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Fish farming
Fish farming
from Wikipedia
A fish farm on the coast of Euboea island, in South Euboean Gulf, Greece

Fish farming or pisciculture involves commercial breeding of fish, most often for food, in fish tanks or artificial enclosures such as fish ponds. It is a particular type of aquaculture, which is the controlled cultivation and harvesting of aquatic animals such as fish, crustaceans, molluscs and so on, in natural or pseudo-natural environments. A facility that releases juvenile fish into the wild for recreational fishing or to supplement a species' natural numbers is generally referred to as a fish hatchery. Worldwide, the most important fish species produced in fish farming are carp, catfish, salmon and tilapia.[1]

Global demand is increasing for dietary fish protein, which has resulted in widespread overfishing in wild fisheries, resulting in significant decrease in fish stocks and even complete depletion in some regions. Fish farming allows establishment of artificial fish colonies that are provided with sufficient feeding, protection from natural predators and competitive threats, access to veterinarian service, and easier harvesting when needed, while being separate from and thus do not usually impact the sustainable yields of wild fish populations. While fish farming is practised worldwide, China alone provides 62% of the world's farmed fish production.[2] As of 2016, more than 50% of seafood was produced by aquaculture.[3] In the last three decades, aquaculture has been the main driver of the increase in fisheries and aquaculture production, with an average growth of 5.3 percent per year between 2000 and 2018, rising from 32.4 to 82.1 million tonnes.[4][5]

Farming carnivorous fish such as salmon, however, does not always reduce pressure on wild fisheries, since such farmed fish are usually fed fishmeal and fish oil extracted from wild forage fish. Fish farming is a source of water pollution, and diseases and parasites can spread to wild populations.[6] There are also fish welfare concerns related to overcrowding, which causes stress, injuries, and disease.[7]

Although fish farming for food is the most widespread, another major fish farming industry provides living fish for the aquarium trade. The vast majority of freshwater fish in the aquarium trade originate from farms in Eastern and Southern Asia, eastern Europe, Florida and South America that use either indoor tank systems or outdoor pond systems, while farming of fish for the marine aquarium trade happens at a much smaller scale.[8] In 2022 24% of fishers and fish farmers and 62% of workers in post-harvest sector were women.[9][10]

Global capture fishery yield in red and aquaculture production in orange, 2021.[11]

Major species

[edit]
Top 15 cultured fish species by weight, according to FAO statistics for 2013 [1]
Species Environment Tonnage
(millions)
Value
(US$ billions)
Grass carp Freshwater 5.23 6.69
Silver carp Freshwater 4.59 6.13
Common carp Freshwater 3.76 5.19
Nile tilapia Freshwater 3.26 5.39
Bighead carp Freshwater 2.90 3.72
Catla (Indian carp) Freshwater 2.76 5.49
Crucian carp Freshwater 2.45 2.67
Atlantic salmon Marine 2.07 10.10
Roho labeo Freshwater 1.57 2.54
Milkfish Marine 0.94 1.71
Rainbow trout
  • Freshwater
  • Brackish
  • Marine
0.88 3.80
Wuchang bream Freshwater 0.71 1.16
Black carp Freshwater 0.50 1.15
Northern snakehead Freshwater 0.48 0.59
Amur catfish Freshwater 0.41 0.55

Categories

[edit]

Aquaculture makes use of local photosynthetic production (extensive) or fish that are fed with external food supply (intensive).

Extensive aquaculture

[edit]

Extensive aquaculture relies on small or no external inputs of labour and feed, compared to what is being produced. The fish are usually kept in natural bodies of water or artificial ponds and are left to reproduce and feed without much intervention, surviving on the natural resources of where they are kept.[12][13] This sort of aquaculture is the oldest, and most likely originated in China around 4000 years ago.[14]

Due to this type of aquaculture usually requiring large bodies of water, lakes and ponds may be converted to fish farms. This can pose a threat to local environments, both in terms of the habitats of local species being destroyed, and invasive species being introduced.[15]

Intensive aquaculture

[edit]
Optimal water parameters for cold- and warm-water fish in intensive aquaculture[16]
Parameter Optimal value
Acidity pH 6–9
Arsenic < 440 μg/L
Alkalinity > 20 mg/L (as CaCO3)
Aluminium < 0.075 mg/L
Ammonia (non-ionized) < 0.02 mg/L
Cadmium
Calcium > 5 mg/L
Carbon dioxide < 5–10 mg/L
Chloride > 4.0 mg/L
Chlorine < 0.003 mg/L
Copper
  • < 0.0006 mg/L in soft water
  • < 0.03 mg/L in hard water
Gas supersaturation
  • < 100% total gas pressure
  • < 103% for salmonid eggs/fry
  • < 102% for lake trout
Hydrogen sulfide < 0.003 mg/L
Iron < 0.1 mg/L
Lead < 0.02 mg/L
Mercury < 0.0002 mg/L
Nitrate < 1.0 mg/L
Nitrite < 0.1 mg/L
Oxygen
  • 6 mg/L for coldwater fish
  • 4 mg/L for warmwater fish
Selenium < 0.01 mg/L
Total dissolved solids < 200 mg/L
Total suspended solids < 80 NTU over ambient levels
Zinc < 0.005 mg/L

In these kinds of systems fish production per unit of surface can be increased at will, as long as sufficient oxygen, fresh water and food are provided. Because of the requirement of sufficient fresh water, a massive water purification system must be integrated in the fish farm. One way to achieve this is to combine hydroponic horticulture and water treatment, see below. The exception to this rule are cages which are placed in a river or sea, which supplements the fish crop with sufficient oxygenated water. Some environmentalists object to this practice.

Expressing eggs from a female rainbow trout

The cost of inputs per unit of fish weight is higher than in extensive farming, especially because of the high cost of fish feed. It must contain a much higher level of protein (up to 60%) than cattle feed and a balanced amino acid composition, as well. These higher protein-level requirements are a consequence of the higher feed efficiency of aquatic animals (higher feed conversion ratio [FCR], that is, kg of feed per kg of animal produced). Fish such as salmon have an FCR around 1.1 kg of feed per kg of salmon[17] whereas chickens are in the 2.5 kg of feed per kg of chicken range. Fish do not use energy to keep warm, eliminating some carbohydrates and fats in the diet, required to provide this energy. This may be offset, though, by the lower land costs and the higher production which can be obtained due to the high level of input control.

Aeration of the water is essential, as fish need a sufficient oxygen level for growth. This is achieved by bubbling, cascade flow, or aqueous oxygen. Catfish in genus Clarias can breathe atmospheric air and can tolerate much higher levels of pollutants than trout or salmon, which makes aeration and water purification less necessary and makes Clarias species especially suited for intensive fish production. In some Clarias farms, about 10% of the water volume can consist of fish biomass.

The risk of infections by parasites such as fish lice, fungi (Saprolegnia spp.), intestinal worms (such as nematodes or trematodes), bacteria (e.g., Yersinia spp., Pseudomonas spp.), and protozoa (such as dinoflagellates) is similar to that in animal husbandry, especially at high population densities. However, animal husbandry is a larger and more technologically mature area of human agriculture and has developed better solutions to pathogen problems. Intensive aquaculture has to provide adequate water quality (oxygen, ammonia, nitrite, etc.) levels to minimize stress on the fish. This requirement makes control of the pathogen problem more difficult. Intensive aquaculture requires tight monitoring and a high level of expertise of the fish farmer.

Controlling roes manually

Very-high-intensity recycle aquaculture systems (RAS, also Recirculating Aquaculture Systems), where all the production parameters are controlled, are being used for high-value species. By recycling water, little is used per unit of production. However, the process has high capital and operating costs. The higher cost structures mean that RAS is economical only for high-value products, such as broodstock for egg production, fingerlings for net pen aquaculture operations, sturgeon production, research animals, and some special niche markets such as live fish.[18][19]

Raising ornamental coldwater fish (goldfish or koi), although theoretically much more profitable due to the higher income per weight of fish produced, has been successfully carried out only in the 21st century. The increased incidences of dangerous viral diseases of koi carp, together with the high value of the fish, has led to initiatives in closed-system koi breeding and growing in a number of countries. Today, a few commercially successful intensive koi-growing facilities are operating in the UK, Germany, and Israel.

Some producers have adapted their intensive systems in an effort to provide consumers with fish that do not carry dormant forms of viruses and diseases.

In 2016, juvenile Nile tilapia were given a food containing dried Schizochytrium in place of fish oil. When compared to a control group raised on regular food, they exhibited higher weight gain and better food-to-growth conversion, plus their flesh was higher in healthy omega-3 fatty acids.[20][21]

Fish farms

[edit]

Within intensive and extensive aquaculture methods, numerous specific types of fish farms are used; each has benefits and applications unique to its design.

Cage system

[edit]
Giant gourami is often raised in cages in central Thailand.

Fish cages are placed in lakes, bayous, ponds, rivers, or oceans to contain and protect fish until they can be harvested.[22] The method is also called "off-shore cultivation"[23] when the cages are placed in the sea. They can be constructed of a wide variety of components. Fish are stocked in cages, artificially fed, and harvested when they reach market size. A few advantages of fish farming with cages are that many types of waters can be used (rivers, lakes, filled quarries, etc.), many types of fish can be raised, and fish farming can co-exist with sport fishing and other water uses.[22]

Fish cages in Lake Victoria, Uganda

Cage farming of fishes in open seas is also gaining in popularity. Given concerns of disease, poaching, poor water quality, etc., generally pond systems are considered simpler to start and easier to manage. Also, the past occurrences of cage-failures leading to escapes, have raised concern regarding the culture of non-native fish species in dam or open-water cages. On August 22, 2017, there was a massive failure of such cages at a commercial fishery in Washington state in Puget Sound, leading to release of nearly 300,000 Atlantic salmon in non-native waters. This is believed to risk endangering the native Pacific salmon species.[24]

Marine Scotland has kept records of caged fish escapes since 1999. They have recorded 357 fish escape incidents with 3,795,206 fish escaping into fresh and salt water. One company, Dawnfresh Farming Limited, has been responsible for 40 incidents and the escape of 152,790 rainbow trout into freshwater lochs.[25]

Fish cages in Castro, Chile

Though the cage-industry has made numerous technological advances in cage construction in recent years, the risk of damage and escape due to storms is always a concern.[22]

Semi-submersible marine technology is beginning to impact fish farming. In 2018, 1.5 million salmon are in the middle of a year-long trial at Ocean Farm 1 off the coast of Norway. The semi-submersible US$300 million project is the world's first deep-sea aquaculture project, and includes 61-meter (200 ft)-high by 91-meter (300 ft)-diameter pen made from a series of mesh-wire frames and nets. It is designed to disperse wastes better than more conventional farms in sheltered coastal waters, therefore supporting higher fish packing density.[26]

In Maritime Southeast Asia, traditional fish cages built around an offshore wooden platform are generally called kelong. They are usually used to temporarily keep caught fish until sold or cooked, but some are used for fish farming.[27]

Copper-alloy nets

[edit]

Recently, copper alloys have become important netting materials in aquaculture. Copper alloys are antimicrobial, that is, they destroy bacteria, viruses, fungi, algae, and other microbes. In the marine environment, the antimicrobial/algaecidal properties of copper alloys prevent biofouling, which can briefly be described as the undesirable accumulation, adhesion, and growth of microorganisms, plants, algae, tube worms, barnacles, mollusks, and other organisms.[28]

The resistance of organism growth on copper alloy nets also provides a cleaner and healthier environment for farmed fish to grow and thrive. Traditional netting involves regular and labor-intensive cleaning. In addition to its antifouling benefits, copper netting has strong structural and corrosion-resistant properties in marine environments.[29]

Copper-zinc brass alloys are deployed in commercial-scale aquaculture operations in Asia, South America, and USA (Hawaii). Extensive research, including demonstrations and trials, are being implemented on two other copper alloys: copper-nickel and copper-silicon. Each of these alloy types has an inherent ability to reduce biofouling, cage waste, disease, and the need for antibiotics, while simultaneously maintaining water circulation and oxygen requirements. Other types of copper alloys are also being considered for research and development in aquaculture operations.[30]

Fish pens

[edit]
Square stick and net enclosures in a shallow river bed
Small fish pens in the Bued River in Pangasinan, Philippines
Patchwork of very large fish pens in Laguna de Bay, Philippines

In the Philippines, traditional enclosures used to farm fish directly on shallow bodies of water are called fish pens. They differ from fish cages in that fish pens are not floating and do not have an artificial bottom. Instead, the seabed, riverbed, or the lakebed provides the floor of the enclosure. They are usually much larger than fish cages and come in various shapes like circles, squares, or rectangles. The fences that enclose the fish pen area are made from bamboo or wooden poles, netting, and ropes. The poles are sunk into the substrate at depths of 15 to 30 centimetres (0.49 to 0.98 ft). Fish pens often have a hut raised on stilts nearby that function as a warehouse and accommodations for caretakers that may be necessary to guard against poachers.[31]

Fish pens commonly cover large areas of bodies of water (both freshwater and marine) in the Philippines, similar to farm plots. Licenses are required to operate fish pens, and operators are usually granted a limited area for fish farming.[32]

Different pen sizes are required for different species of fish.[33] Freshwater fish pens are traditionally used to farm milkfish (Chanos chanos) using wild-caught fingerlings, with much higher survival and harvesting yields than conventional fish pond farming. They can also be used to farm other food fish like the Nile tilapia (Oreochromis niloticus), but in general, fish cages are preferred for smaller fish species instead.[31][32] Marine fish pens are commonly used to farm wild-caught juvenile groupers.[33]

Due to their open-water nature and their typically large areas, supplemental feeding is typically not required for fish pens (unlike in fish cages and fish ponds), though some operators may provide additional feed for fingerlings like bread crumbs, fish meal, egg yolk, or plant leaves.[31]

Fish pens are cheap and generate high profit margins, but they are more vulnerable to typhoons, floods, water pollution (including algal blooms and oxygen depletion), and fry shortage.[34][31]

Open net pen system

[edit]

The open net pens system is a method that takes place in natural waters, such as rivers, lakes, near the coast or offshore. The breeders rear the fish in large cages floating in the water.[35] The fish are living in natural water but are isolated with a net. Because the only barrier separating the fish from the surrounding environment is a net, this allows the water to flow from the 'natural' surrounding through the fish farms.

The site of the fish farm is crucial for the farm to be a success or not. Before any fish farm is settled, it is highly recommended to be selective with the site location of the farm. The site must be examined on some essential elements. Important conditions on the location are:[36]

  1. A good interchange of water and also a high replacement of bottom water.
  2. At all depths should be a good current condition. This is necessary because the organic particles should be able to be carried away using the current.
  3. A gravel and sand bottom are qualified for fish farming, although bottoms with silt and mud are not qualified. These should be avoided.
  4. A net should be at least 10 metres (33 ft) or more above the bottom, so depth is important.

Despite these important site conditions, the open net pen method was very popular in Norway and China. This is because of the cost friendliness and efficiency of this method.[37]

Negative external effects

[edit]

Because of the ocean's water flow and other reasons, open net pen culture is seen as a high-risk method for the environment.[38] The flow allows chemicals, parasites, waste and diseases to spread in the enclosed environment, and this is not beneficial for the natural environment. Another negative consequence is the high escape rate of the cultured fish from these open net pens. These escaped fish also pose a high risk to the surrounding ecosystems.

The amount of organic waste produced by fish farms is also alarming. A salmon farm in Scotland, for instance, is estimated to produce as much organic waste as equivalent to a town of people between 10,000 and 20,000 people each year.[39]

Today 50% of the world's seafood is farm-raised.[40]

Irrigation ditch or pond systems

[edit]
A row of square artificial ponds, with trees on either side
These fish-farming ponds were created as a cooperative project in a rural village in the Congo.

These use irrigation ditches or farm ponds to raise fish. The basic requirement is to have a ditch or pond that retains water, possibly with an above-ground irrigation system (many irrigation systems use buried pipes with headers).[41]

Using this method, water allotments can be stored in ponds or ditches, usually lined with bentonite clay. In small systems, the fish are often fed commercial fish food, and their waste products can help fertilize the fields. In larger ponds, the pond grows water plants and algae as fish food. Some of the most successful ponds grow introduced strains of plants, as well as introduced strains of fish.[42]

Control of water quality is crucial. Fertilizing, clarifying, and pH control of the water can increase yields substantially, as long as eutrophication is prevented and oxygen levels stay high. Yields can be low if the fish grow ill from electrolyte stress.[43]

Composite fish culture

[edit]

The composite fish culture system is a technology developed in India by the Indian Council of Agricultural Research in the 1970s. In this system, of both local and imported fish, a combination of five or six fish species is used in a single fish pond. These species are selected so that they do not compete for food among them by having different types of food habitats.[44][45] As a result, the food available in all the parts of the pond is used. Fish used in this system include catla and silver carp (surface feeders), rohu (a column feeder), and mrigal and common carp (bottom feeders). Other fish also feed on the excreta of the common carp, and this helps contribute to the efficiency of the system which in optimal conditions produces 3000–6000 kg of fish per hectare per year.[46]

One problem with such composite fish culture is that many of these fish breed only during monsoon. Even if fish are collected from the wild, they can be mixed with other species, as well. Thus, a major problem in fish farming is the lack of availability of good-quality stock. To overcome this problem, ways have now been worked out to breed these fish in ponds using hormonal stimulation. This has ensured the supply of pure fish stock in desired quantities.[47]

Integrated recycling systems

[edit]
Aerators in a fish farm (Ararat plain, Armenia)

One of the largest problems with freshwater pisciculture is that it can use a million gallons of water per acre (about 1 m3 of water per m2) each year. Extended water purification systems allow for the reuse (recycling) of local water.

The largest-scale pure fish farms use a system derived (admittedly much refined) from the New Alchemy Institute in the 1970s. Basically, large plastic fish tanks are placed in a greenhouse. A hydroponic bed is placed near, above or between them. When tilapia are raised in the tanks, they are able to eat algae, which naturally grow in the tanks when the tanks are properly fertilized.[48]

The tank water is slowly circulated to the hydroponic beds, where the tilapia waste feeds commercial plant crops. Carefully cultured microorganisms in the hydroponic bed convert ammonia to nitrates, and the plants are fertilized by the nitrates and phosphates.Other wastes are strained out by the hydroponic media, which double as an aerated pebble-bed filter.[49]

This system, properly tuned, produces more edible protein per unit area than any other. A wide variety of plants can grow well in the hydroponic beds. Most growers concentrate on herbs (e.g. parsley and basil), which command premium prices in small quantities all year long. The most common customers are restaurant wholesalers.[50]

Since the system lives in a greenhouse, it adapts to almost all temperate climates, and may also adapt to tropical climates. The main environmental impact is discharge of water that must be salted to maintain the fishes' electrolyte balance. Current growers use a variety of proprietary tricks to keep fish healthy, reducing their expenses for salt and wastewater discharge permits. Some veterinary authorities speculate that ultraviolet ozone disinfectant systems (widely used for ornamental fish) may play a prominent part in keeping the tilapia healthy with recirculated water.[citation needed]

A number of large, well-capitalized ventures in this area have failed. Managing both the biology and markets is complicated. One future development is the combination of integrated recycling systems with urban farming as tried in Sweden by the Greenfish Initiative.[51][52]

Classic fry farming

[edit]

This is also called a "flow through system".[53] Trout and other sport fish are often raised from eggs to fry or fingerlings and then trucked to streams and released. Normally, the fry are raised in long, shallow, concrete tanks, fed with fresh stream water. The fry receive commercial fish food in pellets. While not as efficient as the New Alchemists' method, it is also far simpler and has been used for many years to stock streams with sport fish. European eel (Anguilla anguilla) aquaculturalists procure a limited supply of glass eels, juvenile stages of the European eel which swim north from the Sargasso Sea breeding grounds, for their farms. The European eel is threatened with extinction because of the excessive catch of glass eels by Spanish fishermen and overfishing of adult eels in, e.g., the Dutch IJsselmeer. Although European eel larvae can survive for several weeks, the full life cycle has not yet been achieved in captivity.[54]

Issues

[edit]
Mean eutrophying emissions (water pollution)
of different foods per 100g of protein[55]
Food types Eutrophying emissions (g PO43-eq per 100g protein)
Beef
365.3
Farmed fish
235.1
Farmed crustaceans
227.2
Cheese
98.4
Lamb and mutton
97.1
Pork
76.4
Poultry
48.7
Eggs
21.8
Groundnuts
14.1
Peas
7.5
Tofu
6.2
Mean greenhouse gas emissions for different food types[56]
Food types Greenhouse gas emissions (g CO2-Ceq per g protein)
Ruminant meat
62
Recirculating aquaculture
30
Trawling Fishery
26
Non-recirculating aquaculture
12
Pork
10
Poultry
10
Dairy
9.1
Non-trawling fishery
8.6
Eggs
6.8
Starchy roots
1.7
Wheat
1.2
Maize
1.2
Legumes
0.25

Welfare

[edit]

There is a growing consensus that fish can feel pain.[57][58] Despite the vast number of fish consumed, fish welfare has historically received little attention.[7]

Farmed fish are usually raised in overcrowded environments, making them susceptible to stress, injuries, aggression and diseases. These conditions prevent them from engaging in natural behaviors such as nesting or migration. Overcrowding often leads to poor water quality due to fish waste and antibiotics use. Sea lice infestations are common and can cause painful lesions, but are typically treated with harsh chemicals. Additionally, fish are genetically engineered to grow larger and faster, leading to health problems such as cataracts and abnormal heart shapes.[7]

Feeding

[edit]
Mean acidifying emissions (air pollution)
of different foods per 100g of protein[55]
Food types Acidifying emissions (g SO2eq per 100g protein)
Beef
343.6
Cheese
165.5
Pork
142.7
Lamb and mutton
139.0
Farmed crustaceans
133.1
Poultry
102.4
Farmed fish
65.9
Eggs
53.7
Groundnuts
22.6
Peas
8.5
Tofu
6.7

The issue of feeds in fish farming has been a controversial one. Many cultured fishes (tilapia, carp, catfish, many others) can be raised on a strictly herbivorous diet. Top-level carnivores (most salmonidae species in particular) on the other hand, depend on fish feed, of which a large portion is usually derived from wild-caught fish (anchovies, menhaden, etc.). Vegetable-derived proteins have successfully replaced fish meal in feeds for carnivorous fishes, but vegetable-derived oils have not successfully been incorporated into the diets of carnivores. Research is underway to try to change this, such that even salmon and other carnivores could be successfully fed with vegetable products. The F3 Challenge (Fish-Free Feed Challenge),[59] as explained by a report from Wired in February 2017, "is a race to sell 100,000 metric tons of fish food, without the fish. Earlier this month, start-ups from places like Pakistan, China, and Belgium joined their American competition at the Google headquarters in Mountain View, California, showing off feed made from seaweed extracts, yeast, and algae grown in bioreactors."[60]

Not only do the feeds for carnivorous fish, like certain salmon species, remain controversial due to the containment of wild caught fish like anchovies, but they are not helping the health of the fish, as is the case in Norway. Between 2003 and 2007, Aldrin et al. examined three infectious diseases in Norwegian salmon fish farms—heart and skeletal muscle inflammation, pancreas disease, and infectious salmon anemia.[61]

In 2014, Martinez-Rubio et al. conducted a study in which cardiomyopathy syndrome (CMS), a severe cardiac disease in Atlantic salmon (Salmo salar), was investigated pertaining the effects of functional feeds with reduced lipid content and increased eicosapentaenoic acid levels in controlling CMS in salmon after infection with piscine myocarditis virus (PMCV). Functional feeds are defined as high-quality feeds that beyond purposes of nutrition, they are formulated with health promoting features that could be beneficial in supporting disease resistance, such as CMS.[62]

Choosing a clinical nutrition approach using functional feeds could potentially move away from chemotherapeutic and antibiotic treatments, which could lower the costs of disease treatment and management in fish farms. In this investigation three fishmeal-based diets were served—one made of 31% lipid and the other two made of 18% lipid (one contained fishmeal and the other krill meal. Results demonstrated a significant difference in the immune and inflammatory responses and pathology in heart tissue as the fish were infected with PMCV. Fish fed with functional feeds with low lipid content demonstrated milder and delayed inflammatory response and therefore, less severe heart lesions at earlier and later stages after PMCV infection.[62]

Stocking density

[edit]

Secondly, farmed fish are kept in concentrations never seen in the wild (e.g. 50,000 fish in a 2-acre (8,100 m2) area.[63]). However, fish tend also to be animals that aggregate into large schools at high density. Most successful aquaculture species are schooling species, which do not have social problems at high density. Aquaculturists feel that operating a rearing system above its design capacity or above the social density limit of the fish will result in decreased growth rate and increased feed conversion ratio (kg dry feed/kg of fish produced), which results in increased cost and risk of health problems along with a decrease in profits. Stressing the animals is not desirable, but the concept of and measurement of stress must be viewed from the perspective of the animal using the scientific method.[64]

Parasites and disease

[edit]

Sea lice, particularly Lepeophtheirus salmonis and various Caligus species, including C. clemensi and C. rogercresseyi, can cause deadly infestations of both farm-grown and wild salmon.[65][66] Sea lice are ectoparasites which feed on mucus, blood, and skin, and migrate and latch onto the skin of wild salmon during free-swimming, planktonic nauplii and copepodid larval stages, which can persist for several days.[67][68][69] Large numbers of highly populated, open-net salmon farms can create exceptionally large concentrations of sea lice; when exposed in river estuaries containing large numbers of open-net farms, many young wild salmon are infected, and do not survive as a result.[70][71]

Adult salmon may survive otherwise critical numbers of sea lice, but small, thin-skinned juvenile salmon migrating to sea are highly vulnerable. On the Pacific coast of Canada, the louse-induced mortality of pink salmon in some regions is commonly over 80%.[72] In Scotland, official figures show that more than nine million fish were lost to disease, parasites, botched treatment attempts and other problems on fish farms between 2016 and 2019.[73] One of the treatments for parasite infestations involved bathing fish in hydrogen peroxide,[74] which can harm or kill farmed fish if they are in a weak condition or if the chemical concentration is too strong.

A 2008 meta-analysis of available data shows that salmon farming reduces the survival of associated wild salmon populations. This relationship has been shown to hold for Atlantic, steelhead, pink, chum, and coho salmon. The decrease in survival or abundance often exceeds 50%.[75]

Diseases and parasites are the most commonly cited reasons for such decreases. Some species of sea lice have been noted to target farmed coho and Atlantic salmon.[76] Such parasites have been shown to have an effect on nearby wild fish. One place that has garnered international media attention is British Columbia's Broughton Archipelago. There, juvenile wild salmon must "run a gauntlet" of large fish farms located off-shore near river outlets before making their way to sea. The farms allegedly cause such severe sea lice infestations that one study predicted in 2007 a 99% collapse in the wild salmon population by 2011.[77] This claim, however, has been criticized by numerous scientists who question the correlation between increased fish farming and increases in sea lice infestation among wild salmon.[78]

Because of parasite problems, some aquaculture operators frequently use strong antibiotic drugs to keep the fish alive, but many fish still die prematurely at rates up to 30%.[79] Additionally, other common drugs used in salmonid fish farms in North America and Europe include anesthetic, chemotherapeutic, and anthelmintic agents.[80] In some cases, these drugs have entered the environment.[81]

The residual presence of these drugs in human food products has become controversial. Use of antibiotics in food production is thought to increase the prevalence of antibiotic resistance in human diseases.[82] At some facilities, the use of antibiotic drugs in aquaculture has decreased considerably due to vaccinations and other techniques.[83] However, most fish-farming operations still use antibiotics, many of which escape into the surrounding environment.[84]

The lice and pathogen problems of the 1990s facilitated the development of current treatment methods for sea lice and pathogens, which reduced the stress from parasite/pathogen problems. However, being in an ocean environment, the transfer of disease organisms from the wild fish to the aquaculture fish is an ever-present risk.[85]

A North American lake trout fishing farm on Lake Titicaca near Copacabana, Bolivia. Since their introduction in the 1930s, trout have been an invasive species endangering the local fish population.[86]

Ecosystem impacts

[edit]

The large number of fish kept long-term in a single location contributes to habitat destruction of the nearby areas.[87] The high concentrations of fish produce a significant amount of condensed faeces, often contaminated with drugs, which again affects local waterways.

Aquaculture not only impacts the fish on the farm, but it also influences other species, which in return are attracted to or repelled by the farms.[88] Mobile fauna, such as crustaceans, fish, birds, and marine mammals, interact with the process of aquaculture, but the long-term or ecological effects as a result of these interactions is still unknown. Some of these fauna may be attracted or demonstrate repulsion.[88] The attraction/repulsion mechanism has various direct and indirect effects on wild organisms at individual and population levels. The interactions that wild organisms have with aquaculture may have implications on the management of fisheries species and the ecosystem in relation to how the fish farms are structured and organized.[88]

Siting

[edit]

If aquaculture farms are placed in an area with strong current, pollutants can be flushed out of the area fairly quickly.[89][90] This helps manage the pollution problem and also aids in overall fish growth. Concern remains that resultant bacterial growth fertilised by fish faeces strips the water of oxygen, reducing or killing off the local marine life. Once an area has been so contaminated, fish farms are typically moved to new, uncontaminated areas. This practice has angered nearby fishermen.[91]

Other potential problems faced by aquaculturists include the obtaining of various permits and water-use rights, profitability, concerns about invasive species and genetic engineering depending on what species are involved, and interaction with the United Nations Convention on the Law of the Sea.

Genetic engineering

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In regards to genetically engineered, farmed salmon, concern has been raised over their proven reproductive advantage and how it could potentially decimate local fish populations, if released into the wild. Biologist Rick Howard did a controlled laboratory study where wild fish and genetically engineered fish were allowed to breed.[92] In 1989, AquaBounty Technologies developed the AquAdvantage salmon. The concerns and critiques of cultivating this genetically engineered fish in aquaculture are that the fish will escape and interact with other fish ultimately leading to the reproduction with other fishes. However, the FDA, has determined that while net pens would not be the most appropriate to prevent escapes, raising the salmon in Panama waters would effectively prevent escape because the water conditions there would fail to support long-term survival of any escaped salmon.[93]

Another method of preventing Aqua Advantage fish from impacting the ecosystems in the case they escape suggested by the FDA was to create sterile triploid females. This way concerns on reproducing with other fishes would be out of the question.[93] The genetically engineered fish crowded out the wild fish in spawning beds, but the offspring were less likely to survive. The colorant used to make pen-raised salmon appear rosy like the wild fish has been linked with retinal problems in humans.[91]

Labeling

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In 2005, Alaska passed legislation requiring that any genetically altered fish sold in the state be labeled.[94] In 2006, a Consumer Reports investigation revealed that farm-raised salmon is frequently sold as wild.[95]

In 2008, the US National Organic Standards Board allowed farmed fish to be labeled as organic provided less than 25% of their feed came from wild fish. This decision was criticized by the advocacy group Food & Water Watch as "bending the rules" about organic labeling.[96] In the European Union, fish labeling as to species, method of production and origin has been required since 2002.[97]

Concerns continue over the labeling of salmon as farmed or wild-caught, as well as about the humane treatment of farmed fish. The Marine Stewardship Council has established an Eco label to distinguish between farmed and wild-caught salmon,[98] while the RSPCA has established the Freedom Food label to indicate humane treatment of farmed salmon, as well as other food products.[97]

Indoor fish farming

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Other treatments such as ultraviolet sterilization, ozonation, and oxygen injection are also used to maintain optimal water quality. Through this system, many of the environmental drawbacks of aquaculture are minimized including escaped fish, water usage, and the introduction of pollutants. The practices also increased feed-use efficiency growth by providing optimum water quality.[99]

One of the drawbacks to recirculating aquaculture systems is the need for periodic water exchanges. However, the rate of water exchange can be reduced through aquaponics, such as the incorporation of hydroponically grown plants[100] and denitrification.[101] Both methods reduce the amount of nitrate in the water, and can potentially eliminate the need for water exchanges, closing the aquaculture system from the environment. The amount of interaction between the aquaculture system and the environment can be measured through the cumulative feed burden (CFB kg/M3), which measures the amount of feed that goes into the RAS relative to the amount of water and waste discharged. The environmental impact of larger indoor fish farming system will be linked to the local infrastructure, and water supply. Areas which are more drought-prone, indoor fish farms might flow out wastewater for watering agricultural farms, reducing the water affliction.[102]

From 2011, a team from the University of Waterloo led by Tahbit Chowdhury and Gordon Graff examined vertical RAS aquaculture designs aimed at producing protein-rich fish species.[103][104] However, because of its high capital and operating costs, RAS has generally been restricted to practices such as broodstock maturation, larval rearing, fingerling production, research animal production, specific pathogen-free animal production, and caviar and ornamental fish production. As such, research and design work by Chowdhury and Graff remains difficult to implement. Although the use of RAS for other species is considered by many aquaculturalists to be currently impractical, some limited successful implementation of RAS has occurred with high-value product such as barramundi, sturgeon, and live tilapia in the US,[105][106][107][108][109] eels and catfish in the Netherlands, trout in Denmark[110] and salmon is planned in Scotland[111] and Canada.[112]

Slaughter methods

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Tanks saturated with carbon dioxide have been used to make fish unconscious. Their gills are then cut with a knife so that the fish bleed out before they are further processed. This is no longer considered a humane method of slaughter. Methods that induce much less physiological stress are electrical or percussive stunning and this has led to the phasing out of the carbon dioxide slaughter method in Europe.[113]

Inhumane methods

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According to T. Håstein of the National Veterinary Institute (Oslo, Norway), "Different methods for slaughter of fish are in place and it is no doubt that many of them may be considered as appalling from an animal welfare point of view."[114] A 2004 report by the EFSA Scientific Panel on Animal Health and Welfare explained: "Many existing commercial killing methods expose fish to substantial suffering over a prolonged period of time. For some species, existing methods, whilst capable of killing fish humanely, are not doing so because operators don't have the knowledge to evaluate them."[115] Following are some less humane ways of killing fish.

  • Air asphyxiation amounts to suffocation in the open air. The process can take upwards of 15 minutes to induce death, although unconsciousness typically sets in sooner.[116]
  • Ice baths or chilling of farmed fish on ice or submerged in near-freezing water is used to dampen muscle movements by the fish and to delay the onset of post-death decay. However, it does not necessarily reduce sensibility to pain; indeed, the chilling process has been shown to elevate cortisol. In addition, reduced body temperature extends the time before fish lose consciousness.[117]
  • CO2 narcosis
  • Exsanguination without stunning is a process in which fish are taken up from water, held still, and cut so as to cause bleeding. According to references in Yue,[118] this can leave fish writhing for an average of four minutes, and some catfish still responded to noxious stimuli after more than 15 minutes.
  • Immersion in salt followed by gutting or other processing such as smoking is applied to eel.[119]

More humane methods

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Proper stunning renders the fish unconscious immediately and for a sufficient period of time such that the fish is killed in the slaughter process (e.g. through exsanguination) without regaining consciousness.

  • Percussive stunning involves rendering the fish unconscious with a blow on the head.
  • Electric stunning can be humane when a proper current is made to flow through the fish brain for a sufficient period of time. Electric stunning can be applied after the fish has been taken out of the water (dry stunning) or while the fish is still in the water. The latter generally requires a much higher current and may lead to operator safety issues. An advantage could be that in-water stunning allows fish to be rendered unconscious without stressful handling or displacement.[120] However, improper stunning may not induce insensibility long enough to prevent the fish from enduring exsanguination while conscious.[115] Whether the optimal stunning parameters that researchers have determined in studies are used by the industry in practice is unknown.[120]
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See also

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References

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Further reading

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Revisions and contributorsEdit on WikipediaRead on Wikipedia
from Grokipedia
Fish farming, a principal component of , entails the controlled breeding, rearing, and harvesting of finfish species—such as , , , and —in enclosed systems including ponds, raceways, tanks, or offshore net pens to yield for human consumption, feed, and other uses. This practice implies human intervention to boost production beyond natural levels through stocking, feeding, and husbandry techniques. Originating in ancient around 2500 BCE with early pond systems for common carp, fish farming expanded globally through Roman-era and fish culture, medieval European husbandry, and 19th-century advancements in hatchery technology, culminating in explosive modern growth since the driven by population demands and technological innovations like recirculating systems. By 2022, global output reached 87.5 million tonnes of aquatic animals, surpassing wild capture fisheries in volume for direct supply and comprising over half of the world's consumption. Dominant producers include , which accounts for the majority of freshwater species like and tilapias, alongside and for marine farming. While fish farming has alleviated pressure on overexploited wild stocks and enhanced , it faces scrutiny for environmental externalities, including from uneaten feed and waste leading to , pathogen transmission to wild populations via escapes, and reliance on wild-caught fish for feed, though improvements in plant-based diets and closed systems mitigate some risks. Controversies persist over localized degradation and overuse, yet empirical assessments highlight that indirect impacts, such as altered wild fish behaviors, may outweigh direct transfers in certain contexts, underscoring the need for site-specific regulation over blanket prohibitions.

History

Ancient Origins and Early Practices

The earliest known evidence of systematic fish farming emerges from around 6200–5800 BCE, based on of otoliths from the site in province, indicating that carpio populations were deliberately managed in ponds rather than solely harvested from wild rivers, providing a buffer against fluctuating wild availability and agricultural inconsistencies. By the (circa 1046–256 BCE), textual records describe of common carp in integrated pond systems alongside and production, exploiting natural fertilization from agricultural runoff to sustain growth without supplemental feeds, as a response to population pressures and seasonal protein deficits. In , aquaculture practices are documented from approximately 2500 BCE through tomb bas-reliefs and paintings depicting rectangular s stocked with (Oreochromis niloticus), where were held for controlled fattening and harvest, leveraging the Nile's annual floods for pond filling and waste recycling in a system tightly coupled to basin irrigation agriculture to counter Nile-dependent harvest variability. A joint German-Israeli archaeozoological study of remains confirms these enclosures supported semi-domesticated stocks, with ponds serving as reservoirs during low-water periods to ensure elite and communal protein access amid reliance on unpredictable riverine captures. Roman piscinae, artificial coastal and lagoon ponds proliferating from the late (circa 100 BCE) onward, featured sluice-gated enclosures for rearing high-value species like murena eels (Muraena helena) and , often adjacent to elite villas, motivated by luxury consumption and status signaling in an era of expanding trade but finite wild supplies from Mediterranean fisheries. These installations used tidal flows for oxygenation and waste flushing, yet remained extensive due to manual stocking from nets. In , Hawaiian loko iʻa wall ponds emerged around 1200 CE, engineering or barriers across estuaries to impound juvenile herbivorous fish like Acanthurus species, addressing island food scarcity by converting marginal coastal zones into productive enclosures dependent on tidal recruitment and natural . Across these early systems, technological constraints precluded artificial breeding or formulated feeds, compelling reliance on capturing wild fry or spawners for , which tied yields to natural recruitment cycles and environmental factors like and predation, inherently limiting densities and reliability compared to later innovations.

Industrialization and Modern Expansion

The establishment of the United States Commission of Fish and Fisheries in 1871 represented a pivotal step toward industrialized aquaculture, tasked with investigating declining coastal fish stocks and implementing artificial propagation to replenish them. Under Commissioner Spencer Fullerton Baird, the agency built the first federal hatcheries, such as those at Green Lake, Maine, and Baird Station, Virginia, focusing on incubating eggs and rearing juveniles of species like shad, salmon, and trout for release into natural waters. These efforts introduced scalable hatchery techniques, including controlled incubation and transport methods, which transitioned from restocking to foundational commercial breeding practices by the early 20th century. Technological breakthroughs in the mid-20th century enabled offshore scale-up, particularly in , where floating sea cages were developed in the late 1960s for farming. Pioneers like the Grøndal brothers adapted plastic nets and feeding systems to rear smolts in fjords, achieving commercial viability by the 1970s and spurring a production surge from experimental tons to millions by the . This cage-based intensive model spread globally, supported by advancements in pelleted feeds and disease management, while the shrimp aquaculture boom in —led by and —intensified pond systems with aerators and high-density stocking, driven by export demand and yielding rapid output growth from negligible levels to over 500,000 tonnes annually by decade's end. Declining wild capture fisheries, plateaued at around 90 million tonnes since the amid widespread , causally accelerated 's expansion as a supply alternative, with farmed production filling gaps in protein demand without relying on depleting ocean stocks. By 2022, aquaculture output of aquatic animals reached 94.4 million tonnes, overtaking capture fisheries (79.7 million tonnes) for the first time, contributing to a combined global total of 223.2 million tonnes including . Post-2000 innovations like recirculating aquaculture systems (RAS) for land-based containment and genetic selection for faster growth and disease resistance further industrialized operations, reducing environmental footprints and enabling year-round production in regions like and .

Core Principles and Methods

Fundamental Concepts of Aquaculture

Aquaculture constitutes the farming of aquatic organisms, encompassing , molluscs, crustaceans, and aquatic , through processes of breeding, rearing, and harvesting in managed water environments such as ponds, tanks, or open waters. This approach enables direct intervention in organism lifecycles, including control over stocking densities, reproduction, and harvesting timing, in contrast to capture fisheries that depend on exploiting naturally occurring populations without such regulatory mechanisms. At its core, aquaculture relies on manipulating physical and chemical water parameters to sustain organism health and maximize accumulation. Essential factors include maintaining dissolved oxygen concentrations above 5 mg/L to support metabolic demands and avert physiological stress, alongside regulating , , , and nutrient levels to align with tolerances. These interventions facilitate elevated stocking densities—often orders of magnitude higher than in natural habitats—while mitigating limitations like oxygen depletion from respiration and organic . Biomass yield optimization hinges on efficient resource conversion, quantified by the , which measures feed mass input per unit of harvestable output and typically ranges from 1.0 to 2.0 for many finfish under controlled feeding regimes. Optimized conditions, including consistent and environmental stability, accelerate growth rates relative to wild counterparts by enabling uninterrupted feeding and reduced energy expenditure on or predator avoidance, thereby compressing production cycles.

Classification of Systems: Extensive, Semi-Intensive, and Intensive

Aquaculture systems are classified by the intensity of management inputs, including , artificial feeding, fertilization, and , which causally determine resource utilization efficiency and output yields per . Low-input systems leverage ambient cycles and blooms for food supply, yielding modest harvests with minimal external or capital. Higher-intensity approaches amplify through engineered delivery and environmental controls, but escalate operational demands and vulnerability to perturbations like oxygen depletion or proliferation. This spectrum enables adaptation to local ecologies and economic constraints, from rural subsistence to commercial . Extensive systems minimize human intervention, relying on natural primary productivity in enclosed water bodies such as or lagoons, with stocking densities often below 1 organism per square meter. Fertilization or manuring may occur sporadically, but feeding is absent, constraining yields to under 1 per hectare per year due to limited biomass accumulation from ambient and . These operations predominate in resource-poor regions of and , where they support small-scale livelihoods with production costs below $1,000 per , though outputs rarely exceed natural carrying capacities without enhancements. Semi-intensive systems bridge natural and controlled production by applying supplemental fertilizers to boost growth alongside occasional formulated feeds, elevating densities to 1-5 organisms per square meter. This yields 1-5 s per annually, as augmented food webs sustain intermediate without full reliance on external rations. Prevalent in in developing economies, these methods balance moderate capital needs—around $2,000-5,000 per —with resilience to fluctuating inputs, though incomplete can lead to risks from excess organic loading. Intensive systems employ high stocking densities exceeding 10-50 organisms per square meter, complete pelleted feeds providing 90-100% of , and mechanical aeration to counteract oxygen deficits from rapid . Yields surpass 10 per per year, driven by precise feed conversion ratios (often 1.2-1.5 kg feed per kg ) that maximize growth under controlled conditions. These dominate commercial volumes for fed , comprising over half of global output in high-value sectors, but demand vigilant monitoring to avert cascading failures from amplification or waste accumulation, with mismanagement inflating costs to $4,000+ per . Across intensities, trade-offs manifest in versus stability: extensive approaches yield low but ecologically buffered outputs suited to marginal lands, while intensive variants achieve 10-20-fold gains through input-output optimization, accounting for the bulk of the sector's growth from 32 million tonnes in 2000 to over 87 million tonnes of aquatic animals by 2020. However, intensive reliance on finite feed proteins and inputs heightens to supply shocks, underscoring the need for hybrid models to sustain expansion amid resource limits.

Cultured Species

Dominant Finfish Species

Atlantic salmon (Salmo salar) represents the leading marine finfish in aquaculture by value, with global production reaching approximately 2.6 million tonnes in 2022, primarily from Norway and Chile. Norway harvested 1.48 million tonnes in 2023, while Chile produced over 1 million tonnes of salmon in the same year, with Atlantic salmon comprising about 73 percent of Chilean output. These species are favored for their high market price, driven by demand for premium protein, and selective breeding programs that enhance growth rates to 4-5 kg in 18-24 months and improve disease resistance, prioritizing farmed traits over wild migration behaviors. Typical biomass densities in sea cages reach 20-25 kg/m³, supporting efficient yields in open-water systems. Tilapia species, particularly (Oreochromis niloticus), dominate tropical and subtropical freshwater and brackish production, with global output estimated at around 6 million tonnes annually as of recent years, concentrated in and . In , production exceeded 2.2 million tonnes in 2022, led by at over 67 percent of continental , followed by and ; , including and , accounts for the majority of global volume due to the species' omnivorous diet, tolerance to low dissolved oxygen levels below 3 mg/L, and up to 15 ppt, enabling cultivation in varied, often marginal water conditions. Fast growth to market size (300-500 g) in 6-8 months and hybrid strains with enhanced fillet yield and resistance to streptococcosis underpin their selection over less adaptable natives. Carp species—silver carp (Hypophthalmichthys molitrix), (Ctenopharyngodon idella), common carp (Cyprinus carpio), and (Hypophthalmichthys nobilis)—lead overall finfish volume, comprising over 12 million tonnes globally in recent years, with producing more than 17 million tonnes projected for 2024 and historically over 60 percent of its freshwater output. These filter- and herbivore-feeding species suit extensive , achieving densities up to 10-15 kg/m³ with minimal supplemental feed, owing to plankton-based nutrition and rapid growth to 1-2 kg in 1-2 years; breeding focuses on sterility induction to prevent escapes and populations, alongside resistance to hypoxia and parasites. Channel catfish (Ictalurus punctatus) is the primary U.S. farmed finfish, with production valued at approximately $405 million in 2023 from 322 million pounds processed, concentrated in pond systems across the region. Selected for bottom-feeding efficiency, tolerance to high densities (10-20 kg/m³), and growth to 1-1.5 kg in 18 months, hybrids improve feed conversion and resistance to enteric septicemia, supporting economic viability amid competition from imports.

Shellfish, Crustaceans, and Other Aquatic Organisms

Crustacean aquaculture is dominated by penaeid , particularly Litopenaeus vannamei, which comprises over 70% of global farmed shrimp production due to its fast growth, disease resistance, and adaptability to intensive pond systems. In 2024, global shrimp aquaculture output reached approximately 5.88 million metric tons, primarily from countries like , , and . This production accounts for over half of total shrimp supply, reducing reliance on wild capture fisheries that involve destructive with bycatch rates often exceeding 60% of the catch. Shrimp farming contributes disproportionately to aquaculture's economic value, representing about one-fifth of the worth of internationally traded products despite lower volume shares, driven by premium pricing of USD 10-15 per . Bivalve , including oysters ( spp.) and mussels (Mytilus spp.), are cultured mainly through suspension systems such as longlines, rafts, and ropes that position seed stock in the for natural filtration, eliminating the need for formulated feeds after spat settlement. Global molluscan production, largely bivalves, totaled around 17.7 million tonnes in 2020, with values exceeding USD 29.8 billion, reflecting steady growth in and . These low-input methods enhance , as bivalves filter up to 50 liters of water per individual daily, potentially mitigating while supplying protein with minimal compared to fed . Other cultured aquatic organisms include sea cucumbers (Holothuroidea spp.), farmed in seabed pens or ponds primarily in China and Southeast Asia for their medicinal and culinary value, with production nearing 0.2 million tonnes annually; and macroalgae like kelp, integrated into polyculture for feed supplements or direct harvest, yielding over 35 million tonnes globally but often outside strict animal aquaculture metrics. These niche sectors diversify production, with echinoderms and gastropods like abalone (Haliotis spp.) addressing localized demand while easing harvest pressures on overexploited wild populations through restocking and containment.

Aquaculture Facilities and Infrastructure

Open-Water Systems

Open-water systems in , often termed net-pen or sea-cage systems, consist of enclosed net structures deployed in marine or freshwater environments such as coastal fjords, lakes, or rivers, where natural currents facilitate oxygenation, exchange, and waste dilution. These systems prioritize harnessing ambient flows for while employing measures to retain cultured ; typical designs feature floating or frames with mesh nets tethered to the , allowing tidal or current-driven throughput but minimizing escape risks through reinforced materials. Copper-alloy nets have gained adoption for their properties, which empirically reduce accumulation by inhibiting algal and bacterial growth, thereby preserving net volume, enhancing circulation, and lowering maintenance frequency compared to traditional meshes. In marine applications, such as (Salmo salar) farming in Norwegian fjords, sea cages typically comprise 6–12 units per site, enabling high-volume production with annual outputs reaching up to 12,000 metric tons per facility through sustained levels often exceeding 5,000 tonnes. This scale leverages low infrastructure costs, as minimal artificial circulation or filtration is required, contrasting with enclosed systems and allowing economic viability in regions with strong tidal regimes. Freshwater variants, including riverine pens, similarly exploit natural currents but face heightened containment challenges from variable flows and predation. Causal dynamics in these systems hinge on hydrodynamic factors: waste particulates like uneaten feed and disperse via near-bottom currents, with empirical modeling indicating deposition predominantly within 100–500 meters of cages in fjord-like settings, though distances extend farther in open coastal zones depending on and . Escapes remain a persistent , exacerbated by events or structural failures, underscoring the between open-flow benefits and imperatives; site selection thus emphasizes sheltered yet dispersive locales to mitigate localized benthic enrichment while curbing broader ecological dispersal.

Land-Based and Closed Systems

Land-based aquaculture systems employ constructed ponds, raceways, tanks, or irrigation ditches on terrestrial sites, decoupling production from natural water bodies and enabling precise management of water flow, temperature, and quality. These setups are prevalent for species like and common carp, which thrive in warm-water environments and can utilize organic inputs efficiently. In the United States, production occurs predominantly in such land-based facilities, contributing to the national total of 3,453 aquaculture farms with sales reported in 2023, an 18% increase from 2018. Carp farming similarly leverages repurposed ditches or shallow ponds for cost-effective rearing, often in regions with limited coastal access. Closed containment systems, particularly recirculating aquaculture systems (RAS), represent an advanced subset of land-based operations, where water is filtered, oxygenated, and reused through biofilters and mechanical treatments, achieving rates of 90-99% and near-zero discharge. This design supports high-density stocking and year-round production in controlled indoor environments, mitigating seasonal constraints and disease transmission risks associated with open systems. RAS facilities have expanded for farming near urban centers, such as large-scale operations in producing Norwegian salmon to reduce transport emissions and supply fresh product to metropolitan markets. Despite requiring substantial energy for pumps, , and heating—potentially 15-20% higher than pond systems without optimization—RAS demonstrate superior and land efficiency, yielding over 100 kg of per square meter annually in optimized setups. Hybrid approaches within land-based frameworks incorporate composite or techniques, stocking complementary to optimize nutrient cycling and resource utilization. For instance, combining surface-feeding carps like with bottom-feeders such as in shared ponds promotes synergism, where waste from one serves as feed for another, enhancing overall without supplemental inputs. These methods, rooted in traditional practices but adaptable to controlled land-based tanks, have proven effective in intensive setups, increasing yields by leveraging ecological interactions while maintaining system stability.

Integrated and Offshore Innovations

Integrated multi-trophic aquaculture (IMTA) systems cultivate species from different trophic levels within the same facility, such as finfish alongside and , to promote nutrient recycling and ecosystem-like balances that mitigate waste accumulation inherent in operations. In these setups, extractive species like mussels and assimilate dissolved inorganic nutrients, particularly and , from finfish excreta and uneaten feed, thereby reducing effluent loads that contribute to coastal . Empirical assessments of IMTA configurations, including those pairing with blue mussels and sugar , demonstrate enhanced nutrient retention efficiencies, with extractive components capturing up to 20-40% of released and depending on biomass ratios and site . Offshore aquaculture innovations relocate production to deeper, open-ocean sites using larger, more robust net pens, which disperse wastes over greater volumes and distances, alleviating localized benthic deposition and hypoxia risks prevalent in nearshore farms. Post-2020 pilot projects, such as those deploying cages in exposed Norwegian waters, have shown improved hydrodynamic flushing that limits nutrient hotspots, with modeling indicating 50-70% reductions in seabed sediment accumulation compared to coastal baselines. These developments address capacity constraints in saturated coastal zones by harnessing stronger currents for natural dilution, though challenges like structural integrity against waves persist, as evidenced by iterative designs tested since 2021. Emerging floating closed containment systems (FCCS), deployed offshore, enclose in rigid or flexible barriers to fully retain solids and pathogens, further minimizing environmental releases while enabling high-density production in dynamic sea conditions. In , full-scale FCCS trials during the 2020s, including the Marine Donut prototype stocked with 195,000 smolts in 2024, reported mortalities below 5%, outperforming open-net averages and containing over 99% of waste within the structure for potential recapture. Government-backed growth schemes launched in 2025 support scaling these technologies, integrating real-time monitoring to optimize oxygen and feed distribution, thus scaling production without proportional increases in coastal ecological footprints.

Operational Processes

Breeding, Hatchery, and Stocking Practices

Artificial propagation techniques enable controlled in , primarily through hormone induction to trigger and spermiation in . Common methods include hypophysation, where extracts or synthetic gonadotropins like (hCG) are administered to females and males, facilitating egg stripping and fertilization outside natural breeding cycles. These approaches, grounded in manipulating endocrine signals, allow year-round seed production but require precise dosing to avoid physiological stress, with success dependent on species-specific responses and parameters. Selective breeding programs, conducted without genetic modification, focus on of traits such as growth rate and disease resistance through family-based selection. In , these efforts have yielded annual genetic gains of approximately 10-15% in growth performance since the 1990s, shortening time to market size and reducing feed conversion ratios via polygenic improvements. Such programs leverage principles, selecting superior sires and dams from performance-tested offspring, thereby enhancing overall farm productivity while preserving through effective population size management. Hatchery operations incubate fertilized eggs in controlled trays or jars, hatching into yolk-sac larvae or fry that transition to exogenous feeding. Rearing progresses fry to juveniles in tanks with optimized flows and oxygenation, achieving survival rates above 90% in benchmark systems for like under monitored conditions. These facilities minimize wild capture dependency, supplying over 90% of seedstock for intensive in many regions, as empirical data from controlled environments demonstrate high propagation efficiency when densities and nutrition align with physiological tolerances. Stocking practices transfer juveniles to grow-out systems at densities calibrated to species tolerance, typically 10-100 kg/m³ biomass equivalents during initial phases to prevent stress-induced or growth stagnation. For instance, juveniles thrive at around 200-300 individuals per m³ in biofloc systems, corresponding to low initial biomass that scales with size. optimization follows first-principles of oxygen demand and waste assimilation, with empirical trials showing reduced and improved uniformity when avoids overcrowding thresholds. This phase ensures viable integration into production cycles, directly linking hatchery outputs to sustainable scaling without overreliance on unpredictable wild .

Nutrition, Feeding, and Growth Management

In , feed efficiency is quantified by the (FCR), defined as the mass of feed input per unit of animal gain. For salmonid farming, commercial data reveal a 53.4% improvement in FCR from 1980 onward, driven by refined formulations and operational practices that lowered the ratio from historical levels around 2:1 to current values below 1.2:1. This progress reflects causal factors such as enhanced digestibility of feeds and reduced energy losses in . The incorporation of plant-based alternatives like has substantially decreased reliance on fishmeal from , with the overall fish-in fish-out (FIFO) ratio—measuring wild fish equivalents used in feed relative to farmed output—declining from peaks of 5:1 in the to under 1.5:1 today across fed sectors. These shifts stem from first-principles optimization of nutrient profiles, where plant ingredients supply essential at lower ecological cost in terms of marine inputs, though full replacement requires supplementation to match carnivorous ' requirements. Precision feeding technologies, including automatic dispensers and sensor-integrated systems, deliver rations based on real-time biomass estimates and indicators, minimizing excess provision. Overfeeding empirically leads to uneaten pellets sinking and decomposing, inflating FCR by 10-20%; optimized sensor-guided protocols counteract this by adjusting daily allocations to match metabolic demands, achieving waste reductions of 20-30% in controlled trials. Growth management employs acoustic and optical sensors to track size uniformity and feeding response, enabling data-driven adjustments that accelerate development under stable conditions. Empirical records show farmed carnivorous attaining harvest weights in 12-24 months, versus 3-5 years for wild conspecifics reliant on variable natural . This disparity arises from consistent high-protein rations sustaining elevated specific growth rates (2-3% body weight daily) unattainable in wild habitats subject to prey scarcity and predation risks.

Health, Disease Control, and Biosecurity

Biosecurity protocols form the cornerstone of disease prevention in aquaculture, focusing on excluding through measures such as restricted site access, equipment disinfection, of new stock, and zoning to minimize transfers between facilities. These strategies, outlined in frameworks like the FAO's Progressive Management Pathway, reduce pathogen entry risks by addressing vectors including water, feed, and personnel. Empirical assessments show that farms implementing such protocols experience lower burdens, with global losses to infectious estimated at 10% of production potentially mitigated through consistent application. Vaccination targets specific pathogens, particularly bacterial ones prevalent in finfish culture; for example, inactivated vaccines against spp. and prevent vibriosis and furunculosis in salmonids, activating immune responses without antibiotics. In parasite management, sea lice (Lepeophtheirus salmonis) on are controlled via integrated methods including deployment of like lumpfish or , which remove lice biologically, alongside mechanical delousing and judicious in-feed treatments; experimental vaccines have demonstrated up to 90% reduction in lice counts in challenge trials. High densities in net pens amplify transmission via proximity, mirroring contact rates in wild fish schools during migration or spawning, but monitoring mitigates amplification through early intervention. Antimicrobial use is curtailed in regulated systems prioritizing prevention, with Norway's salmon sector exemplifying this: in 2020, 1.3 million metric tons of production required only 222 kg of antibiotics, or approximately 0.17 mg per kg of fish produced, and over 99% of salmon received no treatment. Routine surveillance, including water quality checks, , and like PCR for or infectious salmon anemia, enables detection before clinical outbreaks, supporting containment without broad therapeutics.

Harvesting, Processing, and Slaughter Methods

Harvesting in pond-based aquaculture typically involves partial or complete draining of the pond through outlets, followed by seining with nets of 3-3.5 cm mesh to capture fish, often concentrated in catch basins for efficiency. In cage systems, fish are crowded using mechanical barriers or pumps to facilitate removal via lift nets or suction devices, minimizing escape and injury. Mechanized approaches, including hydraulic lifts and electrical herding, are employed in larger operations to handle volumes exceeding thousands of kilograms per harvest. Slaughter methods prioritize rapid induction of insensibility to limit stress responses, with percussive —delivered by automated machines applying a targeted blow to the head above the —achieving immediate brain disruption in species like and . Electrical , involving immersion in electrified or application, renders fish insensible within 1 second for many finfish, followed by killing via or spiking. These mechanical methods yield lower blood indicators of stress, such as and , compared to alternatives like CO2 narcosis or ice-slurry immersion, which can elevate glucose and pH decline rates indicative of prolonged agitation. In optimized systems, percussive and electrical techniques show stress markers in under 5% of cases exceeding baseline thresholds, outperforming variable capture stresses in where net entanglement or exhaustion often prolongs physiological distress. Post-slaughter processing begins with rapid chilling in slurries at 0-4°C to halt microbial growth and enzymatic degradation, preserving flesh quality and extending for like to 10-14 days under refrigerated conditions. Gutting removes viscera within hours to prevent autolysis, followed by filleting, , and portioning in automated lines; freezing via (IQF) at -30°C or below maintains quality for 4-8 months in lean fillets. Proper handling, including hygiene and temperature control per FAO guidelines, reduces spoilage rates, with microbial limits aligned to time-temperature models where halves per 10°C rise above 0°C.

Economic and Societal Contributions

Role in Global Food Security and Protein Supply

Aquaculture has become the primary source of aquatic animals for human consumption, accounting for 51 percent of the 185 million tonnes produced globally in 2022, or 94 million tonnes, surpassing capture fisheries for the first time. This milestone underscores its role in bolstering global protein supply, as fisheries and aquaculture together contribute around 20 percent of the average per capita intake of animal protein for 3.2 billion people worldwide. With global apparent fish consumption reaching approximately 20.4 kg per capita in 2022, aquaculture's expansion helps meet rising demand without relying on wild stocks, 35.5 percent of which are overfished and an additional portion fully exploited, limiting further gains from capture methods. The sector's production has grown at an average annual rate exceeding 5 percent over recent decades, contrasting with the stagnation in capture fisheries output, which has hovered around 90-95 million tonnes since the due to and environmental pressures. This differential growth provides a buffer against variability in wild catches influenced by oscillations and depletion, ensuring more predictable availability of as a nutrient-dense protein source. In regions like , where aquaculture dominates production, it supports by offering affordable aquatic proteins amid population growth and limited . In and other developing areas, aquaculture's potential remains underutilized but critical for addressing protein deficits, with initiatives aimed at scaling operations to enhance local supplies and reduce import dependence. By alleviating pressure on depleted —where nearly 90 percent of stocks face maximal exploitation—aquaculture fosters sustainable augmentation of global provision, pivotal for dietary diversity and resilience in vulnerable populations.

Employment, Trade, and Industry Economics

generates substantial worldwide, with the sector supporting an estimated 20 million direct jobs, predominantly in where small-scale operations dominate labor needs in countries like , , and . Including indirect in processing and supply chains, the contribution extends further, aiding rural economies through value-added activities. In 2022, the combined primary sector of fisheries and employed 61.8 million people globally, with 's share expanding due to its labor-intensive nature in developing regions. In the United States, aquaculture production reached a value of $1.7 billion in 2022, encompassing 663 million pounds of output from freshwater and marine operations, primarily and finfish. Major exporting nations underscore the sector's trade significance: Norway's aquaculture exports, dominated by , totaled NOK 128.7 billion (approximately $12 billion USD) in 2023, representing 75% of its overall export value. Similarly, Chile's and exports generated $6.1 billion in 2023, positioning aquaculture as a key driver of national trade balances and foreign exchange earnings. Intensive aquaculture systems, particularly for high-value species like , demonstrate strong economic viability through scalable production and market premiums, often achieving returns on investment exceeding those of extensive methods via optimized feed and inputs. In developing economies, which produce over 90% of global farmed volume, technology transfers—such as improved techniques and feed formulations—have causally boosted output and incomes by enabling transitions from subsistence to commercial scales, as seen in Southeast Asia's and sectors. Empirically, frequently delivers protein at lower costs per kilogram than many terrestrial options in tropical and subtropical regions, where like and exhibit feed conversion ratios of 1.5-2.0:1 compared to 6-10:1 for , translating to competitive pricing for staple protein sources amid rising agricultural input costs. This efficiency supports trade competitiveness and household affordability, with global output valued at $313 billion in 2022.

Nutritional Advantages and Human Health Impacts

Farmed exhibit nutritional profiles comparable to wild-caught counterparts in key macronutrients and essential fatty acids, with protein content typically ranging from 15-25% of wet weight across species like and seabass, and omega-3 levels such as EPA and DHA averaging 500-600 mg per 100g in both farmed and wild . Farmed varieties often contain equivalent or higher total omega-3s due to elevated content from controlled feeding, providing similar cardiovascular benefits without the variability inherent in wild diets influenced by seasonal prey availability. Contrary to persistent claims of elevated contaminants in farmed , empirical from regulated European operations demonstrate that polychlorinated biphenyls (PCBs) and dioxins are frequently lower in farmed than in wild counterparts, with Norwegian studies reporting toxic compounds more prevalent in wild fish due to uncontrolled environmental exposure versus feed screening in . Levels in compliant farmed fish remain below safety thresholds, posing negligible risks to from typical consumption patterns, as quantitative risk-benefit analyses confirm that associated nutrient gains outweigh potential exposures. Aquaculture feeds enable fortification with bioavailable minerals, enhancing levels of iodine, selenium, and iron in fillets—such as through iodine-rich macroalgae supplementation increasing muscle iodine by up to 50% in seabream—directly addressing global deficiencies that affect over 2 billion people, with consistent year-round supply mitigating the intermittency of wild fisheries subject to seasonal and overexploitation fluctuations. This reliability supports sustained intake of these nutrients, causal to improved thyroid function and anemia prevention, without the supply disruptions that limit wild fish accessibility.

Environmental Dimensions

Benefits: Reducing Pressure on Wild Fisheries

's expansion has substituted for in meeting global demand, thereby alleviating harvest pressure on depleted . In , global aquaculture production of reached 94.4 million tonnes, surpassing capture fisheries output of 91 million tonnes for the first time and comprising 51 percent of total production. This shift correlates with the stabilization of wild capture volumes, which have hovered around 90-100 million tonnes since the peak, despite rising consumption, as aquaculture absorbed incremental demand growth exceeding 50 million tonnes cumulatively. Empirical models indicate that such substitution supports wild stock conservation by curtailing , with aquaculture growth exerting a net positive effect on levels even accounting for feed-related predator-prey dynamics. In specific cases like salmonids, aquaculture dominance—producing over 90 percent of market supply—has enabled quota reductions and recovery programs for wild populations by diminishing economic incentives for excessive wild harvesting. For instance, wild catches have declined as farmed output scaled to 2.5 million tonnes annually, allowing targeted management to rebuild spawning stocks in regions like and . This causal mechanism operates through market displacement: farmed alternatives lower prices and supply risks, prompting regulatory harvest limits that foster stock rebound, as evidenced by increased wild salmon returns in areas with stringent farming-supported conservation. From a production standpoint, aquaculture's controlled environments inherently bypass the incidental ecosystem disruptions of capture methods, such as trawling-induced and , which annually discard millions of tonnes of non-target and exacerbate stock declines. By channeling protein output through enclosed systems, aquaculture offsets equivalent wild harvest volumes—estimated at over 50 million tonnes in recent decades—without propagating these collateral damages, thereby preserving marine biodiversity and fishery resilience. This is particularly pronounced for high-value , where farmed volumes directly supplant wild equivalents, stabilizing global catches and enabling natural replenishment cycles.

Empirical Assessments of Impacts: Waste, Emissions, and Biodiversity

Fish farming generates organic waste primarily from uneaten feed, , and exudates, leading to localized enrichment in surrounding waters. Studies indicate that significant benthic impacts from loading are confined to areas within approximately 130 meters of net-pen sites, with effects diminishing rapidly beyond this distance due to dispersion and dilution in marine environments. For instance, empirical monitoring in coastal zones shows elevated and levels primarily affecting sediments directly beneath cages, with enrichment limited to proximal zones. Greenhouse gas emissions from , calculated on a life-cycle basis including feed production and farm operations, average around 2.5 to 3 s of CO₂ equivalent per of harvested , with variations by region and feed sourcing. This footprint is substantially lower than production (typically 20-60 s CO₂e per ) but comparable to or slightly below (around 4-6 s CO₂e per ), reflecting 's reliance on plant-based feeds offset by energy-intensive operations. Per unit of edible protein, waste and emissions intensity is lower than terrestrial like , where higher feed conversion ratios amplify resource demands, though intensive farming exceeds capture fisheries in direct emissions. Biodiversity impacts include alterations to benthic communities from organic deposition, but empirical data demonstrate recovery potential following site fallowing. Subtidal sediments beneath fallowed farms show partial to full benthic recolonization within 6-12 months, with oxygen levels and rebounding as waste ceases. Fish escapes from modern net pens, enhanced by stronger materials and monitoring, occur at rates below 0.1% of stocked populations annually in well-managed operations, minimizing genetic risks to wild stocks compared to historical incidents. In contrast, wild capture fisheries often impose broader through , which disrupts seafloor ecosystems across vast areas—exceeding aquaculture's localized benthic footprints in scale and persistence, per comparative environmental assessments.

Mitigation Techniques and Data-Driven Improvements

Fallowing periods and rotational site use in finfish aquaculture, particularly salmon farming, allow sediments beneath cages to recover from organic enrichment, reducing anoxia by enabling reoxygenation and microbial degradation of accumulated waste. Empirical studies demonstrate partial restoration of benthic community similarity to reference sites, with increases from 11-25% to 27-31% following short-term fallowing, thereby mitigating persistent accumulation and imbalances. Integrated multi-trophic aquaculture (IMTA) systems co-culture fed species like with extractive organisms such as and , which assimilate dissolved nutrients from uneaten feed and excreta, retaining a substantial fraction—often exceeding 30% in modeled efficiencies—to prevent and improve . Quantitative assessments across IMTA configurations confirm these retention rates, with bio-mitigation reducing and loads through complementary trophic levels, as evidenced in pilot operations recycling wastes into . Transitioning operations to offshore locations disperses effluents via stronger currents and deeper waters, substantially lowering benthic impacts compared to coastal sites by diluting and minimizing loading within 150 meters of cages. Field data from offshore farms indicate reduced localized anoxia and geochemical alterations, with organic dispersion promoted by oceanographic conditions that limit persistent effects on cohesive s. Vaccination protocols have achieved use reductions of 70-99% in targeted , curbing environmental release of residues that contribute to resistance in aquatic ecosystems; for instance, in U.S. farming, medicated feed orders dropped 69-78% post-vaccine adoption from 2018-2024, while Norwegian sectors maintain usage at 0.002 kg per kg produced through widespread . Data-driven tools, including AI-enabled sensors for real-time monitoring of parameters like dissolved oxygen and , optimize feeding and stocking densities to minimize waste outputs, with 2024-2025 implementations forecasting hypoxia events and enabling predictive adjustments toward near-zero net environmental footprints in monitored farms. These systems integrate for environmental analytics, reducing overfeeding-induced nutrient excess by up to 20-30% in predictive models.

Controversies and Empirical Critiques

Animal Welfare and Ethical Debates

In aquaculture, animal welfare concerns primarily revolve around stocking density, which can elevate stress hormones such as cortisol in fish, potentially leading to suppressed growth, impaired immunity, and increased aggression. However, peer-reviewed studies indicate that domesticated farmed fish often exhibit lower baseline cortisol levels compared to wild counterparts under chronic stress, as selective breeding and management practices mitigate long-term physiological burdens. For instance, in Atlantic salmon farming, optimized water velocities up to 1.5 body lengths per second have been shown to reduce cortisol spikes, aggression, and dominance hierarchies while enhancing growth rates. Empirical mortality data further contextualize these debates: farmed fish typically experience annual mortality rates below 15-20% in well-managed systems, contrasting sharply with wild , where natural losses from predation, , and environmental stressors often exceed 80-95% before maturity. This disparity underscores a causal advantage in controlled environments, where risks like predation are eliminated, enabling faster growth cycles—often 1-2 years to harvest versus 3-5 years in the wild—and reducing overall lifetime exposure to stressors. Debates on fish sentience complicate ethical assessments, with evidence suggesting capacities for pain perception and stress responses in species like and , though skeptics argue that behavioral indicators do not conclusively prove subjective equivalent to higher vertebrates. Activists frequently characterize high-density farming as inherently inhumane due to crowding-induced damage and behavioral restriction, yet first-principles comparisons reveal fish endure unrelenting threats of predation and absent in farms, where enrichment strategies—such as structural hides or variable feeding—have demonstrably improved foraging skills and reduced abnormal behaviors. Slaughter methods represent another focal point, with traditional practices like live chilling or asphyxiation criticized for prolonging distress; however, advancements in electrical or percussive have increased humane endpoints, rendering fish insensible within seconds, as validated in salmonid studies. Ethically, while some viewpoints prioritize absolute minimization of confinement regardless of outcomes, data-driven analyses emphasize that aquaculture's net welfare gains—via control, nutrition consistency, and predator exclusion—outweigh wild analogs, provided ongoing refinements address verifiable stressors. This tension reflects broader philosophical divides, with empirical metrics favoring scalable improvements over ideological bans on farming.

Disease Transmission and Wild Stock Interactions

Recent empirical studies in , a major center for open-net pen salmon aquaculture, indicate that pathogen transmission from farmed to wild Pacific salmon populations does not pose a significant threat. A 2025 analysis by researchers, reviewing two decades of data, found weak evidence linking farmed salmon pathogens to substantial mortality or decline in wild stocks, challenging narratives of high-risk spillover. Similarly, a peer-reviewed assessment published in July 2025 concluded that the evidence for pathogens transmitted from farmed salmon causing significant impacts on wild populations is limited, with prevalence in wild fish often attributable to natural reservoirs rather than farms. Piscine orthoreovirus (PRV), a prevalent in British Columbia salmon farms, demonstrates high infectivity but low virulence in of Pacific , rarely leading to clinical disease or mortality in wild Pacific . Canadian assessments confirm PRV's low disease-causing potential in regional salmonids, with infections typically subclinical and not driving population-level effects. Infectious hematopoietic necrosis (IHNV), another concern, has been documented in wild Pacific since the 1950s—predating commercial farming by decades—indicating its persistence in natural ecosystems independent of . Escaped farmed salmon can interbreed with populations, but genetic dilution remains minimal, with models estimating impacts below 1% in most scenarios due to lower fitness of farmed strains in natural environments. strategies in further mitigate outbreak risks, reducing and downstream transmission potential; for instance, against viruses like has achieved relative percent survival rates up to 86% while curbing loads. While some outbreaks have been correlated with farm proximity, causal attribution is confounded by endemic reservoirs, and activist claims of existential threats to stocks often exceed the empirical data, as evidenced by longitudinal monitoring showing stable or recovering populations despite farming presence.

Feed Resources and Resource Efficiency Claims

The proportion of wild-caught fish in aquaculture feeds has declined substantially, with global fishmeal and fish oil inclusion rates dropping from 23% to 8% between 2000 and 2020, driven by substitutions with plant proteins, , and meals; for feeds, marine ingredients now constitute under 20%. This shift has stabilized wild fish inputs despite production growth, as usage per ton of farmed output has fallen, often yielding a fish-in-fish-out (FIFO) ratio below 1 for species like . Feed conversion ratios (FCR) in aquaculture have improved to 1.1–1.3 kg of feed per kg of harvest weight, reflecting genetic selection, precise feeding technologies, and optimized formulations that enhance retention and result in net protein gains when non-marine feeds predominate. These efficiencies arise from farmed fish converting dietary protein into edible more directly than the multi-trophic losses in wild ecosystems, though FCR remains higher than in (typically 1.5–2.0) due to carnivorous digestive constraints. Assertions that aquaculture systematically depletes wild stocks for feed overlook the fact that over 30% of global fishmeal derives from by-products of human-edible fisheries (e.g., trimmings from and ), which would otherwise be wasted, and that small pelagic used (e.g., anchoveta) exhibit rapid turnover and are not direct competitors for higher-value catches. Plant-based feed transitions further reduce marine dependency, countering depletion narratives, while causal analyses show aquaculture's protein yield per unit input exceeds the fuel-intensive caloric costs of wild , which can require 10–20 times more energy per kg of protein landed. Critics, including environmental advocacy groups, contend that reliance on soy and other crops indirectly drives habitat loss through agricultural expansion, citing Amazon deforestation tied to soy monocultures. However, accounts for less than 2% of global soy protein demand, dwarfed by sectors, limiting its marginal contribution to such pressures relative to overall feed . Empirical tracking of supply chains underscores that certified sustainable soy sourcing mitigates these risks without compromising feed efficacy.

Regulatory and Activist Challenges

In Washington state, a net-pen collapse in November 2022 released thousands of non-native Atlantic salmon into Puget Sound, prompting regulators to enforce a ban on commercial finfish net-pen aquaculture on state-owned aquatic lands, with the prohibition taking full effect in early 2025. This followed a 2017 escape of over 250,000 fish and built on a 2018 restriction on non-native species farming, driven by concerns over ecological risks despite industry assessments indicating that such incidents, while notable, have not demonstrably caused widespread genetic dilution or population crashes in native stocks. Critics from aquaculture advocates argue that the bans reflect precautionary politics prioritizing activist pressures over site-specific risk data, which shows containment technologies have improved post-incident, potentially limiting innovation in closed-containment alternatives. Activist campaigns often portray aquaculture expansion as a driver of ocean "decimation," yet (FAO) records indicate global aquaculture production reached 130.9 million tonnes in 2022—surpassing wild capture for the first time—while wild fisheries output has plateaued around 90 million tonnes since the without evidence of systemic collapse. This divergence undercuts causal claims linking farm growth to wild stock declines, as overexploitation in capture fisheries predates modern aquaculture surges, with 89% of assessed stocks fully exploited or overfished independently of farmed production increases. Empirical tracking by FAO attributes wild fishery stability to management reforms rather than aquaculture substitution alone, highlighting how unsubstantiated alarmism from environmental groups can amplify regulatory scrutiny without proportional evidence. Regulatory frameworks like the Aquaculture Stewardship Council's (ASC) updated Farm Standard, launched in May 2025, mandate enhanced transparency in feed sourcing and operations, requiring certified farms to use conforming feeds from ASC-accredited mills by October 31, 2025. While intended to build accountability, stringent standards in developed markets correlate with slower growth rates, as cross-country analyses show environmental regulations disproportionately burden smaller operators in developing nations, where compliance costs hinder scalability and local innovation. Overregulation risks exacerbating gaps in these regions, where contributes up to 50% of animal protein in some low-income countries, by favoring large-scale exporters over adaptive, smallholder models.

Recent Developments and Future Outlook

Technological Advancements Post-2020

Since 2020, (AI) has been integrated into for precision feeding and , enabling real-time optimization of feed distribution based on fish behavior, estimates, and environmental data. Systems employing AI models, such as convolutional neural networks combined with self-attention mechanisms, predict dissolved oxygen levels and growth rates, reducing overfeeding by up to 20% and minimizing waste while enhancing feed conversion efficiency. In , DNV's 2025 AI-powered Smarter Compliance tool automates regulatory monitoring of fish farm integrity, cutting manual documentation by automating compliance checks on parameters like net integrity and , thereby addressing operational densities that previously risked escapes or inefficiencies. Drone-based monitoring has advanced post-2020, with unmanned aerial vehicles equipped for overhead of and conditions, detecting anomalies in schooling or to reduce labor requirements by automating patrols that previously demanded manual inspections. These systems, including hybrid aerial-underwater drones, collect data on water parameters and health, potentially lowering operational losses from undetected issues by 30% through timely interventions that mitigate high-density stressors like uneven feeding. programs, accelerated by genomic selection tools since 2021, have targeted disease resistance in species like , yielding strains with 10-15% improved survival rates against pathogens such as sea lice without relying on gene editing. Recirculating aquaculture systems (RAS) have expanded significantly post-2020, with land-based facilities reusing up to 99% of water through advanced biofiltration and hydrodynamics, slashing freshwater demands compared to traditional flow-through methods and enabling higher stocking densities with controlled environments that boost yields by 10-20% via reduced disease transmission. Integration of microalgae in RAS biofilters removes 60-90% of nutrients while producing biomass for feed, further enhancing resource efficiency in commercial operations like salmon smolt production. These advancements collectively tackle density-related challenges, such as oxygen depletion and waste accumulation, by enabling data-driven adjustments that sustain productivity without expanding physical footprints.

Sustainability Standards and Policy Evolutions

The Aquaculture Stewardship Council (ASC) released an updated Feed Standard (version 1.1) in 2024, mandating its full effect from November 1, 2025, to align aquafeed production with farm-level reporting and prioritize ingredients that reduce environmental footprints, such as through sourcing from low-impact fisheries and minimizing wild fish use. This builds on prior iterations by incorporating criteria for entire feed facilities, even those producing non-aquatic feeds, to curb broader ecological pressures from raw material extraction. In the , the Commission issued staff working documents in April 2024 outlining regulatory and administrative frameworks to foster sustainable expansion, including access to coastal spaces, adaptation to variability, and energy transitions aimed at lowering carbon intensities. These guidelines emphasize voluntary good practices over stringent mandates, with a focus on integrating into maritime spatial planning to balance growth against preservation. United States policy has supported aquaculture scaling, evidenced by an 18% rise in operational farms from 2,924 in 2018 to 3,453 in 2023, alongside a 26% increase in total sales to $1.9 billion, driven by federal censuses tracking production amid incentives for domestic supply . Market-driven certifications like ASC have incentivized compliance more effectively than top-down regulations, as producers respond to premium pricing for verified low-impact operations, yielding measurable environmental gains such as reduced (GWP) in certified production to around 4.98 kg CO₂ equivalent per kg harvested. Enforcement remains uneven, particularly in regions where regulatory gaps exacerbate challenges like inconsistent monitoring of use and discharges, limiting standard adherence despite policy frameworks. Nonetheless, rising volumes—such as ASC's 20% site growth in prior years—and policy evolutions signal a positive shift toward data-verified , with empirical compliance correlating to 15-20% GWP reductions in aligned operations per lifecycle assessments.

Projections for Expansion and Challenges

The OECD-FAO Agricultural Outlook 2025-2034 forecasts global production, encompassing capture fisheries and , to expand by 14% over the projection period, with driving the majority of growth through productivity gains in emerging markets of and . In the preceding 2024-2033 outlook, total production was projected to rise from 185 million tonnes in the base period to 206 million tonnes by 2033, a trend expected to continue as 's share of overall output increases to 56% by 2034 from 52%, outpacing stagnant wild capture volumes. This expansion positions to satisfy rising protein needs for a growing , supplying scalable protein without relying on overexploited wild stocks, which have plateaued amid maximum sustainable yields. Key challenges include climate-induced stressors such as ocean warming, which elevate water temperatures and disrupt fish , , and susceptibility, potentially reducing yields in tropical and coastal zones. Rising sea levels may further degrade coastal habitats like mangroves essential for larval nurseries, exacerbating vulnerabilities in nearshore farms. mitigates these risks by leveraging deeper, more stable waters less prone to temperature extremes and , though it demands advancements in durable and monitoring to address higher operational costs and storm exposure. Sustained innovation in alternative feeds, genetic selection for resilient strains, and integrated multi-trophic systems—combining fish with extractive species like seaweed and shellfish—can enhance resource efficiency and ecosystem resilience, enabling hybrid models that buffer against wild fishery declines. Regulatory streamlining and investment in these technologies are projected to accelerate adoption, provided empirical data from pilot operations inform scalable deployment without undue constraints from environmental advocacy. By 2034, such adaptations could stabilize supply amid demand pressures, with aquaculture markets valued at up to USD 513 billion, underscoring its role in global food security if causal factors like technological diffusion prevail over localized hurdles.

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