Individual fishing quota

Individual fishing quotas (IFQs) also known as "individual transferable quotas" (ITQs) are one kind of catch share, a means by which many governments regulate fishing. The regulator sets a species-specific total allowable catch (TAC), typically by weight and for a given time period. A dedicated portion of the TAC, called quota shares, is then allocated to individuals. Quotas can typically be bought, sold and leased, a feature called transferability. As of 2008, 148 major fisheries (generally, a single species in a single fishing ground) around the world had adopted some variant of this approach,^[1] along with approximately 100 smaller fisheries in individual countries. Approximately 10% of the marine harvest was managed by ITQs as of 2008.^[2]:218 The first countries to adopt individual fishing quotas were the Netherlands, Iceland and Canada in the late 1970s, and the most recent is the United States Scallop General Category IFQ Program in 2010.^[3] The first country to adopt individual transferable quotas as a national policy was New Zealand in 1986.^[4]

Command and control approaches

Historically, inshore and deep water fisheries were in common ownership where no one had a property right to the fish (i.e., owned them) until after they had been caught. Each boat faced the zero-sum game imperative of catching as many fish as possible, knowing that any fish they did not catch would likely be taken by another boat.

Commercial fishing evolved from subsistence fishing with no restrictions that would limit or direct the catch. The implicit assumption was that the ocean's bounty was so vast that restrictions were unnecessary. In the twentieth century, fisheries such as Atlantic cod and California sardines collapsed, and nations began to limit access to their fishing grounds by boats from other countries, while in parallel, international organizations began to certify that specific species were "threatened", "endangered", etc.

One early management technique was to define a "season" during which fishing was allowed. The length of the season attempted to reflect the current abundance of the fishery, with bigger populations supporting longer seasons. This turned fishing into a race, driving the industry to bigger, faster boats, which in turned caused regulators to repetitively shorten seasons, sometimes to only a few days per year. Landing all boats over an ever-shorter interval also led to glut/shortage market cycles with prices crashing when the boats came in. A secondary consequence was that boats sometimes embarked when the fishery was "open" regardless of weather or other safety concerns.^[5]

A move to privatization and market based mechanisms

The implementation of ITQs or IFQs works in tandem with the privatization of common assets. This regulatory measure seeks to economically rationalise access to a common-pool resource.^[6] This type of management is based in the doctrine of natural resource economics. Notably the use of ITQs in environmental policy has been informed by the work of economists such as Jens Warming,^[7] H. Scott Gordon ^[8] and Anthony Scott.^[9] It is theorised that the primary driver of over-fishing is the rule of capture externality. This is the idea that the fisher does not have a property right to the resource until point of capture, incentivising competitive behavior and overcapitalisation in the industry. It is theorized that without a long-term right to fish stocks, there is no incentive to conserve fish stocks for the future.

The use of ITQs in resource management dates back to the 1960s and was first seen in ‘pollution quotas’, which are now widely used to manage carbon emissions from power utilities.^[10] For both air and marine resources ITQs use a ‘cap-and-trade’ approach by setting typically annual limits on resource exploitation (TAC in fisheries) and then allowing trade of quotas between industry users. However, ITQ use in fisheries is fundamentally different from pollution quotas, since the latter regulates the byproduct of an industry, whereas fishery ITQ's regulate the actual output product of the fishing industry, and thus amount to exclusive industry participation rights.

The use of IFQs has often been related to broader processes within neoliberalism that tend to utilise markets as a regulatory tool.^[11] The rationale behind such neoliberal mechanisms situates itself in the belief that market mechanisms harness profit motive to more innovative and efficient environmental solutions than those devised and executed by states.^[12] Whilst such neoliberal regulation has often been posited as a move away from state governance,^[13] in the case of privatization the state is integral in the process of creating and maintaining property rights.

The use of neoliberal privatizing regimes has also often raised contradictions with the rights of indigenous communities. For example, the exclusion of Māori tribes in the initial allocation of fishing quota in New Zealand's quota management system led to a lengthy legal battle delaying development in national fisheries policy and resulting in a large settlement from the crown. There have also been similar legal battles regarding the allocation of fishing rights with the Mi'kmaq in Canada and the Saami in North Norway. Aboriginal fishing rights are said to pose a challenge to the authoritative claims of the state as the final arbitors in respect of access and participation in rights-based regimes.^[14]

Catch shares

The term catch share has been used more recently to describe the range of programs similar to ITQs. Catch shares expanded the concept of daily catch limits to yearlong limits, allowed different fishers to have different limits based on various factors, and also limited the total catch.

Catch shares eliminate the "race to the fish" problem, because fishers are no longer restricted to short fishing seasons and can schedule their voyages as they choose. Boom/bust market cycles disappear, because fishing can continue throughout a typically many-month season. Some safety problems are reduced because there's no need to fish in hazardous conditions just because the fishery happens to be open.

A crucial element of catch share systems is how to distribute/allocate the shares and what rights come with them. The initial allocation can be granted or auctioned. Shares can be held permanently ("owned") or for a fixed period such as one year ("rented"). They can be salable and/or leasable or not, with or without limits. Each variation has advantages and disadvantages, which may vary given the culture of a given fishing community.

Initial distribution

ITQs are typically initially allocated as grants according to the recent catch history of the fishery. Those with bigger catches generally get bigger quotas. The primary drawback is that individuals receive a valuable right at no cost. Grants are somewhat analogous to an "homestead", in which settlers who developed farms in the American wilderness eventually received title without payment to what had been public land. In some cases, less than 100% of the TAC becomes ITQs, with the remainder allocated to other management strategies.

The grant approach is inherently political, with attendant benefits and costs. For example, related industries such as fish processing and other non-participants may seek quota grants. Also, fishers are often excluded from receiving quota if they are not also boat owners, however boat owners who do not fish do receive quota, such as was the case in Alaskan IFQ distributions. The offshore pollock cooperative in the Pacific Northwest allocated initial quotas by mutual agreement and allows quota holders to sell their quotas only to the cooperative members.^[15]

Quota auctions recompense the public for access to fisheries. They are somewhat analogous to the spectrum auctions that the U.S. held to allocate highly valuable radio spectrum. These auctions raised 10s of billions of dollars for the public. Note however that the television industry did not have to pay for the necessary spectrum to switch from analog to digital broadcasting, which is more like quota grants for incumbent fishers.

Trading

ITQs can be resold to those who want to increase their presence in the fishery. Alternatively, quotas can be non-tradeable, meaning that if a fisher leaves the industry, the quota reverts to the government to retire or to grant/auction to another party.

Once distributed, quotas can be regranted/reauctioned periodically or held in perpetuity. Limiting the time period lowers the quota's value and its initial auction price/cost, but subsequent auctions create recurring revenues. At the same time, "privatizing" such a public resource reduces the remaining amount of public resources and can be thought of as "giving away our future". In the industry, rented quotas are often referred to as "dedicated access privileges" (DAP).

Another issue with tradability is that large enterprises may buy all the quotas, ending what may be a centuries-long tradition of small-scale operations. This may benefit the sellers (and the buyers and those who buy the fish) but can potentially cause large changes in the culture of fishing communities. Consolidation of quota accompanies every IFQ program, and typically works to phase out smaller, less profitable fishing operations in favor of larger, often corporate owned fleets who have better financing capabilities.

Some fisheries require quota holders to be participating fishermen to prevent absentee ownership and limit the quota that a captain can accumulate. In the Alaska halibut and black cod fisheries, only active fishers can buy quota, and new entrants may not sublease their quota. However, these measures have only served to mitigate outside speculation in IFQ's by non-fishers. A lack of regulatory policy or enforcement still results in the prevalence of "armchair fishermen" (those who own quota but do not materially participate in the fishery).^[16] Since IFQ's began in 1995, the commercial longline fleet has never exceeded these fisheries' TACs.

Other characteristics

ITQs may have the effect of changing the criteria that fishers apply to their catch. Highgrading involves catching more fish than the quota allows and dumping specimens that are less valuable because of size, age or other criteria. Many of the discarded fish are already dead or quickly die, increasing fishing's impact on stocks.^[17]

Effectiveness

In 2008 a large scale study concluded that ITQs can help to prevent collapses and restore declining fisheries when compared to a data set including 11,000 fisheries of various management structures (some entirely unmanaged).^[18][19] While nearly a third of open-access fisheries have collapsed, catch share fisheries are only half as likely to fail.^[5] However, when compared to other modern fishery management schemes, IFQ managed fisheries exhibit no long term ecological advantages.^[20][21] A study of the 14 IFQ programs in the United States revealed that fish stocks are unaffected by these management schemes.^[22]

In 1995, the Alaskan halibut fishery converted to ITQs, after regulators cut the season from about four months down to two or three days. Today, due to the pre-allocation of catch that accompanies IFQ's, the season lasts nearly eight months and boats deliver fresh fish at a steadier pace. However, halibut stocks have been in continuous decline for over a decade, as poor stock assessments leading to overfishing has caused a substantial decline in biomass. Additionally, despite the increase in landings value, the number of quota holders have declined by 44%, as consolidation and quota pricing has served to prevent new entrants.^[23]

Not all fisheries have thrived under ITQs, in some cases experiencing reduced or static biomass levels,^[2] because of factors such as:

• TACs may be set at too high a level
• Migratory species may be overfished in parts of their habitat not covered by the TAC
• Habitats may incur damage
• Enforcement may be lax

In the United States

The Magnuson-Stevens Fishery Conservation and Management Act defines individual transferable quotas (ITQs) as permits to harvest specific quantities of fish of a particular species. Fisheries scientists decide the maximum annual harvest in a certain fishery, accounting for carrying capacity, regeneration rates and future values. This amount is called the total allowable catch (TAC). Under ITQs, participants in a fishery receive rights to a portion of the TAC without charge. Quotas can be fished, bought, sold, or leased. Twenty-eight U.S. fisheries have adopted ITQs as of 2008.^[1] Concerns about distributional impacts led to a moratorium on moving other fisheries into the program that lasted from 1996 to 2004.^[2]

Starting in January 2011, fishermen in California, Oregon and Washington will operate via tradeable catch shares. Fishers have been discarding bycatch that is not their target, typically killing the individuals. Catch shares allow trawlers to exchange bycatch with each other, benefiting both. Goals of the system include increased productivity, reduced waste, and higher revenues for fishers. More than a dozen other U.S. fisheries are now managed by catch shares. Fishery managers say that in Alaska, where catch shares have been in place for several years, fishermen are now getting higher prices for their catch.^[24]

Criticisms and controversies

Private control of public resource

IFQ’s are usually initiated through the de facto privatization of an otherwise public resource: the fisheries. Initial recipients of quota receive windfall profits through the gifting of share ownership, while all future entrants are forced to purchase or lease the right harvest fish. Many have questioned both the ethical and economic repercussions of dedicating a secure, exclusive privilege to access this public resource. For example, in the US, during a presentation given to the Gulf Fishery Management Council, Fishery Manager Larry Abele stated that the present value of the Gulf Fishery IFQ Harvest amounted to $345,000,000 and this was given without requiring of any return to the public from IFQ holders.^[25]

Quota consolidation

Virtually every IFQ program results in substantial consolidation of quota. For example, it is estimated that 8 companies control 80% of New Zealand's fisheries through quota acquisition, 4 companies control 77% of one Alaska crab fishery, and 7% of shareholders control 60% of the US Gulf Red Snapper quota.^[25][26] The consolidation results in job loss, reduced wages, and decreased entry opportunities into the fishery.

Leasing practices

Many IFQ systems involve the temporary transfer of fishing rights, whereby the owner of quota leases the fishing rights to active fishermen in exchange for a fixed percentage of the landed value of fish. Since quota acquisition is often beyond the financial means of many fishermen, they are forced to sacrifice substantial portions of their income in order to lease fishing rights. For example, Bering Sea crab lease fees can be as high as 80% of the landed value of the crab, meaning that the active fishermen only retain 20% of the revenue, much which is needed to cover costs.^[27] In some fisheries, the majority of quota is leased to active fishermen, often by individuals who do not material participate in the fishery, but have been able to acquire shares. This makes quota acquisition even less likely for active fishermen, results in diversion of wealth away from fishing communities and into the hands of private investors, and can cause major financial strain on fishermen along with the economic contraction of fishing communities.^[28]

Economic depression of coastal communities

The transition to IFQ management tends to cause considerable economic harm to coastal communities that are dependent on commercial fisheries.^[29] Although IFQ management systems are designed to enhance the economic performance of the fishing industry, this usually comes at the cost of coastal communities whose economies rely principally on their fishing fleet. This cost results from the re-equilibration of the quota-regime market, revealing the inefficient over-investment that had taken place in the industry prior to implementation of the quota regime.

See also

• List of harvested aquatic animals by weight

References

Further reading

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