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Environmental impact of fishing

The environmental impact of fishing includes issues such as the availability of fish, overfishing, fisheries, and fisheries management; as well as the impact of industrial fishing on other elements of the environment, such as bycatch.[1] These issues are part of marine conservation, and are addressed in fisheries science programs. According to a 2019 FAO report, global production of fish, crustaceans, molluscs and other aquatic animals has continued to grow and reached 172.6 million tonnes in 2017, with an increase of 4.1 percent compared with 2016.[2] There is a growing gap between the supply of fish and demand, due in part to world population growth.[3]

Greenhouse gas emissions (kg / kg edible weight) of wild-caught and farmed seafood products

Fishing and pollution from fishing are the largest contributors to the decline in ocean health and water quality. Ghost nets, or nets abandoned in the ocean, are made of plastic and nylon and do not decompose, wreaking extreme havoc on the wildlife and ecosystems they interrupt. The ocean takes up 70% of the earth, so overfishing and hurting the marine environment affects everyone and everything on this planet. On top of the overfishing, there is a seafood shortage resulting from the mass amounts of seafood waste, as well as the microplastics that are polluting the seafood consumed by the public. The latter is largely caused by plastic-made fishing gear like drift nets and longlining equipment, that are wearing down by use, lost or thrown away.[4][5]

The journal Science published a four-year study in November 2006, which predicted that, at prevailing trends, the world would run out of wild-caught seafood in 2048. The scientists stated that the decline was a result of overfishing, pollution and other environmental factors that were reducing the population of fisheries at the same time as their ecosystems were being annihilated. Many countries, such as Tonga, the United States, Australia and Bahamas, and international management bodies have taken steps to appropriately manage marine resources.[6][7]

Reefs are also being destroyed by overfishing because of the huge nets that are dragged along the ocean floor while trawling. Many corals are being destroyed and, as a consequence, the ecological niche of many species is at stake.

Mean greenhouse gas emissions for different food types[8]
Food types Greenhouse gas emissions (g CO2-Ceq per g protein)
Beef
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


Effects on marine habitat edit

 
A sea turtle killed by a boat propeller

Some fishing techniques cause habitat destruction.[9][10] Blast fishing and cyanide fishing, which are illegal in many places, harm surrounding habitats.[9] Blast fishing refers to the practice of using explosives to capture fish.[9] Cyanide fishing refers to the practice of using cyanide to stun fish for collection.[9] These two practices are commonly used for the aquarium trade and the live fish food trade.[9] These practices are destructive because they impact the habitat that the reef fish live on after the fish have been removed. Bottom trawling, the practice of pulling a fishing net along the sea bottom behind trawlers, removes around 5 to 25% of an area's seabed life on a single run.[11] This method of fishing tends to cause a lot of bycatch.[10] A study of La Fonera Canyon compared trawled versus non-trawled areas. The results show that areas at 500 to 2000 meters depth that is non-trawled have more biodiversity, biomass, and variation of meiofauna than trawled areas at 500 meters depth.[12] Most of the impacts are due to commercial fishing practices.[13] A 2005 report of the UN Millennium Project, commissioned by UN Secretary-General Kofi Annan, recommended the elimination of bottom trawling on the high seas by 2006 to protect seamounts and other ecologically sensitive habitats. This was not done.

In mid-October 2006, United States President George W. Bush joined other world leaders calling for a moratorium on deep-sea trawling. The practice has shown to often have harmful effects on sea habitat and, hence, on fish populations,[14] yet no further action was taken (Vivek). The sea animal's aquatic ecosystem may also collapse due to the destruction of the food chain.

Additionally, ghost fishing is a major threat due to capture fisheries.[15] Ghost fishing occurs when a net, such as a gill net or trawl, is lost or discarded at sea and drifts within the oceans and can still act to capture marine organisms.[15] According to the FAO Code of Conduct for Responsible Fisheries, States should act to minimize the amount of lost and abandoned gear and work to minimize ghost fishing.[16]

Overfishing edit

 
Jack mackerel caught by a Chilean purse seiner
 
Fishing down the food web

Overfishing is the removal of a species of fish (i.e. fishing) from a body of water at a rate greater than that the species can replenish its population naturally (i.e. the overexploitation of the fishery's existing fish stock), resulting in the species becoming increasingly underpopulated in that area. Overfishing can occur in water bodies of any sizes, such as ponds, wetlands, rivers, lakes or oceans, and can result in resource depletion, reduced biological growth rates and low biomass levels. Sustained overfishing can lead to critical depensation, where the fish population is no longer able to sustain itself. Some forms of overfishing, such as the overfishing of sharks, has led to the upset of entire marine ecosystems.[17] Types of overfishing include: growth overfishing, recruitment overfishing, ecosystem overfishing.

The ability of a fishery to recover from overfishing depends on whether its overall carrying capacity and the variety of ecological conditions are suitable for the recovery. Dramatic changes in species composition can result in an ecosystem shift, where other equilibrium energy flows involve species compositions different from those that had been present before the depletion of the original fish stock. For example, once trout have been overfished, carp might exploit the change in competitive equilibria and take over in a way that makes it impossible for the trout to re-establish a breeding population.

Since the growth of global fishing enterprises after the 1950s, intensive fishing has spread from a few concentrated areas to encompass nearly all fisheries. The scraping of the ocean floor in bottom dragging is devastating to coral, sponges and other slower-growing benthic species that do not recover quickly, and that provide a habitat for commercial fisheries species. This destruction alters the functioning of the ecosystem and can permanently alter species' composition and biodiversity. Bycatch, the collateral capture of unintended species in the course of fishing, is typically returned to the ocean only to die from injuries or exposure. Bycatch represents about a quarter of all marine catch. In the case of shrimp capture, the bycatch is five times larger than the shrimp caught.

A report by FAO in 2020 stated that "in 2017, 34 percent of the fish stocks of the world's marine fisheries were classified as overfished".[18]: 54  Mitigation options include: Government regulation, removal of subsidies, minimizing fishing impact, aquaculture and consumer awareness.

Ecological disruption edit

Overfishing can result in the over-exploitation of marine ecosystem services.[19] Fishing can cause several negative physiological and psychological effects for fish populations including increased stress levels and bodily injuries resulting from lodged fish hooks.[20] Often, when this threshold is crossed, hysteresis may occur within the environment.[19] More specifically, some ecological disturbances observed within the Black Sea marine ecosystem resulted from a combination of overfishing and various other related human activities which adversely affected the marine environment and ecosystem.[21] Ecological disruption can also occur due to the overfishing of critical fish species such as the tilefish and grouper fish, which can be referred to as ecosystem-engineers.[22]

Fishing may disrupt food webs by targeting specific, in-demand species. There might be too much fishing of prey species such as sardines and anchovies, thus reducing the food supply for the predators. Disrupting these types of wasp-waist species may have effects throughout the ecosystem.[23] It may also cause the increase of prey species when the target fishes are predator species, such as salmon and tuna.

Overfishing and pollution of the oceans also affect their carbon storage ability and thus contribute to the climate crisis.[24][25][26] Carbon stored in seafloor sediments risk release by bottom-trawling fishing.[27][28]

Fisheries-induced evolution edit

Fisheries-induced evolution or evolutionary impact of fishing is the various evolutionary effects of the fishing pressure, such as on size or growth. It is manly caused by selective fishing on size, bigger fish being more frequently caught. Moreover, policy of minimum landing size, based on the idea that it spares young fishes, have many negative impacts on a population by selecting slow growth individuals.

Bycatch edit

 
Bird unintentionally caught as bycatch in drift net

Bycatch is the portion of the catch that is not the target species.[29] Unintentional bycatch occurs when fishing gear with poor selectivity is used.[29] These are either kept to be sold or discarded. In some instances the discarded portion is known as discards. Even sports fisherman discard a lot of non-target and target fish on the bank while fishing. For every pound of the target species caught, up to 5 pounds of unintended marine species are caught and discarded as bycatch.[30] As many as 40% (63 billion pounds) of fish caught globally every year are discarded, and as many as 650,000 whales, dolphins and seals are killed every year by fishing vessels.[31][32]

Shark finning and culling edit

Shark finning edit

Shark finning is the act of removing fins from sharks and discarding the rest of the shark. The sharks are often still alive when discarded, but without their fins.[33][34] Unable to swim effectively, they sink to the bottom of the ocean and die of suffocation or are eaten by other predators.[35] Though studies suggest that 73 million sharks are finned each year,[36] scientists have noted that the numbers may actually be higher, with roughly 100 million sharks being killed by finning each year.[37] The deaths of millions of sharks has caused catastrophic damage to the marine ecosystem.[36]

Shark culling edit

Shark culling is the killing of sharks in government-run "shark control" programs.[38] These programs exist to reduce the risk of shark attacks — however, environmentalists say that they do not reduce the risk of shark attacks; they also say that shark culling harms the marine ecosystem.[39][40] Shark culling currently occurs in New South Wales, Queensland, KwaZulu-Natal and Réunion.[40][41][42] Queensland's "shark control" program killed roughly 50,000 sharks between 1962 and 2018 — Queensland's program uses lethal devices such as shark nets and drum lines.[43][40] Thousands of other animals, such as turtles and dolphins, have been killed in Queensland as bycatch.[44] Queensland's shark culling program has been called "outdated, cruel and ineffective".[45] The shark culling program in New South Wales (which uses nets) has killed thousands of sharks, turtles, dolphins and whales.[40] KwaZulu-Natal's shark culling program killed more than 33,000 sharks in a 30-year period.[41]

Marine debris edit

 
Turtle entangled in marine debris

Recent research has shown that, by mass, fishing debris, such as buoys, lines, and nets, account for more than two-thirds of large plastic debris found in the oceans.[46] In the Great Pacific Garbage Patch, fishing nets alone comprise at least 46% of the debris.[47] Similarly, fishing debris has been shown to be a major source of plastic debris found on the shores of Korea.[48] Marine life interacts with debris in two ways: either through entanglement (where debris entangles or entraps animals), or ingestion of the debris (either intentionally or accidentally).[49] Both are harmful to the animal.[49] Marine debris consisting of old fishing nets or trawls can often be linked to phenomena such as ghost fishing, wherein the netting debris, referred to as ghost nets, continues to entangle and capture fish.[50] A study performed in southern Japan on octopuses noted that there was an estimated mortality rate of 212,000–505,000 octopuses per year within the area's fishing grounds, due in large part to ghost fishing.[51] Tracking garbage and monitoring the logistics of human waste disposal, especially waste materials primarily associated with fishing, is one method to reduce marine debris.[50][52] Using technological or mechanical innovations such as marine debris-clearing drones can further serve to reduce the amount of debris within oceans.[50][52]

Recreational fishing impacts edit

Recreational fishing is fishing done for sport or competition, whereas commercial fishing is catching seafood, often in mass quantities, for profit. Both can have different environmental impacts when it comes to fishing.[53]

Though many assume recreational fishing does not have a large impact on fish, it actually accounts for almost a quarter of the fish caught in the United States, many of those being commercially valuable fish.[54] Recreational fishing has its biggest impact on marine debris, overfishing, and fish mortality. Release mortality in recreational fisheries is the same as the impacts of bycatch in commercial fisheries.[53] Studies have suggested that improving recreational fisheries management on a global scale could generate substantial social benefits of the same scale as reforming commercial fisheries.[55]

Catch and Release edit

Catch and release fishing involves several practices that aim to reduce the negative environmental impacts of fishing.[20] This refers to the duration, timing, and type of hook used during angling.[20] To increase the effectiveness of catch and release fishing and mitigate its negative impacts, species-specific guidelines are required.[20] These guidelines help tailor specific rules and regulations to specific species of fish in relation to their locations and mating and migration cycles.[20] A metastudy in 2005 found that the average catch and release mortality rate was 18%, but varied greatly by species.[56] While catch-and-release fishing has been wildly used in recreational fishing, it is also beneficial for maintaining fish populations at a stable level for commercial fisheries to receive social and economic benefits.[57] Combining catch and release fishing with biotelemetry data collection methods allows for researchers to study the biological effects of catch and release fishing on fish in order to better suit future conservation efforts and remedies.[57]

Countermeasures edit

Fisheries management edit

Much of the scientific community blames the mismanagement of fisheries for global collapses of fish populations.[58] One method for increasing fish population numbers and reduce the severity of adverse environmental impacts and ecological disturbances is the use of fisheries management systems.[59] Traditional fisheries management techniques can signify restricting certain types of fishing gear, reducing the total allowable catch, decreasing fishing efforts as a whole, implementing catch shares, involving communities with conservation efforts and defining areas closed to fishing.[59][60] In order to implement any of these tactics on a fishery, ample data collection and statistical analysis are necessary.[59]

Whether or not traditional fisheries management techniques are effective at restoring fish populations is often seen as a debate in the fisheries science community.[59] However, there are a few factors to consider when evaluating the efficiency of fisheries management techniques.[59] For example, large fisheries are more likely to be managed whereas small fisheries are commonly left unassessed and unmanaged.[59] Unassessed fisheries are thought to represent about 80% of all fisheries.[61] Some researchers believe that the stability and health of these unassessed fisheries are worse than the assessed fisheries, justifying the premise that traditional fisheries management techniques are ineffective.[61] However, many scientists highlight that those fish populations are declining due to the fact that they have not been assessed and therefore adequate fisheries management techniques have not been applied.[58][59] Further, most of the assessed fisheries (and hence managed fisheries) are biased towards large populations and commercially lucrative species.[59] Assessments are often performed by nations that are able to afford the assessment process and implementation of fisheries management tools.[59]

Determining sustainable harvest quotas are another example of a traditional fisheries management technique.[58] However, the intention behind harvest quotas are often not a big enough incentive for fishermen to adhere to them.[58] This is because limiting individual harvests often leads to a smaller profit for the fleet.[58] Since these fishermen are not guaranteed compensation for part of the quota, they tend to resolve to the method of harvesting as many fish as possible.[58] This competitiveness among fishermen and their fleets leads to the increased use of harmful fishing practices, extremely large harvests, periods of reduced stocks and the eventual collapse of the fishery.[58] To eliminate the need for such competitiveness among fishermen, many scientists suggest the implementation of rights-based fisheries reforms.[59][58] This can be done by granting Individual Transferable Quotas (ITQs) or catch shares, a set portion of a scientifically calculated total allowable catch, to individual fishermen, communities and cooperatives.[58] ITQs incentivize fishermen because the value of catch shares grows as the stability of the fishery improves.[58]

It is estimated that around 27% of global fisheries were classified as collapsed in 2003 and that by 2048, 100% of global fisheries would be considered collapsed.[62] In a study compiling data from 11,135 fisheries around the world (some ITQ-managed, some non-ITQ managed), the potential impact of ITQs on fisheries if they all implemented a rights-based management approach since 1970 was estimated.[58] In that case, the percentage of collapsed fisheries in 2003 was projected as 9%, which remained fairly stable for the rest of the experiment's time period.[58] Despite the projected success of the ITQ-managed fisheries, the results of this study may not be a completely accurate representation of the true impact of right-based management.[58] This is due to the fact that the data used to create these results was limited to one type of catch share and that the true effects of ITQs can only be assessed if social, ecological and economic factors were also considered.[58]

In some cases, changing fishing gear can have an impact on habitat destruction.[63] In an experiment with three different types of gears used for oyster harvesting, compared to dredging and tonging, hand-harvesting by divers resulted in the collection of 25-32% more oysters within the same amount of time.[63] In terms of habitat conservation, the reef habitat sustained damage to its height during the use of all three gear types.[63] Specifically, dredging cut the height of the reef by 34%, tonging by 23% and diver hand-harvesting by 6%.[63]

 
A 9/0 J hook and a 18/0 circle hook.

Opting for a different hook design or bait type can make fishing practices less dangerous and lead to less bycatch.[64] Using 18/0 circle hooks and mackerel for bait has been shown to greatly reduce the amount of leatherback sea turtles and loggerheads caught as bycatch.[64] The use of circle hooks was shown to decrease the amount of hooks ingested by loggerheads.[64] Further, with the target species being swordfish, the use of both circle hooks and mackerel for bait had no negative impact on the amount of swordfish caught.[64]

Ecosystem-based management of fisheries is another method used for fish conservation and impact remediation.[59][61] Instead of solely focusing conservation efforts on a single species of marine life, ecosystem-based management is used across various species of fish within an environment.[59][61] To improve the adoption of these types of fisheries management, it is important to reduce barriers to entry for management scenarios in order to make these methods more accessible to fisheries globally.[59]

Many governments and intergovernmental bodies have implemented fisheries management policies designed to curb the environmental impact of fishing. Fishing conservation aims to control the human activities that may completely decrease a fish stock or washout an entire aquatic environment. These laws include the quotas on the total catch of particular species in a fishery, effort quotas (e.g., number of days at sea), the limits on the number of vessels allowed in specific areas, and the imposition of seasonal restrictions on fishing.

Fish farming edit

 
Fish farm near Amarynthos Euboea Greece

Fish farming, aquaculture, or pisciculture, has been proposed as a more sustainable alternative or as a supplement to the traditional capture of wild fish.[65] Fish farms are usually located in coastal waters and can involve netpens or cages that are anchored to the sediment at the bottom.[65] As many fisheries have been heavily depleted, farming profitable and commonly consumed fish species is a method used to supply larger quantities of seafood for human consumption.[65] This is especially the case for marine aquatic species such as salmon and shrimp [65] and freshwater species such as carp and tilapia.[66] In fact, approximately 40% of seafood consumed by humans is produced in fish farms.[65]

Even though fish farming does not require a lot of space, they can have significant ecological impacts on the fish around them and marine resources.[65] For instance, low trophic level, wild caught fish like anchovies, capelin and sardines are used to feed marine and freshwater farmed fish.[67] Farmed marine fish species, usually carnivores, tend require more fishmeal and fish oil to thrive.[66] On the opposite end, farmed freshwater fish, usually herbivores and omnivores, are not as dependent on them.[66] This can be problematic because the small fish used for the production of fishmeal also serve as food for predators living outside the enclosures.[65]

It is not uncommon for farmed fish to escape their enclosures.[65][68] This can lead to the introduction of non-native species to a new environment.[68] Farmed species breeding with wild fish species of the same type, called interbreeding, can cause offspring to have reduced fitness.[68]

Marine reserves edit

Marine reserves serve to foster both environmental protection and marine wildlife safety.[69] The reserves themselves are established via environmental protection plans or policies which designate a specific marine environment as protected.[69] Coral reefs are one of the many examples which involve the application of marine reserves in establishing marine protected areas.[69] There have also been marine reserve initiatives located in the United States, Caribbean, Philippines and Egypt.[69] To mitigate the negative environmental impacts of fishing within marine environments, marine reserves are intended to create, enhance and re-introduce biodiversity within the area.[69][70] As a result, the primary benefits arising from the implementation of this type of management effort include positive impacts towards habitat protection and species conservation.[69]

See also edit

Books:

Related:

References edit

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Further reading edit

  • Castro, P. and M. Huber. (2003). Marine Biology. 4thed. Boston: McGraw Hill.
  • Hampton, J.; Sibert, J. R.; Kleiber, P.; Maunder, M. N.; Harley, S. J. (2005). "Changes in abundance of large pelagic predators in the Pacific Ocean". Nature. 434: E2–E3.
  • Maunder, M.N.; Sibert, J.R.; Fonteneau, A.; Hampton, J.; Kleiber, P.; Harley, S. (2006). "Interpreting catch-per-unit-of-effort data to assess the status of individual stocks and communities". ICES Journal of Marine Science. 63 (8): 1373–1385. doi:10.1016/j.icesjms.2006.05.008.
  • Myers, Ransom; Worm, Boris (2003). "Rapid worldwide depletion of predatory fish communities". Nature. 423 (6937): 280–3. Bibcode:2003Natur.423..280M. doi:10.1038/nature01610. PMID 12748640. S2CID 2392394.
  • Polacheck, T (2006). "Tuna longline catch rates in the Indian Ocean: did industrial fishing result in a 90% rapid decline in the abundance of large predatory species?". Marine Policy. 30 (5): 470–482. doi:10.1016/j.marpol.2005.06.016.
  • FAO Fisheries Department. (2002). The State of World Fisheries and Aquaculture. Rome: Food and Agriculture Organization of the United Nations.
  • Sibert; et al. (2006). "Biomass, Size, and Trophic Status of Top Predators in the Pacific Ocean". Science. 314 (5806): 1773–1776. Bibcode:2006Sci...314.1773S. doi:10.1126/science.1135347. PMID 17170304. S2CID 7449502.
  • Walters, C. J. (2003). "Folly and fantasy in the analysis of spatial catch rate data". Canadian Journal of Fisheries and Aquatic Sciences. 60 (12): 1433–1436. doi:10.1139/f03-152. S2CID 16062938.

External links edit

  • Pelagic Fisheries Research Program
  • International Collective in Support of Fishworkers website
  • United Nations conference in criticism of deep-sea trawling
  • UK Database of commercially sold fish with stock status
  • Conservation Science Institute
  • Global Fishing Fleets Project Regeneration

environmental, impact, fishing, environmental, impact, fishing, includes, issues, such, availability, fish, overfishing, fisheries, fisheries, management, well, impact, industrial, fishing, other, elements, environment, such, bycatch, these, issues, part, mari. The environmental impact of fishing includes issues such as the availability of fish overfishing fisheries and fisheries management as well as the impact of industrial fishing on other elements of the environment such as bycatch 1 These issues are part of marine conservation and are addressed in fisheries science programs According to a 2019 FAO report global production of fish crustaceans molluscs and other aquatic animals has continued to grow and reached 172 6 million tonnes in 2017 with an increase of 4 1 percent compared with 2016 2 There is a growing gap between the supply of fish and demand due in part to world population growth 3 Fishing down the food webGreenhouse gas emissions kg kg edible weight of wild caught and farmed seafood productsFishing and pollution from fishing are the largest contributors to the decline in ocean health and water quality Ghost nets or nets abandoned in the ocean are made of plastic and nylon and do not decompose wreaking extreme havoc on the wildlife and ecosystems they interrupt The ocean takes up 70 of the earth so overfishing and hurting the marine environment affects everyone and everything on this planet On top of the overfishing there is a seafood shortage resulting from the mass amounts of seafood waste as well as the microplastics that are polluting the seafood consumed by the public The latter is largely caused by plastic made fishing gear like drift nets and longlining equipment that are wearing down by use lost or thrown away 4 5 The journal Science published a four year study in November 2006 which predicted that at prevailing trends the world would run out of wild caught seafood in 2048 The scientists stated that the decline was a result of overfishing pollution and other environmental factors that were reducing the population of fisheries at the same time as their ecosystems were being annihilated Many countries such as Tonga the United States Australia and Bahamas and international management bodies have taken steps to appropriately manage marine resources 6 7 Reefs are also being destroyed by overfishing because of the huge nets that are dragged along the ocean floor while trawling Many corals are being destroyed and as a consequence the ecological niche of many species is at stake Mean greenhouse gas emissions for different food types 8 Food types Greenhouse gas emissions g CO2 Ceq per g protein Beef 62Recirculating aquaculture 30Trawling fishery 26Non recirculating aquaculture 12Pork 10Poultry 10Dairy 9 1Non trawling fishery 8 6Eggs 6 8Starchy roots 1 7Wheat 1 2Maize 1 2Legumes 0 25 Contents 1 Effects on marine habitat 2 Overfishing 3 Ecological disruption 4 Fisheries induced evolution 5 Bycatch 6 Shark finning and culling 6 1 Shark finning 6 2 Shark culling 7 Marine debris 8 Recreational fishing impacts 8 1 Catch and Release 9 Countermeasures 9 1 Fisheries management 9 2 Fish farming 9 3 Marine reserves 10 See also 11 References 12 Further reading 13 External linksEffects on marine habitat editMain articles Blast fishing Cyanide fishing Bottom trawling and Ghost net nbsp A sea turtle killed by a boat propellerSome fishing techniques cause habitat destruction 9 10 Blast fishing and cyanide fishing which are illegal in many places harm surrounding habitats 9 Blast fishing refers to the practice of using explosives to capture fish 9 Cyanide fishing refers to the practice of using cyanide to stun fish for collection 9 These two practices are commonly used for the aquarium trade and the live fish food trade 9 These practices are destructive because they impact the habitat that the reef fish live on after the fish have been removed Bottom trawling the practice of pulling a fishing net along the sea bottom behind trawlers removes around 5 to 25 of an area s seabed life on a single run 11 This method of fishing tends to cause a lot of bycatch 10 A study of La Fonera Canyon compared trawled versus non trawled areas The results show that areas at 500 to 2000 meters depth that is non trawled have more biodiversity biomass and variation of meiofauna than trawled areas at 500 meters depth 12 Most of the impacts are due to commercial fishing practices 13 A 2005 report of the UN Millennium Project commissioned by UN Secretary General Kofi Annan recommended the elimination of bottom trawling on the high seas by 2006 to protect seamounts and other ecologically sensitive habitats This was not done In mid October 2006 United States President George W Bush joined other world leaders calling for a moratorium on deep sea trawling The practice has shown to often have harmful effects on sea habitat and hence on fish populations 14 yet no further action was taken Vivek The sea animal s aquatic ecosystem may also collapse due to the destruction of the food chain Additionally ghost fishing is a major threat due to capture fisheries 15 Ghost fishing occurs when a net such as a gill net or trawl is lost or discarded at sea and drifts within the oceans and can still act to capture marine organisms 15 According to the FAO Code of Conduct for Responsible Fisheries States should act to minimize the amount of lost and abandoned gear and work to minimize ghost fishing 16 Overfishing editThis section is an excerpt from Overfishing edit nbsp Jack mackerel caught by a Chilean purse seiner nbsp Fishing down the food webOverfishing is the removal of a species of fish i e fishing from a body of water at a rate greater than that the species can replenish its population naturally i e the overexploitation of the fishery s existing fish stock resulting in the species becoming increasingly underpopulated in that area Overfishing can occur in water bodies of any sizes such as ponds wetlands rivers lakes or oceans and can result in resource depletion reduced biological growth rates and low biomass levels Sustained overfishing can lead to critical depensation where the fish population is no longer able to sustain itself Some forms of overfishing such as the overfishing of sharks has led to the upset of entire marine ecosystems 17 Types of overfishing include growth overfishing recruitment overfishing ecosystem overfishing The ability of a fishery to recover from overfishing depends on whether its overall carrying capacity and the variety of ecological conditions are suitable for the recovery Dramatic changes in species composition can result in an ecosystem shift where other equilibrium energy flows involve species compositions different from those that had been present before the depletion of the original fish stock For example once trout have been overfished carp might exploit the change in competitive equilibria and take over in a way that makes it impossible for the trout to re establish a breeding population Since the growth of global fishing enterprises after the 1950s intensive fishing has spread from a few concentrated areas to encompass nearly all fisheries The scraping of the ocean floor in bottom dragging is devastating to coral sponges and other slower growing benthic species that do not recover quickly and that provide a habitat for commercial fisheries species This destruction alters the functioning of the ecosystem and can permanently alter species composition and biodiversity Bycatch the collateral capture of unintended species in the course of fishing is typically returned to the ocean only to die from injuries or exposure Bycatch represents about a quarter of all marine catch In the case of shrimp capture the bycatch is five times larger than the shrimp caught A report by FAO in 2020 stated that in 2017 34 percent of the fish stocks of the world s marine fisheries were classified as overfished 18 54 Mitigation options include Government regulation removal of subsidies minimizing fishing impact aquaculture and consumer awareness Ecological disruption editOverfishing can result in the over exploitation of marine ecosystem services 19 Fishing can cause several negative physiological and psychological effects for fish populations including increased stress levels and bodily injuries resulting from lodged fish hooks 20 Often when this threshold is crossed hysteresis may occur within the environment 19 More specifically some ecological disturbances observed within the Black Sea marine ecosystem resulted from a combination of overfishing and various other related human activities which adversely affected the marine environment and ecosystem 21 Ecological disruption can also occur due to the overfishing of critical fish species such as the tilefish and grouper fish which can be referred to as ecosystem engineers 22 Fishing may disrupt food webs by targeting specific in demand species There might be too much fishing of prey species such as sardines and anchovies thus reducing the food supply for the predators Disrupting these types of wasp waist species may have effects throughout the ecosystem 23 It may also cause the increase of prey species when the target fishes are predator species such as salmon and tuna Overfishing and pollution of the oceans also affect their carbon storage ability and thus contribute to the climate crisis 24 25 26 Carbon stored in seafloor sediments risk release by bottom trawling fishing 27 28 Fisheries induced evolution editMain article Fisheries induced evolution Fisheries induced evolution or evolutionary impact of fishing is the various evolutionary effects of the fishing pressure such as on size or growth It is manly caused by selective fishing on size bigger fish being more frequently caught Moreover policy of minimum landing size based on the idea that it spares young fishes have many negative impacts on a population by selecting slow growth individuals Bycatch editMain article Bycatch nbsp Bird unintentionally caught as bycatch in drift netBycatch is the portion of the catch that is not the target species 29 Unintentional bycatch occurs when fishing gear with poor selectivity is used 29 These are either kept to be sold or discarded In some instances the discarded portion is known as discards Even sports fisherman discard a lot of non target and target fish on the bank while fishing For every pound of the target species caught up to 5 pounds of unintended marine species are caught and discarded as bycatch 30 As many as 40 63 billion pounds of fish caught globally every year are discarded and as many as 650 000 whales dolphins and seals are killed every year by fishing vessels 31 32 Shark finning and culling editShark finning edit Main article Shark finning Shark finning is the act of removing fins from sharks and discarding the rest of the shark The sharks are often still alive when discarded but without their fins 33 34 Unable to swim effectively they sink to the bottom of the ocean and die of suffocation or are eaten by other predators 35 Though studies suggest that 73 million sharks are finned each year 36 scientists have noted that the numbers may actually be higher with roughly 100 million sharks being killed by finning each year 37 The deaths of millions of sharks has caused catastrophic damage to the marine ecosystem 36 Shark culling edit Main article Shark culling Shark culling is the killing of sharks in government run shark control programs 38 These programs exist to reduce the risk of shark attacks however environmentalists say that they do not reduce the risk of shark attacks they also say that shark culling harms the marine ecosystem 39 40 Shark culling currently occurs in New South Wales Queensland KwaZulu Natal and Reunion 40 41 42 Queensland s shark control program killed roughly 50 000 sharks between 1962 and 2018 Queensland s program uses lethal devices such as shark nets and drum lines 43 40 Thousands of other animals such as turtles and dolphins have been killed in Queensland as bycatch 44 Queensland s shark culling program has been called outdated cruel and ineffective 45 The shark culling program in New South Wales which uses nets has killed thousands of sharks turtles dolphins and whales 40 KwaZulu Natal s shark culling program killed more than 33 000 sharks in a 30 year period 41 Marine debris editMain article Marine debris nbsp Turtle entangled in marine debrisRecent research has shown that by mass fishing debris such as buoys lines and nets account for more than two thirds of large plastic debris found in the oceans 46 In the Great Pacific Garbage Patch fishing nets alone comprise at least 46 of the debris 47 Similarly fishing debris has been shown to be a major source of plastic debris found on the shores of Korea 48 Marine life interacts with debris in two ways either through entanglement where debris entangles or entraps animals or ingestion of the debris either intentionally or accidentally 49 Both are harmful to the animal 49 Marine debris consisting of old fishing nets or trawls can often be linked to phenomena such as ghost fishing wherein the netting debris referred to as ghost nets continues to entangle and capture fish 50 A study performed in southern Japan on octopuses noted that there was an estimated mortality rate of 212 000 505 000 octopuses per year within the area s fishing grounds due in large part to ghost fishing 51 Tracking garbage and monitoring the logistics of human waste disposal especially waste materials primarily associated with fishing is one method to reduce marine debris 50 52 Using technological or mechanical innovations such as marine debris clearing drones can further serve to reduce the amount of debris within oceans 50 52 Recreational fishing impacts editMain article Recreational fishing Recreational fishing is fishing done for sport or competition whereas commercial fishing is catching seafood often in mass quantities for profit Both can have different environmental impacts when it comes to fishing 53 Though many assume recreational fishing does not have a large impact on fish it actually accounts for almost a quarter of the fish caught in the United States many of those being commercially valuable fish 54 Recreational fishing has its biggest impact on marine debris overfishing and fish mortality Release mortality in recreational fisheries is the same as the impacts of bycatch in commercial fisheries 53 Studies have suggested that improving recreational fisheries management on a global scale could generate substantial social benefits of the same scale as reforming commercial fisheries 55 Catch and Release edit Catch and release fishing involves several practices that aim to reduce the negative environmental impacts of fishing 20 This refers to the duration timing and type of hook used during angling 20 To increase the effectiveness of catch and release fishing and mitigate its negative impacts species specific guidelines are required 20 These guidelines help tailor specific rules and regulations to specific species of fish in relation to their locations and mating and migration cycles 20 A metastudy in 2005 found that the average catch and release mortality rate was 18 but varied greatly by species 56 While catch and release fishing has been wildly used in recreational fishing it is also beneficial for maintaining fish populations at a stable level for commercial fisheries to receive social and economic benefits 57 Combining catch and release fishing with biotelemetry data collection methods allows for researchers to study the biological effects of catch and release fishing on fish in order to better suit future conservation efforts and remedies 57 Countermeasures editFisheries management edit Main article Fisheries management This section may be too long to read and navigate comfortably Please consider splitting content into sub articles condensing it or adding subheadings Please discuss this issue on the article s talk page May 2023 Much of the scientific community blames the mismanagement of fisheries for global collapses of fish populations 58 One method for increasing fish population numbers and reduce the severity of adverse environmental impacts and ecological disturbances is the use of fisheries management systems 59 Traditional fisheries management techniques can signify restricting certain types of fishing gear reducing the total allowable catch decreasing fishing efforts as a whole implementing catch shares involving communities with conservation efforts and defining areas closed to fishing 59 60 In order to implement any of these tactics on a fishery ample data collection and statistical analysis are necessary 59 Whether or not traditional fisheries management techniques are effective at restoring fish populations is often seen as a debate in the fisheries science community 59 However there are a few factors to consider when evaluating the efficiency of fisheries management techniques 59 For example large fisheries are more likely to be managed whereas small fisheries are commonly left unassessed and unmanaged 59 Unassessed fisheries are thought to represent about 80 of all fisheries 61 Some researchers believe that the stability and health of these unassessed fisheries are worse than the assessed fisheries justifying the premise that traditional fisheries management techniques are ineffective 61 However many scientists highlight that those fish populations are declining due to the fact that they have not been assessed and therefore adequate fisheries management techniques have not been applied 58 59 Further most of the assessed fisheries and hence managed fisheries are biased towards large populations and commercially lucrative species 59 Assessments are often performed by nations that are able to afford the assessment process and implementation of fisheries management tools 59 Determining sustainable harvest quotas are another example of a traditional fisheries management technique 58 However the intention behind harvest quotas are often not a big enough incentive for fishermen to adhere to them 58 This is because limiting individual harvests often leads to a smaller profit for the fleet 58 Since these fishermen are not guaranteed compensation for part of the quota they tend to resolve to the method of harvesting as many fish as possible 58 This competitiveness among fishermen and their fleets leads to the increased use of harmful fishing practices extremely large harvests periods of reduced stocks and the eventual collapse of the fishery 58 To eliminate the need for such competitiveness among fishermen many scientists suggest the implementation of rights based fisheries reforms 59 58 This can be done by granting Individual Transferable Quotas ITQs or catch shares a set portion of a scientifically calculated total allowable catch to individual fishermen communities and cooperatives 58 ITQs incentivize fishermen because the value of catch shares grows as the stability of the fishery improves 58 It is estimated that around 27 of global fisheries were classified as collapsed in 2003 and that by 2048 100 of global fisheries would be considered collapsed 62 In a study compiling data from 11 135 fisheries around the world some ITQ managed some non ITQ managed the potential impact of ITQs on fisheries if they all implemented a rights based management approach since 1970 was estimated 58 In that case the percentage of collapsed fisheries in 2003 was projected as 9 which remained fairly stable for the rest of the experiment s time period 58 Despite the projected success of the ITQ managed fisheries the results of this study may not be a completely accurate representation of the true impact of right based management 58 This is due to the fact that the data used to create these results was limited to one type of catch share and that the true effects of ITQs can only be assessed if social ecological and economic factors were also considered 58 In some cases changing fishing gear can have an impact on habitat destruction 63 In an experiment with three different types of gears used for oyster harvesting compared to dredging and tonging hand harvesting by divers resulted in the collection of 25 32 more oysters within the same amount of time 63 In terms of habitat conservation the reef habitat sustained damage to its height during the use of all three gear types 63 Specifically dredging cut the height of the reef by 34 tonging by 23 and diver hand harvesting by 6 63 nbsp A 9 0 J hook and a 18 0 circle hook Opting for a different hook design or bait type can make fishing practices less dangerous and lead to less bycatch 64 Using 18 0 circle hooks and mackerel for bait has been shown to greatly reduce the amount of leatherback sea turtles and loggerheads caught as bycatch 64 The use of circle hooks was shown to decrease the amount of hooks ingested by loggerheads 64 Further with the target species being swordfish the use of both circle hooks and mackerel for bait had no negative impact on the amount of swordfish caught 64 Ecosystem based management of fisheries is another method used for fish conservation and impact remediation 59 61 Instead of solely focusing conservation efforts on a single species of marine life ecosystem based management is used across various species of fish within an environment 59 61 To improve the adoption of these types of fisheries management it is important to reduce barriers to entry for management scenarios in order to make these methods more accessible to fisheries globally 59 Many governments and intergovernmental bodies have implemented fisheries management policies designed to curb the environmental impact of fishing Fishing conservation aims to control the human activities that may completely decrease a fish stock or washout an entire aquatic environment These laws include the quotas on the total catch of particular species in a fishery effort quotas e g number of days at sea the limits on the number of vessels allowed in specific areas and the imposition of seasonal restrictions on fishing Fish farming edit Main article Fish farming nbsp Fish farm near Amarynthos Euboea GreeceFish farming aquaculture or pisciculture has been proposed as a more sustainable alternative or as a supplement to the traditional capture of wild fish 65 Fish farms are usually located in coastal waters and can involve netpens or cages that are anchored to the sediment at the bottom 65 As many fisheries have been heavily depleted farming profitable and commonly consumed fish species is a method used to supply larger quantities of seafood for human consumption 65 This is especially the case for marine aquatic species such as salmon and shrimp 65 and freshwater species such as carp and tilapia 66 In fact approximately 40 of seafood consumed by humans is produced in fish farms 65 Even though fish farming does not require a lot of space they can have significant ecological impacts on the fish around them and marine resources 65 For instance low trophic level wild caught fish like anchovies capelin and sardines are used to feed marine and freshwater farmed fish 67 Farmed marine fish species usually carnivores tend require more fishmeal and fish oil to thrive 66 On the opposite end farmed freshwater fish usually herbivores and omnivores are not as dependent on them 66 This can be problematic because the small fish used for the production of fishmeal also serve as food for predators living outside the enclosures 65 It is not uncommon for farmed fish to escape their enclosures 65 68 This can lead to the introduction of non native species to a new environment 68 Farmed species breeding with wild fish species of the same type called interbreeding can cause offspring to have reduced fitness 68 Marine reserves edit Further information Marine protected area Marine reserves serve to foster both environmental protection and marine wildlife safety 69 The reserves themselves are established via environmental protection plans or policies which designate a specific marine environment as protected 69 Coral reefs are one of the many examples which involve the application of marine reserves in establishing marine protected areas 69 There have also been marine reserve initiatives located in the United States Caribbean Philippines and Egypt 69 To mitigate the negative environmental impacts of fishing within marine environments marine reserves are intended to create enhance and re introduce biodiversity within the area 69 70 As a result the primary benefits arising from the implementation of this type of management effort include positive impacts towards habitat protection and species conservation 69 See also editFinless Foods Population dynamics of fisheries List of harvested aquatic animals by weight Shark culling Shark finning Sustainable seafood Marine debris Individual fishing quota Destructive fishing practicesBooks The End of the Line How Overfishing Is Changing the World and What We Eat book One Fish Two Fish Crawfish Bluefish book Related Environmental effects of meat production Human impact on the environmentReferences edit Frouz Jan Frouzova Jaroslava 2022 Applied Ecology doi 10 1007 978 3 030 83225 4 ISBN 978 3 030 83224 7 S2CID 245009867 Food and Agriculture Organization of the United Nations FAO 2019 Fishery and Aquaculture Statistics 2017 PDF Archived PDF from the original on 2019 10 26 Global population growth wild fish stocks and the future of aquaculture Shark Research amp Conservation Program SRC University of Miami sharkresearch rsmas miami edu Retrieved 2018 04 02 Laville Sandra 2019 11 06 Dumped fishing gear is biggest plastic polluter in ocean finds report The Guardian Retrieved 2022 05 10 Magazine Smithsonian Kindy David With Ropes and Nets Fishing Fleets Contribute Significantly to Microplastic Pollution Smithsonian Magazine Retrieved 2022 05 10 Worm Boris et al 2006 11 03 Impacts of Biodiversity Loss on Ocean Ecosystem Services Science 314 5800 787 790 Bibcode 2006Sci 314 787W doi 10 1126 science 1132294 PMID 17082450 S2CID 37235806 Juliet Eilperin 2 November 2006 Seafood Population Depleted by 2048 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World Fisheries and Aquaculture 2020 FAO 2020 doi 10 4060 ca9229en hdl 10535 3776 ISBN 978 92 5 132692 3 S2CID 242949831 a b Daskalov Georgi M Grishin Alexander N Rodionov Sergei Mihneva Vesselina 2007 06 19 Trophic cascades triggered by overfishing reveal possible mechanisms of ecosystem regime shifts Proceedings of the National Academy of Sciences 104 25 10518 10523 Bibcode 2007PNAS 10410518D doi 10 1073 pnas 0701100104 PMC 1965545 PMID 17548831 a b c d e Cooke Steven J Suski Cory D 2005 05 01 Do we need species specific guidelines for catch and release recreational angling to effectively conserve diverse fishery resources Biodiversity amp Conservation 14 5 1195 1209 doi 10 1007 s10531 004 7845 0 ISSN 0960 3115 S2CID 16894387 Daskalov Georgi M 2002 Overfishing drives a trophic cascade in the Black Sea Marine Ecology Progress Series 225 53 63 Bibcode 2002MEPS 225 53D doi 10 3354 meps225053 ISSN 0171 8630 Coleman Felicia C Williams Susan L 2002 Overexploiting marine ecosystem engineers 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PMID 19528053 a b J Cooke Steven G Cowx Ian 2004 09 01 The Role of Recreational Fishing in Global Fish Crises BioScience 54 9 857 doi 10 1641 0006 3568 2004 054 0857 TRORFI 2 0 CO 2 ISSN 0006 3568 a href Template Cite journal html title Template Cite journal cite journal a CS1 maint multiple names authors list link Study In Science Reveals Recreational Fishing Takes Big Bite Of Ocean Catch ScienceDaily Retrieved 2018 04 02 Joshua K Abbott Patrick Lloyd Smith Daniel Willard and Wiktor Adamowicz September 4 2018 Status quo management of marine recreational fisheries undermines angler welfare PNAS 115 36 8948 8953 Bibcode 2018PNAS 115 8948A doi 10 1073 pnas 1809549115 PMC 6130401 PMID 30127021 a href Template Cite journal html title Template Cite journal cite journal a CS1 maint multiple names authors list link Bartholomew Aaron Bohnsack James A 2005 02 01 A Review of Catch and Release Angling Mortality with Implications for No take Reserves Reviews in Fish Biology and Fisheries 15 1 129 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325 578W doi 10 1126 science 1173146 hdl 11336 100063 ISSN 0036 8075 PMID 19644114 S2CID 2805799 a b c d Pikitch Ellen K 2012 10 26 The Risks of Overfishing Science 338 6106 474 475 Bibcode 2012Sci 338 474P doi 10 1126 science 1229965 ISSN 0036 8075 PMID 23112316 S2CID 206545165 Worm Boris Hilborn Ray Baum Julia K Branch Trevor A Collie Jeremy S Costello Christopher Fogarty Michael J Fulton Elizabeth A Hutchings Jeffrey A Jennings Simon Jensen Olaf P Lotze Heike K Mace Pamela M McClanahan Tim R Minto Coilin 2009 07 31 Rebuilding Global Fisheries Science 325 5940 578 585 Bibcode 2009Sci 325 578W doi 10 1126 science 1173146 hdl 11336 100063 ISSN 0036 8075 PMID 19644114 S2CID 2805799 a b c d Lenihan Hunter S Peterson Charles H 2004 How Habitat Degradation Through Fishery Disturbance Enhances Impacts of Hypoxia on Oyster Reefs Fishery Bulletin 102 2 298 doi 10 1890 1051 0761 1998 008 0128 hhdtfd 2 0 co 2 ISSN 1051 0761 a b c d Watson John W Epperly Sheryan P Shah Arvind K Foster Daniel G 2005 05 01 Fishing methods to reduce sea turtle mortality associated with pelagic longlines Canadian Journal of Fisheries and Aquatic Sciences 62 5 965 981 doi 10 1139 f05 004 ISSN 0706 652X a b c d e f g h Goldburg Rebecca Naylor Rosamond February 2005 Future seascapes fishing and fish farming Frontiers in Ecology and the Environment 3 1 21 28 doi 10 1890 1540 9295 2005 003 0021 fsfaff 2 0 co 2 ISSN 1540 9295 a b c Naylor Rosamond L Goldburg Rebecca J Primavera Jurgenne H Kautsky Nils Beveridge Malcolm C M Clay Jason Folke Carl Lubchenco Jane Mooney Harold Troell Max June 2000 Effect of aquaculture on world fish supplies Nature 405 6790 1017 1024 Bibcode 2000Natur 405 1017N doi 10 1038 35016500 ISSN 0028 0836 PMID 10890435 S2CID 4411053 Tacon AGJ April 2003 Sustainable aquaculture feeds an overview and global perspective SEAfeeds Workshop Stirling Scotland UK a b c McGinnity Philip Prodohl Paulo Ferguson Andy Hynes Rosaleen Maoileidigh Niall o Baker Natalie Cotter Deirdre O Hea Brendan Cooke Declan Rogan Ger Taggart John Cross Tom 2003 12 07 Fitness reduction and potential extinction of wild populations of Atlantic salmon Salmo salar as a result of interactions with escaped farm salmon Proceedings of the Royal Society of London Series B Biological Sciences 270 1532 2443 2450 doi 10 1098 rspb 2003 2520 ISSN 0962 8452 PMC 1691531 PMID 14667333 a b c d e f Roberts Callum M Polunin Nicholas V C 1993 Marine Reserves Simple Solutions to Managing Complex Fisheries Ambio 22 6 363 368 JSTOR 4314106 Aburto Oropeza Octavio Erisman Brad Galland Grantly R Mascarenas Osorio Ismael Sala Enric Ezcurra Exequiel 2011 08 12 Large Recovery of Fish Biomass in a No Take Marine Reserve PLOS ONE 6 8 e23601 Bibcode 2011PLoSO 623601A doi 10 1371 journal pone 0023601 ISSN 1932 6203 PMC 3155316 PMID 21858183 Further reading editCastro P and M Huber 2003 Marine Biology 4thed Boston McGraw Hill Hampton J Sibert J R Kleiber P Maunder M N Harley S J 2005 Changes in abundance of large pelagic predators in the Pacific Ocean Nature 434 E2 E3 Maunder M N Sibert J R Fonteneau A Hampton J Kleiber P Harley S 2006 Interpreting catch per unit of effort data to assess the status of individual stocks and communities ICES Journal of Marine Science 63 8 1373 1385 doi 10 1016 j icesjms 2006 05 008 Myers Ransom Worm Boris 2003 Rapid worldwide depletion of predatory fish communities Nature 423 6937 280 3 Bibcode 2003Natur 423 280M doi 10 1038 nature01610 PMID 12748640 S2CID 2392394 Polacheck T 2006 Tuna longline catch rates in the Indian Ocean did industrial fishing result in a 90 rapid decline in the abundance of large predatory species Marine Policy 30 5 470 482 doi 10 1016 j marpol 2005 06 016 FAO Fisheries Department 2002 The State of World Fisheries and Aquaculture Rome Food and Agriculture Organization of the United Nations Sibert et al 2006 Biomass Size and Trophic Status of Top Predators in the Pacific Ocean Science 314 5806 1773 1776 Bibcode 2006Sci 314 1773S doi 10 1126 science 1135347 PMID 17170304 S2CID 7449502 Walters C J 2003 Folly and fantasy in the analysis of spatial catch rate data Canadian Journal of Fisheries and Aquatic Sciences 60 12 1433 1436 doi 10 1139 f03 152 S2CID 16062938 External links edit nbsp Wikimedia Commons has media related to Environmental impact of fishing Pelagic Fisheries Research Program International Collective in Support of Fishworkers website United Nations conference in criticism of deep sea trawling Bush backs international deep sea trawling moratorium Re interpreting the Fisheries Crisis seminar by Prof Ray Hilborn UK Database of commercially sold fish with stock status Database on stock status of US seafood Conservation Science Institute The facts about the Commercial Fishing Environment Global Fishing Fleets Project Regeneration Retrieved from https en wikipedia org w index php title Environmental impact of fishing amp oldid 1190387384, wikipedia, wiki, book, books, library,

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