SUSTAINABLE BALLAST WATER MANAGEMENT: MITIGATING ECOLOGICAL IMPACTS AND SUPPORTING MARINE AND COASTAL BIODIVERSITY

ARTICLE HIGLIGHTS
• Reviews global ballast water management for ecological sustainability
• Integrates technological, policy, and social perspectives
• Links ballast water control to Sustainable Development Goals (SDGs)
• Identifies hybrid treatment systems as most effective and eco-safe
• Proposes strategies for harmonized global compliance and cooperation

ABSTRACT
Ballast water is crucial for the stability and safety of ships but poses significant environmental, economic, and public health risks due to the introduction of invasive species, pathogens, and pollutants into marine ecosystems. This review explores the ecological impacts of ballast water discharge, including biodiversity loss, ecosystem disruption, and public health threats from pathogens and harmful algal blooms. Economic consequences, such as damage to fisheries, aquaculture, and coastal infrastructure, are discussed, along with the social impacts on communities reliant on marine resources. Existing regulatory frameworks, such as the International Maritime Organization's Ballast Water Management Convention, and national policies aim to mitigate these challenges but face implementation and enforcement hurdles. Advancements in treatment technologies are reviewed, including mechanical, chemical, physical, and emerging methods like advanced oxidation processes, electrochlorination, and nanotechnology. Integrated treatment systems are highlighted for their potential to address the limitations of single-method approaches. Case studies illustrate successful implementations, while challenges in cost, scalability, and compliance are identified. The review emphasizes the alignment of ballast water management practices with sustainable development goals, advocating for innovation, international collaboration, and capacity building to enhance effectiveness. Future directions include the optimization of treatment technologies, harmonization of regulations, and incentivization of compliance to achieve global environmental and economic resilience. This review underscores the urgency of advancing sustainable ballast water management to protect marine ecosystems, support coastal economies, and promote public health worldwide.

INTRODUCTION

Ballast water is indispensable for maritime operations, providing stability and safety for ships during voyages (Dobrucali et al., 2024). Yet its uncontrolled discharge remains a critical pathway for invasive species and pathogens, driving biodiversity loss, ecological imbalance, and significant economic and public health costs (Kraus, 2023);(Sempere-Valverde et al., 2021). Despite decades of awareness, effective solutions remain fragmented, with uneven adoption of treatment technologies and weak enforcement capacity across regions. These persistent gaps make ballast water management a pressing international challenge requiring coordinated innovation and governance.

The introduction of invasive species through ballast water has caused major ecological disruptions, undermining biodiversity and ecosystem stability worldwide (Slišković et al., 2021). For example, zebra mussels in North America clogged water intake systems and displaced native species, leading to severe economic losses (Lower et al., 2024), while the comb jelly Mnemiopsis leidyi in the Black Sea collapsed fisheries by consuming key plankton resources (Javidpour et al., 2020). These well-documented cases illustrate both the ecological and economic stakes of unmanaged ballast water and highlight why stronger, globally coordinated management strategies remain urgently needed (Dobrucali et al., 2024).

To address these risks, international frameworks such as the International Maritime Organization’s (IMO) Ballast Water Management Convention (BWMC) were introduced to minimize the transfer of harmful aquatic organisms and pathogens. While the BWMC represents a critical step forward, its global effectiveness remains limited by uneven enforcement capacity, disparities in national resources, and variable compliance levels (Global Maritime Transport and Ballast Water Management: Issues and Solutions [Internet, 2015). At the same time, ballast water treatment technologies remain complex and resource-intensive, creating further barriers to universal adoption. These challenges underscore the persistent gap between regulation, technological readiness, and global implementation.

This review responds to these challenges by providing a structured analysis of the ecological, economic, health, and social consequences of ballast water discharge. It critically evaluates advances in treatment technologies; including ultraviolet irradiation, filtration systems, and chemical methods, and assesses their effectiveness in limiting invasive species transfer (Obayomi et al., 2024). In addition, case studies of implementation are reviewed to highlight both successful practices and persistent barriers, offering insight into the feasibility and scalability of different approaches (C, 2022); (Kraus, 2023).

A distinctive contribution of this review is its explicit integration of ballast water management with the United Nations Sustainable Development Goals (SDGs) (I.M.O., 2017). By linking regulatory and technological strategies to global sustainability targets, the review highlights the need to balance environmental protection with economic and social priorities. In particular, ballast water management contributes not only to SDG 14 (Life below Water) but also to SDG 3 (Health) and SDG 8 (Decent Work and Economic Growth), positioning the maritime sector as a key actor in advancing sustainability objectives (Olaniyi et al., 2024); (Kolios, 2024) .

This review addresses critical dimensions of ballast water management, including biodiversity loss, economic risks for fisheries and coastal communities, and the health and social consequences of disrupted ecosystems (Andrews et al., 2021); (Ward et al., 2022). It evaluates regulatory frameworks and recent technological advancements while identifying persistent barriers to adoption and enforcement. Actionable insights for research and policy are emphasized, with attention to feasibility and scalability of proposed solutions (Bailey et al., 2022). By bridging research, policy, and practice, this review seeks to strengthen international efforts to mitigate the impacts of ballast water discharge and to advance a more sustainable and equitable maritime sector (Olaniyi et al., 2024); (Bulgakov et al., 2025);(Mba, 2025).

METHODOLOGY

To achieve the objectives outlined above, this review analyzed published studies, policy reports, and technical documents from 2000 to 2025 relevant to ballast water management and its ecological, economic, and technological dimensions. Relevant literature was collected from peer-reviewed journals, books, and international agency publications. The information was then classified thematically into ecological, economic, health, and social impacts, regulatory frameworks, and treatment technologies. Thematic analysis was used to synthesize insights from different disciplines and identify research gaps related to policy, technology, and sustainability.

The literature search was performed using databases including Scopus, Web of Science, and Google Scholar with keywords such as “ballast water management,” “invasive species,” “treatment technologies,” and “sustainable development goals.” Studies were included if they presented ecological, economic, health, or policy implications of ballast water management, while purely engineering-focused technical papers without environmental relevance were excluded. Duplicates were removed, and relevant non-English sources were included when they provided substantial regional or contextual insights. This approach ensured comprehensive and balanced coverage of interdisciplinary perspectives relevant to sustainable ballast water management.

REVIEW

Ecological Impacts of Ballast Water

Ballast water introduces invasive species and pollutants such as heavy metals and microplastics that disrupt marine ecosystems and food webs (Landrigan et al., 2020);(Kurniawan et al., 2022). These invasions alter biodiversity patterns and ecological functioning, but also generate long-term risks for public health and food security (Kraus, 2023);(Adeniran-Obey & Osagie, 2024). Well-documented cases such as zebra mussels in the Great Lakes and comb jellies in the Black Sea demonstrating significant environmental and economic impacts (Shiganova et al., 2019); (Burlakova et al., 2023).

Invasive species not only reduce biodiversity but also destabilize nutrient cycles and transform habitats. A prominent example is the lionfish invasion in the Atlantic, which has led to marked declines in native fish populations and disrupted trophic dynamics (A et al., 2019); (Mayfield et al., 2021). Such biodiversity erosion diminishes ecosystem resilience, weakening the capacity of marine systems to buffer against climate change impacts and pollution stressors (Gallardo et al., 2024).

Ballast water also acts as a vector for pathogens such as Vibrio cholerae, associated with cholera outbreaks, and for harmful algal blooms (HABs) that contaminate seafood and coastal waters (Yñiguez et al., 2021). Beyond biological threats, chemical pollutants, including microplastics, bioaccumulate in marine organisms, infiltrating the food chain and posing direct risks to human health and food security (Jahromi et al., 2021); (Zendehboudi et al., 2024). As global shipping intensifies, these combined pressures amplify, underscoring the urgency of implementing scalable treatment systems and stricter regulatory enforcement (Dobrucali et al., 2024).

The cumulative ecological and health impacts of ballast water highlight the importance of developing evidence-based strategies that integrate ecological risk assessment with policy and technology innovation (Adraktas, 2024);(Onyena & Nwaogbe, 2024). To provide a structured overview, Table 1 synthesizes key ecological impacts, their underlying causes, and representative references, offering a concise reference point for subsequent analysis.

Table 1.Overview of the ecological impacts, causes, and references for each invasive species introduced through ballast water

Species	Effect	Cause	References
Lionfish (Pterois volitans) in its native Indo-Pacific region	Disrupt native marine populations in the Gulf of Mexico, the Caribbean, and US Eastern Seaboard	Introduced via ornamental fish trade and possible via ballast water from Indo-pacific regions	(MacIsaac et al., 2016); (Williams et al., 2013)
Zebra Mussel (Dreissena polymorpha)	Clogs water intake pipes, outcompetes native species, alters aquatic food web	Introduced via ballast water from transoceanic ships from Europe	(Gaag M et al., 2016); (Burlakova et al., 2023)
Comb Jelly (Mnemiopsis leidyi)	Collapse of anchovy fishery, impacting local biodiversity and fishing industry	Transported via ballast water from ships from the eastern US	(Shiganova et al., 2023)
European Green Crab (Carcinus maenas) in North America	Significant ecological disruptions, predation on native shellfish, competition with local species, impacted shellfish industries	Introduced via ballast water from Europe	(Grosholz et al., 2000);(Jeffery et al., 2017)
Chinese Mitten Crab (Eriocheir sinensis)	Ecological disruption, erosion, damage to flood control systems, competition with native species	Introduced via ballast water from ships traveling from Asia	(Crocetta et al., 2020); (Trichkova et al., 2017)
Round Goby (Neogobius melanostomus)	Outcompetes native fish, alters benthic communities, preys on eggs and young of native fish	Introduced via ballast water from the Black and Caspian Seas	(Cerwenka et al., 2023); (Deurs M et al., 2021)
Japanese Kelp (Undaria pinnatifida)	Forms dense underwater forests, outcompetes native seaweeds, impacts native marine life and mussel farms	Introduced via ballast water from ships traveling from Asia	(Epstein & Smale, 2017); (South et al., 2017)
Asian Tiger Shrimp (Penaeus monodon) in the United States	Dominant predator, impacts native shrimp and fish species, alters food webs	Introduced via ballast water from seafood and aquaculture products	(Aguirre-Pabón et al., 2023); (Petatán-Ramírez et al., 2020)
Northern Pacific Seastar (Asterias amurensis) in Australia	Preys on native marine organisms, declines in native species, disrupts marine ecosystems. impacts local fisheries	Introduced via ballast water from ships from Asia	(Byrne et al., 2016); (Ellis, 2022)
Asian Shore Crab (Hemigrapsus sanguineus) in the Northeastern United States	Outcompetes native species, alters coastal community structure, reduction in native crab and mollusk populations.	Introduced via ballast water	(Espinosa-Novo et al., 2023); (Griffen et al., 2020)
Brown Tree Snake (Boiga irregularis)	Caused extinction of bird and reptile species, threatens biodiversity and human health	Introduced via ballast water and cargo shipments	(Boback et al., 2022); (Siers et al., 2024)
Vibrio cholerae and Escherichia coli	Risk of cholera outbreaks in coastal communities	Ballast water from regions with cholera outbreaks	(Lakshmi et al., 2021); (Soleimani et al., 2021)
Harmful Algal Blooms (HABs) in the Baltic Sea and Mediterranian Sea	Production of toxins that contaminate seafood and water supplies, health risks to humans and marine life	Spread via ballast water carrying algal cysts	(Karlson et al., 2021); (Karlson et al., 2021)
Cryptosporidium and Giardia	Causes gastrointestinal illness outbreaks	Ballast water from contaminated regions.	(Kraus, 2023)
Sea lamprey (Petromyzon marinus)	Cause declines in native fish populations, such as lake trout (Salvelinus namaycush)	Introduction to the Great Lakes	(Mattes & Kitson, 2021)
Heavy metals (Fe, Cu, Pb)	Bioaccumulation	Ballast water from vessels from various regions	(Hassaan & El Nemr, 2021); (Onyena & Nwaogbe, 2024)
Microplastic	Threat to wildlife and marine environment	Ballast water	(Naik et al., 2021); (Thushari & Senevirathna, 2020)

Economic, Environmental, and Social Impacts

Ballast water discharge produces significant economic and social consequences by disrupting ecosystem services that support fisheries, aquaculture, and tourism (Gollasch & David, 2019); (Kraus, 2023). Ballast water discharge produces significant economic and social consequences by disrupting ecosystem services that support fisheries, aquaculture, and tourism.

Fisheries and aquaculture are particularly vulnerable to the cascading effects of invasive species and pathogens introduced via ballast water. The collapse of the Black Sea’s anchovy population following the invasion of the comb jelly Mnemiopsis leidyi created severe economic hardship for fishing communities (Knowler, 2005). Similarly, the spread of pathogens such as Cryptocaryon irritans has disrupted aquaculture production, undermining food security and market stability (Giari et al., 2022). Coastal infrastructure also bears high costs: zebra mussel infestations in the Great Lakes have demanded costly recovery and repair interventions (Lower et al., 2024). In addition, tourism and recreational fishing decline when degraded ecosystems deter visitors, reducing local business income and weakening regional economic resilience (Beukering P et al., 2014);(Sukhikh et al., 2019).

The social consequences of ballast water discharge are equally profound, especially in coastal regions where cultural identity and livelihoods are deeply intertwined with native marine species. Invasive organisms displace native stocks, eroding traditional fishing practices, weakening intergenerational knowledge transfer, and threatening cultural heritage. For example, the Mediterranean fisheries disrupted by the comb jelly have not only suffered ecological and economic setbacks but also cultural dislocation for communities whose identities are bound to these fisheries (Zenetos et al., 2010);(Kraus, 2023).

Implementing ballast water management systems requires substantial financial investment, with installation costs estimated between USD 500,000 and USD 5 million per vessel, in addition to significant operational and maintenance expenses (Gerhard et al., 2019);(Hardiyanto et al., 2023). While these upfront costs pose challenges for shipowners, they are outweighed by the long-term savings achieved through avoided ecological damage and infrastructure repair. For example, proactive measures could have significantly reduced the billions spent on recovery and restoration efforts necessitated by the zebra mussel invasion (Gaag M et al., 2016); (Team, 2025). Such cost-benefit framing highlights ballast water management not only as an ecological imperative but also as a financially rational investment.

International frameworks such as the IMO Ballast Water Management Convention introduce additional compliance costs for shipowners, yet they remain critical instruments for averting large-scale ecological disruption and economic loss (Outinen et al., 2024). To balance regulatory stringency with feasibility, governments can deploy supportive measures, such as tax incentives, subsidies, and resource-sharing programs, that lower financial barriers, foster equitable compliance across regions, and accelerate the adoption of cost-effective treatment technologies (Becqué et al., 2018).

Regulatory Frameworks and Policies

The International Maritime Organization’s Ballast Water Management Convention (BWMC) establishes the first binding global framework for regulating ballast water treatment and discharge, requiring vessels to implement exchange and onboard treatment systems to limit invasive species transfer (Global Maritime Transport and Ballast Water Management: Issues and Solutions [Internet, 2015). However, its enforcement varies widely due to institutional and financial disparities among member states (I.M.O., n.d.). The hierarchical structure of international, national, and regional governance frameworks is summarized in Figure 1.

Figure 1.Regulatory framework for ballast water management

Beyond the BWMC, individual nations and regions have enacted supplementary frameworks tailored to local contexts. For example, the United States enforces the National Invasive Species Act (NISA), which obliges vessels to treat or exchange ballast water, while China has formally aligned with BWMC standards (Verna & Harris, 2016);(Hao, 2020);(Guard, 2023). Regional initiatives, such as those in the Baltic Sea and the Great Lakes, target specific ecological vulnerabilities and complement international obligations. Yet, disparities in enforcement and implementation across jurisdictions expose persistent gaps in global governance, underscoring the importance of harmonized policies and mechanisms for sharing best practices (Jetoo 2018).

Enforcing ballast water regulations remains a persistent challenge, constrained by technical limitations such as the absence of reliable real-time compliance detection and the high costs of advanced monitoring technologies. Effective enforcement requires rigorous inspections and international coordination, which are unevenly implemented. Promising developments include targeted surveillance in high-risk areas and collaborative port programs, both of which have demonstrated early success (Wang et al., 2020);(Bailey et al., 2022). In addition, emerging tools, such as automated monitoring systems and integrated data-sharing platforms, offer pathways to more scalable and transparent compliance regimes (Fournier et al., 2018);(Olaniyi et al., 2024); Melnyk et al. 2025). Strengthening these measures is essential not only to maximize the impact of existing frameworks but also to enhance global trust in regulatory effectiveness.

Ballast Water Treatment Technologies

Ballast water treatment employs a diverse range of approaches, mechanical, chemical, physical, biological, and increasingly integrated systems, to mitigate the risks of invasive species and pathogen transfer. Filtration remains the most widely adopted baseline method and is frequently paired with complementary techniques such as electrolysis, electrochlorination, or UV disinfection. More advanced options, including ozonation, cavitation, deoxygenation, and advanced oxidation processes, provide additional pathways for compliance but present varying levels of cost, operational complexity, and ecological trade-offs (Balaji et al., 2019);(Duan et al., 2023). Treatment choices should be evaluated not only by efficacy but also by scalability and environmental footprint, aligning with SDG sustainability principles. Figure 2 provides a flowchart summarizing these categories of treatment technologies, complementing the detailed comparisons presented in Table 2 and 3.

Figure 2.Ballast water treatment systems

Table 2.Comparison of physical and mechanical methods for ballast water treatment

Treatment method	Advantage	Disadvantage	Effectiveness	Operational complexity	References
Mechanicalfiltration	Effective in removing large particles and organisms	Requires regularmaintenance	Effective for larger organisms, limited for smaller microorganisms	Simple operation, requires regular maintenance	Williams et al. (2013); Naik et al. (2021)
Multistagefiltration	High efficiency in removing large particles and organisms	Requires regular filter changes and space	High for particles and larger organisms	Moderate, requiresspace and labor	Guilbaud et al. (2019); Naik et al. (2021); Duan et al. (2023)
Membranefiltration	High efficiency in removing particles and microorganisms	High capital and operational costs	Very high	High, requiresadvanced systems	Dong et al. (2021)
UV Treatment	No chemical residues in the environment	Less effective in turbid waters, requires clear water	Effective against bacteria, viruses, protozoa	Moderate, requires system management and lamp maintenance	Ejder et al. (2024); Sari & Gunawan (2024)
Heat Treatment	Effective against a wide range of microorganisms	Requires high energy and costly infrastructure	High effectiveness	High, requires advanced systems and monitoring	Balaji et al. (2019); Iswantoro et al. (2023)

Table 3.Comparison of chemical and biocide-based methods for ballast water treatment

Treatment method	Advantage	Disadvantage	Effectiveness	Operational complexity	References
Chemical Disinfection (e.g., Chlorine, Sodium Hypochlorite)	Effective against a broad range of microorganisms	Chemical residues can impact environment	High disinfectionefficiency	Moderate, requires handling chemicals and monitoring dosages	Kurniawan et al.(2022)
Biobased Biocides	Natural and environmentally friendly substances	May be less effective against allmicroorganisms	Variableeffectiveness	Moderate, requires biocide management	Kim et al. (2018)
Ozonation	Effective against many pathogens and microorganisms	High cost and operational complexity	Very higheffectiveness	High, requires specialized equipment and monitoring	Herwig et al.(2006); Díaz-Domínguez et al.(2024)
Electro-coagulation	Treats small particles and organic matter	Energy-intensive, requires electrode maintenance	High in removing particles and organic matter	Moderate to high, complex operation	Duan et al. (2023); Effendi et al. (2024)

Mechanical Methods

Mechanical methods, including filtration and cyclonic separation, remain foundational to ballast water treatment, physically removing particulate matter and organisms. Filtration technologies such as disk filters, filter bags, and cartridges differ in efficiency depending on pore size, filter design, and cleaning mechanisms. These approaches are highly effective at capturing larger particles, microplastics, and soft-bodied plankton but are less successful against microorganisms below the filtration threshold. Their overall performance is strongly contingent on maintenance practices, as heavy sediment loads reduce flow rates and increase pressure drops, thereby influencing operational reliability and long-term cost efficiency (Drake et al., 2016);(Naik et al., 2021). While effective as a first barrier, mechanical methods require pairing with other treatments to ensure microbial safety.

Chemical Methods

Chemical methods aim to balance disinfection effectiveness with ecological safety, offering multiple options for ship operators. Chlorination remains cost-effective and widely adopted but generates harmful by-products such as trihalomethanes (THMs), which raise ecological and regulatory concerns (Kurniawan et al., 2022). Ozonation is rapid and leaves no persistent residues, yet it produces toxic bromate in seawater and requires substantial energy inputs (Seridou et al., 2024). UV radiation combined with hydrogen peroxide offers a more environmentally friendly approach, though its efficiency declines in turbid waters. Peracetic acid is another low-impact disinfectant but poses handling challenges due to its corrosive properties. Selecting among these methods requires balancing operational feasibility, regulatory compliance, and environmental impact, highlighting the trade-offs inherent in chemical approaches (Hess-Erga et al., 2019);(Yoon et al., 2021). Chemical approaches remain cost-effective but risk undermining sustainability unless by-product management strategies are prioritized.

Physical Methods

Physical approaches, including UV radiation, heat treatment, deoxygenation, cavitation, and ultrasound, neutralize organisms by altering environmental conditions rather than adding chemicals. UV radiation is widely adopted for its ability to damage microbial DNA across a broad spectrum of organisms without producing chemical residues, though its effectiveness declines in turbid waters. Heat treatment achieves full sterilization by elevating water temperature but is energy-intensive and often impractical at scale. Deoxygenation suppresses aerobic organisms through inert gas injection, reducing chemical dependency but requiring specialized infrastructure. Cavitation and ultrasound disrupt microbial cell structures via rapid pressure fluctuations and acoustic energy, though both are limited by high energy demands(Estévez-Calvar et al., 2018);(Hess-Erga et al., 2019);(Balaji et al., 2019). These methods are valued for minimizing chemical use but face feasibility challenges related to energy efficiency and equipment requirements. Physical methods are environmentally preferable but require optimization for variable water conditions and energy efficiency.

Biological Methods

Biological methods, while still largely experimental, represent innovative approaches that harness ecological interactions to manage invasive species. Strategies include introducing natural predators, parasites, or competitors (Dafforn, 2025) and exploring genetic biocontrol techniques (Teem et al., 2020). These approaches carry the advantage of potentially reducing chemical and energy use, yet they require rigorous ecological risk assessment to avoid unintended disruptions. Current research emphasizes combining biological agents with mechanical, chemical, or physical methods to enhance sustainability and long-term effectiveness (Drake et al., 2016);(Kraus, 2023). Biological methods are promising for long-term sustainability but should only be deployed as part of controlled, integrated approaches.

Combined Systems

Integrated systems combine mechanical, chemical, physical, and in some cases biological methods to maximize treatment efficiency while minimizing ecological side effects. For example, filtration can precede UV or heat treatment to lower turbidity and enhance disinfection, while electrochlorination can complement UV systems to maintain performance under challenging conditions. Experimental biological techniques, such as the use of natural predators, are also being incorporated into hybrid frameworks (Nwigwe & Kiyokazu, 2023).

The strength of integrated approaches lies in their ability to address diverse contaminants simultaneously, thereby reducing chemical dependency, minimizing by-product formation, and improving overall sustainability. Nevertheless, these systems are constrained by high complexity, steep regulatory requirements, and significant financial costs. Ongoing research is focused on optimizing configurations and reducing operational burdens, positioning integrated systems as a promising long-term solution for balancing ecological protection with regulatory compliance in ballast water management (Eleyadath et al., 2021). Integrated systems illustrate the shift toward holistic solutions, though cost barriers must be addressed for widespread scalability.

Comparison among Treatments

A comparative overview of available treatment methods is presented in Tables 2 and3, which synthesize the relative strengths, limitations, and contextual suitability of physical, chemical, biological, and integrated approaches. Rather than serving as exhaustive descriptions, these summaries provide a framework for aligning technological choices with ecological, economic, and regulatory priorities. Comparative frameworks highlight not just technical differences but also policy relevance, supporting decision-making at both ship and regulatory level.

Industry Trends and Best Practices

The ballast water treatment industry is increasingly adopting innovative practices and standards to develop systems that are both efficient and environmentally responsible. Key trends include modular and scalable designs that provide flexibility across vessel types and operational profiles. Best practices emphasize sustainability by integrating energy-efficient designs, minimizing waste, and lowering operational footprints. At the same time, industry-wide collaboration is strengthening standardized guidelines and certification processes, which enhance consistency, reliability, and compliance across diverse treatment technologies (Apetroaei et al., 2018); (Lakshmi et al., 2021).

Emerging Technologies for Ballast Water Treatment

Emerging technologies such as advanced oxidation processes (AOPs), electrochlorination, and nanotechnology are reshaping ballast water management by offering alternatives that balance disinfection efficiency with sustainability. AOPs, which rely on reactive hydroxyl radicals generated by ozone or UV with hydrogen peroxide, demonstrate strong efficacy but remain limited by high energy demands, advanced infrastructure needs, and by-product management challenges (Golfinopoulos et al., 2024). Electrochlorination, which generates chlorine-based disinfectants through seawater electrolysis, is already widely adopted due to its cost-effectiveness and ease of integration into ship systems, though careful monitoring of toxic by-products like trihalomethanes is essential (Moreno-Andrés et al., 2018); (Park et al., 2025). Nanotechnology methods, including nanofiltration and photocatalytic nanoparticles, show promise for high efficiency but face barriers related to cost, scalability, and uncertain environmental risks (Poornima et al., 2022); (Melnyk et al., 2025).

Adoption patterns reflect these strengths and weaknesses: electrochlorination dominates current use, AOPs are operational but require optimization for energy and ecological safety, and nanotechnology remains experimental. Collectively, these approaches illustrate a research gap: while promising, they require further refinement and scaling before contributing fully to sustainable ballast water management.

Innovations in Existing Technologies

Recent innovations in traditional ballast water treatment methods, mechanical, chemical, physical, and biological, aim not only to improve efficiency and reduce costs but also to align with stricter global sustainability and regulatory demands (V et al., 2021). Mechanical systems now incorporate advanced pore designs and optimized flow rates to enhance particle retention while minimizing energy penalties (Tsolaki & Diamadopoulos, 2010). Chemical treatments increasingly emphasize reducing by-product toxicity, while physical methods such as UV radiation are being adapted to function reliably under varied water qualities (Kurniawan et al., 2022);(Golfinopoulos et al., 2024).

The critical shift lies in their integration with regulatory compliance: rather than incremental improvements, these advances address enforcement gaps by offering more predictable performance, lower operational costs, and reduced ecological risks (Feng et al., 2023);(Durlik et al., 2024). This highlights both progress achieved and the need for further innovation to ensure that treatment technologies remain scalable and feasible across diverse shipping contexts.

Economic and Environmental Considerations

The adoption of ballast water treatment technologies depends on balancing economic feasibility with long-term environmental sustainability (Makkonen & Inkinen, 2021);(Ishola & Kontovas, 2022);(Nie et al., 2023);(Ejder et al., 2024). Beyond simple cost-benefit calculations, stakeholders increasingly rely on life cycle assessments (LCAs) to account for environmental footprints from production through disposal (Kurniawan et al., 2022). This shift highlights a research gap: while LCAs are widely applied in other maritime sectors, their use in ballast water management remains limited and inconsistent.

Electrochlorination continues to be attractive due to lower upfront costs, but unresolved challenges with toxic by-products complicate its sustainability profile (Kurniawan et al., 2022). By contrast, advanced oxidation processes (AOPs) and nanotechnology require high initial investments but offer greater efficiency, regulatory alignment, and reduced ecological risks in the long term (Devendrapandi et al., 2024). Thus, selecting appropriate technologies is not just a technical or financial decision but a strategic trade-off among compliance requirements, ecological responsibility, and operational viability (Durlik et al., 2024).

Case Studies and Practical Applications

Case studies of ballast water management highlight not only the strategies and technologies employed, but also the lessons learned that can inform broader adoption. While successful implementations exist, widespread uptake is still constrained by technical challenges, financial burdens, and uneven regulatory enforcement (Wang et al., 2020). Addressing these barriers requires innovation and cooperation, but also analytical reflection on what has worked and why. Capacity building, technological innovation, and regional collaboration remain essential, yet the real value of case studies lies in their transferability and potential to guide scalable, sustainable ballast water practices (Khaskheli et al. 2023).

Port-level Initiatives

The Great Lakes region has implemented rigorous ballast water inspection and treatment requirements, leading to measurable reductions in invasive species introductions. Although compliance monitoring is resource-intensive, this case demonstrates that early detection and strict enforcement can prevent long-term ecological damage (Bailey et al., 2022). Investing in strong port-level monitoring yields high ecological returns and can be adapted to other high-risk entry points.

National and Regional Frameworks

The Baltic Sea Action Plan integrates ballast water management into a wider regional marine protection framework. By combining IMO guidelines with coordinated monitoring, Baltic states achieved higher compliance compared to individual enforcement alone (Baltic Marine Environment Protection Commission 2021). Regional harmonization reduces loopholes and enables smaller states to share resources for compliance.

Industry-led Adoption

Some shipping companies, particularly those operating globally, have installed treatment systems ahead of regulatory deadlines. This has given them operational flexibility across jurisdictions and improved corporate reputation. Early voluntary adoption can lower long-term costs and create competitive advantage, aligning compliance with business interests (Rivas-Hermann et al. 2015; Celestin 2023).

Sustainable Development and Future Directions

Ballast water discharge remains a major pathway for invasive species and pathogen spread, imposing significant ecological, economic, and public health costs worldwide. These challenges also hinder progress toward Sustainable Development Goals (SDGs) related to marine conservation, public health, and sustainable economic growth (Lv et al., 2023). Although multiple treatment technologies exist, their adoption remains uneven, depending on vessel type, shipping route, and financial capacity. Addressing these disparities requires ongoing research to develop efficient and eco-friendly treatment systems, alongside stronger global monitoring and compliance mechanisms (Melnyk et al. 2025).

Mechanical filtration and UV treatment remain widely applied but are constrained by water turbidity and maintenance needs. Chemical disinfection provides broad efficacy yet generates toxic by-products requiring careful neutralization. Advanced oxidation processes and nanotechnology demonstrate superior microbial inactivation but remain costly and energy-intensive, limiting scalability. A key contribution of this review is the comparative evidence that hybrid systems, such as filtration combined with UV or electrochlorination, offer higher compliance rates and improved sustainability compared to single-method approaches (Hess-Erga et al., 2019); (Dong et al., 2021).

Policymakers play a critical role in strengthening regulatory frameworks, funding capacity building, and facilitating technology transfer. Effective enforcement requires investment in port inspection capabilities, standardized reporting, and international cooperation to assist low-resource flag states in meeting BWMC requirements (Bailey et al., 2022);(Feng et al., 2023);(Durlik et al., 2024).

Summary of Key Findings

Ballast water threatens aquatic ecosystems and economies by introducing non-native species that outcompete native fauna, alter food webs, and disrupt ecosystem services. These invasions cause direct economic losses in fisheries, aquaculture, and tourism, while also imposing long-term costs related to ecosystem restoration and public health measures (McLaughlan & Aldridge, 2013).

Improved ballast water management is essential to mitigate these impacts while supporting broader sustainability objectives. This review integrates technological, regulatory, and socio-economic perspectives to propose measurable SDG-aligned indicators, thereby enabling assessment of progress toward SDG 14 and related targets.

Effective regulations are critical to successful ballast water management, but regulatory alignment and enforcement remain uneven across regions (Olaniyi et al., 2024). We recommend harmonized standards, incentive mechanisms for adoption of hybrid technologies, and the establishment of regional monitoring hubs to support compliance and data sharing (Zreik, 2024).

CONCLUSION

Effective ballast water management is essential to mitigate environmental, economic, and public health challenges caused by untreated discharges. Such discharges introduce invasive species, reduce biodiversity, and spread pathogens, directly affecting marine ecosystems, and industries such as fisheries, aquaculture, and tourism.

Global standards, such as the IMO’s Ballast Water Management Convention provide a critical framework for risk reduction but continue to face uneven enforcement and resource disparities across regions. Emerging technologies, including advanced oxidation processes, electrochlorination, and nanotechnology, demonstrate strong potential for enhancing efficiency and sustainability. Further research is required to optimize these methods for ecological safety, operational reliability, and cost effectiveness.

Integrated systems that combine mechanical, chemical, and physical treatments offer robust solutions by overcoming the limitations of single-method approaches. Their broader adoption, however, depends on harmonized international policies, compliance incentives, and capacity-building in resource-limited regions. Importantly, aligning ballast water management with Sustainable Development Goal (SDG) 14 provides a novel pathway for protecting marine ecosystems, strengthening coastal economic resilience, and advancing global environmental health.

Policymakers, researchers, and industry stakeholders must prioritize refining technologies, enhancing monitoring and compliance systems, and fostering stronger cooperation. By embedding these efforts within the SDG framework, the maritime sector can accelerate innovation, achieve measurable sustainability outcomes, and mitigate ballast water’s negative impacts, ensuring the long-term protection of marine ecosystems for future generations.

RECOMMENDATION

Effective ballast water management requires a comprehensive approach that integrates advanced treatment technologies, strengthened regulatory frameworks, international collaboration, and alignment with sustainability goals. Hybrid systems combining mechanical, chemical, and physical methods should be prioritized, along with continued research into innovative solutions like advanced oxidation processes and nanotechnology. Global and regional policies, such as the International Maritime Organization’s Ballast Water Management Convention, need harmonization and consistent enforcement, supported by financial incentives to ease the adoption of advanced technologies. International cooperation is essential for sharing best practices and building capacity in under-resourced regions. By embedding ballast water management within sustainable development strategies, the maritime industry can protect biodiversity, support economic resilience, and promote global environmental health.

References

1. A Acero P., D Bustos-Montes, P Pabón Quintero, CJ Polo-Silva, AS Muñoz.In: Makowski C., Finkl C.W.. Impacts of Invasive Species on Coastal Environments [Internet. Springer International Publishing: Springer International Publishing; 2019:269-314. DOI
2. Adeniran-Obey S.O., Osagie D.A..In: Isibor P.O.. Arctic Marine Ecotoxicology [Internet. Springer Nature Switzerland: Springer Nature Switzerland; 2024:381-402. DOI
3. Adraktas G.. Ballast Water Treatment Systems in Vessels [Internet. 2024. Publisher Full Text
4. Aguirre-Pabón J., Chasqui L., Muñoz E., Narváez-Barandica J.. Multiple origins define the genetic structure of tiger shrimp Penaeus monodon in the colombian Caribbean Sea. Heliyon [Internet. 2023. DOI
5. Andrews N., Bennett N.J., Le Billon P., Green S.J., Cisneros-Montemayor A.M., Amongin S., Gray N.J., Sumaila U.R.. Oil, fisheries and coastal communities: A review of impacts on the environment, livelihoods, space and governance. Energy Research & Social Science [Internet. 2021. DOI
6. Apetroaei M.R., Atodiresei D.V., Rău I., Apetroaei G.M., Lilios G., Schroder V.. Overview on the practical methods of ballast water treatment. J Phys. 2018. DOI
7. Bailey S.A., Brydges T., Casas-Monroy O., Kydd J., Linley R.D., Rozon R.M., Darling J.A.. First evaluation of ballast water management systems on operational ships for minimizing introductions of nonindigenous zooplankton. Marine Pollution Bulletin [Internet. 2022. DOI
8. Balaji R., Yaakob O., Koh K.K., Adnan F.A.B., Ismail N.B., Ahmad B.B., Ismail M.A.B.. A Study of Ballast Water Treatment Using Engine Waste Heat. J Inst Eng India Ser C [Internet. 2019; 100(2):255-269. DOI
9. Team B.C.W.F.Watershed. Invasive Mussels: An Immediate and Preventable Threat [Internet. 2025. Publisher Full Text
10. Becqué R., Fung F., Zhu Z.. Incentive Schemes for Promoting Green Shipping [Internet. 2018. Publisher Full Text
11. Beukering PR Brouwer, S Schep, E Wolfs, L Brander, G Ebanks-Petrie, T Austin. The impact of invasive species on tourism [Internet. 2014. Publisher Full Text
12. C Bi̇Lgi̇N Güney. Ballast Water Problem: Current Status and Expected Challenges. Marine Science and Technology Bulletin [Internet. 2022; 11(4):397-415. DOI
13. Boback S.M., Nafus M.G., Yackel Adams A.A., Reed R.N.. Invasive brown treesnakes (Boiga irregularis) move short distances and have small activity areas in a high prey environment. Sci Rep [Internet. 2022; 12(1)DOI
14. Britton Lynch, AJ Bardal, H Bradbeer, SJ Coetzee, JA Coughlan, NE Dalu, T Tricarico, E Gallardo, B Lintermans, M.. Preventing and controlling nonnative species invasions to bend the curve of global freshwater biodiversity loss. Environ Rev [Internet. 2023; 31(2):310-326. DOI
15. Bulgakov M., Melnyk O., Kuznichenko S., Zaporozhets A., Sagaydak O., Shcheniavskyi G..In: Melnyk O., Onishchenko O., Zaporozhets A.. Maritime Systems, Transport and Logistics I [Internet. Springer Nature Switzerland: Springer Nature Switzerland; 2025:107-119. DOI
16. Burlakova L.E., Karatayev A.Y., Boltovskoy D., Correa N.M.. Ecosystem services provided by the exotic bivalves Dreissena polymorpha, D. rostriformis bugensis, and Limnoperna fortunei. Hydrobiologia [Internet. 2023. DOI
17. Byrne M., Gall M., Wolfe K., Agüera A.. From pole to pole: the potential for the Arctic seastar Asterias amurensis to invade a warming Southern Ocean. Global Change Biology [Internet. 2016. DOI
18. Cerwenka A.F., Brandner J., Dashinov D., Geist J.. Small but Mighty: The Round Goby (Neogobius melanostomus) as a Model Species of Biological Invasions. Diversity [Internet. 2023; 15(4)DOI
19. Chen Y., Wang N., Ola O., Xia Y., Zhu Y.. Porous ceramics: Light in weight but heavy in energy and environment technologies. Materials Science and Engineering. 2021. DOI
20. Cohen N.J., Slaten D.D., Marano N., Tappero J.W., Wellman M., Albert R.J., Hill V.R., Espey D., Handzel T., Henry A., Tauxe R.V.. Preventing Maritime Transfer of Toxigenic Vibrio cholerae. Emerg Infect Dis [Internet. 2012; 18(10):1680-1682. DOI
21. Crocetta F., Tanduo V., Osca D., Turolla E.. The Chinese mitten crab Eriocheir sinensis H. Milne Edwards, 1853 (Crustacea: Decapoda: Varunidae) reappears in the northern Adriatic Sea: Another intrusion attempt or the trace of an overlooked population?. Marine Pollution Bulletin [Internet. 2020. DOI
22. Dafforn K.. Current Opinion in Environmental Sustainability [Internet. 2025. DOI
23. Global Maritime Transport and Ballast Water Management: Issues and Solutions [Internet. 2015. DOI
24. Gaag MVelde GS Wijnhoven, RSEW Leuven. Salinity as a barrier for ship hull-related dispersal and invasiveness of dreissenid and mytilid bivalves. Mar Biol [Internet. 2016; 163(7)DOI
25. Deurs MNP Moran, K Schreiber Plet-Hansen, GE Dinesen, F Azour, H Carl, PR Møller, JW Behrens. Impacts of the invasive round goby (Neogobius melanostomus) on benthic invertebrate fauna: a case study from the Baltic Sea. NB [Internet. 2021. DOI
26. Devendrapandi G., Liu X., Balu R., Ayyamperumal R., Valan Arasu M., Lavanya M., Minnam Reddy V.R., Kim W.K., Karthika P.C.. Innovative remediation strategies for persistent organic pollutants in soil and water: A comprehensive review. Environmental Research [Internet. 2024. DOI
27. Díaz-Domínguez E., Romero-Martínez L., Ibáñez-López M.E., Acevedo-Merino A., García-Morales J.L.. Evaluation of ozone treatment for bacterial disinfection of ballast water. Journal of Environmental Chemical Engineering [Internet. 2024; 12(1)DOI
28. Dobrucali E., Uyanik S., Altuntaş V., Yilmaz M., Balci M., Şahan A.N., Gerçek A.B., Erçetin V.E., Uçar D.. Physicochemical and microbiological investigation of ballast waters of the ships operating in the Marmara Sea. Ocean & Coastal Management [Internet. 2024. DOI
29. Dong X., Guan Fang, Xu Liting, Duan Jizhou, Hou Baorong. Progress on the Corrosion Mechanism of Sulfate-reducing Bacteria in Marine Environment on Metal Materials. Journal of Chinese Society for Corrosion and Protection [Internet. 2021; 41(1):1-12. DOI
30. Drake L.A., Wier T.P., Parson E.W.J., Grant J.F.. Recommendations for Evaluating Multiple Filters in Ballast Water Management Systems for US Type Approval: [Internet. 2016. DOI
31. Duan D., Xu F., Wang T., Guo Y., Fu H.. The effect of filtration and electrolysis on ballast water treatment. Ocean Engineering [Internet. 2023. DOI
32. V Duc Bui, PQ Phong Nguyen, D Tuyen Nguyen. Water conserv manag [Internet. 2021. DOI
33. Durlik I., Miller T., Kostecka E., Łobodzińska A., Kostecki T.. Harnessing AI for Sustainable Shipping and Green Ports: Challenges and Opportunities. Applied Sciences [Internet. 2024; 14(14)DOI
34. Effendi I., Ghifari M.F., Fisheries Faculty, Sciences Marine, Riau University, Indonesia Nedi, S Faculty of Fisheries, Sciences Marine, Riau University, Indonesia Effendi, S School of Vocation, Gajah Mada University, Yogjakarta Indonesia. Electrocoagulation System for Treatment of Ballast Water. Carpathian J Earth Environ Sci [Internet. 2024; 19(2):217-232. DOI
35. Ejder E., Ceylan B.O., Celik M.S., Arslanoğlu Y.. Sustainability in maritime transport: Selecting ballast water treatment for a bulk carrier. Marine Environmental Research [Internet. 2024. DOI
36. Eleyadath L., Machinchery P., Achari V.S.. An overview on the treatment of ballast water in ships. Ocean & Coastal Management [Internet. 2021. DOI
37. Ellis M.R.. Invasive Species Ecology of the Northern Pacific Seastar (Asterias amurensis. 2022.
38. Epstein G., Smale D.A.. Undaria pinnatifida : A case study to highlight challenges in marine invasion ecology and management. Ecology and Evolution [Internet. 2017. DOI
39. Espinosa-Novo N., Giménez L., Boersma M., Torres G.. On their way to the north: larval performance of Hemigrapsus sanguineus invasive on the European coast—a comparison with the native European population of #Carcinus maenas#. Biol Invasions [Internet. 2023; 25(10):3119-3136. DOI
40. Estévez-Calvar N., Gambardella C., Miraglia F., Pavanello G., Greco G., Faimali M., Garaventa F.. Potential use of an ultrasound antifouling technology as a ballast water treatment system. Journal of Sea Research [Internet. 2018. DOI
41. Feng W., Chen Y., Zhang T., Xue J., Wu H.. Evaluate the compliance of ballast water management system on various types of operational vessels based on the D-2 standard. Marine Pollution Bulletin [Internet. 2023. DOI
42. Fournier M., Casey Hilliard R., Rezaee S., Pelot R.. Past, present, and future of the satellite-based automatic identification system: areas of applications (2004–2016. WMU J Marit Affairs [Internet. 2018; 17(3):311-345. DOI
43. Gallardo B., Bacher S., Barbosa A.M., Gallien L., González-Moreno P., Martínez-Bolea V., Sorte C., Vimercati G., Vilà M.. Risks posed by invasive species to the provision of ecosystem services in Europe. Nat Commun [Internet. 2024; 15(1)DOI
44. Gerhard W.A., Lundgreen K., Drillet G., Baumler R., Holbech H., Gunsch C.K.. Installation and use of ballast water treatment systems – Implications for compliance and enforcement. Ocean & Coastal Management [Internet. 2019. DOI
45. Giari L., Castaldelli G., Timi J.T.. Ecology and effects of metazoan parasites of fish in transitional waters. Parasitology [Internet. 2022; 149(14):1829-1841. DOI
46. Golfinopoulos S.K., Nikolaou A.D., Alexakis D.E.. Innovative Approaches for Minimizing Disinfection Byproducts (DBPs) in Water Treatment: Challenges and Trends. Applied Sciences [Internet. 2024; 14(18)DOI
47. Gollasch S., David M.. World Seas: An Environmental Evaluation [Internet. Elsevier: Elsevier; 2019:237-250. DOI
48. Griffen B.D., Bailey J., Carver J., Vernier A., DiNuzzo E.R., Anderson L., Meidell M., Potter B.. Mechanisms of possible self-limitation in the invasive Asian shore crab Hemigrapsus sanguineus. Sci Rep [Internet. 2020; 10(1)DOI
49. Grosholz E.D., Ruiz G.M., Dean C.A., Shirley K.A., Maron J.L., Connors P.G.. The Impacts of A Nonindigenous Marine Predator in A California Bay. Ecology [Internet. 2000. DOI
50. Guilbaud J., Wyart Y., Moulin P.. Economic viability of treating ballast water of ships by ultrafiltration as a function of the process position. J Mar Sci Technol [Internet. 2019. DOI
51. Hao S.. China’s Implementation of the Ballast Water Convention, Analysis of Treatment Technology and Main Points of Psc Inspection [Internet. 2020. Publisher Full Text
52. Hardiyanto H., Pitana T., Handani D.. Development dynamic compliance cost model for implementation of ballast water management convention: shipowner perspective. J Appl Eng Science [Internet. 2023; 21(2):698-711. DOI
53. Hassaan M.A., El Nemr A..In: Inamuddin Ahamed M.I., E Lichtfouse, T Altalhi. Remediation of Heavy Metals [Internet. Springer International Publishing: Springer International Publishing; 2021:289-304. DOI
54. Herwig R., Cordell J., Perrins J., Dinnel P., Gensemer R., Stubblefield W., Ruiz G., Kopp J., House M., Cooper W.. Ozone treatment of ballast water on the oil tanker S/T Tonsina: chemistry, biology and toxicity. 2006. DOI
55. Hess-Erga O.-K., Moreno-Andrés J., Enger Ø., Vadstein O.. Microorganisms in ballast water: Disinfection, community dynamics, and implications for management. Science of The Total Environment [Internet. 2019. DOI
56. I.M.O.. Economic Assessment of Ballast Water Management: A Synthesis of the National Assessments conducted by the Lead Partnering Countries of the GEF-UNDP-IMO GloBallast Partnerships Programme [Internet. 2017. Publisher Full Text
57. I.M.O.. International Maritime Organization [Internet. Publisher Full Text
58. Ishola A., Kontovas C.A.. Managing Ship’s Ballast Water: A Feasibility Assessment of Mobile Port-Based Treatment. Sustainability [Internet. 2022; 14(22)DOI
59. Iswantoro A., Semin Pitana, T Zaman, MB Ahsan, F.I.. Ballast Water Treatment with Heat Exchanger Modeling Simulation. IOP Conf Ser: Earth Environ Sci [Internet. 2023; 1198(1)DOI
60. Jahromi F.A., Keshavarzi B., Moore F., Abbasi S., Busquets R., Hooda P.S., Jaafarzadeh N.. Source and risk assessment of heavy metals and microplastics in bivalves and coastal sediments of the Northern Persian Gulf, Hormogzan Province. Environmental Research [Internet. 2021. DOI
61. Javidpour J., Molinero J.-C., Ramírez-Romero E., Roberts P., Larsen T.. Cannibalism makes invasive comb jelly, Mnemiopsis leidyi, resilient to unfavourable conditions. Commun Biol [Internet. 2020; 3(1)DOI
62. Jeffery N.W., DiBacco C., Wringe B.F., Stanley R.R.E., Hamilton L.C., Ravindran P.N., Bradbury I.R.. Genomic Evidence of Hybridization Between Two Independent Invasions of European Green Crab (Carcinus maenas. Northwest Atlantic. Heredity [Internet. 2017; 119(3):154-165. DOI
63. Mba Joy Uchechukwu. Advancing maritime operations sustainable practices and enhanced safety protocols for global shipping. World J Adv Res Rev [Internet. 2025. DOI
64. Karlson B., Andersen P., Arneborg L., Cembella A., Eikrem W., John U., West J.J., Klemm K., Kobos J., Lehtinen S.. Harmful algal blooms and their effects in coastal seas of Northern Europe. Harmful Algae [Internet. 2021; 102(101989)DOI
65. Kim H., Lee S., Son B., Jeon J., Kim D., Lee W., Youn H., Lee J.-M., Youn B.. Biocidal effect of thymol and carvacrol on aquatic organisms: Possible application in ballast water management systems. Marine Pollution Bulletin [Internet. 2018. DOI
66. Knowler D.. Reassessing the costs of biological invasion: Mnemiopsis leidyi in the Black sea. Ecological Economics [Internet. 2005. DOI
67. Kolios A.. Retrofitting Technologies for Eco-Friendly Ship Structures: A Risk Analysis Perspective. JMSE [Internet. 2024; 12(4)DOI
68. Kraus R.. Ballast Water Management in Ports: Monitoring, Early Warning and Response Measures to Prevent Biodiversity Loss and Risks to Human Health. JMSE [Internet. 2023; 11(11)DOI
69. P Kumar Rai, JS Singh. Invasive alien plant species: Their impact on environment, ecosystem services and human health. Ecological Indicators [Internet. 2020. DOI
70. Kurniawan S.B., Pambudi D.S.A., Ahmad M.M., Alfanda B.D., Imron M.F., Abdullah S.R.S.. Ecological impacts of ballast water loading and discharge: insight into the toxicity and accumulation of disinfection by-products. Heliyon [Internet. 2022. DOI
71. Lakshmi E., Priya M., Achari V.S.. An overview on the treatment of ballast water in ships. Ocean & Coastal Management [Internet. 2021. DOI
72. Landrigan P.J., Stegeman J.J., Fleming L.E., Allemand D., Anderson D.M., Backer L.C., Brucker-Davis F., Chevalier N., Corra L., Czerucka D.. Human Health and Ocean Pollution. Annals of Global Health [Internet. 2020; 86(1)DOI
73. Loucks D.P.. The Impacts of Climate Change [Internet. Elsevier: Elsevier; 2021:19-50. DOI
74. Lower E., Sturtevant R., Iott S., Martinez F., Rutherford E., Mason D.M., Redinger J., Elgin A.K.. The Great Lakes’ most unwanted: Characterizing the impacts of the top ten Great Lakes aquatic invasive species. Journal of Great Lakes Research [Internet. 2024. DOI
75. Lv B., Zhu G., Tian W., Guo C., Lu X., Han Y., An T., Cui Y., Jiang T.. The prevalence of potential pathogens in ballast water and sediments of oceangoing vessels and implications for management. Environmental Research [Internet. 2023. DOI
76. MacIsaac H.J., Roy E.M., Leung B., Grgicak-Mannion A., Ruiz G.M.. PLoS ONE [Internet. 2016. DOI
77. Makkonen T., Inkinen T.. Systems of environmental innovation: sectoral and technological perspectives on ballast water treatment systems. WMU J Marit Affairs [Internet. 2021. DOI
78. MarineLinkcom. New Ballast Water Regulations Add Costs for Shipowners. 2013. Publisher Full Text
79. Mattes W.P., Kitson J.C.. Sea lamprey control in the Great Lakes: A Tribal/First Nations Representative’s perspective. Journal of Great Lakes Research [Internet. 2021. DOI
80. Mayfield A.E., Seybold S.J., Haag W.R., Johnson M.T., Kerns B.K., Kilgo J.C., Larkin D.J., Lucardi R.D., Moltzan B.D., Pearson D.E..In: Poland T.M., Patel-Weynand T., Finch D.M., Miniat C.F., Hayes D.C., Lopez V.M.. Invasive Species in Forests and Rangelands of the United States [Internet. Springer International Publishing: Springer International Publishing; 2021:5-39. DOI
81. McLaughlan C., Aldridge D.C.. Cultivation of zebra mussels (Dreissena polymorpha) within their invaded range to improve water quality in reservoirs. Water Research [Internet. 2013. DOI
82. Melnyk O., Bulgakov M., Vorokhobin I., Onishchenko O., Shibaev O., Sagaydak O., Kurdiuk S., Volianska Y..In: Gökçekuş H., Kassem Y.. Climate Change and Water Resources in Mediterranean Countries [Internet. Springer Nature Switzerland: Springer Nature Switzerland; 2025:157-171. DOI
83. Melnyk O.M., Onishchenko O.A., Shumylo O.M., Lohinov O.V., Pavlova N.L., Bulgakov M.P., Shapovalova I.O.S., Dolia O.E.. Chemical Methods and Nanotechnology Integration in Ship Ballast Water Management for Maritime Transport Sustainability. J of Chem and Tech [Internet. 2025; 32(4):1137-1148. DOI
84. Moreno-Andrés J., Ambauen N., Vadstein O., Hallé C., Acevedo-Merino A., Nebot E., Meyn T.. Inactivation of marine heterotrophic bacteria in ballast water by an Electrochemical Advanced Oxidation Process. Water Research [Internet. 2018. DOI
85. Motlagh Z.K., Tavakoli M., Sayadi M.H.. Microplastics and heavy metals in the coastal areas: Marine health assessment and ecosystem services values. Environmental Development [Internet. 2025. DOI
86. Naik R.K., Chakraborty P., D’Costa P.M., A N., Mishra R.K., Fernandes V.. A simple technique to mitigate microplastic pollution and its mobility (via ballast water) in the global ocean. Environmental Pollution [Internet. 2021. DOI
87. Nie A., Wan Z., Shi Z., Wang Z.. Cost-benefit analysis of ballast water treatment for three major port clusters in China: evaluation of different scenario strategies. Front Mar Sci [Internet. 2023. DOI
88. Nwigwe T., Kiyokazu M.. Review Study of Ballast Water Treatment System: Review of Ballast Water Treatment System Technologies. Journal of Maritime Research. 2023; XX(1):90-97.
89. Obayomi O.V., Olawoyin D.C., Oguntimehin O., Mustapha L.S., Kolade S.O., Oladoye P.O., Oh S., Obayomi K.S.. Exploring emerging water treatment technologies for the removal of microbial pathogens. Current Research in Biotechnology [Internet. 2024. DOI
90. Olaniyi E.O., Solarte-Vasquez M.C., Inkinen T.. Smart regulations in maritime governance: Efficacy, gaps, and stakeholder perspectives. Marine Pollution Bulletin. 2024; 202(116341)DOI
91. Onyena A.P., Nwaogbe O.R.. Assessment of water quality and heavy metal contamination in ballast water: Implications for marine ecosystems and human health. 2024. DOI
92. Outinen O., Bailey S.A., Casas-Monroy O., Delacroix S., Gorgula S., Griniene E., Kakkonen J.E., Srebaliene G.. Biological testing of ships’ ballast water indicates challenges for the implementation of the Ballast Water Management Convention. Front Mar Sci [Internet. 2024. DOI
93. Park P.J., Jang W.J., Lee D.J., Park T.J., Kim S.Y.. Electrochemical Detection of Free Chlorine in Ballast Water Management System. Advanced Sensor Research [Internet. 2025. DOI
94. Petatán-Ramírez D., Hernández L., Becerril-García E.E., Berúmen-Solórzano P., Auliz-Ortiz D., Reyes-Bonilla H.. an invasive species in the Atlantic Ocean. RBT [Internet. 2020. DOI
95. Poornima S., Manikandan S., Karthik V., Balachandar R., Subbaiya R., Saravanan M., Lan Chi N.T., Pugazhendhi A.. Emerging nanotechnology based advanced techniques for wastewater treatment. Chemosphere [Internet. 2022. DOI
96. Racault M.-F., Abdulaziz A., George G., Menon N., J C., Punathil M., McConville K., Loveday B., Platt T., Sathyendranath S., Vijayan V.. Environmental Reservoirs of Vibrio cholerae: Challenges and Opportunities for Ocean-Color Remote Sensing. Remote Sensing [Internet. 2019; 11(23)DOI
97. Sari W.R., Gunawan G.. Systematic Considerations for a Ballast Water Treatment System (BWTS) Retrofits: A Review. Kapal [Internet. 2024; 21(1):61-72. DOI
98. Sempere-Valverde J., Ostalé-Valriberas E., Maestre M., González Aranda R., Bazairi H., Espinosa F.. Impacts of the non-indigenous seaweed Rugulopteryx okamurae on a Mediterranean coralligenous community (Strait of Gibraltar): The role of long-term monitoring. Ecological Indicators [Internet. 2021. DOI
99. Seridou P., Kotzia E., Katris K., Kalogerakis N.. Ballast water treatment by ozone nanobubbles. J of Chemical Tech & Biotech [Internet. 2024. DOI
100. Shiganova T.A., Kamakin A.M., Pautova L.A., Kazmin A.S., Roohi A., Dumont H.J.. Advances in Marine Biology [Internet. Elsevier: Elsevier; 2023:69-157. DOI
101. Shiganova T.A., Sommer U., Javidpour J., Molinero J.C., Malej A., Kazmin A.S., Isinibilir M., Christou E., Siokou- Frangou I., Marambio M.. Patterns of invasive ctenophore Mnemiopsis leidyi distribution and variability in different recipient environments of the Eurasian seas: A review. Marine Environmental Research [Internet. 2019. DOI
102. Siers Nafus, MG Calaor, JE Volsteadt, RM Grassi, MS Volsteadt, M Collins, AF Barnhart, PD Huse, LT Yackel Adams, AA Vice, D.L.. Limitations of invasive snake control tools in the context of a new invasion on an island with abundant prey. NB [Internet. 2024. DOI
103. Slišković M., Piria M., Nerlović V., Ivelja K.P., Gavrilović A., Mrčelić G.J.. Non-indigenous species likely introduced by shipping into the Adriatic Sea. Marine Policy [Internet. 2021. DOI
104. Soleimani F., Taherkhani R., Dobaradaran S., Spitz J., Saeedi R.. Molecular detection of E. coli and Vibrio cholerae in ballast water of commercial ships: a primary study along the Persian Gulf. J Environ Health Sci Engineer [Internet. 2021; 19(1):457-463. DOI
105. South P.M., Floerl O., Forrest B.M., Thomsen M.S.. A review of three decades of research on the invasive kelp Undaria pinnatifida in Australasia: An assessment of its success, impacts and status as one of the world’s worst invaders. Marine Environmental Research [Internet. 2017. DOI
106. Sukhikh N., Souissi A., Souissi S., Holl A.-C., Schizas N.V., Alekseev V.. Life in sympatry: coexistence of native Eurytemora affinis and invasive Eurytemora carolleeae in the Gulf of Finland (Baltic Sea. Oceanologia [Internet. 2019. DOI
107. Teem J.L., Alphey L., Descamps S., Edgington M.P., Edwards O., Gemmell N., Harvey-Samuel T., Melnick R.L., Oh K.P., Piaggio A.J.. Genetic Biocontrol for Invasive Species. Front Bioeng Biotechnol [Internet. 2020. DOI
108. Thushari G.G.N., Senevirathna J.D.M.. Plastic pollution in the marine environment. Heliyon [Internet. 2020. DOI
109. Trégarot E., D’Olivo J.P., Botelho A.Z., Cabrito A., Cardoso G.O., Casal G., Cornet C.C., Cragg S.M., Degia A.K., Fredriksen S.. Effects of climate change on marine coastal ecosystems – A review to guide research and management. Biological Conservation [Internet. 2024. DOI
110. Trichkova T., Kutsarov Y., Todorov M., Puky M., Hubenov Z.K.. The Chinese Mitten Crab Eriocheir sinensis H. Milne Edwards, 1853 (Crustacea: Decapoda: Varunidae), a New Invasive Alien Species to the Bulgarian Fauna. Acta Zoologica Bulgarica [Internet. 2017; 9:149-154. Publisher Full Text
111. Tsikoti C., Genitsaris S.. Review of Harmful Algal Blooms in the Coastal Mediterranean Sea, with a Focus on Greek Waters. Diversity [Internet. 2021; 13(8)DOI
112. Tsolaki E., Diamadopoulos E.. Technologies for ballast water treatment: a review. J of Chemical Tech & Biotech [Internet. 2010. DOI
113. Guard U.S.Coast. Ballast Water Management Enforcement [Internet. 2023. Publisher Full Text
114. Verna D.E., Harris B.P.. Review of ballast water management policy and associated implications for Alaska. Marine Policy [Internet. 2016. DOI
115. Wang Q., Lin L., Chen X., Wu W., Wu H.. Transportation of bloom forming species in ballast water by commercial vessels at Yangshan deep water port. Ocean & Coastal Management [Internet. 2022. DOI
116. Wang Z., Nong D., Countryman A.M., Corbett J.J., Warziniack T.. Potential impacts of ballast water regulations on international trade, shipping patterns, and the global economy: An integrated transportation and economic modeling assessment. Journal of Environmental Management [Internet. 2020. DOI
117. Ward D., Melbourne-Thomas J., Pecl G.T., Evans K., Green M., McCormack P.C., Novaglio C., Trebilco R., Bax N., Brasier M.J.. Safeguarding marine life: conservation of biodiversity and ecosystems. Rev Fish Biol Fisheries [Internet. 2022; 32(1):65-100. DOI
118. Williams S., Davidson I.C., Pasari Ashton, GV Carlton, JT Crafton, RE Fontana, RE Grosholz, E Miller, AW Ruiz, G Zabin, C.J.. Managing Multiple Vectors for Marine Invasions in an Increasingly Connected World. BioScience [Internet. 2013; 63(12):952-966. DOI
119. Yñiguez A.T., Lim P.T., Leaw C.P., Jipanin S.J., Iwataki M., Benico G., Azanza R.V.. Over 30 years of HABs in the Philippines and Malaysia: What have we learned?. Harmful Algae [Internet. 2021; 102(101776)DOI
120. Yoon H.K., Park S.Y., Kim C.G.. Comparison of the bacterial viability assessments for the disinfected quarantined water along with an effect of total residual oxidants. Environ Monit Assess [Internet. 2021; 193(12)DOI
121. Zendehboudi A., Mohammadi A., Dobaradaran S., De-la-Torre G.E., Ramavandi B., Hashemi S.E., Saeedi R., Tayebi E.M., Vafaee A., Darabi A.. Analysis of microplastics in ships ballast water and its ecological risk assessment studies from the Persian Gulf. Marine Pollution Bulletin [Internet. 2024. DOI
122. Zenetos A., Gofas S., Verlaque M., Cinar M.E., Garcia Raso J.E., Bianchi C.N., Morri C., Azzurro E., Bilecenoglu M., Froglia C.. Alien species in the Mediterranean Sea by. Part I. Spatial distribution. Medit Mar Sci [Internet. 2010; 11(2)DOI
123. Zreik M.. Synergizing trade and sustainability: advancing SDG 14 through international trade dynamics. Mar Dev [Internet. 2024. DOI