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

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44<br />

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

existing trapping grounds with subsequent<br />

economic impacts for all trappers. We believe<br />

an onboard observer program is needed to<br />

assess the type and magnitude of bycatch in<br />

trap and trawl fisheries. After a year of data<br />

collection, potential bycatch problems in the<br />

fisheries can be addressed from a scientific<br />

basis. Certain gear restrictions or area closures<br />

may become necessary to minimize<br />

bycatch, particularly for shelf rockfish<br />

species. In addition, the establishment of a<br />

restricted-access fishery program for trap<br />

and trawl vessels should reduce the amount<br />

of fishing effort and its consequent impact<br />

(California Fish and Game Commission<br />

2000a).<br />

SPOT PRAWN BYCATCH — STATUS OF THE<br />

OBSERVER PROGRAM<br />

<strong>The</strong> numbers of bycatch observations and data<br />

available from the spot prawn fishery are limited.<br />

Many variables affect both the amount and type<br />

of bycatch caught, particularly in trawl gear.<br />

<strong>The</strong>se factors range from location, time of year,<br />

tow speed, tow duration, type and diameter of<br />

roller gear, mesh size, presence or absence of a<br />

fish-excluder device, and the type of excluder<br />

used (Reilly, CDFG. Pers. comm., June 2001).<br />

<strong>The</strong> field of Ecological Economics<br />

“is not a single, new paradigm<br />

based in shared assumptions and<br />

theory” (Costanza et. al. 1997, p. 50).<br />

It is a transdisciplinary field that<br />

uses methods and information<br />

from economics, ecology, and other<br />

fields to address the difficult areas<br />

of development and environmental<br />

sustainability. <strong>The</strong> discipline<br />

works from the initial premise that<br />

the “earth has a limited capacity for<br />

sustainably supporting people and<br />

their artifacts determined by combinations<br />

of resource limits and<br />

ecological thresholds” (Costanza et<br />

al. 1997, p. 75). It places the human<br />

economic system as a subset of,<br />

and entirely dependent on, natural<br />

ecosystems. <strong>The</strong> relationship is<br />

explicit.<br />

Ecological Economics incorporates<br />

the strengths of traditional economics<br />

and includes additional<br />

ECOLOGICAL ECONOMICS<br />

areas critical to development and<br />

natural resource management in<br />

the 21st century. <strong>The</strong>re are four<br />

general categories of decisionmaking<br />

criteria: 1) economic scale,<br />

environmental impacts, and sustainability;<br />

2) fair distribution of<br />

opportunity and benefits; 3) economic<br />

efficiency; and 4) democracy<br />

in governance.<br />

Traditional economics assumes<br />

that with economic growth, problems<br />

of sustainability, distribution,<br />

and efficiency will be solved. Issues<br />

of governance and democracy are<br />

believed to be beyond the scope of<br />

economics. Ecological Economics,<br />

on the other hand, does not<br />

assume that growth is a cure-all.<br />

Ecological sustainability, fairness,<br />

economic efficiency, and democratic<br />

decision-making processes must<br />

be part of the definition of success<br />

for any development project or<br />

<strong>The</strong>se factors, in combination with limited observation<br />

and analysis, have restricted the CDFG’s<br />

capacity to determine the nature and extent of<br />

bycatch issues in the fishery. As a result, the<br />

CDFG stated, in a memo to the California Fish<br />

and Game Commission, that a “more extensive<br />

observer program would be desirable if the funds<br />

were available” (CDFG 1999).<br />

<strong>The</strong> Commission approved the request for an<br />

observer program effective July 2000. As of late<br />

2000, 21 trap vessels and 21 trawl vessels were participating<br />

in the program. To date, CDFG has collected<br />

observations from approximately 80 spot<br />

prawn trawl tows, representing fishing grounds<br />

off Fort Bragg and south to the northern Channel<br />

Islands off Point Conception. Data have also been<br />

gathered from about 200 trap strings, covering fishing<br />

grounds from Monterey south to San Diego,<br />

and including the islands off Southern California<br />

(Reilly, CDFG. Pers. comm., June 2001).<br />

California’s Observer Program is funded through<br />

an observer fee. Fees have been set as follows:<br />

•$250 for each trap vessel, $250 for any trawl vessel<br />

with spot prawn landings of less than 1,000<br />

pounds in 1998 and 1999.<br />

•$500 for each vessel landing 1,000 pounds or<br />

management system, and must be<br />

directly integrated into plans and<br />

policy from the beginning.<br />

For example, the World Bank and private<br />

financiers have provided thousands<br />

of loans for shrimp aquaculture<br />

in developing nations.Yet neither<br />

the project plans nor the<br />

appraisal reports included the: loss<br />

in value associated with the reduction<br />

or destruction of ecological<br />

services such as water purification;<br />

declining coastal fisheries; compromised<br />

water quality; salinization of<br />

coastal farmland; or displacement of<br />

coastal communities.<strong>The</strong>se loans are<br />

now recognized as having been<br />

profitable for shrimp farmers, but<br />

also responsible for creating much<br />

greater social costs overall. Some<br />

countries, like India, have banned<br />

shrimp farming nationwide.<br />

Fisheries management failures and<br />

resulting fisheries collapses can be<br />

directly attributed to the failure of<br />

traditional economic analysis to<br />

consider the negative externalities

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