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The Spot Prawn Fishery The Spot Prawn Fishery - Basel Action ...

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20<br />

<strong>The</strong> <strong>Spot</strong> <strong>Prawn</strong> <strong>Fishery</strong>: A Status Report<br />

•“To ensure conservation and protection of<br />

invertebrate stocks and their habitat through the<br />

application of scientific management principles<br />

applied in a risk averse and precautionary manner<br />

based on the best scientific advice available.<br />

•“To meet the federal Crown’s obligations regarding<br />

Aboriginal fisheries for food, social, and ceremonial<br />

purposes.<br />

•“To develop sustainable fisheries through<br />

partnership and co-management arrangements<br />

with client groups and stakeholders to share in<br />

decision-making, responsibilities and costs and<br />

benefits.<br />

•“To develop fishing plans and co-operative<br />

research programs which will contribute to<br />

improving the knowledge base and understanding<br />

the resource.<br />

•“To consider the goals of stakeholders with<br />

respect to the social, cultural and economic<br />

value of the fishery”<br />

(Fisheries and Oceans Canada 2000a).<br />

This is a fully competitive, limited-entry fishery<br />

that is managed through seasonal closures, inseason<br />

closures, gear limits, mesh size requirements,<br />

and minimum size limits. Two biological<br />

objectives have directed the choice of management<br />

tools: the prevention of growth overfishing<br />

(size limits and trap escapement modifications)<br />

and the prevention of recruitment overfishing (fixed<br />

escapement standard; i.e., spawner index model).<br />

Summary of Commercial Management and<br />

Regulatory Measures<br />

British Columbia’s spot prawn management system<br />

is different from all other spot prawn management<br />

systems. According to Fisheries and Oceans, spot<br />

prawn management in Canada is a “work in progress.”<br />

While management paradigms have historically<br />

focused on short-term yield, there is a need to<br />

change this culture and move toward a more longterm,<br />

precautionary, ecosystem approach. BC is<br />

continually evolving in this direction (Boutillier,<br />

Fisheries and Oceans Canada. Pers. comm., June<br />

2001). Precaution and ecosystem considerations<br />

are central to the BC system. Management operates<br />

on a very fine scale and is highly adaptive.<br />

Fine-scale management is fundamental to achieving<br />

BC’s management goals and central to achieving<br />

long-term sustainability for the spot prawn<br />

fishery. It is obtained through reliance on realtime<br />

management decisions and an involved atsea<br />

monitoring system. This fine-scale management<br />

system is at the crux of reducing the spot<br />

prawn’s vulnerability to serial depletion and<br />

localized overfishing (Boutillier, Fisheries and<br />

Oceans Canada. Pers. comm., October 2001).<br />

This section offers an overview of Canada’s spot<br />

prawn management measures and regulatory<br />

system. For a complete description of British<br />

Columbia’s spot prawn management regime,<br />

see Fisheries and Oceans Canada’s website<br />

(www.pac.dfompo.gc.ca/ops/fm/shellfish/<br />

<strong>Prawn</strong>/prawn).<br />

•In 1979, a biological reference point—the spawner<br />

index—was instituted to manage<br />

fishing effort.<br />

•Harvest log requirements were mandatory as<br />

of 1983. Fishers are required to complete logbooks<br />

describing fishing effort and catch by midnight<br />

of each fishing day. <strong>The</strong> information must<br />

be delivered to Fisheries and Oceans within four<br />

weeks of the month in which fishing occurred.<br />

•Coast-wide seasonal closures were set in place<br />

for the South Coast (Areas 11–29) in 1984 and<br />

along the North Coast (Areas 1–10) in 1989. Prior<br />

to 1984, closures were set to coincide with the<br />

period in which eggs are incubated and larvae<br />

hatched (January–March). Closure timing is<br />

now based on a biological reference point: a<br />

minimum spawner index.<br />

•In 1985, a minimum size limit of 30 mm (1.18<br />

in.) carapace length was instituted. <strong>The</strong> size<br />

limit was increased to 32 mm (1.26 in.) in 1996<br />

and to 33 mm (1.30 in.) in 1997. A minimum<br />

length of telson (middle segment of the tail fan<br />

at the most posterior portion of the tail) of 20<br />

mm (0.79 in.) was established in 1998.<br />

•Trap mesh size limits became obligatory in 1988<br />

to reduce the capture of undersized prawns and<br />

mortality associated with bycatch and sorting.<br />

•A license limitation system, with a length restriction<br />

on transferability, was established in 1990.<br />

•Hailing requirements—i.e., fishers must report in<br />

prior to beginning fishing and on completion of<br />

fishing—were instituted in 1992. Hailing data<br />

facilitates in-season managment of the fishery.

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