1131
1 INTRODUCTION
The Baltic Sea connects all the countries in the Baltic
region, including, among others, Finland, Sweden, and
Estonia. The location makes its maritime routes vital in
supporting reliable and sustainable transportation in
Europe [1-3]. Sea ice dynamics challenges shipping in
the Baltic Sea. Several countries in the region have
established centralized systems providing icebreaking
assistance, including the most northern Finnish
Swedish Winter Navigation System (FSWNS),
maintaining safe and efficient year-round navigation
in the Gulf of Bothnia [4, 5].
A typical winter navigation system (WNS) consists
of ship traffic, icebreakers, and an organizing
framework setting up the principles of their operation.
The required icebreaking assistance (i.e., number,
location of icebreakers, and their characteristics) in
specific ice conditions depends on the icebreaking
capabilities of the ship traffic: the less ice-strengthened
the ships, the more icebreaker resource is needed. The
winter navigation system is developed to guarantee
safe and reliable shipping throughout the winter. It
also imposes some minimum size and ice class
requirements on the ships to ensure safe and efficient
operations. Moreover, ships must be built and
operated following the corresponding ice-class rules
applied in the region [5, 6].
Climate change will affect future ice conditions, so
the maximum ice extent and average ice thickness
might decrease [7]. At the same time, climate change
might result in more stormy winds and waves,
increasing ice movements. This makes the ice more
dynamic, results in a higher possibility of forming
ridged ice, and makes the ice conditions more spatially
heterogeneous and less predictable. Offshore wind
farms affect the local ice conditions so that the typical
ice patterns and related ice parameter statistics may no
System-level Simulation for Sustainable Winter
Navigation
A. Kondratenko
1,2
, K. Kulkarni
3,4
, L. Lu
4
, C. Winberg
4
, F. Li
5
, P. Kujala
4,6
, K. Kamberov
1
&
R. Leiger
6
1
Technical University of Sofia, Sofia, Bulgaria
2
Chalmers University of Technology, Gothenburg, Sweden
3
Hanken School of Economics, Helsinki, Finland
4
Aalto University, Espoo, Finland
5
Shanghai Jiao Tong University, Shanghai, China
6
Estonian Maritime Academy, Tallinn University of Technology, Tallinn, Estonia
ABSTRACT: Many European countries are connected to the Baltic Sea, making it vital for transporting goods and
passengers in the region. Because of its northern location, a significant part of the Baltic Sea is ice-covered in
winter, resulting in complications for ship navigation. Icebreakers may allow for safe and efficient transportation
in ice conditions, which requires their organizing in a centralized system aimed at efficient and sustainable
navigation. It is vital to analyze maritime traffic in ice to understand better the future need for icebreakers in the
Baltic Sea. The paper applies agent-based simulation to enhance the performance of winter navigation and
icebreaking assistance in the Bay of Bothnia. We developed novel algorithms upgrading our decision-support
tool to model the dynamics of the icebreaker resource availability, optimize icebreaker allocation in the Bay of
Bothnia, and study how changing the directed pathways affects the efficiency of the winter navigation system.
We demonstrated the capabilities of the developed algorithms in the case studies.
http://www.transnav.eu
the International Journal
on Marine Navigation
and Safety of Sea Transportation
Volume 19
Number 4
December 2025
DOI: 10.12716/1001.19.04.10
1132
longer be relevant, e.g., they change the dynamics of
ice development and break and redirect the moving ice
[8, 9].
The size of a typical ship seems to grow in the
future, and the new strict environmental regulations
will decrease the engine power installed on ships. The
International Maritime Organization (IMO) adopted
Energy Efficiency Design Index (EEDI) regulations in
2011 to reduce the amount of greenhouse gases (GHGs)
emitted by ships [10]. These regulations promote
energy-efficient solutions [11] but may prioritise
underpowering of fossil-fuelled ships and their
optimization for open water conditions. This will
decrease the ice-going capabilities of these ships
dramatically and possibly will result in higher demand
for icebreaker assistance. Therefore, developing
system-level simulation tools that study such factors is
essential to understand and reliably predict future
trends.
Over the last decades, a number of studies have
contributed to the topic at hand by modeling the
system-level performance of winter navigation. They
aim to develop [4, 12-14], upgrade, and apply [15-16]
software that can be used to simulate the need for
icebreakers in the future when ice conditions, maritime
traffic, and characteristics of ice-strengthened ships are
under dynamic change.
The present paper upgrades the method by
Kulkarni et al. [4] to account for the new WNS features.
This allows for a more realistic simulation of the WNS
operation by considering additional practical
navigation aspects not presented in [4]. Specifically, we
developed the novel algorithms and prepared the
input data to model the dynamics of the icebreaker
resource availability, optimize icebreaker allocation in
the Bay of Bothnia, and study how changing the
directed pathways affects WNS efficiency. The
remainder of this paper is structured as follows.
Section II analyses existing approaches and models for
the simulation of winter navigation in the Baltic Sea
and their applications. Section III describes newly
developed algorithms and input data for the case
studies and demonstrates the results of thirty-six
simulation experiments, followed by a discussion of
the results and conclusions.
2 DEVELOPMENT OF SIMULATION
FRAMEWORKS FOR WINTER NAVIGATION IN
THE BALTIC SEA
2.1 Existing approaches for simulation of the winter
navigation in the Baltic Sea
One of the early models of winter navigation in the
Baltic Sea [12] considered navigation in the Bay of
Bothnia, estimating the performance of independent
and icebreaker-assisted ships in the ice. However, the
outlook of the framework is not systemic, which limits
the number of factors that can be analyzed. Lindeberg
et al. [13] proposed a new systemic simulation
approach, individually modeling ships and icebreakers
to address this problem. The approach considered
vessel performance in ice for different regimes, e.g.,
independent navigation in level and brash ice,
icebreaker-assisted navigation in convoy, and towed
mode [15]. Transport ships and icebreakers follow the
network of fairways (see Fig. 1) that consist of linear
and y-shaped segments whose location may change
over time. The limitations of the approach are long
running time and limited visualizing capabilities.
Figure 1. The fairway network implemented in the
simulation approach by Lindeberg et al. [13]. It consists of the
building blocks sections (black) and junctions (yellow). The
red stripes show an example of one operational area.
Bergström and Kujala [14] developed a stochastic
discrete-event approach in the Simulink modeling
environment for the FSWNS simulation, which can
change the environment parameters with a specific
time step inside the event. The discrete-event
simulation allows the creation of the model from the
standard building blocks predefined templates of
different events like delay, queue, service by resource,
or moving. The stochastic ice parameters are defined
individually for each segment of the route. The
approach considered the possibility of convoy
formation, with an icebreaker assisting up to two
transport vessels. It allows for estimating the total
waiting time of transport ships for icebreaking
assistance and the transport capacity of the FSWNS for
a specific period.
Figure 2. The flowchart of the stochastic discrete-event model
of the FSWNS by Bergström and Kujala [14].
Fig. 2 shows an example of the event diagram
provided in the study, where a ship is modeled as a
passive entity, and an icebreaker is modeled as a
limited resource. The behavior of ships and icebreakers
is assigned collectively based on a specific general
pattern. In other words, ordering a particular ship to
1133
move to a specific point would require changing the
structure of the model, which would affect all vessels
and icebreakers. The approach has high computational
efficiency of the simulation, making it faster. It benefits
from using stochastic parameters, as it allows the
capture of complexities of nature and conducting
reliability studies by assigning the confidence level to
a specific conclusion.
Kulkarni et al. [4] proposed an agent-based
approach developed in the AnyLogic modeling
environment for the simulation of the WNS in the
Baltic Sea. The approach stands out from the previous
state of the art by individually modeling the behavior
of the WNS elements called agents (i.e., transport
vessels, icebreakers, ports, routes, ice). Thus, transport
vessels and icebreakers may behave differently
depending on the dynamic circumstances (i.e.,
environment and other agents) they encounter. This
feature allows for significant modularity of the model,
resulting in some benefits. Firstly, it provided great
potential for analysis of how different factors of winter
navigation affect system performance indicators.
Secondly, modularity made the model easy to upgrade
for new functionality, as the changes will only
influence the corresponding modules of the model. The
model has advanced capabilities for visualizing the
simulation process, allowing for more accessible
verification and interpretation of the results. The
approach has favorable computational efficiency. An
average run of a simulation model for one winter
month takes from thirty minutes to one hour for the
average office laptop. Considering the benefits of the
approach by Kulkarni et al. [4], different studies
extended the approach to account for new features and
regions of application [15-16]. The present study
upgrades the method by Kulkarni et al. [4] to account
for the dynamics of the icebreaker resource availability
and optimization of icebreaker allocation in the Bay of
Bothnia and to analyze how changing the directed
pathways affects the WNS efficiency.
2.2 System-level simulation model for sustainable winter
navigation in the Baltic Sea
Fig. 3 shows the principle organizational scheme of the
approach by Kulkarni et al. [4]. It is based on two
primary model layers: Traffic flows and Environment.
Traffic flows include necessary data on transport ships,
icebreakers, and their operation. The definition of
Traffic flows starts from processing raw Automatic
Identification System (AIS) data, i.e., automatic regular
reports of coordinates of the vessels with specific time
intervals. The data are processed for a specific area and
period into the unified information on voyages of
transport vessels. The voyage data includes the
Maritime Mobile Service Identity (MMSI) number of
the vessel, starting and destination ports, and the time
when the voyage commences and finishes. The finish
time of the voyage is used to verify the estimated
voyage duration by comparing it with the actual
practical data. Alongside vessel location, the input
traffic data include the basic vessel parameters
corresponding to a specific MMSI number, i.e., vessel
type (e.g., tanker, bulker, containership, Ro-Ro), ice
class, the total engine power, deadweight, maximum
speed in open water, and breadth. Considering that the
number of merchant vessels in the traffic may include
hundreds of vessels, it is often time-consuming to
specify the individual technical information for every
ship. For that purpose, about fifty default ship
descriptions further called ship types are entered
into the model, which includes detailed technical
information on the most typical merchant vessels in the
Baltic region.
The technical information includes the necessary
data to model the performance of ships in ice and open
water (i.e., to estimate attained speed at specific power
output). For every merchant vessel, the closest default
ship is selected using the basic parameters from the
input data, as shown in Fig. 4. Later, in calculations, the
merchant ship is assumed to be identical to the selected
default ship.
The attained ship speed v in specific ice conditions
is calculated based on the cubic polynomial h-v curves
(see Fig. 5), where h stands for the equivalent ice
thickness. The h-v curves are defined for independent
operation and moving behind an icebreaker, assuming
100% power output. The h-v curves for the default ship
types were developed in Project Winmos II [17-19] by
Aker Arctic. When a ship is moving at a partial engine
load (i.e., the power output is less than 100%), the h-v
curve is recalculated assuming the speed in the limit ice
proportional to power output to the 4/9 power, and the
speed in open water proportional to the 1/3 power as
described in Kulkarni et al. [4]. The limit level ice
thickness of a ship is typically defined by conditions
when it cannot move faster than from 1.5 to 2 knots.
Independent navigation in thicker ice is considered
unsafe and is not allowed.
Figure 3. The organizational scheme of the simulation
approach by Kulkarni et al. [4].
All icebreakers are divided into three types (A, B,
and C) with specified h-v curves, where A has the most
advanced icebreaking characteristics. The model
allows for up to two vessels in an icebreaker convoy.
The speed of the convoy is calculated as the minimum
of values of attained speed for an icebreaker and
assisted vessels considering their h-v curves. Convoys
are moving along the directed pathways, similar to the
fairway network shown in Fig. 1. In practice,
authorities issue the directed pathways as
recommended routes for merchant vessels, considering
ice conditions, available icebreaker resources, and their
allocation. The directed pathways consist of waypoints
connected by linear paths. Since the voyage data are
limited by starting and destination ports, the
information on reaching from one port to another is
stored separately for all possible combinations as a
sequence of waypoints a ship passes along the way.
1134
Figure 4. Mapping the merchant ship to the closest prototype
ship [4].
Figure 5. Estimating the ship transit speed in specific ice
conditions [4].
The second model layer is the Environment, which
includes a Geographical Information System (GIS) map
of the studied region (see Fig. 6) with directed
pathways, ports, waypoints, and ice conditions
presented corresponding to their geographical
coordinates. Considering that h-v curves for vessels
and icebreakers are specified for level ice thickness,
complex ice conditions are modeled using the concept
of the equivalent ice thickness. As per this concept, the
complex ice conditions with many properties (e.g.,
thickness, ridging, concentration, size of the ice floe)
may be replaced in the model by only one characteristic
equivalent level ice thickness, assuming
corresponding ship speed is the same in both complex
and level-ice conditions [4].
The quality of ice data significantly affects the
accuracy of simulation results. The ice information is
available through ice forecast data published by the
Finnish Meteorological Institute (FMI). The
Environment layer is divided into cells with a
geographical area of a square mile. The ice data in the
model are specified for each cell with a time resolution
of one day, allowing for the trade-off between
calculation time and accuracy. The equivalent ice
thickness is calculated as a function of concentration
and thickness [4]. Besides ice data, each cell has
information to which icebreaker assistance zone it
belongs. The GIS map is divided into icebreaker
assistance zones, allowing for allocating icebreakers
based on ice conditions. One or more icebreaker zones
are identified, through which the vessel will navigate
to its destination. At least one icebreaker is available in
each zone [20].
Figure 6. The GIS map of the simulation model [4]. Ice
conditions are shown by different grades of blue color, where
darker shades indicate thicker ice.
When the data from the Traffic flows and
Environment layers are read, the voyages are
simulated chronologically. The individual flow charts
of agents guide the simulation. Every vessel aims to
finish the voyage from the start port to the end port
using the directed pathways. The speed of the vessel is
recalculated every time the ice parameters change. If
the vessel speed drops below a certain threshold, it
requests assistance from the ice-breakers available for
the relevant icebreaker assistance zone. The
icebreaking assistance threshold may not be less than
the limit level ice thickness of a ship specified for the h-
v curve. Each icebreaker serves first the vessel that
waited the longest for assistance according to the first
in, first out principle. The same icebreakers may assist
multiple vessels through convoys if they are headed in
the same direction. The simulation ends when all
vessels in the considered period have completed their
schedules.
Vessels often need assistance across multiple
icebreaker zones. Typically, each icebreaker guides a
vessel through its operating zone, leaving it at a
boundary waypoint unless the port is in the zone [20].
The next icebreaker takes over the assistance mission at
the waypoint, guiding the vessel further along its
navigational journey. However, icebreakers can
operate outside their operating zones to ease traffic
build-up or help larger vessels that need two
icebreakers. A list of requests for each icebreaker is
maintained and updated as the vessel moves from one
zone to another. The vessel is removed from all lists
once it reaches a port [20].
The model can change the directed pathways
during the model run, which allows for adjusting the
shipping routes for more favorable ice conditions.
Respectively, there is a need for an algorithm for
transition between the directed pathways. The ongoing
journeys are completed on the old directed pathways,
and the new journeys are scheduled on the new
directed pathways [20]. Icebreakers need to coordinate
between both sets of directed pathways until all traffic
flows smoothly on new directed pathways. Lu et al.
[16] applied the model to a new region the Gulf of
Finland and the Gulf of Riga considering Estonian
and Finnish traffic and a new set of icebreakers. This
did not require modifying the core modules of the
model and demonstrated its significant flexibility.
1135
2.3 Key performance indicators for assessing the efficiency
of the winter navigation system
The assessment criterion has a critical role in estimating
the efficiency of the winter navigation system. The
winter navigation system is a complex entity with
many qualities. Most of them are naturally
contradicting, resulting in the need to find a trade-off
between different KPIs. Kulkarni et al. [4] proposed
measuring the efficiency of the FSWNS using the total
waiting time (TWT) of merchant ships for icebreaking
assistance as per (1). The total waiting time is often
used in the FSWNS shipping practice.
,
10
v max
v
v
n
T
n
n
TWT W
=
=

(1)
where nv is the number of a simulated merchant ship,
T is the simulation time (days), Wnv is the accumulated
waiting time of the vessel number nv in minutes.
The total waiting time is the most straightforward
KPI. Advancing the framework [4], Kondratenko et al.
[15] demonstrated that although the total waiting time
is an important KPI, it may prioritize less sustainable
solutions. Minimizing the total waiting time of the
WNS corresponds to more intensive use of the
resources, e.g., leads to faster speeds of merchant ships
and icebreakers with a higher total running time of the
icebreakers, resulting in increased fuel consumption.
Kondratenko et al. [15] proposed using the total CO2
emissions (2) and the total cost of the WNS operation
(3) as additional KPIs for more sustainable and
informed decision-making. The total CO2 emissions
(ECO2) and cost are estimated for all merchant ships and
icebreakers.
(2)
where n is the number of simulated vessels, including
icebreakers, t is the number of the simulation period,
and Δt' is the duration of the simulation period. The
simulation period ends if external circumstances affect
the speed or the propulsion power in use Pd (kW). Cf is
the conversion factor between fuel consumption and
CO2 emissions [21-26]. Phl is the hotel load the power
required for non-propulsion power consumers of a
ship, estimated as a function of vessel type, size, and
capacity using the statistical method by the Central
Marine Research & Design Institute [27]. SFC1 and SFC2
are the specific fuel consumptions (t/kWh) for the main
engine and the electric generator. The specific fuel
consumption is calculated using quadratic polynomial
approximations [15] depending on the engine load in
% of the total maximum continuous rating (MCR).
Approximations are provided for low-speed engines
and medium-speed engines. ηtr and ηhl are the power
transmission efficiencies for propulsion and the hotel
load.
'
12
11
max max
nt
d hl
n fuel
tr hl
nt
P SFC P SFC
Cost t R C

==


= + +






(3)
where Rn is the time charter rate (USD/hour) of a
transport vessel or an icebreaker, and Cfuel is the fuel
price (USD/t).
Using several discussed KPIs together results in a
more systemic overview of the WNS system efficiency.
Kondratenko et al. [15] demonstrated that their
approach may provide the WNS with about a 7%
decarbonizing effect or up to 14.2% cost reduction,
depending on the priorities. They also show that the
hotel loads are responsible for from 13.4% (moving at
the max speed) to 100% (waiting for icebreaker
assistance) of CO2 emissions of a merchant ship on
different modes of operation, and correspondingly
must be considered in sustainable decision-making.
3 STUDYING NEW OPPORTUNITIES TO
ENHANCE THE EFFICIENCY OF WINTER
NAVIGATION SYSTEMS
Lu et al. [16] demonstrated that different ice conditions
associated with different winters significantly affect
the total waiting time, the need for icebreakers, and
CO2 emissions. Lu et al. [16] and Kondratenko et al. [15]
also concluded that providing a more capable
icebreaker fleet (in terms of their number and ice class)
with fixed ice conditions improves the efficiency of the
WNS till a specific point when further strengthening of
the icebreaking fleet results in high additional cost with
insignificant effect.
The present study provides further analysis of how
the icebreaker assistance parameters and ice conditions
affect the efficiency of the FSWNS. In the original
approach by Kulkarni et al. [4], all the modeled
icebreakers are available for the entire simulation time.
However, in the shipping practice, the number of
icebreakers is adjusted considering the dynamics of ice
conditions, starting from a few icebreakers in the early
winter and gradually adding more icebreakers later. In
the present research, we implement the algorithm to
account for the dynamics of the icebreaker resource
availability and provide the corresponding simulation
experiments. We also study the influence of the
icebreaker allocation in different icebreaking zones on
the efficiency of the FSWNS. Finally, we analyze how
the location of the directed pathways influences the
WNS efficiency and provide insights into the
importance of ice routing of ships in the FSWNS.
3.1 Preparing new algorithms and input data for
modeling more WNS features
The new features to be modeled are dynamics of the
icebreaker availability, optimization of icebreaker
allocation, and dynamics of the directed pathways. The
basic scenario (Scenario 1) is discussed with the Finnish
Transport Infrastructure Agency specialists and
represents the existing practice. The selected AIS traffic
data corresponds to one month of winter 2018 (15 Jan
15 Feb) an average winter from traffic and ice
perspectives. The AIS data includes 485 voyages of 181
merchant vessels. Icebreaker data is provided in Table
I, where all icebreakers have medium-speed engines.
Fig. 7 shows on the map the icebreaking assistance
zones applied in the simulation, and Fig. 8 shows the
relevant zones for icebreakers and their operating
schedule. According to the schedule, the number of
operating icebreakers grows from four at the beginning
of the simulation to nine at the end. Technically, this is
achieved by blocking the ability of a merchant ship to
1136
select the icebreaker for assistance before its starting
date of operation.
Figure 7. Icebreaking assistance zones in the Bay of Bothnia
assumed in the simulation.
Table 1. Parameters of the icebreakers for the case study,
where home port identification numbers are as follows: 25 is
Quarken, 3 is Oulu, and 56 is Lulea.
Name
Type
Home
port
Engine
power,
kW
Propulsion,
kW
Transmission
Engine
SFC
(100%
power),
g/kWh
Polaris
A
25
21000
19000
Diesel-
electric
Medium-
speed
185
Otso
A
3
21840
15000
Diesel-
electric
Medium-
speed
185
Kontio
A
3
21840
15000
Diesel-
electric
Medium-
speed
185
Urho
B
25
17100
16200
Diesel-
electric
Medium-
speed
175
Frej
B
56
17100
16200
Diesel-
electric
Medium-
speed
175
Oden
A
56
18000
18000
Shaft
Medium-
speed
185
Ymer
B
56
17100
16200
Diesel-
electric
Medium-
speed
175
Thetis
C
56
3500
3500
Shaft
Medium-
speed
180
Ale
C
56
3500
3500
Shaft
Medium-
speed
180
In the original model by Kulkarni et al. [4], the
maximum number of icebreakers per zone is assumed
to be two. The ID number of the last used icebreaker in
a specific zone is stored in a variable, and the vessel
selects another icebreaker to assist vessels in this zone.
According to the icebreaker schedule assumed in the
present study (see Fig. 8), the available icebreaker
resources are dynamic, and the maximum number of
icebreakers per zone is up to four. This is achieved
through the vessel selecting the icebreaker (see Fig. 9)
according to the uniform distribution by drawing the
random number from 0 to the maximum number of
icebreakers in the zone. The random number is drawn
again if the number belongs to an icebreaker whose
schedule has not started.
Figure 8. Operation schedule for icebreakers in the Bay of
Bothnia with the starting dates.
Figure 9. The algorithm for a vessel to select an icebreaker for
assistance during the simulation.
Figure 10. The directed pathways in the Bay of Bothnia for
the considered case studies.
We consider two options for directed pathways (see
Figure 10) to study the effect of their change on the
WNS efficiency. Directed pathway (Dirway) 1 is closer
to the Eastern coast of the Bay of Bothnia, and Dirway
2 is near its center. Because of spatial ice variation, ice
conditions are different for different directed
pathways. This allows us to analyze the importance of
providing accurate recommendations on directed
pathways, i.e., whether it is worth carefully selecting
the most beneficial directed pathways or whether it
could be deemed insignificant for the chosen type of
winter. In the case studies, we considered three
different options for using directed pathways: vessels
moving along Dirway 1, Dirway 2, and stochastically
migrating between them. For example, in the basic
scenario (Scenario 1), directed pathways are randomly
changed one time per day.
The case studies include seven different scenarios
(see Table II). Considering that the model is stochastic,
several simulation rounds were performed for every
scenario, resulting in 36 simulation runs in total, with
an accumulated simulation time of about 21 hours for
the average office laptop. The simulation assumes that
the icebreaking assistance threshold is 5 knots and that
every merchant vessel is assisted individually.
1137
3.2 Simulation results for the case studies
Simulation results for different scenarios are presented
in Table III and Figure 11. Most simulations (16 rounds)
are performed for the basic Scenario 1. It is noted that
the number of simulation rounds is different for some
scenarios, which may cause a selection bias of
unequally represented statistics. Figure 11 shows
significant variations in KPIs for Scenario 1, e.g., about
a 45% difference in the total waiting time and a 7.5%
difference in CO2 emissions. This difference is caused
by the stochasticity associated with the icebreaking
decision-making and changes of the directed
pathways. Finding the reasons behind those
fluctuations may unlock significant potential for
optimization of the FSWNS. Scenario 2 differs from
Scenario 1 by deterministic directed pathways: the
vessels navigate using only Dirway 1. Variations for
Scenario 2 (5 rounds) account for about a 24%
difference in the total waiting time and a 3.7%
difference in CO2 emissions. The average CO2
emissions for Scenario 2 are only about 1% lower than
for Scenario 1, but the corresponding average total
waiting time is almost 17% higher. This means that for
the considered conditions, ice routing of ships (i.e., the
directed pathways optimization) may be beneficial to
significantly reduce the total waiting time of the
FSWNS if the icebreaker resource is limited (e.g., by the
limited number of available icebreakers and their
schedule) and their location is not optimized.
Scenario 3 (3 rounds) is compared with Scenario 1
to analyze how the availability of all icebreakers during
the simulation period affects the KPIs. The results
show that the difference in KPIs is insignificant, which
means that the schedule (see Figure 8) proposed by the
Finnish Transport Infrastructure Agency experts is
nearly optimal for the proposed allocation of the
icebreakers.
Table 2. Values of the WNS parameters in the case studies.
Icebreakers are abbreviated as IB.
Case
Dirway
Schedule
IB Location
Scenario 1
Stochastic
Dynamic
Basic
Scenario 2
Dirway 1
Dynamic
Basic
Scenario 3
Stochastic
All IB available
Basic
Scenario 4
Stochastic
Dynamic
Optimized
Scenario 5
Stochastic
All IB available
Optimized
Scenario 6
Dirway 1
All IB available
Optimized
Scenario 7
Dirway 2
All IB available
Optimized
Figure 11. The values of KPIs for different scenarios of the
case study.
Simulations for Scenarios 1 3 showed that they
have shared problems starting from the beginning of
February, many ships are stuck in Zone 3, but Zones 1
and 2 are free from the ship traffic (see Figure 12). This
problem can be mitigated by optimizing the allocation
of the icebreakers (Scenario 4), using the rest of the
parameters as in Scenario 1. Figure 13 shows the
improved schedule, where the icebreakers are
redistributed to provide more assistance in Zone 3, and
their operation time is kept unchanged.
The simulation results for Scenario 4 (see Figure 11
and Table III) demonstrate a 35% reduction in the
average total waiting time of the FSWNS compared to
Scenario 1, when the average CO2 emissions stay
almost the same. This means that optimized allocation
of icebreakers without changing their operation time
may be a very efficient method to improve the
performance and cost-efficiency of the FSWNS.
Previously, Scenario 3 demonstrated that the
availability of icebreakers during the entire simulation
period insignificantly affects the KPIs for the basic
allocation of the icebreakers. Scenario 5 is designed to
check if this conclusion is still relevant for their
optimized allocation. The corresponding simulation
results demonstrate a 42% average reduction in the
total waiting time of the FSWNS and the same CO2
emissions compared to Scenario 1. This demonstrates
an additional 7% reduction in the total waiting time of
the FSWNS compared to Scenario 4 due to extended
icebreaker re-sources assuming the optimized
allocation of icebreakers. Figure 14 shows that unlike
Scenario 3 (Figure 12), the vessels are evenly
distributed between the icebreaker assistance zones for
the same virtual date, resulting in enhanced
performance of the FSWNS, especially at the final
stages of the simulation when the ice is the thickest.
Scenarios 6 and 7 show that using deterministic
directed pathways may result in about a 6% additional
reduction of the total waiting time, associated with no
need for transition between the directed pathways.
Table 3. Simulation results for different scenarios.
Number of the
round
The average
waiting time,
minutes
The total fuel
consumption,
tonnes
CO2 emissions,
tonnes
Scenario 1
1
746
6853
21587
2
633
7191
22652
3
517
6987
22009
4
728
6962
21930
5
409
6662
20985
6
662
6932
21836
7
661
6932
21836
8
547
7081
22305
9
538
6743
21240
10
521
7049
22204
11
751
6767
21316
12
718
7154
22535
13
723
7033
22154
14
596
6902
21741
15
567
6808
21445
16
535
6778
21351
Scenario 2
1
622
6862
21615
2
656
6720
21168
3
816
6897
21726
4
779
6981
21990
5
726
6906
21754
Scenario 3
1
676
6866
21628
2
570
6816
21470
3
630
6825
21499
1138
Scenario 4
1
415
6886
21691
2
388
6921
21801
3
405
6966
21943
Scenario 5
1
359
6988
22012
2
333
6815
21467
3
377
6839
21543
Scenario 6
1
291
6772
21332
2
309
7012
22088
3
362
6870
21641
Scenario 7
1
331
6886
21691
2
338
6866
21628
3
370
6993
22028
4 DISCUSSION
The developed simulation tool aims to capture all the
main elements of the winter navigation system: ice-
going ships, icebreakers, varying ice conditions, and
varying situations for independent navigation and
assisting ships in ice. These elements are challenging to
simulate. Firstly, the ice-going performance of vessels
and icebreakers depends on many specific technical
parameters of a ship and may vary for different ice
conditions. For example, an icebreaker designed for
navigation in a lake may not necessarily show the best
performance for navigation in sea ice. Secondly,
modeling ice conditions is challenging. Ice is very
dynamic it changes fast, even for one day. Moreover,
it is usually necessary to reflect all the complexities of
ice conditions and reliably simulate the average speed
of a ship using only one value of the equivalent ice
thickness. That is why the evaluation of the equivalent
ice thickness needs accurate physics-based models to
simulate the ship performance in varying ice
conditions.
A critical aspect of the WNS simulation studied in
the present research is how to model the decision-
making process of icebreaker captains coordinating all
maritime operations during wintertime. This has a
significant effect on the efficiency of the winter
navigation system. This decision-making process
should include knowledge of the allocation of
icebreakers in the studied region and how their
availability changes in time, a summary of the ships
being in or approaching the studied area and their ice-
going performance, recommended routes for ships to
follow and receive icebreaker assistance, and the most
probable development of ice conditions in the near
future.
Figure 12. Scenario 3, vessels are congested in Zone 3, but
Zones 1 and 2 are free from the ship traffic.
Figure 13. Optimized operation schedule for icebreakers in
the Bay of Bothnia. The icebreakers are redistributed to
provide more assistance in Zone 3.
Figure 14. Scenario 5, awaiting vessels are equally distributed
per zones.
The newly developed functionality allowed us to
analyze how some of these parameters affect the WNS
performance. We studied the isolated and combined
influence of changing the dynamics of the icebreaker
resource availability, optimizing ice-breaker allocation
in the Bay of Bothnia, and varying the directed
pathways on the WNS efficiency. The results of the case
studies revealed the complex, non-trivial effects of the
studied factors, especially when different measures are
applied simultaneously. We conclude that the total
waiting time is susceptible to the examined factors and
recommend considering them if the total waiting time
is essential for decision-making. However, unlike some
WNS parameters considered in the study by
Kondratenko et al. [15], the examined factors affect
CO2 emissions insignificantly under the studied
conditions and assumptions.
The calculations indicated that optimizing
icebreaker allocation in the Bay of Bothnia is the most
effective isolated measure to reduce the total waiting
time by up to 35%. Based on the case studies, we
concluded that solely extending the availability of all
icebreakers for the entire simulation period does not
improve the performance of the WNS. The latter,
however, may indicate that the icebreaker availability
schedule used in the basic scenario is already near-
optimal for the basic allocation of the icebreakers.
Complementing the optimized icebreaker allocation
with the extended availability of the icebreakers
provides an additional 7% reduction in the total
waiting time, resulting in a 42% reduction compared to
the basic scenario. Further enhancing the WNS through
the improved directed pathways gives 6% less total
waiting time, resulting in a 48% total reduction
compared to the basic scenario.
The case studies, therefore, demonstrate that more
intelligent usage of the existing resources (through
optimizing icebreaker allocation and directed
pathways) may be much more efficient than the
expensive usage of more resources (through the charter
1139
of icebreakers for a more extended period). We may
conclude that the development of the WNS simulation
tools has significant prospects for uncovering the full
potential of the ice-going fleet.
The demonstrated simulation tool has the following
limitations. Firstly, in the present form, the tool mainly
uses the maximum waiting time for ice-going ships as
the main decision-making criteria, which is naturally
too simple. Secondly, the methods used to evaluate the
equivalent ice thickness for these ice conditions need
further re-search on how to link the equivalent ice
thickness calculation methods to the main particulars
of the ice-going ships so that the performance-
equivalence, rather than volume-equivalence, ice
thickness can be achieved. Historically, ship
performance in level ice has been the dominating
research area for developing analytical formulations
for ship resistance. The other ice conditions, such as
ridges, dynamic moving ice, and ice floes with varying
concentrations, have obtained less attention. Although
some randomness has been included in this paper,
significant uncertainties are still associated with
information about ice conditions and ship performance
evaluation. Quantification of such uncertainties can be
an important direction for future work.
However, the results of applying the system-level
simulation tool are promising despite the existing
challenges. This is a unique tool worldwide simulating
all the main elements of the winter navigation system.
5 CONCLUSIONS
The ice presence complicates maritime navigation in
northern regions, which requires better ice-going
qualities of ships and icebreaking assistance.
Developing a simulation tool to study the performance
of winter navigation activities in the Baltic Sea region
at the maritime system level may significantly improve
the quality of decision-making, resulting in more
efficient and sustainable shipping. In the present
paper, we demonstrated newly developed algorithms
and case studies for the simulation of the Finnish-
Swedish Winter Navigation System to predict the need
for icebreakers and to plan their operation policies in
the future. Specifically, extending the methods [4] and
[15] with the newly developed functionality allowed us
to analyze the influence of changing the dynamics of
the icebreaker resource availability, optimizing ice-
breaker allocation in the Bay of Bothnia, and varying
the directed pathways on the WNS efficiency. The
results of the case studies demonstrated that the total
waiting time is significantly sensitive to the studied
factors.
We concluded that optimizing icebreaker allocation
in the Bay of Bothnia is the most effective isolated
measure to reduce the total waiting time and that solely
extending the availability of all icebreakers for the
entire simulation period is not always effective.
Complementing the optimized icebreaker allocation
with the extended availability of the icebreakers and
the improved directed pathways may result in a 48%
total re-duction of the total waiting time compared to
the basic scenario. The case studies demonstrated that
more intelligent usage of the existing icebreaker
resources may be much more efficient than the
expensive usage of more resources.
The tool has significant potential to provide
recommendations to reduce the total waiting time of
the transport ships for icebreaking assistance.
However, it is necessary to advance the methodology
for estimating the equivalent ice thickness [28-30] and
calculating h-v curves for different ships and ice
conditions for more reliable modeling of the ship
performance in ice, e.g., by means of ice tank
experiments [31-35].
STATEMENTS AND DECLARATIONS
The paper reuses the vector map of Europe distributed under
the Creative Commons Attribution-Share Alike 4.0
International license
(https://commons.wikimedia.org/wiki/File:Blank_map_of_E
urope_cropped_%28blue%29.svg). In addition, the authors
would like to thank Aker Arctic Technology Inc for providing
the sample ship database containing established h-v curves.
FUNDING STATEMENT
This work has been realized with financial support by the
European Regional Development Fund within the
Operational Programme “Bulgarian national recovery and
resilience plan”, Procedure for direct provision of grants
“Establishing of a network of research higher education
institutions in Bulgaria”, under the Project BG-RRP-2.004-
0005 “Improving the research capacity and quality to achieve
international recognition and resilience of TU-Sofia.
Author 1 is also supported by the POTENT-X project funded
under the Clean Energy Technology Partnership (CETP) with
funding from the Swedish Energy Agency, Innovation Fund
Denmark, Agencia Estatal de Investigación (AEI), Spain, and
the European Commission (GA N°101069750).
Author 2 was supported by the Academy of Finland project:
Towards human-centered intelligent ships for winter
navigation (Decision number: 351491). Author 5 received
funding from the Science and Technology Commission of
Shanghai Municipality (Project No. 23YF1419900).
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