Architects LNG/LPG and Alternative Fuels. UK,
2020.
[33] G. Nikolau, N. Xydas, “LPG bunkering: guide for LPG
marine fuel supply”, World LPG Association, 2019.
[34] A. Foretich, G. D. Zaimes, T.R. Hawkins, E. Newes,
2021, “Challenges and opportunities for alternative fuels
in the maritime sector”, Marit. Transp. Res. 2. 100033.
Available: https://doi.org/ 10.1016/j.martra.2021.100033
[35] D. A. Chisalita, L. Petrescu, C. C. Cormos, 2020, „
Environmental evaluation of European ammonia
production considering various hydrogen supply
chains”, Renewable Sustainable Energy Rev., 130.
Available: https://doi.org/10.1016/j.rser. 2020.109964.
[36] T. Ayvalı, S. C. Edman Tsang, “The Position of
Ammonia in Decarbonising Maritime Industry: An
Overview and Perspectives: Part II”, Johnson Matthey
Technol. Rev., 65(2), pp. 291300, 2021.