Individual Transferable Quotas (Fishing)

nature of policy instrument

case study

history

30 year history of use in many fishery management strategies ( Chu, 2008)

benefits and implementation of them presently remains controversial ( Chu, 2008)

benefits

alternatives to ITQ

marine protected areas

ecosystem-based management plans

Nature/Function

global spread of uptake

ITQs are fee-based

fees help fund enforcement, management and scientific research (Grafton et al. 1996; Sutinen 1999 from Chu, 2008)

10% of total marine harvest (several hundred fisheries worldwide) currently managed using some form of TAC-ITQ system (Arnason 2005 from (Chu 2008)

end 'race for fish'

improve fleet efficiency

reduce over-exploitation

increase ex-vessel prices

((Grafton 1996; McCay 1996) Chu 2008)

clarification

vessels fish at an ever increasing pace causing fishing season to shorten to just days

drawbacks

relate to

initial allocation of quotas

concentration of the quota to fewer participants

socio-economic consequences for fishers within the ITQ managed fishery

often based on historical landings and vessel characteristics

problem arises with fishermen being disingenuious regarding catch history to attain extra quota ((Branch 2008) Chu, 2008)

because ITQs reduce overcapitalisation

lead to social inequality among fishers groups and between generations ((Eythorsson 2000; Arnason 2005; Hilborn et al. 2005a) Chu, 2008)

present

at least 18 countries utilise ITQ systems to manage their marine resources (Chu, 2008)

first countries adopting

Netherlands, Iceland and Canada (late 1970s)

Falkland Islands most recent (2006) (Chu, 2008)

Several hundred stocks for 249 species managed under ITQ schemes globally

leading countries in ITQ management

Iceland and New Zealand

implemented ITQs for all major commercial species

in terms of no. of species under ITQ management

New Zealand, Canada and Australia

Screenshot 2023-02-17 at 15.06.22 Chu 2008

Screenshot 2023-02-17 at 15.07.12

initial reasons ITQs adopted

stock depletion

safety concerns for fishers (Chu 2008)

related to overfishing and overcapitalisation in fishery (Chu, 2008)

political change (Chu, 2008)

local gishing businesses have flexibility to structure their activites to maximise investment

curb fleet capacity ((Liew 2001) Chu 2008)

Pacific halibut fishery

Location

Off coast of British Columbia

Before IVQ intervention

managed initially as a limited-entry, derby style system (chu, 2008)

induced impact of 'race to the end'

led to fish days reducing from 65 in 1980 to 10 in 1990 (chu, 2008)

further socio-economic impact (according to Chu, 2008)

endangered health and safety of fishers

difficulty of limited entry approach to keep catch within limits

reduced profitability of pacific halibut market

bc oversupply of halibut (market flooded with halibut in Chu, 2008 words), so had to be sold at cheaper prices

After IVQ

when

introduced in 1991

socio-economic impact

fisher safety improved

fishing seasons length increased to 245 days

ex-vessel prices rose as market demand for fresh halibut increased

(Herrmann 1996)

promote investment in long-term research and development of fish resources

evidence by Chu 2008 showed ITQs can 'decelerate the decline of fish stocks, though it was noted in their research the impacts of ITQs are highly variable)

in 12 of fish stocks studied by Chu 2008, biomass increased after ITQ implementation

mechanism by which ITQ causes such changes

  1. removal of excess harvesting capacity from the fishery
  1. end of race for fish
  1. improvement in harvest compliance

mechanism

quota related fees 'may cause some fishers to leave fishery while other may combine resources and consolidate crew' ((Grafton 1996, Wang and Tang 1996; Eythorsson 2000) from Chu 2008)

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occurs in most ITQ fisheries becaus 'fisher can harvest at their own pace, maximisng their resources and optimiszing when the fish goes to market to increase profits ((Grafton 1996, Beddington et al. 2007, Gibbs 2008) from Chu 2008)

quota fees used to fund on-board and/dockside monitoring and enforcement (National Research Council 1999)

51% decrease in marketable discards of most species in BC groundfishery after ITQs introduced ((Branch et al 2006) from Chu, 2008)

practical applications

in fisheries with inadequat monitroign and enforcement, false reporting and quota-busting can be a problem

aid conservation of fish stocks by improving harvest conditions and accounting for quota

moving forward

effectiveness must be looked within a wider context

application of individual transferable quotas alone do not conserve fish stocks

must be looked at within broader context of marine management

wider marine management, including conservation measures can be a major contributor to increases in fish stocks

fish recruitment may be neg affected by other factors or TAC may be set too high causing

a recent decline in fisheries that implement ITQs following a pervious rise

Dutch Place, pacific halibut and American surfclam case studys for this

quota non-complainace

e.g. reducing TAC, applying gear restrictions, size limits and MPAS for nursery and spawning habitat may cntribute to the sustainability of stocks (chu, 2008)

lack of enforcement

in case of squat lobster in Chile after 1996)

conservative TACS found to contributed to catch-per-unit-effort of ITQ-managed offshore scollops in Atlantic Canada ((Branch 2008) Chu, 2008)

long-term adaptive management and importance of science, monitoring and enforcement of ITQ systems

oceanographic, climatic, interspecific and intraspecific dynamics affect stock biomass

effectiveness of ITQs in recovering fish stocks is context-dependant to the fishery

in some places in may not be enough, in others it may have a profound positive effect

in fisheries where biological and environmental factors are not severely limiting ability of fish stocks to recover, science (determining TAC), effective monitoring and enforcement is likely going to contribute to the success of the ITQ

may have little effect on highly migratory species

ecosystem-based management plan may be needed in addition in some cases ((Marasco et al. 2007) Chu 2008)

compliance by all nations is not guaranteed

under-reporting of catches

illegal harvesting by nations

Southern Bluefish Tuna

in these cases a multi-national ITQ system managed by an international agency may be needed (chu 2008)

'the positive changes in 12 of the 20 stocks suggest that ITQs can be a beneficial component of the management for some fisheries while in others, alternative or complementary measures are needed to sustain the fishery. These may combine ITQs with more effective TACs, better enforcement and mon- itoring or ecosystem-based management.' Chu, 2008

overfishing background/context

biomass of top marine predators is now some 10% of what it was half a century a go (ref 1 from Heal 2008)

many species projected to face extinction within decades

bluefin tuna

atlnatic cod

sword fish in atlantic and indian ocean

tragedy of the commons

what?

quotas

in what form?

catch shares of TAC (Chu, 2008) and (Stud 2006)

dedicated access privileges (Chu, 2008) and (Stud 2006)

for who?

individual fishers (Stud 2006)

fishing communities (Stud 2006)

fisher coopertives (Stud 2006)

two forms

individual fishing quotas

assign quotas with individuals

assign quotas to vessels

work within a wider management scheme in which TAC is set by a regulatory body and then sorted into units that can be bough, sold or leased among participants in the fishery

why

physical limit on harvest (stud 2006)

penalities for non-compliance (stud 2006)

create a market (stud 2006)

incentivises fishers to use TAC efficiently (stud 2006)

where marginal cost of permit equal to expected marginal net beneit from sale of permitted catch (stud, 2006)

establishment of property rights through ITQs exclude fishers withouts rights access to fish stocks (stud 2006)

limited geographical application

not able to be used in marine areas beyond national jurisdiction

establishment of a market provides individual fishers or fishing cooperatives with an incentive to maximise efficiency of the total allowable catch.

value of ITQs determined by the productivity of the fishery

collapsed fishery - ITQ permits worth little

healthy fishery

permit prices worth a lot

wealth to be gained

prevents overcapitalisation within the fisheries

bc fewer boats (less effort) (Stud 2006)

bc diverts investment away from racing capital (technology which speeds up boats to access fish stocks) (stud, 2006)

effect of property rights

See Stud 2016

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fishers have an incentive to use the most efficient fishing gear and fishing methods to enhance net benefits of the quota (R. Arnason)

derby style fishery meaning fishing season is only open for a few weeks/months