Abstract
Aquaculture is the world’s fastest-growing industry for food production and serves as a key component in meeting the growing need for animal protein and ensuring food and nutritional security. However, its rapid growth has also led to significant sustainability challenges, such as water scarcity, depletion of feed resources, disease outbreaks, and environmental degradation. To address these issues, numerous management techniques and technological advances are currently underway to make aquaculture more sustainable. Among these, biofloc technology (BFT), recirculating aquaculture systems (RAS), aquaponics, and Integrated Multi-Trophic Aquaculture (IMTA) has emerged as a cost-effective approach for intensive production with low water consumption and effective waste control. With the help of automation, IoT-based sensors, and artificial intelligence, precision aquaculture is transforming real-time monitoring and decision- making, increasing resource efficiency and lowering risks. Disease resistance and enhanced stock performance have also been facilitated by developments in genetics and biotechnology. Furthermore, the discovery of sustainable dietary alternatives reducing dependence on limited marine resources. Global case studies show that adopting these technologies not only increases profitability and production, but also maintains ecological balance. In the future, it is anticipated that aquaculture practices will be redefined to be more resilient and climate-friendly due to the confluence of digital technologies, renewable energy, and circular bioeconomy concepts. The article examines these new developments and highlights how they will help provide aquaculture with a sustainable future. By adopting cutting-edge methods, aquaculture could become a major sector in the future.
1 Introduction
Aquaculture is the fastest-growing food production industry globally, defined as the cultivation of aquatic organisms such as fish, crustaceans, molluscs and aquatic plants under controlled or semi-controlled conditions with intervention in stocking, feeding and other management activities; it also refers to the ownership of the stock. Aquaculture production has increased significantly worldwide over the past several decades due to the increasing need for high-protein foods and technological advances in farming systems (Gephart et al., 2021; FAO, 2024; Serra et al., 2024). Global aquaculture production now reaches approximately 130.9 million tons (94.4 million tonnes from aquatic animals and 36.5 million tons from algae), playing a vital role in food security, nutrition and livelihoods (FAO, 2024). The sector is seen as a sustainable substitute for capture fisheries, with enormous potential to boost economic growth and reduce poverty, especially in developing countries (; ). Despite its significant contributions, aquaculture faces several sustainability challenges, including poor water quality, dependence on fishmeal and fish oil, and high susceptibility to diseases under intensive farming conditions. Furthermore, traditional practices often result in environmental problems such as biodiversity loss, habitat degradation, and nutrient pollution (Tom et al., 2021; Føre et al., 2018). Addressing these challenges requires the development and implementation of innovative strategies that effectively balance environmental sustainability and production efficiency (Henriksson et al., 2021). Recent years have seen significant progress in developing cutting-edge methods and technologies aimed at improving the sustainability of aquaculture. Water management and wastewater recycling issues have been addressed by innovations such as recirculating aquaculture systems (RAS) and biofloc technology (BFT) (Verdegem et al., 2006; De Schryver et al., 2008; Ranjan et al., 2023; Ramiro et al., 2024). Aquaponics and integrated multi-trophic aquaculture (IMTA) are ecological methods that mimic natural food webs to maximize resource use (Kamleshbhai et al., 2023; Stoyanova et al., 2024). Similarly, farmers can now optimize feeding, track water quality in real time in aquaculture using artificial intelligence (AI), Internet of Things (IoT), and automated systems (Føre et al., 2018). The resilience and efficiency of aquaculture systems are further improved by biotechnology, genetic improvement initiatives, and the investigation of substitute feed ingredients (Lakra and Ayyappan, 2003; ).There are several new technological, ecological and socio-economic strategies including water management, nutrient recycling, digital monitoring, and ecosystem-based farming practices have been adopted to address the sustainability challenges associated with advancements in aquaculture (Figure 1). The aim of this article is to summarize innovative and modern methods that contribute to sustainable aquaculture production, and to demonstrate how these methods can address current challenges while maintaining ecological balance, economic viability and long-term sustainability, as well as to highlight their key concepts, applications and advantages.
Figure 1
2 Aquaculture development (1950 onwards)
Over the past seven decades, aquaculture has experienced a remarkable transformation, moving from small-scale traditional techniques to highly sophisticated technological- driven systems for greater production with fewer natural resources and the growing demand for seafood worldwide have influenced all this development that prioritize augmenting production efficiency and fulfill the global demand for nutritional security. This evolutionary process can be divided into major distinct phases which are summarized ahead in this chapter:
2.1 1950s-1970s: Foundation and early intensification
During the 1950s and 1970s, with improvements in early hatchery technology and simple mechanization, aquaculture relied primarily on traditional pond and shore farming. The development of managed ponds and advances in seed production made higher stocking densities possible, while net-pen farming for yellowtail (Seriola quinqueradiata) spread rapidly throughout Japan, laying the foundation for contemporary cage-farming systems (Milne, 1972). In 1953, botanist and zoologist J.H.S. Blaxter reported the first successful attempt at cryopreservation in fish, in which he used cryopreserved sperm to fertilize herring eggs (). The induced breeding technology for carps was developed in 1957 () and popularized for ensuring the quality of seed. The commercial cage farming of Atlantic salmon (Salmo salar) began in Norway in 1960, and similar system was soon adopted by other countries (Grøttum and Beveridge, 2007). At the same time, the scientific foundations of biofloc technology (BFT) were being established and practical studies on microbial flocs began in the early 1970s at Ifremer (France) and the Waddell Mariculture Center in the United States, although the idea was first proposed in the 1960s. These fundamental developments laid the foundation for more complex, technology-based systems developed in subsequent decades.
2.2 1971-1990s: Rapid expansion and environmental challenges
Aquaculture for shrimp and finfish expanded rapidly in this era, particularly in Asia and Latin America. Hatchery development, technological advances, and global market demand led to rapid production growth. However, this boom was also accompanied by serious environmental problems, such as eutrophication, mangrove destruction, and frequent disease outbreaks due to uncontrolled growth. To address these problems, scientists began investigating closed water circulation and recirculation systems. This led to the development of contemporary recirculating aquaculture systems (RAS), which subsequently revolutionized intensive farming methods (Ghosh, 2022; Mugwanya et al., 2022). In 1988, the first commercial application of BFT was realized in Tahiti (Emerenciano et al., 2013). Early aquaponics experiments also emerged during this period (Lennard, 2017). These programs were the first major steps toward more biosecure and sustainable aquaculture practices.
2.3 1991-2000: Technological formalization and system integration
During this period, aquaculture development focused primarily on improving integrated farming methods. The development of recirculating aquaculture systems (RAS) significantly formalized the technology. RAS was made possible by advances in biofiltration, pumping efficiency, water treatment, and automation, leading to the transformation from experimental models to pilot-scale commercial operations (; Lindholm-Lehto, 2023; Gupta et al., 2024). At the same time, studies on the integration of microalgae into RAS gained momentum, emphasizing their functions in nutrient absorption, CO2 sequestration, and oxygen production, facilitating the development of more closed-loop and efficient production systems (Ende et al., 2024). This decade also saw the development of the concept of integrated multi-trophic aquaculture (IMTA), which encourages the ecological engineering of farms by co-culturing host species with extractive species such as seaweeds and bivalves to improve environmental performance and utilize waste nutrients (). The ecological and technological basis for the precise and sustainable production model that would be developed over the next ten years was established at this time.
2.4 2001-2010: Commercial expansion
This period marked a major shift, with cutting-edge sustainable technologies rapidly being adopted commercially. Established over the past decades, biofloc technology (BFT) has rapidly expanded commercially as a low-water exchange, high-efficiency production system, especially for tilapia and shrimp. BFT improves feed utilization and water quality by converting nitrogenous wastes into microbial biomass, which has attracted intensive aquaculture (; Yu et al., 2023). In parallel, governments and academic organizations promoted IMTA and aquaponics as sustainable nutrient recycling methods, and recent advancements have focused on incorporating innovative system designs and digital tools to enhance sustainability and efficiency. By combining multi-trophic species with hydroponic techniques (such as NFT and floating raft systems), modern IMTA-aquaponics research demonstrates improved nutrient and water use efficiency and reduced effluent discharge, enabling greater nutrient retention and total biomass production compared to monoculture (Goda et al., 2024; Ghosh et al., 2025). Furthermore, IoT sensors, artificial intelligence, and machine learning are now being integrated into smart aquaponics systems for automated control and real-time monitoring of water quality and nutrient cycling, increasing yields and resource efficiency while reducing labor input (Niranjan et al., 2020; Gayam et al., 2024; Nair et al., 2025). The development of open sea cage culture has provided a new dimension to the mariculture in India and in the year 2007, the first open sea cage was launched in Bay of Bengal off Visakhapatnam coast (Philipose et al., 2012).
2.5 2011-2020: Precision aquaculture, and policy uptake
Technology has been rapidly integrated into the industry, moving from traditional to data-driven smart farming. The use of automated sensors and real-time monitoring systems for variables such as pH, temperature, and dissolved oxygen has significantly improved decision-making and system management. Automation, IoT-based monitoring, artificial intelligence, and analytics have led to the development of precision aquaculture, which reduces risk and increases production (Lindholm-Lehto, 2023). Meanwhile, ecological farming methods such as aquaponics, BFT, and IMTA gained greater use and support from both research and policy frameworks. Throughout this decade, the combination of ecological sustainability and innovative technology made climate-resilient, resource-efficient aquaculture systems possible.
2.6 2020-2025: Digitalization, climate resilience, and circular bioeconomy
The aquaculture industry has recently entered a new era characterized by digital transformation, climate resilience, and circular bioeconomy models. Since 2020, AI and digitalization technologies have been widely adopted, especially in large-scale operations for high-value species such as shrimp and salmon. By combining predictive analytics, real-time control, and automated monitoring, these systems improve environmental performance and biosecurity (Gupta et al., 2024). To complement nutrient cycling and reduce energy costs, more research is being conducted on integrating microalgae-based systems into RAS (Ende et al., 2024). In addition to enhancing water quality and reducing feed inputs, BFT applications have also expanded to include shellfish production (Manan et al., 2024; Minaz et al., 2024). With the help of machine learning, precision aquaculture based on IoT and AI is improving water quality control and feeding schedules (Lindholm-Lehto, 2023). Significant progress has also been made in sustainable alternative feeds such as single-cell protein, algae oil, and insect meal, which significantly reduce dependence on fishmeal and fish oil and support circular production models (Yu et al., 2023). Taken together, these advances represent an advanced stage in aquaculture development that combines ecological sustainability and technological complexity.
3 Sustainability challenges in aquaculture
The rapid growth of aquaculture has helped meet the world’s aquatic food supply needs; it has also raised serious sustainability challenges. These challenges arise from the need to balance long-term socio-economic sustainability, resource efficiency, environmental protection, and high productivity. The main sustainability issues facing aquaculture are discussed below:
3.1 Water quality and resource management
Aquaculture inherently requires a lot of water, and improper water resource management can have detrimental ecological impacts. Intensive farming practices generate large amounts of nitrogen (N) and phosphorus (P)-rich metabolic waste and unused feed. These nutrients, when released into the open water bodies, can accumulate and cause eutrophication, increase algal blooms, create hypoxic condition, deteriorate water quality and cause disease (Li et al., 2025; Khalili and Moridi, 2025; ). Climate change exacerbates these problems by altering water temperature, salinity, and dissolved oxygen levels, further stressing cultivated species and weakening system resilience. Furthermore, water scarcity in many regions is hampering fisheries development, highlighting the need for efficient water-use technologies. Saltwater is another problem for freshwater species, causing physiological stress that hinders growth and survival. It affects the traditional farming system, raising the expense of water management and forcing a shift towards less suited species or techniques ().
3.2 Feed resource scarcity
Fishmeal and fish oil from wild fisheries have historically been the main sources of protein used in aquaculture production. Because overfishing reduces biodiversity and disrupts aquatic food webs, this dependence places significant pressure on marine ecosystems (Tacon and Metian, 2015). Since global fishmeal production is limited and confined to a few regions, its supply is vulnerable to regulatory changes, overfishing, and climate variability (Naylor et al., 2009). The economic viability of aquaculture enterprises is impacted by rising feed costs, which in turn increase production costs. Demand for protein-rich feed is increasing alongside the rapid growth of aquaculture, further intensifying competition with the livestock and poultry industries. Furthermore, conventional feed ingredients may contain anti-nutritional ingredients, pollutants, or environmental impacts that exacerbate ecological constraints (Gatlin et al., 2007). The industry must provide sufficient quantities of high-quality feed that meet the nutritional requirements for healthy growth, while avoiding over-reliance on wild fisheries and minimizing adverse environmental impacts.
3.3 Disease outbreaks and biosecurity risks
One of the biggest obstacles to the viability of aquaculture is aquatic animal diseases. Cultured species are more susceptible to bacterial, viral, fungal and parasitic diseases due to high stocking densities, poor animal husbandry techniques, and environmental stresses (; Li, 2024). The high stocking densities of fish in aquaculture experience chronic physiological stress due to overcrowding and intense competition for food, oxygen, and space (North et al., 2006; Lupatsch et al., 2010). This stress activates the hypothalamic-pituitary-interrenal (HPI) axis, leading to prolonged release of cortisol (Flik et al., 2006; Mbiydzenyuy and Qulu, 2024). High cortisol level suppresses immunological activities by reducing leukocyte activity, antibody synthesis, and phagocytic function (Gonzalez Herrero and Kuehn, 2021). In addition to the effects mediated by cortisol, high stocking density also alters other stress-related physiological parameters such as high blood glucose and lactate levels, increased metabolic demand, oxidative stress, and impaired osmoregulatory balance (David, 1997; Elnady et al., 2017; Gyamfi et al., 2022; ). Frequent physical contact and aggressive interactions in crowded condition also weaken the primary defense barriers (Dash et al., 2018). All these factors collectively increase the pathogen load and accelerate the spread of infections within the culture system. Consequently, the fish become more susceptible to opportunistic infections, which can lead to disease outbreaks and increased mortality rates (Mishra et al., 2017). Disease outbreaks can have a detrimental impact on global trade, disrupting production cycles and causing significant financial losses (Kumar et al., 2022; Maezono et al., 2025). The World Organization for Animal Health (WOAH, formerly OIE) lists serious diseases of fish, crustaceans and molluscs that commonly affect trade and health. Antimicrobial resistance (AMR), a major threat to aquaculture systems and public health, also results from the excessive use of antibiotics and chemical treatments for disease control (Schmidt et al., 2000; Preena et al., 2020). Climate change, declining water quality, and the movement of living aquatic organisms all contribute to the establishment and spread of diseases.
3.4 Environmental impacts and biodiversity loss
Aquaculture, if not properly managed, it can severely harm the environment. According to Primavera (2000), coastal aquaculture development often leads to the destruction of fragile habitats essential for biodiversity and ecosystem services, such as mangroves, wetlands, and estuarine ecosystems. Ecological concerns include genetic inbreeding with wild populations, competition for resources, and disruption of local food webs when farmed animals escape into natural habitats (). Furthermore, water quality, sediment chemistry, and surrounding biodiversity can all be affected by pesticides, antibiotics, and nutrient-rich wastewater from aquaculture operations ().
3.5 Socio-economic and governance issues
Sustainability in aquaculture encompasses socio-economic and administrative aspects, in addition to environmental ones. In India, small-scale farmers often face significant barriers that prevent them from implementing cutting-edge sustainable technologies, such as limited access to markets, capital, and technology. For example, a study by Haryanto (2023) emphasizes the importance of financial support for small-scale farmers, demonstrating how access to finance from both formal and informal sources impacts food production and technical efficiency. Sustainable development is further hampered by unequal distribution of resources, weak policy frameworks, and ineffective regulation. The challenges faced by small-scale fisheries, such as poor infrastructure and limited space for investment and innovation, are recognized in the National Fisheries Policy, 2020. Concerns regarding food safety, product quality, and environmental impacts also influence societal acceptance of aquaculture operations. According to a FSN, 2025 survey, over 80% of Indians are concerned about food security, highlighting a serious public perception problem that could impact the expansion and long-term viability of the aquaculture industry.
4 Recent advanced techniques in sustainable aquaculture
Sustainability issues in aquaculture require the implementation of innovative technologies that optimize resource utilization, minimize environmental impacts, and increase production efficiency. To address these issues, several cutting-edge technologies have been developed and implemented globally in recent years (Table 1).
Table 1
| Category | Technology/ingredient/species/ tools | Core function/key characteristics | Sustainability impact | References |
|---|---|---|---|---|
| Intensive Aquaculture Systems | Recirculating Aquaculture Systems (RAS) | Minimizes water exchange with optimizing water quality and efficiency; maintains high FCR; integrates solar energy to reduce costs and enable year-round production | Excellent water efficiency and sustainability is enhanced by renewable energy | Yogev et al. (2021) |
| Biofloc Technology (BFT) | Recycle nutrients via microbial flocs; high FCR; low production cost | Reducing waste, increasing feed efficiency, and recycling nutrients | Ekasari et al. (2014) | |
| Aquaponics (AP) | Combines fish and plant production; plants enhance water quality; water is efficiently reused | Co-production of crops and resource efficiency | Rakocy et al. (2006) | |
| Integrated Multi-Trophic Aquaculture (IMTA) | Production is increased by recycling waste through integration of different species | Reduces waste and increases the efficiency of the ecosystem | ||
| Novel Aquafeed Ingredients | Black Soldier Fly Meal (BSFM) | Sustainable protein alternative; promotes circular economy | Reduces fishmeal use and environmental impact | Mohan et al. (2022) |
| Silkworm pupae meal (SPM) | Sustainable protein alternative; promotes circular economy. | Reduces fishmeal use and environmental impact | Rahimnejad et al. (2019); Jeyaprakashsabari and Aanand (2021) | |
| Microalgae | Good source of omega-3; alternative to fish oil | Sustainable supply of DHA/EPA | Liu et al. (2022) | |
| Soybean Meal (SBM) | Inexpensive and widely accessible source of protein | An economically viable option | Kari et al. (2023) | |
| Corn Gluten Meal | Plant-based high protein source that helps replace the fish meal at some levels | Sustainable protein alternative | McLean (2023) | |
| Pea Protein Concentrate | Highly digestible plant protein; balanced amino acids. | Sustainable and eco-friendly alternative | Salin et al. (2018) | |
| Wheat Gluten | Highly digestible; increases protein content and pellet binding | Sustainable and economical source of protein | ||
| Lupin Meal | Protein-rich | Eco-friendly and sustainable alternative | Szczepański et al. (2022) | |
| Sunflower Meal | Protein-rich; cost-effective and regionally available | Economically sustainable plant protein | Eide et al. (2025) | |
| Genetic Improvement | Atlantic Salmon | Selective breeding to increase resistance to sea lice and IPN | increased survival and reduces chemical use | Gharbi et al. (2015) |
| Pacific White Shrimp | Advanced breeding for Taura syndrome virus resistance | Increases productivity and disease resistance | ||
| Nile Tilapia | Improved feed efficiency and growth through selective breeding. | Increased production efficiency and FCR. | ||
| Oysters (Crassostrea sp.) | Higher disease resistance and survival through selection and triploidy | Greater resilience and yield | Jiang et al. (2024) | |
| Atlantic Cod | Improved growth and tolerance to disease through selective breeding | Reduces chemical use and mortality | Rose (2018); Ødegård et al. (2010) | |
| Precision Aquaculture Technologies | AI-Driven Automated Feeding | Increases efficiency and optimizes feeding in real time | Reduces waste and improves FCR | Ragab et al. (2025) |
| Computer Vision for Biomass Estimation | Measures biomass accurately and non-invasively | Facilitates accurate grading and management | ||
| IoT Sensor Arrays & Predictive Analytics | Allows for early intervention and continuous monitoring | Increases agricultural resilience and prevents losses | Flores-Iwasaki et al. (2025) | |
| Deep Learning for Early Disease Detection | Behavioral analysis is used for early detection of diseases | Enhances health and reduces the use of antibiotics |
Overview of technologies, aquafeed ingredients and genetic advances for sustainable aquaculture development.
4.1 Recirculating aquaculture systems
One of the most innovative and environment friendly developments in modern aquaculture is recirculating aquaculture system (RAS). Compared to traditional techniques, these closed-loop production systems typically use 90-95% less freshwater because they reuse water (Timmons et al., 2002). RAS significantly reduces waste emissions and environmental impacts, while also providing a high level of environmental control that allows for efficient use of labor and space (Yogev et al., 2021). Mechanical filters, biological filters and UV radiation are some of the essential elements in a RAS system for water treatment and reuse (Xiao et al., 2019; Ranjan et al., 2023). While biological filtration uses nitrifying bacteria to convert toxic ammonia and nitrite into less dangerous nitrate, mechanical filtration removes suspended matter, including uneaten feed and feces (Martins et al., 2005). Additional equipment’s such as temperature regulator and oxygenation unit promise ideal for culture conditions. Due to controlled conditions and minimal water usage, these techniques are suitable for a wide variety of aquatic organisms (Table 2).
Table 2
| Techniques | Suitable species | References |
|---|---|---|
| RAS | Oreochromis niloticus, Clarias gariepinus, Pangasianodon hypophthalmus, Cyprinus carpio, Ictalurus punctatus, Oncorhynchus mykiss, Salmo salar, Dicentrarchus labrax, Sparus aurata, Lates calcarifer, Seriola lalandi, Epinephelus sp., Litopenaeus vannamei, Penaeus monodon, Macrobrachium rosenbergii | Tseng et al. (1998); Skjølstrup et al. (2000); Yu et al. (2012); Orellana et al. (2014); Sri-uam et al. (2016); Ngoc et al. (2016); Ray and Lotz (2017); ; Hanif et al. (2021); Indriastuti et al. (2022); Crouse et al. (2022); Godoy-Olmos et al. (2022); Ezhilmathi et al. (2023); Dawood et al. (2025); Crouse et al. (2023); ; Nasr-Eldahan et al. (2025); Mihály-Karnai et al. (2025) |
| Biofloc (BFT) | Mugil liza, Litopenaeus vannamei, Labeo rohita, Catla catla and Cirrihinus mrigala, Oreochromis niloticus, Heteropneustes fossilis, Penaeus monodon, Macrobrachium rosenbergii, Clarias gariepinus, Carassius auratus, Pseudotropheus saulosi, Anabus testudineus, Channa striatus | Hari et al. (2004); ; ; ; Emerenciano et al. (2013); Faizullah et al. (2015); Harini et al. (2016); Putra et al. (2019); Prasad et al. (2018); Wankanapol et al. (2020); Elayaraja et al. (2020); Deb et al. (2020); Holanda et al. (2020); Xu et al. (2021); Shamsuddin et al. (2022); Khanjani et al. (2023); Raizada et al. (2023) |
| IMTA | Fed species-Oreochromis niloticus, Oncorhynchus mykis, Salmo salar, Penaeus monodon, Litopenaeus vannamei, Catla catla, Hypophthalmichthys molitrix, Labeo rohita, Cirrhinus cirrhosus, Heteropneustes fossilis, Channa striatus, Sparus aurata Extractice species-Mytilus edulis, Crassostrea gigas, Mytilus edulis, Viviparus bengalensis, Holothuria poli, Paracentrotus lividus; seaweeds-Ulva ohnoi, Ulva lactuca, Gracilaria sp., Hypnea sp., Saccharina latissima, Alaria esculenta, Gracilaria chilensis; aquatic plants-Oxalis sp., Ipomoea aquatica, Azolla sp., Lemna sp. | ; Troell et al. (2009); MacDonald et al. (2011); ; Liutkus et al. (2012); Kibria and Haque (2018); Shpigel et al. (2018); Strand et al. (2018); ; ; ; ; ; Rahman et al. (2020); de Morais et al. (2023); Joseph et al. (2023); ; Cutajar et al., 2022 |
| Aquaponics | Fishes-Rhamdia quelen, Astyanax lacustris, Piaractus mesopotamicus, Colossoma macropomum, Centropomus spp., Oreochromis niloticus, Cyprinus carpio, Ictalurus punctatus, Micropterus salmoides, Oncorhynchus mykiss, Lates calcarifer, Clarias gariepinus | Rakocy et al. (2006); ; ; Espinosa-Moya et al. (2018); Goddek et al. (2019); Yap and Teo (2019); Pinho et al. (2021); Hager et al. (2021); Hager et al. (2021); ; Nishanth (2023); Junaid et al. (2023); Stoyanova et al. (2024) |
| Plants-Ocimum basilicum and Corchorus olitorius, Lactuca sativa, Ocimum basilicum, Ipomoea aquatica, Brassica juncea, Coriandrum sativum, Mentha spicata, Salvia rosmarinus, Origanum vulgare, Thymus vulgaris |
Suitable species to be cultured under various aquaculture techniques.
To enhance the efficiency of water reuse, modern disinfection and oxidation technologies, including ultraviolet (UV) irradiation and ozonation, are being increasingly employed in addition to conventional mechanical and biological filtration. The UV treatment in culture system efficiently inactivates pathogenic microorganisms without leaving harmful residues, while ozonation oxidizes dissolved organic matter, reduces color and odor, and improves biofilter performance by reducing the organic load before nitrification (; Malone and Pfeiffer, 2006). Recently discovered ammonia oxidizers, such as ammonia-oxidizing archaea (AOA) and complete ammonia oxidizers (comammox Nitrospira), which can directly oxidize ammonia to nitrate within a single organism, have also been incorporated into recent advancements in RAS biofiltration, surpassing traditional ammonia-oxidizing bacteria (Nitrosomonas and Nitrobacter). These microbial groups are now considered significant contributors to stable nitrification under low-ammonia and low-oxygen conditions, which are often present in intensive RAS operations (Daims et al., 2015; Van Kessel et al., 2015; ).
4.2 Biofloc technology
Biofloc technology (BFT), based on microbial activity to recycle nutrients within the culture unit, has become another innovative and environment friendly aquaculture technique. Bacteria, algae, protozoa, and organic matter are all part of the diverse microbial community generated by this system (Hargreaves, 2013; Robles-Porchas et al., 2020). BFT reduces the need for water exchange and the discharge of nutrient-rich waste into natural water bodies by encouraging water reuse over multiple cycles (Krummenauer et al., 2014). In this system, host bacteria produce microbial protein aggregates called “bioflocs” from leftover feed and excreta. Cultured species such as fish and shrimp (Table 2) can consume these flocs, increasing feed efficiency and providing an additional source of protein. Studies have shown that BFT enhances environmental control and promotes optimal yields at high stocking densities (Da Silveira et al., 2020; Schveitzer et al., 2024).
The addition of external carbon sources to control the carbon-nitrogen (C:N) ratio and promote the growth of beneficial heterotrophic microbial communities is a crucial management strategy in biofloc system. There are several carbon sources like molasses, wheat flour, rice bran, tapioca flour, cassava powder, jaggery and other agro-industrial by-products have been effectively used to maintain C:N ratio (Wei et al., 2016; Ezhilarasi et al., 2019; Rind et al., 2023). These carbon sources are considered ecological and economical options because they are often derived from locally available agricultural waste and help the system recycle nutrients by converting inorganic nitrogenous waste into microbial biomass (; ; Wei et al., 2016). In addition to improving water quality, the resulting microbial flocs provide an additional source of protein-rich feed for the cultured organisms, increasing feed utilization efficiency and system sustainability (Emerenciano et al., 2013; Hargreaves, 2013). However, there are serious risks associated with poor C:N ratio control in BFT systems, such as disease outbreaks and system instability. If the carbon-nitrogen (C:N) ratio is not properly maintained, the excessive growth of heterotrophic bacteria can lead to oxygen depletion, accumulation of suspended solids, and inhibition of the autotrophic nitrifying bacteria responsible for ammonia oxidation (Michaud et al., 2006). Such imbalances in the culture system can lead to increased levels of ammonia or nitrite, as well as an increased risk of opportunistic infections in the organisms (; Martins et al., 2010). Therefore, regular monitoring and control of carbon inputs are essential to maintain microbial balance, prevent harmful microbial communities from becoming dominant, and guarantee the health and biosecurity of BFT-based aquaculture systems (De Schryver et al., 2008; Ekasari et al., 2014).
4.3 Integrated Multi-Trophic Aquaculture
Integrated Multi-Trophic Aquaculture (IMTA) is a sustainable farming approach that combines fed species with extractive species (Table 2) that utilize organic and inorganic wastes for growth (; Khanjani et al., 2022). In many traditional monoculture systems, species are cultivated independently, leading to nutrient accumulation and environmental damage. By bringing together organisms from different trophic levels, IMTA facilitates the movement of nutrients and energy through the water. By producing a variety of products and reducing production risks, this integrated system not only increases economic sustainability but also improves environmental sustainability by preventing eutrophication and recycling nutrients (biomimetics). Additionally, it improves social acceptance of aquaculture by demonstrating better farm management and ecologically conscious techniques (Sasikumar and Viji, 2016). IMTA is not the same as finfish polyculture, which can disrupt ecosystems because co-cultured species share similar biological and chemical processes. IMTA, on the other hand, deliberately mixes species with complementary ecological roles; inorganic extractive species (seaweeds) collect liquid nutrients, organic extractive species consume particulate organic compounds, and feeder species supply waste nutrients. This technique is a potential strategy for sustainable aquaculture because it allows for more intensive farming while maintaining ecological balance ().
Modern IMTA systems are incorporating IoT-based real-time water quality monitoring to continuously track dissolved oxygen, nutrients, pH, and temperature to effectively manage multiple trophic levels and mitigate environmental concerns (Ruiz-Vanoye et al., 2025). In advanced IMTA setups, artificial intelligence and data-driven decision-support technologies are already being used to predict nutrient flows, optimize species combinations, and improve feeding efficiency (Peres da Silva, 2021; Ruiz-Vanoye et al., 2025). Integrating biofloc systems with soilless plant production (FLOCponics), which improves nutrient recycling through microbial biomass and simultaneously producing fish and plants, is another emerging technology (Pinho et al., 2022). The advancements in system design including modular and recirculating IMTA units further enhance resource use efficiency ().
4.4 Aquaponics
Aquaponics is an integration of hydroponic and aquaculture methods in a single system that create a closed-loop structure by fertilizing plants with nutrient-rich water from fish tanks and then recirculating the treated water back into the fish tanks (Roosta and Mohsenian, 2015; Thomas et al., 2019; ; Stoyanova et al., 2024). Aquaponics achieves water reuse rates of 95-99%, while requiring very little water exchange, effectively recycling nutrients, and significantly reducing wastewater emissions (Goddek et al., 2019; ; Manan et al., 2025). This system has many benefits, such as reduced dependence on external fertilizers, improved water quality, elimination of the need for additional filter systems, and the ability to produce suitable fish and plants species simultaneously (Table 2), thereby increasing sustainability and profitability (Shafahi and Woolston, 2014; Eck et al., 2019). Additionally, aquaponics supports the United Nations Sustainable Development Goals, specifically Goal 2 (Zero Hunger) and Goal 14 (Life Below Water), and helps ensure food security (Goddek et al., 2019; ).
However, recent developments in new system designs, algal co-cultivation, micro-nanobubble technology, biofilter media, and system automation with robotics, artificial intelligence, and the Internet of Things can improve real-time control of water quality parameters, feeding efficiency, freshwater replenishment rates, and nutrient balance in aquaponics (; Gayam et al., 2024; ). Improvements in modular, scalable, and vertical aquaponics systems have enhanced space and resource utilization efficiency, particularly in urban farming settings (). These technological advancements strengthen aquaponics as an essential component of integrated multitrophic aquaculture and circular food production systems.
4.5 Precision aquaculture
The approach to increasing aquaculture productivity through the focused application of technology and automation principles is known as precision aquaculture (Føre et al., 2018). The primary goal of precision aquaculture is to transform the industry from current production patterns, which are primarily manual and experience-based, to a more automated and knowledge-based one (Figure 2). As a result, farmers are able to better monitor and exercise greater control over their fish and surroundings. For aquaculture applications, more advanced and reliable sensors are available that measure water quality parameters such as temperature, oxygen, nitrogen, salinity, and turbidity. With the development of computer vision technology, studies have increased using cameras and imaging-based systems, along with algorithms to extract and analyze the data, as a non-invasive, inexpensive way to track and monitor fish in aquaculture (Zion, 2012; Qian et al., 2016; ; ; Georgopoulou et al., 2021). Low-cost sensor systems and regression techniques have achieved 76-97% accuracy in measuring key water quality parameters such as temperature, dissolved oxygen, and pH in Asian seabass fisheries (Jais et al., 2024). Automated classification of shrimp health using image datasets has helped in early disease detection with deep neural networks (Islam et al., 2025; Zakaria et al., 2025). Improved feeding precision demonstrated by YOLOv8-based computer vision models in tilapia farming has enabled biomass estimation with 94% accuracy and combined with IoT sensors optimized feed use (Hossam et al., 2024). Predictive modeling integrating GIS and machine learning has further aided disease forecasting in shrimp farms, facilitating preventative management of diseases (Khiem et al., 2022). Despite challenges related to sensor reliance, investment costs, and data interoperability, evidence confirms the important role of precision aquaculture in reducing feed costs, preventing disease outbreaks, and promoting environmental sustainability (Su et al., 2020; Rastegari et al., 2023; Future Market Insights, 2025).
Figure 2
4.6 Genetic improvement and biotechnology
Biotechnology and genetic enhancement are increasingly being used to increase sustainability, resilience, and productivity in aquaculture. In species such as carp, tilapia, and salmon selective breeding techniques improving feed efficiency, growth performance and disease resistant (Gedrem and Robinson, 2014). To address production problems and accelerate genetic gain, genomic tools such as marker-assisted and genomic selection are increasingly being used (Houston et al., 2020). In addition to genetic improvement, health management techniques such as probiotics, immunostimulants, and oral vaccinations have helped reduce antibiotic dependence and mitigate the impact of bacterial infections in farmed fish (Farooqi and Qureshi, 2018). Additionally, CRISPR-Cas9 and other gene-editing technologies are becoming effective tools for targeting specific traits (Table 3). Taken together, these developments reduce disease risk, enhance production efficiency, and promote product quality.
Table 3
| Common name | Scientific name | Trait/purpose | Target gene’s | Country of development | References |
|---|---|---|---|---|---|
| Channel catfish | Ictalurus punctatus | Disease resistance and enhanced growth | myostatin (MSTN), LH, GnRH | USA | Khalil et al. (2017); |
| Nile tilapia | Oreochromis niloticus | Growth enhancement, sterility, disease resistance | MSTN, GnRH3, DMRT1 | China | Li et al. (2014) |
| Common carp | Cyprinus carpio | Growth and knockout enhancement for functional research | MSTN, immune genes | China | Zhong et al. (2016) |
| Atlantic salmon | Salmo salar | Sterility induction to prevent interbreeding | GnRH | Norway | Raudstein et al. (2023) |
| Grass carp | Ctenopharyngodon idella | Viral disease resistance | gcvrvp4 receptor genes | China | Ma et al. (2018) |
| Japanese medaka | Oryzias latipes | Sterility, functional gene studies | Various genes | Japan | Watakabe et al. (2018) |
| Zebrafish | Danio rerio | Disease models, transgenics and gene function | Multiple genes | USA, China, Japan | Varshney et al. (2015); Liu et al. (2018); Bai et al. (2020); Yin et al. (2021) |
| Red sea bream | Pagrus major | Increased muscle growth | MSTN | Japan | Washio et al. (2021) |
| Pacific bluefin tuna | Thunnus orientalis | Aquaculture fertility control | Gonadal development genes | Japan | Hayashida et al. (2023); |
| Channel catfish | Ictalurus punctatus | Resistance to Ictalurid herpesvirus | Viral receptor genes | USA | Elaswad et al. (2018) |
| Large yellow croaker | Larimichthys crocea | Growth enhancement through MSTN-B knockout | mstn-b | China | Yan et al. (2022) |
Fish species developed using CRISPR/Cas9 genome editing.
4.7 Alternative sustainable feeds
One of the most significant developments in aquaculture is the use of alternative sustainable feeds, which address the financial and environmental problems posed by excessive reliance on fishmeal and fish oil. Aquatic feeds are being produced using sustainable feed ingredients such as single-cell proteins, microalgae, yeast, insect meal and agricultural byproducts. By reducing reliance on wild fisheries, these alternatives save marine resources and help conserve biodiversity (Turchini et al., 2019). In addition to promoting a circular bioeconomy by valuing food and agricultural waste streams, they also reduce the environmental impact of aquatic feed production by using less land and emitting fewer greenhouse gases than conventional ingredients (Henry et al., 2015). Some of these ingredients have already been incorporated into practical diets by commercial aquatic feed enterprises. For example, salmonid and shrimp aquaculture has effectively utilized black soldier fly larva meal as a protein source, demonstrating growth rates comparable to traditional fishmeal-based diets (Nogales-Merida et al., 2019). Similarly, microalgae-derived oils rich in omega-3 fatty acids have been incorporated into salmon diets, successfully replacing fish oil without compromising fillet health or quality (Zatti et al., 2023). Single-cell proteins derived from bacteria and yeast are also becoming increasingly popular as scalable solutions because they contain high protein content and useful bioactive that support immune and gut health (Koukoumaki et al., 2024). When these sustainable diet options are used together, they reduce environmental pressure, improve resource efficiency, and promote the long-term expansion of the aquaculture industry (Figure 3).
Figure 3
4.7.1 Probiotics and prebiotics application
Probiotics and prebiotics are rapidly gaining recognition as sustainable alternative feed additives in aquaculture, as they enhance growth performance, feed utilization, immune response, disease resistance and reduce reliance on antibiotics and chemotherapy (Dawood et al., 2018). Probiotics are defined as live, beneficial microorganisms that, when administered in adequate amounts, confer a health benefit to the host, while prebiotics are non-digestible feed ingredients that selectively stimulate the growth and activity of beneficial gut microbiota (Gatesoupe, 1999; Ringø et al., 2010). Probiotic microorganisms such as Bacillus sp., Lactobacillus sp., Pseudomonas sp., Enterococcus sp., and Saccharomyces sp. are commonly used in aquaculture. These microorganisms have been shown to enhance digestive enzyme activity, inhibit pathogenic bacteria, and improve water quality by breaking down organic matter (Verschuere et al., 2000; Nayak, 2010). To improve nutrient absorption and immune modulation, prebiotics such as mannan oligosaccharides (MOS), fructooligosaccharides (FOS), galactooligosaccharides (GOS), and inulin are incorporated into aquafeeds to support beneficial microbial populations in the gastrointestinal tract (Ringø et al., 2010; Dawood et al., 2018). In fish and shrimp farming systems, the combined use of probiotics and prebiotics often referred to as synbiotics has demonstrated synergistic effects on growth performance, stress tolerance, and resistance to bacterial infections (Gibson and Roberfroid, 1995; Hoseinifar et al., 2018). Probiotics and prebiotics are interesting alternative feed solutions for sustainable aquaculture development because they are environmentally friendly and compatible with intensive systems such as RAS and biofloc technology.
4.8 Limitations of advanced technologies
Despite the sustainability benefits of modern aquaculture technologies, they also have several drawbacks. Recirculating aquaculture systems require initial high capital investment, trained labor, and a continuous energy supply for aeration and bio-filtration to maintain stocks (
5 Future perspectives
The combination of pioneering technologies, biotechnology, and ecologically conscious methods will influence the direction of sustainable aquaculture production. As artificial intelligence (AI), machine learning, the Internet of Things (IoT), and robotics become more widely used for enabling farms to function as fully data-driven systems. According to Føre et al. (2018), these technologies will improve real-time decision-making, mitigate production risks, boost efficiency, and reduce environmental impacts. In developing countries, due to higher costs and management limitations, AI-based monitoring, automation, and precision management can be adopted in a phased and context-specific manner. Without the need for fully automated infrastructure, smart technologies can be gradually integrated using affordable digital tools such as mobile-based water quality monitoring, cloud-enabled decision support systems, and simple sensor networks (Joffre et al., 2018). Cluster-based aquaculture systems and cooperative farming models can improve access to cutting-edge technology and share facilities to reduce the financial burden of an individual (Kassam et al., 2011; Troell et al., 2014). In developing countries, the promotion and adoption of innovative technologies requires strengthening public-private partnerships, capacity building through farmer training programs and extension services (Nouatin et al., 2025). Furthermore, government subsidies and microcredit programs can ease initial investments and mitigate the financial risks associated with technology adoption (Tietze and Villareal, 2003). Combining contemporary digital technologies with locally available materials, renewable energy sources, and traditional farming knowledge can further enhance affordability and long-term sustainability. Therefore, pioneering technologies like artificial intelligence (AI), when implemented through scalable, inclusive, and policy-supported frameworks, can significantly boost aquaculture production and resilience in developing countries without exacerbating socio-economic inequalities. The use of genomic selection and CRISPR-Cas9 gene editing will be crucial in creating disease-resistant and fast-transmitting strains, and genetic improvement and biotechnology will also continue to advance. In addition to increasing production efficiency, these technologies will reduce dependence on chemical inputs and antibiotics, improving food safety and animal welfare (Houston et al., 2020; Zhu et al., 2024). Their successful implementation will require a robust regulatory framework, ethical governance, and public acceptance, as well as continuous research to mitigate off-target effects and ecological risks. Aquaculture is striving to reduce its reliance on fish oil and fishmeal by exploring alternative, sustainable sources. Improving processing technologies and nutritional value can enhance the development and utilization of insect-based feeds, single-cell proteins, and algal oils, thereby lowering feed costs, increasing sustainability, and promoting the principles of a circular bioeconomy (Henry et al., 2015; Zatti et al., 2023). Climate-friendly aquaculture techniques, such as recirculating aquaculture systems (RAS) can significantly reduce operating costs and carbon footprint by integrating renewable energy sources such as solar and wind power with energy-efficient pumps and intelligent sensor-based monitoring. Promising approaches for nutrient removal and reducing waste discharge include the use of low-energy denitrification units, microbial consortia engineering, and nature-based biofilters (Martins et al., 2010; Van Kessel et al., 2015). Future sustainable approaches for biofloc technology (BFT) include selective microbial control, probiotic-assisted floc management, and the use of locally available agro-industrial by-products as carbon sources to maintain stable C:N ratios and prevent disease outbreaks (
6 Conclusion
In conclusion, sustainable aquaculture is a continuous process that requires a combination of environmental protection, technological innovation, and socio-economic inclusiveness. Innovative technologies such as aquaponics, precision aquaculture, integrated multi-trophic aquaculture (IMTA), biofloc technology (BFT), recirculating aquaculture systems (RAS), and alternative sustainable diets have shown promising results in increasing production, reducing environmental impacts, and improving resource efficiency. The future success of aquaculture will depend on climate-resilient practices, efficient disease management, genetic enhancement and circular bioeconomy initiatives. The strong government support, capacity building and appropriate access to technologies for aquaculture may continue to produce nutritious food, generate livelihoods, and contribute to global food security and maintaining ecological balance for future generations.
Statements
Data availability statement
The original contributions presented in the study are included in the article/supplementary material. Further inquiries can be directed to the corresponding authors.
Author contributions
DR: Writing – review & editing, Writing – original draft. SS: Writing – review & editing, Supervision, Conceptualization. AS: Conceptualization, Writing – original draft. VM: Writing – review & editing. CS: Writing – review & editing. DK: Writing – review & editing.
Funding
The author(s) declared that financial support was not received for this work and/or its publication.
Acknowledgments
The authors thank the previous researchers whose work contributed to the preparation of this publication. We also thank our advisor and teachers for their support and encouragement during the writing process.
Conflict of interest
The author(s) declared that this work was conducted in the absence of any commercial or financial relationships that could be construed as a potential conflict of interest.
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Summary
Keywords
aquaculture, circular bioeconomy, sustainability challenges, sustainable future, technological advances
Citation
Ranjan D, Singh S, Singh A, Misra VK, Singh CP and Kumar D (2026) Recent advancements in sustainable aquaculture: innovative techniques and future prospects. Front. Aquac. 5:1770106. doi: 10.3389/faquc.2026.1770106
Received
17 December 2025
Revised
12 January 2026
Accepted
15 January 2026
Published
18 February 2026
Volume
5 - 2026
Edited by
Bijay Kumar Behera, Central Inland Fisheries Research Institute (ICAR), India
Reviewed by
Ravi Kumar Goswami, University of Delhi, India
Dr. Cherita Devi Khangembam, Allahabad University, India
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© 2026 Ranjan, Singh, Singh, Misra, Singh and Kumar.
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*Correspondence: Shashank Singh, ssingh.aqc.cof@nduat.org; drssaqua@gmail.com; C. P. Singh, cpsingh.frm.cof@nduat.org
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