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Review

A Systematic Mapping of Emission Control Areas (ECAs) and Particularly Sensitive Sea Areas in Maritime Environmental Governance

by
Deniece Melissa Aiken
* and
Ulla Pirita Tapaninen
*
Estonian Maritime Academy, Tallinn University of Technology, Kopli 101, 11712 Tallinn, Estonia
*
Authors to whom correspondence should be addressed.
Oceans 2025, 6(3), 60; https://doi.org/10.3390/oceans6030060
Submission received: 15 July 2025 / Revised: 9 September 2025 / Accepted: 16 September 2025 / Published: 18 September 2025

Abstract

Climate change has exacerbated the need for transitional shifts within high-impact sectors, notably maritime transport, which facilitates nearly 90% of global trade. In response, the International Maritime Organization (IMO) has implemented stricter environmental regulations under MARPOL Annex VI, which includes, among other things, the designation of Emission Control Areas (ECAs) and Particularly Sensitive Sea Areas (PSSAs). These regulatory instruments have prompted the uptake of new technologies, such as scrubbers, LNG propulsion, and low-sulfur fuels to mitigate emissions in these zones. However, emerging evidence has raised environmental concerns about these solutions which may offset their intended climate benefits. This study investigates the hypothesis that ECAs and PSSAs act as catalysts for maritime environmental advancements through a systematic mapping of 76 peer-reviewed articles. Drawing on data from Scopus and Web of Science, the study analyzes trends in technological advances, publication timelines, geographic research distribution, and the increasing role of decision-support tools for regulatory compliance. Findings show increased academic outputs particularly in China, North America, and Europe, and suggest that achieving effective emissions reduction requires globally harmonized policies, bridging research practice gaps, and targeted financial support to ensure sustainable outcomes throughout the sector. The study suggests that for ECAs and PSSAs to deliver truly sustainable outcomes, global regulation must be supported by empirical performance assessments, environmental safeguards for compliance technologies, and targeted support for developing maritime regions.

1. Introduction

The shipping sector, which transports close to 90% of all goods globally, sits at the core of global trade; hence, there is no question about the industry’s economic importance [1,2]. Systemic changes in many industrial sectors have been sparked by the growing urgency of climate change, and maritime transport is coming under increased scrutiny because of its effects on the environment [3]. Large diesel engines burning heavy fuel oil have dominated maritime shipping for decades and have been found to generate air pollutants including sulfur oxides (SOx), nitrogen oxides (NOx), and particulate matter (PM) [4]. Previous studies estimate that PM from shipping emissions resulted in approximately 60,000 cardiopulmonary and lung cancer deaths globally per annum, most of which occurred near coastlines in Europe, East Asia, and South Asia [5].
Maritime decarbonization, which aims for the total elimination of carbon emissions by 2050, has been at the forefront of the international maritime agenda since the early 2000s. To achieve this lofty goal, the International Maritime Organization (IMO) established frameworks to mitigate the environmental impacts of shipping under a global greenhouse gas strategy. This includes the introduction of global fuel standards, mid-term decarbonization measures, and various market-based approaches that aim to incentivize the shift towards more sustainable practices [6]. Prior to the introduction of these recent initiatives, the global focus was geared initially towards the protection of the marine ecosystem. These protection mechanisms were under established as regulatory measures under the International Convention for the Prevention of Pollution from Ships (MARPOL).
Dubbed as special areas, emission control areas more general in scope aim to remove SOx, NOx, and Particulate Matter (PM) from the atmosphere, while particularly sensitive sea areas (PSSA) emerged from a concern due to vessel-source pollution, and require special protection due to their “recognized ecological, socio-economic, or scientific attributes which may be vulnerable to damage by international shipping activities” [7,8,9]. Since 1990, the IMO has established 15 PSSAs, with regulations evolving alongside changing patterns. Sulfur content limits in marine fuel have tightened over time, reaching 0.50% m/m globally in 2020 and 0.10% m/m limit within ECAs since 2015 [10].
Between 2006 and 2016, four emission control areas under MARPOL Annex VI were established. These regulatory zones were initially established in regions such as the Baltic Sea and the North Sea and have since been extended to other regions such as the United States Caribbean Sea and the North American coastline [8]. The Mediterranean became the fifth ECA as of 1 May 2025, with the Canadian Arctic and the Norwegian Sea both concurrently becoming the sixth and seventh ECAs for NOx and SOx on 1 March 2026 and 1 March 2027, respectively [11]. This will result in a close to 50% global regional sea coverage being designated ECAs under MARPOL Annex VI. The introduction of these zones accelerated the adoption of technological and operational innovations in shipping.
To comply with these regulations, shipowners have been forced to choose from a variety of methods, each with significant operational, financial, and technical implications. Switching to low-sulfur fuels or the use of scrubbers have become the most popular mechanisms employed by shipowners due to the lack of technology support and shore-based infrastructure [12]. Scrubbers, also called exhaust cleaning systems, are of two types: dry and wet. Dry scrubbers use absorbents to remove SOx from the exhaust gas, while wet scrubbers are devices that remove SOx and other pollutants by washing them with a liquid before the gases are released. These systems are allowed under MARPOL once the SOx content released remains within the regulatory limits [13]. Both scrubbers and low-sulfur fuels do not require extensive operational intervention and extensive crew restructuring and management and are generally adopted amongst the shipowners. Studies have also shown that alternative fuels, such as LNG, hydrogen, and methanol, have the potential to reduce CO2 emissions by upwards of 20% to 100%, depending on the type [14]. Additionally, other strategies like slow steaming and advanced voyage planning, are increasingly being used to reduce emissions and operating costs.
Regional variations in ECA and PSSA compliance result from a number of factors that ultimately impact their efficacy. Enforcement and supervision are two examples of such factors. Research indicates that enforcement asymmetries result from lack of institutional capacity and resources to oversee adherence to maritime regulations [15,16]. As a crucial enforcement tool, Port State Control (PSC) examines ships to make sure they adhere to international agreements [17]. However, there are issues when state-to-state variations in inspection rates and standards are significant. Thus, this gives ships a way to possibly take advantage of these legal loopholes by strategically changing their routes or fuels to save money on compliance fees [18].
The disparity in enforcement capabilities among MARPOL signatories leads to a patchwork of compliance, where flag states may not always exercise stringent oversight, which could lead to a climate of noncompliance [15]. Coupled with this is the added concern about the environmental effects of the mitigating technologies and strategies. Although scrubbers quickly emerged as the solution of choice for many shipowners, states in exercising their authorities under Article 211(3) of the United Nations Convention on the Law of the Sea (UNCLOS) took a counteractive move. As of June 2020, a total of sixteen ports restricted the use of scrubbers. Specifically, twelve of these banned open-loop scrubbers [19]. Several studies demonstrate that scrubber water contains very high concentrations of pollutants, and implied that the use of scrubbers could potentially even add a new source of metal pollution from ships to the environment [20]. Recognizing this, an increasing number of states have since further imposed strict restrictions or full bans on scrubber water discharge from both open- and closed-loop scrubbers due to concerns over heavy metals in discharge effluent [21].
Similarly, while LNG has been adopted as a cleaner fuel alternative, it has been found that methane slip may undermine its climate benefits, potentially making it more harmful than conventional marine fuels in the long term [22]. This raises questions about the long-term role of LNG in meeting the industry’s decarbonization goals and highlights the need for life cycle assessments when evaluating fuel alternatives [23,24,25]. The evolving role of ECAs and PSSAs in maritime governance underscores not only the progress made in environmental regulation but also the complexity of the environmental performance of the mitigating technologies and strategies, as well as ensuring universal adherence to these standards. Aside from the acknowledged issues of enforcement disparities and exacerbated environmental risks, the impacts of the expansion of ECAs into areas like the Canadian Arctic and the Mediterranean on compliance tactics remain underexplored. Existing research emphasizes that although there is a large body of national, regional, and international regulations, their efficacy depends on strong oversight and effective implementation [2]. Considering that a large share of the world’s energy output still comes from fossil fuels, fragmented investment and adoption of alternative energy solutions alongside uneven regulatory implementation create perpetual industry uncertainty that has not been studied to any great extent.
This study systematically maps the existing literature to clarify how ECAs and PSSAs have influenced compliance strategies and driven innovation within the maritime sector, offering critical insights into jurisdictional approaches and identifying areas in need of further research. While the primary aim is descriptive, capturing trends in technological development, regulatory focus, and regional disparities, the study is also motivated by an exploratory hypothesis: ECAs and PSSAs act as catalysts for maritime environmental advancements, as evidenced through technological responses, policy evolution, and scholarly discourse. In this study, such advancements are conceptualized as technological and operational progress. The hypothesis is supported by four research questions that aim to provide focused, analytical depth. These are as follows: RQ1—How have Emission Control Areas (ECAs) and Particularly Sensitive Sea Areas (PSSAs) influenced the development and adoption of low-emission maritime technologies since their implementation? RQ2—What patterns and trends emerge from the academic literature on ECAs and PSSAs in terms of geographic focus, methodological approaches, and thematic priorities? RQ3—What role do multi-criteria decision-making models play in supporting sustainable fuel selection and operational strategy compliance within special emission zones? RQ4—What are the main regulatory, economic, and operational challenges faced by stakeholders in complying with MARPOL’s emission zone regulations, and how do these challenges vary across global regions?
The study assesses the extent to which peer-reviewed literature supports this proposition and seeks to determine whether special areas not only ensure compliance but also act as catalysts for innovation and systemic change. The remainder of this paper is organized as follows: Section 2 outlines the methodology used for data collection, selection, and analysis, including bibliometric and thematic clustering approaches. Section 3 presents the results, including trends in publication output, geographical distribution of research and key thematic clusters. Section 4 offers a critical discussion of the findings in relation to technological development, economic implications, and regulatory governance. Finally, Section 5 concludes the paper by summarizing key insights and offering recommendations for future research.

2. Materials and Methods

In the study we applied the systematic mapping study (SMS) process, which enabled the authors to cover a wide range of publications within the focus of the study. SMS presents several methodological strengths that make them particularly suitable for interdisciplinary and evolving research domains. The primary advantage of this methodology is that it enables the clear identification of research gaps, state-of-the-art research areas and sub-areas through a structured process [26]. Systematic mapping studies provide a broad coverage of the research landscape, offering a structured overview of the volume, distribution, and thematic orientation of publications. This allows for the clear identification of research gaps, capturing state-of-the-art trends and mapping the diffusion of ideas across disciplines [27]. In essence, it provides a structured way of surveying a broad research domain. While systematic mapping studies are closely related to systematic literature reviews, there are some separative distinctions. Systematic literature reviews focus on synthesizing evidence to answer narrowly defined questions, while SMS emphasizes keyword-based classification and categorization of studies to map the distribution of research activity [28]. Systematic mapping studies differ in terms of how the probe is approached, as well as how publications explored and reviewed, and are particularly valuable in emerging and heterogenous fields where evidence is fragmented and evolving [29,30]. The process began with the development of research questions in support of the main hypothesis. The research questions developed to guide the study are as follows:
  • RQ1—How have Emission Control Areas (ECAs) and Particularly Sensitive Sea Areas (PSSAs) influenced the development and adoption of low-emission maritime technologies since their implementation?
  • RQ2—What patterns and trends emerge from the academic literature on ECAs and PSSAs in terms of geographic focus, methodological approaches, and thematic priorities?
  • RQ3—What role do multi-criteria decision-making models play in supporting sustainable fuel selection and operational strategy compliance within special emission zones?
  • RQ4—What are the main regulatory, economic, and operational challenges faced by stakeholders in complying with MARPOL’s emission zone regulations, and how do these challenges vary across global regions?
These questions focused on the emission control and particularly sensitive sea areas and the resultant effects of these policies on the shipping sector.
The SMS process should be carried out meticulously and transparently according to a prescribed process which aligns consecutive steps with an outcome throughout each phase. The literature analyzed in the study was retrieved from two databases, selected based on their expansive scope and applicability to the domain of study. The strategically selected databases are Scopus and Web of Science, both of which are generally accepted as the most comprehensive multi-purpose data sources [31]. Of the two, Web of Science was first established and emerged as the most influential bibliographic data source; while Scopus, although later established, is now proven to be a reliable source for a wide range of available research across multiple fields [32,33]. The keywords used to conduct the searches were influenced by the research questions probing the study. As such, several combinations of keywords were used, such as “special emission control area AND SECA”, “MARPOL Annex VI AND environmental protection”, “shipping regulations AND technology AND special area”, “particularly sensitive sea area AND PSSA”, and “emission control area AND ECA”.
As depicted in Figure 1, the search yielded an overall total of 358 papers, which were then put through a phased screening process. Following the initial screening, which involved reading of the title, abstract, and keywords, a total of 169 studies deemed irrelevant were removed from the dataset. An additional 39 papers were excluded due to inability to access the full text, leaving a total of 150 papers as potentially relevant to the study. Thereafter, 64 duplicate entries were identified and removed, resulting in a total of 86 unique and potentially relevant papers. At the final stage, a full text review was performed for each paper.
To ensure relevance and contextual appropriateness, the papers were screened based on the inclusion of operations within emission control areas or particularly sensitive sea areas. The papers which included regulatory focus, technological content, as well as environmental and operational aspects were also included. To maintain methodological rigor, the type of study was also taken into consideration, with a focus on empirical investigations or other quantitative or qualitative studies. Following this review, 10 papers were excluded as they were not considered relevant to the focus of the study, leaving a total of 76 relevant papers for analysis.
Among the studies reviewed, 67 studies examined emission control areas, and 9 studies examined particularly sensitive sea areas (see Table 1). None of the studies analyzed both topics together. They were treated separately with no overlap in the same publication.

3. Results

The mapping results are presented according to the research questions. The analysis of the 76 reviewed studies reveals a clear upward trajectory in academic interest surrounding ECAs and PSSAs over the past two decades (see Figure 2). The timeline illustrates a relatively dormant period between 2004 and 2012, with only one to two publications per year. This stagnation reflects the early stages of policy development and limited real-world implementation of ECA and PSSA frameworks during that period.
A gradual increase began in 2013, coinciding with the introduction and enforcement of stricter sulphur emission limits under MARPOL Annex VI. Specifically, this period aligns with the implementation timeline of Resolution MEPC.176(58), adopted in October 2008, which amended Annex VI to reduce allowable sulfur content in marine fuel. Under this amendment, the sulfur cap within designated ECAs was reduced to 0.10% m/m, while the global cap was scheduled to decrease to 0.50% m/m. Although the global sulfur cap did not take effect until later, the 2013–2015 period was marked by compliance preparations, intensified research into technological and economic impacts, and early enforcement measures in existing ECAs such as the Baltic Sea (since May 2005), North Sea (since November 2006), and the North American ECA (August 2011). The number of publications rose steadily from 2014 onward, with notable surges in 2015 and again between 2018 and 2022.
The peak in 2022 (12 papers) marks the highest annual output in the dataset, indicating the intensifying focus on compliance strategies, regulatory enforcement, and technology evaluation as the shipping industry braced for full implementation of the IMO 2020 global sulfur cap. Although there was a temporary decline in 2023, the literature rebounded in 2024, concurrent with discussions about a new PSSA designation in the Arctic and a shift in attention toward institutional governance, regional enforcement disparities, and the integration of ECAs into broader climate regimes. This is followed by a moderate count in 2025 (to date), which reflects sustained engagement, especially around emerging technologies, digital enforcement tools, and evolving policy mechanisms such as carbon pricing and green corridors.
The literature also spans a diverse array of academic journals, reflecting the interdisciplinary nature of maritime environmental governance. As illustrated in Table 2, the highest concentration of publications is found in Transportation Research Part D: Transport and Environment (10 papers), underscoring its central role in publishing work at the intersection of transportation policy and environmental sustainability. Marine Policy (7 papers) also serves as a key outlet for regulatory and governance-focused studies related to maritime emissions and conservation zones. Other journals with notable representation include Marine Pollution Bulletin (4 papers), known for its focus on marine environmental risks and mitigation strategies, and Journal of Cleaner Production and Maritime Policy & Management (2 papers each), which frequently publish techno-economic and operational analyses.
The diverse scope of other journals indicates the breadth of methodological approaches, from atmospheric modeling and life cycle assessment (LCA) to legal analysis and policy evaluation. This distribution reveals that ECA and PSSA research is not confined to a single academic domain but is instead dispersed across transportation, environmental science, technology, law, and engineering. The spread also reflects the growing integration of regulatory discussions into journals with a highly technical focus, highlighting the increasing relevance of emissions control zones in broader environmental and infrastructure discourses.

3.1. Technological Response to Emission Regulations (RQ1)

The introduction of tightening regulations within shipping expectantly results in significant operational, design, and management changes. The findings from the systematic mapping study highlight that since the establishment of ECAs and PSSAs, there have been progressive technological responses and adaptations to meet the new restrictive measures. There was diverse focus within the papers. Only 8 of the papers had a purely technical focus, while 13 included a combined technical and economic analysis, along with other combinations of policy, technical, technological, and economic discussions.

3.1.1. Scrubbers

As depicted in Figure 3, the most frequently analyzed technologies or solutions were scrubbers accounting for 19 studies. According to the literature, these measures were favoured as they facilitated fast compliance at a relatively low cost. With scrubbers or exhaust gas cleaning systems, shipowners can continue operating on high-sulfur fuels and removing sulfur oxides from the exhaust gases before they pollute the air. Many of the studies explored the technical efficiency of scrubbers and their ability to enable compliance with the IMO sulphur regulations. Studies discussed the design of scrubbers, discussing the efficiency of closed loop as opposed to open loop scrubbers. However, the analysis extended into looking at the cost-effectiveness, return on investments and a few on the environmental impacts. It was highlighted that this measure came with a high capital cost but with long term benefits. As such, as mentioned in some studies, these are primarily suitable for large vessels which frequent the emission control areas or multiple ECAs throughout their voyages. By comparison, shore power appeared less frequently in the reviewed studies (2 studies), despite it being a highly regarded measure in port areas, especially in ECAs and PSSAs where local air quality is a high concern, such as the Baltic Sea area.

3.1.2. Alternative Fuels

The use of alternative fuels was also mentioned in a significant number of studies. Liquified natural gas (LNG) is used as a compliance strategy in a number of studies—17 in total. Despite recognized infrastructure limitations and high investment requirements, LNG was popular among newly constructed vessels (Figure 4). Numerous studies also addressed the need for port bunkering facilities. However, it was discovered to have provided notable decreases in SOx, NOx, and particulate matter. Low-sulfur fuels were also considered to be MARPOL Annex VI compliant but were not very effective in contributing to long-term GHG mitigation. Four studies discussed other alternative fuels, such methanol, biodiesel, and ammonia which are mostly evaluated in simulation or pilot contexts as their real-world application is affected by lack of knowledge, technical immaturity, danger risks, and lack of or limited bunkering and safety infrastructure.

3.1.3. Dual-Fuel Engines and Selective Reduction Systems

The use of selective catalytic reduction systems and dual-fuel engines was elaborated in 3 studies each. Other technological measures included unmanned aerial vehicles or drone-based emission monitoring which was in 4 studies and artificial intelligence-based routing in 1 study. Methanol, waste heat recovery and shore power were included in 2 studies. In contrast, the few studies that addressed PSSAs emphasized operational adjustments rather than technological adoption. These included rerouting, speed reductions, and increased navigational awareness, particularly in biodiversity-sensitive zones such as the Tubbataha Reefs or the Bering Strait. No studies reported the direct adoption of emissions reduction technologies in response to PSSA designation.

3.2. Geographic, Methodological, and Thematic Patterns (RQ2)

3.2.1. Geographic Distribution of Studies

There is significant regional, methodological, and thematic clustering in the literature on ECAs and PSSAs. A proportionate breakdown of studies by region is shown in Figure 5, which emphasizes the concentration of ECA and PSSA research in a small number of jurisdictions. According to the country’s policy on domestic ECAs in the Pearl River Delta (2016), Yangtze River Delta (2017), and Bohai Rim (2018–2019), 29% of the studies in the dataset are from China. Policy enforcement, fuel switching tactics, and the use of remote sensing technologies like satellite-AIS and unmanned aerial vehicles (UAVs) for emissions monitoring and compliance verification were the main topics of research in this area.
In order to assess government-led subsidy schemes and infrastructure retrofitting programs targeted at reducing emissions, Chinese studies generally combine empirical ship-level data with techno-economic modelling. Among the first ECAs designated under MARPOL Annex VI were the North Sea and Baltic Sea regions, which accounted for 24% of studies. Research in this area focusses on the economic effects of strict emissions regulations as well as technological mitigation strategies, such as the use of LNG propulsion technologies and exhaust gas cleaning systems (scrubbers). The modal shift risk, where stringent sulfur caps may unintentionally divert cargo from maritime to road or rail transport, recurs frequently. Thanks to consistent EU funding and data availability, these studies commonly use cost–benefit analyses, optimization modeling, and policy scenario evaluations.
Literature from North America (20%) which covers the U.S. and Canadian ECAs and the Caribbean Sea, primarily address regulatory enforcement, cost-mitigation strategies, and compliance behaviour. The Mediterranean Sea, representing 11% of studies, is currently undergoing deliberations for ECA designation. Accordingly, studies in this region are largely predictive and policy-driven, using scenario-based modeling and stakeholder engagement analysis to project the environmental, economic, and political consequences of ECA implementation. These studies underscore the need for regulatory harmonization among EU and non-EU Mediterranean states, reflecting the region’s complex geopolitical fabric. Southeast Asia accounts for 9% of studies, predominantly related to PSSA proposals and governance design. Areas like the Lombok Strait and Tubbataha Reefs are commonly cited as high-priority regions for protection. The Arctic and Bering Strait region, representing 7% of the literature, adds a unique dimension by emphasizing climate vulnerability, indigenous governance structures, and resilience-based maritime policy frameworks.

3.2.2. Methodological Patterns in the Literature

The study shows that empirical and optimization-based methods clearly predominate, especially in research pertaining to ECA, as shown in Figure 6. About one-third (25) of the reviewed papers are empirical studies, making them the largest methodological category. To assess ship-level compliance, emissions trends, and enforcement results, these investigations usually make use of Automatic Identification System (AIS) data, port call logs, and onboard fuel sampling. Remarkably, Chinese research was the first to monitor compliance using remote sensing technologies, such as high-resolution satellite imagery and unmanned aerial vehicles (UAVs). On the other hand, studies conducted in North America and Europe use longitudinal data from emissions inventories and vessel tracking systems.
With 18 studies, optimization modeling is the second-most common approach, as shown in the figure. These studies examine compliance tactics, technology investments, and financial trade-offs using mathematical programming, route and speed optimization, and multi-objective decision-making frameworks. Decisions regarding the installation of scrubbers, the use of dual-fuel engines, and the best routes for navigation within and around ECAs are among the subjects covered. The PSSA literature is primarily linked to case study methodologies, which are used in 14 studies. These studies examine how policies are implemented, how stakeholders interact, and how institutions have changed.
Legal analyses, found in 9 studies, are similarly concentrated in the PSSA literature, where regulatory innovation, normative discourse, and jurisdictional complexity play a central role. These studies interpret international legal frameworks, including MARPOL Annex VI and relevant IMO resolutions, and frequently engage with governance challenges in Areas Beyond National Jurisdiction (ABNJ). A smaller yet emerging strand of the literature (6 studies) employs life cycle assessment (LCA) methodologies to evaluate the full environmental footprint of emission reduction technologies and alternative fuels.

3.2.3. Thematic Patterns in the Literature

Five related thematic clusters that represent changing research priorities can be found in the literature on ECAs and PSSAs. These clusters, which are compiled in Table 3, are influenced by disciplinary influences, methodological philosophies, and region-specific issues. The majority of the reviewed literature focusses on technological interventions. This body of work makes extensive use of key terms like “scrubbers”, “LNG”, “fuel switching”, and “shore power”. In areas with strong environmental enforcement regimes, such as the North and Baltic Seas, China, and North America, empirical case studies, techno-economic analysis, and simulation modeling are particularly common.
The application and effectiveness of regulatory tools under MARPOL Annex VI represent yet another recurring theme. This category of studies focusses on ECA enforcement mechanisms, frequently using compliance metrics and real-time tracking technologies to evaluate the effectiveness of port-state control and flag-state behavior. A key component of this line of work is the incorporation of digital surveillance technologies, such as Automatic Identification Systems (AIS), Unmanned Aerial Vehicles (UAVs), and on-board fuel sampling. This cluster also includes a significant number of legal analyses that look at the uniformity and jurisdictional scope of international enforcement regimes. Scholarship pertaining to PSSA is typically more institutionally orientated, with a focus on stakeholder engagement, designation procedures, and governance innovation. The application of qualitative techniques like discourse analysis, institutional mapping, and policy analysis defines this cluster. Intergovernmental coordination, ecological vulnerability assessments, PSSA designation criteria, and integration into marine spatial planning are common themes. Growing regional interest in flexible, context-specific governance models is reflected in case studies from the Mediterranean, Southeast Asia, and the Arctic.
Novel regulatory and technological paradigms related to maritime decarbonization from the Mediterranean and globally are covered in a more recent and forward-looking body of literature. This cluster is dominated by scenario modeling and policy forecasting techniques, which demonstrate an interdisciplinary shift towards long-term, scalable solutions. The International Maritime Organization’s (IMO) changing stance on greenhouse gas emissions and the industry-wide movement towards low- and zero-emissions shipping are closely aligned with this literature. The externalities and system-wide feedback effects of regional environmental regulations are the focus of a critical line of research. Under this theme, studies look into topics like emissions leakage from deliberate route changes to avoid ECAs and modal shifts from sea to land transportation. To measure these effects, cost–benefit analysis and optimization modeling are commonly used.

3.3. Role of Decision Models in Fuel Selection and Compliance Strategy (RQ3)

A key tool in the literature on maritime emissions compliance, especially in ECAs, is decision-support modeling. At least 15 of the 76 reviewed studies use formalized modeling techniques to guide compliance strategies in the face of uncertainty. Real Options Analysis (ROA) is a well-known method in this field that has been used to evaluate the timing of capital-intensive decisions like installing LNG propulsion systems or equipping ships with scrubbers. Based on dynamic factors like anticipated fuel price spreads, anticipated ECA enforcement dates, or anticipated regulatory tightening, ROA offers a framework for delaying or staging investments. This approach recognizes the importance of managerial adaptability in a setting where market and regulatory conditions are constantly changing.
Another popular method is Multi-Criteria Decision Analysis (MCDA), which is especially useful when there are several, frequently incompatible goals that need to be reconciled, like technical viability, cost reduction, and emissions reduction. Structured comparisons of alternative technologies or operational configurations are made possible by MCDA frameworks, such as weighted-sum and Pareto-front approaches. These models facilitate integrated decision-making in a variety of domains, including adaptive routing, dual-fuel engine installation, and fuel switching. The most widely used optimization technique for operational planning is Mixed Integer Programming (MIP). Routing, bunkering, and retrofit scheduling problems, where discrete decisions must be made under capacity, time, and emissions constraints, are especially well-suited for MIP models. Granular planning is made possible by these models, which frequently include regulatory thresholds, geographic ECA boundaries, and technical vessel specifications.
Complementing this systems-based overview, Figure 7 illustrates a matrix heatmap detailing the frequency and specificity of modeling approaches across different application areas.
The image demonstrates that MIP is primarily utilized in operational decision-making, ROA in investment timing and uncertainty management, and MCDA in fuel choice evaluations. Although they are less frequently used, game theory and portfolio optimization models aid in the analysis of competitive behavior and compliance strategy diversification under emissions regulation. The literature on investment planning is where portfolio optimization techniques are most commonly found. Game theory models, on the other hand, shed light on the strategic relationships between businesses subject to emissions regulations.

3.4. Regional Variation in Compliance Challenges (RQ4)

In addition to modeling, the literature finds enduring regional disparities in MARPOL Annex VI implementation and adherence. A radar chart that summarizes the five main aspects of the compliance burden in five important maritime regions is shown in Figure 8. Based on qualitative and quantitative indicators taken from the literature, each axis is given a score on a scale from 1 (low challenge) to 5 (high challenge). The overall burden of compliance is lowest in the European Union. Consistent monitoring and enforcement have been made possible by robust institutional infrastructure, harmonized legal frameworks, and high port-state control capacity. As a result of its developed regulatory framework, the EU scores particularly low for infrastructure and monitoring-related issues. The US, on the other hand, shows moderate levels of challenge. Despite a strong enforcement infrastructure, legal complexity is introduced by the coexistence of federal and state regulations. For example, California’s separate emissions regulations can occasionally make it difficult for ships travelling between domestic and foreign waters to comply.
Despite significant investments in technologies like AIS-based tracking systems and UAV surveillance, China poses the greatest challenges for monitoring and enforcement. Despite the state and its region’s strong interest in green shipping initiatives, effective compliance is hampered by a lack of standardized regulations and a lack of adequate technical infrastructure. Due to its harsh climate, lack of regulatory infrastructure, and high operating costs, the Arctic region presents enforcement and financial challenges. This region’s strategic significance necessitates creative and collaborative compliance solutions, particularly in light of trans-Arctic shipping and proposed PSSA designations.
The absence of internationally standardized enforcement procedures is a recurring theme in the literature. Other regions, especially Southeast Asia and parts of the Global South, suffer from overlapping jurisdictions, inconsistent enforcement, and a lack of institutional capacity, while the US and the EU enjoy the advantages of well-funded and clearly defined enforcement systems. The practical effectiveness of PSSAs in safeguarding delicate marine environments is limited because enforcement mechanisms are frequently optional or symbolic. Route changes and speed reductions are also two examples of the logistical compromises frequently required to comply with ECA regulations. Although methods like slow steaming are good at reducing NOx, they can interfere with just-in-time port arrival systems and delivery schedules that are time-sensitive.
The stacked column chart in Figure 9 provides a comparative visual of compliance challenges across the five regions.
China has the most challenges mentioned overall, with economic (4 studies) and regulatory (5 studies) concerns taking center stage. China’s phased approach and top-down policy structure lead to implementation asymmetries despite significant investments in surveillance and regulatory rollout. While technological issues are less noticeable (2 studies), probably as a result of large state investments in innovation, operational issues, particularly those related to fuel switching and port compliance, are also noteworthy. With four studies each cited for technological, economic, and regulatory issues, the EU exhibits a more balanced challenge profile. These results demonstrate a robust legal system, the widespread use of alternative fuels, and intricate member-state coordination. Because of established infrastructure and reliable enforcement methods, operational issues are less commonly mentioned (2 studies).
Economic issues predominate in the U.S. (4 studies), which is indicative of the financial strains brought on by strict ECA laws at the federal and state levels. Concerns about technology (3 studies) and operations (3 studies) are also pertinent, especially in relation to the use of scrubbers and LNG compatibility. Due to the clarity of MARPOL’s incorporation into U.S. law and the ability of federal agencies to enforce it, regulatory issues (3 studies) are relatively subdued.
There is a clear trend in Southeast Asia, where the most commonly mentioned barriers are operational (4) and regulatory (4). These reflect the disparities in port readiness and the region’s disjointed legal systems. Two studies indicate that technological readiness is still in its infancy, indicating inadequate infrastructure and nascent shifts towards cleaner maritime technologies. According to one study, technological concerns are the least common in the Arctic, which is in line with the region’s limited emissions control infrastructure. However, jurisdictional complexity, delicate ecosystems, and a lack of adequate monitoring tools make regulatory (5) and operational (3) issues the most pressing. There are financial obstacles (2), especially for indigenous fleets and small operators who lack the funding necessary for complete compliance.
This comparative study shows that while highly developed maritime regions place a higher priority on cost effectiveness and technological advancements, other regions deal with more fundamental issues related to infrastructure, institutional capacity, and legal consistency.

4. Discussion

The discussion evaluates the review findings against the research questions and supports the hypothesis that special areas such as emission control areas and particularly sensitive sea areas serve as catalysts for operational and technological progress in the shipping sector.

4.1. RQ1—Scholarly Landscape of ECAs and PSSAs

The review reveals that research output on ECAs and PSSAs is concentrated in jurisdictions with strong regulatory frameworks such as China, North America, and the European Union. This is directly aligned to the global ECA and PSSA designation [42,108]. Further to the Baltic Sea, North Sea, and the U.S. Caribbean ECA designation under MARPOL Annex VI [8], China subsequently introduced its own Domestic Emission Control Areas (DECAs) in the Pearl River Delta, Yangtze River Delta, and Bohai Rim regions [52] aligning with the international sulphur limit standards. This mirrors the global distribution of designated areas and demonstrates the link between regulatory activity and academic attention.
A similar trend is seen in PSSA designation with the Wadden Sea, the Western European Waters PSSA, and the Florida Keys PSSA designation. More recently, the 2023 IMO Revised Strategy on the Reduction in GHG Emissions from Ships set more ambitious goals for the sector to reach net-zero GHG emissions by 2050, with indicative checkpoints in 2030 and 2040, and measures such as carbon pricing mechanisms, market-based measures (MBMs), and the promotion of green shipping corridors [6].
In parallel, recent regional initiatives such as the European Union’s Fit-for-55 package and FuelEU Maritime Regulation (Regulation 2023/1805), extend beyond traditional ECA/PSSA structures and incorporate lifecycle emissions accounting, shore power mandates, and stricter GHG intensity reduction thresholds for all European ports. These frameworks build on initial ECA and PSSA designations, reinforcing their catalytic role in the evolution of maritime environmental governance.
However, despite these advances, research remain disproportionately focused on high-regulation jurisdictions, with the absence of substantial contributions from developing regions, the Global South, and the Arctic reflecting a knowledge imbalance. As reflected in the literature, these regions often face greater compliance and enforcement challenges in upholding maritime environmental governance within their territories [16]. This imbalance risks overlooking key vulnerabilities due to limited institutional and regulatory capacity.

4.2. RQ2—Emerging Technological Patterns

The second research question (RQ2) explores the technical and strategic responses stimulated by the introduction of ECAs and PSSAs. The review showed that sulfur regulations have acted as regulatory triggers, accelerating the adoption of scrubbers, LNG propulsion, low-sulfur fuels, and digital emissions monitoring systems [11,12,13,14]. These regulatory mechanisms not only made immediate emissions reductions easier but also impacted fleet renewal plans and compliance expenditures. A key distinction emerging from the literature is between short-term and long-term compliance strategies. Switching to cleaner fuels and low sulphur fuels offered a comparatively lower capital requirement but resulted in higher operational costs. This pattern was typical of vessels operating in ECAs, especially those engaged in short sea shipping and feeder services with short transits and fixed routes. In contrast, LNG retrofits, scrubbers, and digital monitoring technologies involved higher investment but positioned operators for long-term regulatory resilience. These trade-offs highlight how compliance choices are shaped by both economic capacity and operational profile.
The review also exposes gaps in academic emphasis. Shore power, although widely recognized in policy and industry debates as a key emissions reductions measure, was underrepresented in the literature within the study. In the EU, the binding Alternative Fuels Infrastructure Regulation (AFIR), as well as the FuelEU Maritime Regulation mandate onshore power deployment and ship connection by 2030, underscoring the importance of this overlooked measure in the literature. This disconnect suggests that scholarly literature has focused on at-sea technologies, while underplaying port-based solutions that are increasingly central to the growing regulatory agenda.
On the other hand, PSSAs play a smaller role in operational compliance but remain significant in framing ecological vulnerability and conservation priorities.

4.3. RQ3—Decision Support Tools and Modeling

The literature indicates a growing use of modeling techniques such as Mixed Integer Programming (MIP), Real Options Analysis (ROA), and Multi-Criteria Decision Analysis (MCDA) to optimize fuel selection, investment timing, and routing [31,32]. These frameworks provide insights into trade-offs around fuel availability, emissions reduction potential, and regulatory uncertainty. However, while they demonstrate analytical sophistication, their reliance on simplified assumptions often strips away the political and institutional realities that ultimately determine compliance outcomes. This reliance on abstraction risks presenting compliance as a purely rational choice problem, when in reality it is shaped by uneven enforcement, lobbying, and geopolitical pressures. Regulatory compliance goes beyond technology and is shaped by political, institutional, and behavioral dynamics.
A recurring finding is the disconnect between technical modeling and real-world application. Most tools are developed in academic contexts that rarely account for institutional behaviour, enforcement capacity, or market constraints. As a result, their practical relevance is limited, and those facing the greatest regulatory uncertainty are often the least able to benefit from them. The review also highlights structural inequities in access to these tools. Small- and medium-sized operators frequently lack the knowledge, financial resources, or data inputs required to use these tools efficiently. Therefore, rather than levelling the regulatory playing field, decision-support frameworks run the risk of enhancing already-existing asymmetries in capacity and influence. As such, unless explicitly designed with inclusivity in mind, such models may worsen disparities in compliance, privileging resource-rich actors while leaving smaller operators behind.
More contextualized, multidisciplinary modeling approaches that take qualitative aspects into account are becoming more necessary in this context. Co-development of these models with industry actors is essential to ensure relevance and optimal applicability.

4.4. RQ4—Challenges and Compliance Gaps

The fourth question (RQ4) examines the regulatory, economic, and operational challenges stakeholders face in complying with MARPOL’s emission zone regulations, and how these challenges vary across regions. The review reveals sharp contrasts: developed jurisdictions such as North America and Europe benefit from access to capital, advanced Port State Control (PSC) systems, and digital monitoring tools, making compliance more manageable. On the other hand, as recent literature suggests, a “patchwork” of regulatory outcomes results from the lack of enforcement, a lack of personnel, and inadequate infrastructure in many coastal states in the Global South [16]. This imbalance suggests that global environmental governance risks reinforcing regional divides with ambitious rules benefitting those already well-equipped to comply while marginalized weaker actors lag behind.
The literature also shows that operational feasibility often trails regulatory ambition [33,69]. Financially constrained small- and medium-sized ship operators are more likely to rely on temporary compliance strategies like fuel-switching or slow steaming as they cannot afford to invest in alternative fuels or retrofit technologies. Emerging global measures like GHG pricing and fuel standards are likely to exacerbate these disparities. Recent policy shifts further complicate compliance strategies. As of July 2025, open-loop scrubber bans in several ports and coastal states, have reduced the viability of these abatement technologies, pushing shipowners toward LNG as a preferred alternative. Yet, LNG conversions can account for more than 15% of vessel construction costs, while scrubber retrofits can cost anywhere from $3 to $5 million per unit.
Even fuel switching entails significant operational costs due to volatility and dual-fuel management. This underlines the short-term financial pressures operators face, particularly in regions with limited access to maritime finance, where even cost-effective long-term solutions may be out of reach. The climate implications of LNG also challenge its role as a transitional fuel. Methane slip during combustion and handling carries a global warming potential over 80 times that of CO2, raising concern that this ultimately undermines decarbonization efforts [11]. The IMO has moved toward life cycle emissions accounting, reflected in recent regulations that are influencing global approaches to both new and existing emissions rules [8]. This development takes into account that technologies such as LNG or open-loop scrubbers, although better understood today, are unlikely to serve as long-term solutions due to their potential harmful impacts over time.
The review reveals an accelerating interest in maritime technological research and underscores the importance of future research on maritime environmental governance.

5. Conclusions

This study involves a systematic mapping of 76 peer-reviewed articles to assess the evolution and impact of Emission Control Areas (ECAs) and Particularly Sensitive Sea Areas (PSSAs) within the broader framework of maritime environmental governance. The review highlights several interconnected challenges. First, there is limited research on how these regulatory frameworks influence compliance mechanisms and the uptake of technological solutions, creating a gap between regulatory intent and operational outcomes. Second, despite the concerted push towards decarbonization, the shipping industry is still heavily reliant on fossil fuels and focused on transitional operational strategies rather than wholesale technological adoption due to cost, availability and other factors. Third, substantial regional disparities persist in the implementation of regulations which affect intended regulatory outcomes. Third, the decision-making models emerging from the literature, are highly theoretical with limited practical insights.
The findings support the central hypothesis that ECAs and PSSAs have served as catalysts for maritime environmental advancement, understood here as technological and operational progress. ECAs spurred the adoption of technologies and operations that support compliance with environmental regulations, including alternative fuels, the adoption of scrubbers, LNG propulsion, and digital emissions monitoring. ECAs have also influenced long-term fleet planning and compliance-related expenditures. On the other hand, PSSAs, although less impactful operationally, continue to play a key role in raising awareness of ecological vulnerability and governance.
The review reveals a rich and varied body of work that is primarily coming from high-regulation jurisdictions like China, North America, and the European Union. These studies illustrate the multifaceted nature of shipping decarbonization challenges by spanning disciplines such as engineering, economics, environmental science, and law. Furthermore, decision-making tools, such as multi-criteria decision analysis, real options analysis, and mixed integer programming are increasingly used to evaluate trade-offs in sustainable fuel adoption of compliance strategies, although their practical application remains limited. These tools help policymakers and shipowners make difficult decisions about fuel availability, potential for emissions reduction, when to invest, route selections, and regulatory uncertainty. However, because the many of the tools are created in academic settings and do not integrate with operational realities like institutional behavior, port-state enforcement, or commercial constraints, their impact is still primarily theoretical.
The study’s findings are limited by its reliance on English-language, peer-reviewed publications indexed in Scopus and Web of Science, excluding gray literature, regional policy reports, and non-English regional studies. The relatively narrow categorization of studies may oversimplify the interdisciplinary nature of maritime environmental research, limiting the ability to fully capture cross-cutting insights. Moreover, conclusions regarding post-2025 regulatory developments remain preliminary due to their ongoing implementation.
Future studies should broaden their geographic focus, to include perspectives from the Global South, and seek comparative and longitudinal evaluations of recently designated areas like the Mediterranean ECA and the Canadian Arctic. Equally important is the need to examine the use and compatibility of new digital compliance technologies, like digital twins, blockchain-based emissions tracking, and AI-driven regulation, which hold promise for enhancing compliance. Further inquiry into how industry strategies, compliance mechanisms, and technological choices evolve under conditions of climate stress, geopolitical contestation, and increasingly stringent environmental regulation will also be increasingly relevant.
Overall, the study amplifies that ECAs and PSSAs continue to be essential frameworks for forming an environmentally conscious and climate-resilient future for international shipping as regulations tighten and expectations change.

Author Contributions

Conceptualization, D.M.A. and U.P.T.; methodology, D.M.A.; validation, D.M.A.; formal analysis, D.M.A. and U.P.T.; writing—original draft preparation, D.M.A.; writing—review and editing, D.M.A. and U.P.T.; visualization, D.M.A. All authors have read and agreed to the published version of the manuscript.

Funding

This research was funded by the Interreg Central Baltic Programme under grant agreement no. CB0300186 project titled “Reducing CO2 emissions in island ferry traffic”. The views and opinions expressed are those of the author(s) only and do not necessarily reflect those of the granting authority as such the granting authority should not be held responsible for these views and opinions.

Data Availability Statement

No new data were created or analyzed in this study. Data sharing is not applicable to this article.

Conflicts of Interest

The authors declare no conflicts of interest.

Correction Statement

This article has been republished with a minor correction to the Data Availability Statement. This change does not affect the scientific content of the article.

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Figure 1. Systematic mapping process for the study.
Figure 1. Systematic mapping process for the study.
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Figure 2. Yearly distribution of peer-reviewed publications on ECAs and PSSAs from 2004 to 2005.
Figure 2. Yearly distribution of peer-reviewed publications on ECAs and PSSAs from 2004 to 2005.
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Figure 3. Technological adaptations reflected in the studies.
Figure 3. Technological adaptations reflected in the studies.
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Figure 4. Technology focus by study type.
Figure 4. Technology focus by study type.
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Figure 5. Geographic focus of the studies.
Figure 5. Geographic focus of the studies.
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Figure 6. Methodological patterns from the study.
Figure 6. Methodological patterns from the study.
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Figure 7. Heatmap of decision models.
Figure 7. Heatmap of decision models.
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Figure 8. Regional variation in compliance challenges from the study.
Figure 8. Regional variation in compliance challenges from the study.
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Figure 9. Stacked column of regional distribution of challenges from the study.
Figure 9. Stacked column of regional distribution of challenges from the study.
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Table 1. Overview of the literature contained in the study.
Table 1. Overview of the literature contained in the study.
Methodology/DisciplineArticles
AI/Operations Research & Scheduling[34,35]
Atmospheric Science/Policy Impact[36]
Data Analysis/AIS & Emissions[37]
Econometrics/Economic Modeling/Economics[38,39,40,41,42,43,44]
Energy-Markets/Policy/Technology Review[45,46,47,48]
Engineering/Emissions Control/Energy Systems/Machine Learning/Simulation [49,50,51,52,53,54,55,56]
Environmental Assessment/Policy/Impact/Governance[57,58,59,60,61]
Finance/Game Theory/Operations[62,63]
Modeling/Management Science[64]
Monitoring/Methods/Remote Sensing[65,66,67]
Network Analysis/Maritime Business[68]
Operations/Research/Fleet Management/Routing/
Optimization/Monitoring/Technology Adoption
[44,69,70,71,72,73,74,75,76,77,78,79,80,81,82,83,84,85,86]
Policy/Environmental Assessment/Economic Assessment[85,86,87]
Policy/Governance/Review/Scenario Analysis[88,89,90,91,92,93,94],
Environmental Assessment [95,96,97]
Law/Policy/Governance[9,98,99,100,101,102,103,104,105]
Security[106]
Table 2. Distribution of publications by Journal source.
Table 2. Distribution of publications by Journal source.
JournalArticle Count
Applied Energy1
Atmosphere2
Atmospheric Chemistry and Physics1
Atmospheric Measurement Technology1
Coastal Management1
Computers & Industrial Engineering1
Computer & Operation Research1
Drones1
E3S Web of Conference1
Ecology & Society1
Environmental Development1
Environmental Impact Assessment Review1
Environmental Science & Technology1
Euro-Mediterranean Journal for Environmental Integration1
International Conference on Frontiers of Traffic & Transportation Engineering 1
International Journal of Marine & Coastal Law1
IOP Conference Series: Earth & Environmental Science2
Journal of Cleaner Production1
Journal of Combinatorial Optimization1
Journal of Engineering for Gas Turbines & Power1
Journal of Eta Maritime Science1
Journal of Maritime Analytics1
Journal of Marine Engineering & Technology1
Journal of Marine Science & Engineering2
Journal of Operational Research Society1
Marine Policy 7
Marine Pollution Bulletin1
Maritime Business Review1
Maritime Policy & Management 1
Norwegian School of Economics1
Ocean & Coastal Management1
Ocean Development & International Law1
Ocean Engineering4
Pomorstvo1
Review of European Comparative & Environmental Law1
Science of Total Environment1
Scientific Journals of the Maritime University of Szczecin1
Seventh International Conference on
Traffic Engineering & Transport System
1
Sustainable Horizons1
Transport1
Transport & Sustainable Development1
Transport & Telecommunication 2
Transport Policy2
Transportation Research Part A: Policy & Practice1
Transportation Research Part B: Methodological1
Transportation Research Part C: Emerging Technologies3
Transportation Research Part D: Transport & Environment10
Transportation Research Part E: Logistics & Transportation Review1
Transportation Research Record1
Turkish Journal of Electrical Engineering & Computer Science1
WMU Journal of Maritime Affairs1
Table 3. Thematic overview of the studies.
Table 3. Thematic overview of the studies.
ThemeRepresentative TermsPrimary Region(s) of
Focus
Methodological
Orientation
Representative Authors/Studies
Technological Abatement
Solutions
Scrubbers, LNG,China, Simulation modeling,[38,45]
Fuel switching,Baltic/North Sea,Techno-economic
Shore powerNorth Americaanalysis
Regulatory Enforcement and ComplianceECA enforcement, SECA, IMO strategy,Global, China,
North America
Empirical monitoring, legal analysis[67,74]
UAV monitoring, AIS tracking
Policy and Governance InnovationGovernance, Southeast Asia, Arctic,Qualitative policy [9,98,107]
PSSA designation,Mediterraneananalysis, stakeholder
subsidies mapping
Unintended
Consequences and Systemic Effects
Modal shift,Baltic/North Sea,Optimization modeling,[71,80]
Emissions leakageNorth AmericaCost–benefit analysis
Emerging and Cross-Cutting ConceptsGreen corridors,Mediterranean, Scenario modeling,[88,94]
Carbon pricing,
methanol
GlobalPolicy forecasting
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Aiken, D.M.; Tapaninen, U.P. A Systematic Mapping of Emission Control Areas (ECAs) and Particularly Sensitive Sea Areas in Maritime Environmental Governance. Oceans 2025, 6, 60. https://doi.org/10.3390/oceans6030060

AMA Style

Aiken DM, Tapaninen UP. A Systematic Mapping of Emission Control Areas (ECAs) and Particularly Sensitive Sea Areas in Maritime Environmental Governance. Oceans. 2025; 6(3):60. https://doi.org/10.3390/oceans6030060

Chicago/Turabian Style

Aiken, Deniece Melissa, and Ulla Pirita Tapaninen. 2025. "A Systematic Mapping of Emission Control Areas (ECAs) and Particularly Sensitive Sea Areas in Maritime Environmental Governance" Oceans 6, no. 3: 60. https://doi.org/10.3390/oceans6030060

APA Style

Aiken, D. M., & Tapaninen, U. P. (2025). A Systematic Mapping of Emission Control Areas (ECAs) and Particularly Sensitive Sea Areas in Maritime Environmental Governance. Oceans, 6(3), 60. https://doi.org/10.3390/oceans6030060

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