
10
The Economics of Oshore Wind-Based Hydrogen Production in Saudi Arabia
to expand its renewable energy infrastructure and reduce
carbon emissions, with operations expected to begin by
the early 2030s (Enerdata 2024). In Vietnam, the use of
2 GW of oshore wind for hydrogen production by 2035
has been proposed. This proposal is part of the country’s
broader energy transition strategy, which includes
significant oshore wind development and the integration
of green hydrogen production to support its 2050 net-
zero emission target (Enerdata 2024).
2.2 Literature
Review of Oshore
Wind and Hydrogen
Production
Recent studies have focused on evaluating the
technoeconomic feasibility of integrating oshore wind
energy with hydrogen production to increase energy
sustainability and reduce curtailment issues. Oshore
wind farms face significant challenges related to high
installation costs and grid connection diculties,
particularly due to the higher capacitance in underwater
AC cables. While HVDC systems can mitigate energy
loss, they have higher installation costs than do other
systems. This situation has prompted the exploration of
innovative alternatives, such as producing hydrogen at
sea and transporting it to land without direct electricity
grid connections (Calado et al. 2024; Kang, Gbadago,
and Hwang 2024). In fact, some studies have reported
that oshore hydrogen production is more cost-eective
than is the construction of HVDC networks for onshore
hydrogen production, especially in remote locations and
for large capacities (Glaum, Neumann, and Brown 2024;
Ibrahim et al. 2022; Wang et al. 2024). Conversely, wind
farms located close to shore are likely connected to
onshore facilities via power cables (Lüth et al. 2023).
Compared with underwater electrical cables, the
transportation of energy via underwater hydrogen
pipelines is an appealing option because of lower energy
losses, lower costs, and improved scalability (Calado
et al. 2024). This approach allows oshore wind farms
to bypass grid connections entirely, increasing their
feasibility and eciency when combined with onsite
hydrogen production in areas with high wind power
density (Bonacina, Bordbar Gaskare, and Valenti 2022;
Giampieri, Ling-Chin, and Roskilly 2024).
Promising developments in the oshore wind-to-hydrogen
sector involve the use of ammonia as a renewable
hydrogen carrier for long-distance interoceanic transport.
Studies have suggested that the transportation costs of
ammonia are lower than are the expenses associated with
hydrogen conversion, storage, and reconversion. While
liquid hydrogen is also considered promising because
of its lower cost and greater flexibility in delivery, it faces
significant energy loss during storage and transport (Díaz-
Motta, Díaz-González, and Villa-Arrieta 2023; Bonacina,
Bordbar Gaskare, and Valenti 2022). Ammonia, with its
relatively high volumetric energy density and existing
global infrastructure for storage and transport, is gaining
attention as a critical component in the emerging hydrogen
and green hydrogen economy (Díaz-Motta, Díaz-González,
and Villa-Arriet 2023; Perez-Vigueras et al. 2023).
Proton exchange membrane (PEM) electrolyzers are well
suited for oshore wind integration because of their high
eciency, rapid response to variable loads, and ability
to adapt to the intermittency of wind power. Compared
with other electrolysis technologies, the superior
performance of PEM electrolyzers makes them ideal for
oshore hydrogen production (Farahmand, Günther, and
Kristiansen 2024; Guven 2024; Akdağ 2023; Luo et al.
2022). To produce hydrogen at sea, electrolyzers require
high-purity water, which is typically obtained through
reverse osmosis or other water treatment processes to
ensure the necessary quality (Komorowska, Benalcazar,
and Kamiński 2023). Desalination coupled with
seawater electrolysis is feasible but requires significant
technological advancements (Ramakrishnan et al. 2024).
The integration of hydrogen production into oshore
wind shows promise, but several challenges need to
be addressed. Farahmand, Günther, and Kristiansen
(2024); Komorowska, Benalcazar, and Kamiński (2023)
have highlighted the need for substantial investments in
infrastructure, such as pipelines and storage facilities, to
manage the produced hydrogen. Additionally, the above
authors have noted that regulatory frameworks and
market mechanisms need to evolve to support the large-
scale deployment of these systems. Distributed hydrogen
production, which eliminates the need for centralized
onshore facilities, has been demonstrated to be more
cost-eective than other types of hydrogen production,
especially in marine environments (Kang, Gbadago, and
Hwang 2024).
In recent studies, Bonacina, Bordbar Gaskare, and Valenti
(2022) and Díaz-Motta, Díaz-González, and Villa-Arriet