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Testimony: 

United States General Accounting Office: 
GAO: 

Before the Committee on Commerce, Science, and Transportation, U.S. 
Senate: 

For Release on Delivery: 
Expected at 9:30 a.m. EST: 
Wednesday, February 25, 2004: 

Individual Fishing Quotas: 

Economic Effects on Processors and Methods Available to Protect 
Communities: 

Statement of Anu K. Mittal, Director: 
Natural Resources and Environment: 

GAO-04-487T: 

GAO Highlights: 

Highlights of GAO-04-487T, testimony before the Committee on Commerce, 
Science, and Transportation, United States Senate. 

Why GAO Did This Study: 

To address overfishing, the National Marine Fisheries Service started 
using individual fishing quotas (IFQ) as a fishery conservation and 
management tool in 1990. Under an IFQ program, a regional fishery 
management council sets a maximum, or total allowable catch, and 
allocates the privilege to harvest a certain portion of the catch in 
the form of quota to individual vessels, fishermen, or other eligible 
recipients. 

IFQ programs have achieved many of the desired conservation and 
management benefits, such as helping to stabilize fisheries, reducing 
excessive investment in fishing capacity, and improving safety. 
However, concerns have been raised about the economic effects of IFQ 
programs on fish processors and fishing communities, among others. 

This testimony is based on two GAO reports on issues related to the 
use of IFQs (Individual Fishing Quotas: Better Information Could 
Improve Program Management, GAO-03159, Dec. 11, 2002, and Individual 
Fishing Quotas: Methods for Community Protection and New Entry Require 
Periodic Evaluation, GAO-04-277, Feb. 24, 2004). 

Specifically, GAO addressed the (1) economic effects of the Alaskan 
halibut IFQ program on processors and (2) the methods available for 
protecting communities under an 

What GAO Found: 

The Alaskan halibut IFQ program has had varied economic effects on 
processors. The program extended the halibut fishing season to 8 
months, allowing more halibut to be processed and sold as a fresh 
product. This shift to fresh product led to the emergence of the buyer 
broker, an increased competition for fish, and higher halibut ex-
vessel prices (prices paid to fishermen for raw product). In addition, 
a net decrease of 12 shore-based plants that processed halibut 
occurred between 1995, when the IFQ program was implemented, and 2001, 
as well as a reallocation of market share. For the 28 companies that 
processed halibut in both 1995 and 2001, 15 lost market share and 13 
gained market share. 

Factors other than the implementation of the IFQ program, such as the 
diversity and value of species processed, could also have impacted the 
well-being of Alaskan halibut processors. For example, halibut 
represented a relatively small portion of the fish processed by shore-
based plants in Alaska and of total plant value. Specifically, from 
1994 to 2001, halibut represented, on average, 2 percent to 4.1 
percent of all fish processed at a plant and accounted for 4.4 percent 
of total plant value in 1994 and 7.9 percent in 2001. The only 
estimate of the program's economic effects on processors is a 2002 
study commissioned by the state of Alaska. This study estimated that 
halibut processors experienced a 56-percent loss in gross operating 
margins. However, GAO's analysis, as well as the analyses of others, 
identified concerns about the study's assumptions, representiveness, 
and potential for participant bias that raise questions about the 
reliability of its estimates. 

Several methods are available for protecting the economic viability of 
fishing communities under an IFQ program. The easiest and most direct 
way is to allow communities to hold harvesting quota and decide how 
this quota is to be used. In addition, fishery managers can help 
ensure the economic viability of communities by adopting quota 
management rules aimed at protecting certain groups of fishery 
participants. However, protecting the economic viability of 
communities is a social objective, and realizing such an objective may 
undermine economic efficiency and raise questions of equity. For 
example, rules that allow communities to hold harvesting quota may 
result in allocations to communities that do not have the knowledge 
and skills to manage the quota effectively and thus increase costs 
and/or decrease revenues. Similarly, rules that appear to favor one 
group of fishermen over another may result in fairness and equity 
challenges. Fishery managers also face a number of challenges 
associated with the methods available to protect communities. The 
resolution of these issues ultimately will depend on the specific 
circumstances within a fishery and the overall program objectives. 

[hyperlink, http://www.gao.gov/cgi-bin/getrpt?GA0-04-487T]. 

To view the full product, including the scope and methodology, click 
on the link above. For more information, contact Anu Mittel at (202) 
512-3841 or mittala@gao.gov. 

[End of section] 

Mr. Chairman and Members of the Committee: 

We are pleased to be here today to discuss the economic effects of 
individual fishing quotas (IFQ) on processors and methods available 
for protecting communities under an IFQ program. 

Overfishing is a problem with far-reaching ecological and economic 
consequences. About one-third of the fish stocks assessed by the 
Department of Commerce's National Marine Fisheries Service (NMFS) are 
overfished or will become overfished if conditions do not change. When 
a fishery—composed of one or more fish stocks within a geographic area—
cannot be sustained, the marine ecosystem can be transformed, thus 
threatening the livelihood of fishermen and the way of life in many 
communities. 

Fishery management practices in U.S. waters are developed primarily by 
regional fishery management councils established under the Magnuson-
Stevens Fishery Conservation and Management Act (Magnuson-Stevens 
Act).[Footnote 1] Fishery councils, under the direction of NMFS, have 
used several types of controls to maintain the health of U.S. 
fisheries. In 1990, NMFS started using IFQs as a conservation and 
management tool. Under an IFQ program, a regional fishery management 
council sets a maximum, or total allowable catch, and allocates the 
privilege to harvest a certain portion of the catch in the form of 
quota to individual vessels, fishermen, or other eligible recipients. 

IFQ programs have achieved many of the desired conservation and 
management benefits, such as helping to stabilize fisheries, reducing 
excessive investment in fishing capacity, and improving safety. 
However, concerns have been raised about the economic effects of IFQ 
programs on fish processors and fishing communities, among others. 

Our testimony is based on two reports we prepared at the request of 
this Committee's Subcommittee on Oceans, Fisheries, and Coast Guard. 
[Footnote 2] The first report focused on the consolidation and foreign 
holdings of quota and the economic effects on processors. The second 
report addressed the methods available to protect the economic 
viability of communities and facilitate new entry into IFQ fisheries. 
For our study of the economic effects on processors, we focused on the 
Alaskan halibut IFQ program, which began in 1995. We interviewed 
fishery participants, visited processing plants in Alaska, analyzed 
public data, and reviewed the only study that attempted to quantify 
the economic effects of the program on processors. For our study of 
community protection methods available under an IFQ program, we 
visited domestic and foreign fishing communities in Alaska, Maine, 
Iceland, Scotland, and New Zealand In these communities and elsewhere, 
we spoke with fishery managers, participants, and researchers; 
reviewed literature on domestic and foreign quota-based programs; and 
reviewed key regulations and studies. Our testimony today discusses 
the (1) economic effects of the Alaskan halibut IFQ program on 
processors and (2) the methods available for protecting communities 
under an IFQ program. 

In summary, we found the following: 

* The Alaskan halibut IFQ program had varied economic effects on 
processors—some processors were adversely affected while others 
benefited. First, the program extended the halibut fishing season to 8 
months, thus allowing more halibut to be processed and sold as a 
higher-value fresh product than as a lower-value frozen product. 
Second, this shift to fresh product led to the emergence of the buyer 
broker, generally a one-person operation with lower overhead costs, 
which resulted in increased competition for fish and contributed to 
higher ex-vessel prices (prices paid to fishermen for raw product) for 
halibut. Third, there was a net decrease of 12 shore-based plants that 
processed halibut between 1995 and 2001-68 plants stopped processing 
halibut and 56 started. Over three-quarters of the plants that stopped 
or started processing processed less than 100,000 pounds of halibut 
annually. Finally, there was a reallocation of market share. Of the 28 
companies that processed halibut in both 1995 and 2001, 15 lost market 
share and 13 gained market share. 

* The economic well-being of processors may also have been impacted by 
factors other than the implementation of the IFQ program, such as the 
diversity and value of species processed. Our analysis indicates that 
halibut represented a relatively small portion of the fish processed 
by shore-based plants in Alaska. Specifically, from 1994 to 2001, 
halibut represented, on average, 2 percent to 4.1 percent of all fish 
processed at a plant and accounted for 4.4 percent of total plant 
product value in 1994 and 7.9 percent in 2001. 

* We identified only one study that estimated the economic effects of 
the IFQ program on halibut processors. This study, commissioned by the 
state of Alaska, concluded that halibut processors experienced a 56-
percent ($8.7 million) loss in gross operating profits, primarily 
because of the IFQ. However, our analysis, as well as the analyses of 
others, identified concerns about the study's assumptions, 
representiveness, and potential participant bias, that raise questions 
about the reliability of the study's estimates. 

* Several methods are available to help protect the economic viability 
of fishing communities under an IFQ program. The easiest and most 
direct way is to allow the communities themselves to hold harvesting 
quota and decide how this quota is to be used. In addition, fishery 
managers can help ensure the economic viability of communities by 
adopting quota management rules aimed at protecting certain groups of 
fishery participants. However, it is important to recognize that 
protecting the economic viability of communities is a social 
objective, and realizing such an objective may undermine economic 
efficiency and raise questions of equity. For example, rules that 
allow communities to hold harvesting quota may result in allocations 
to communities that do not have the knowledge and skills to manage the 
quota effectively and thus increase costs and/or reduce revenues. 
Similarly, rules that appear to favor one group of fishermen over 
another may result in fairness and equity challenges. Fishery managers 
also face a number of challenges associated with the methods available 
to protect communities. The resolution of these issues ultimately will 
depend on the specific circumstances within a fishery and the overall 
program objectives. 

Background: 

The Magnuson-Stevens Act granted responsibility for managing marine 
resources to the Secretary of Commerce. The Secretary delegated this 
responsibility to NMFS, which is part of Commerce's National Oceanic 
and Atmospheric Administration. The act established eight regional 
fishery management councils, each with responsibility for making 
recommendations to the Secretary of Commerce about management plans 
for fisheries in federal waters. 

The Magnuson-Stevens Act also established national standards for 
fishery conservation and management. These standards, among other 
things, require the fishery management councils to consider the 
importance of fishery resources to fishing communities. The act 
defines a fishing community as one that is substantially dependent on, 
or engaged in, harvesting or processing fishery resources to meet 
social and economic needs. The definition includes fishing vessel 
owners, operators, and crew, and fish processors based in the 
community. NMFS guidance further defines fishing community to mean a 
social or economic group whose members reside in a specific location. 
[Footnote 3] 

Alaskan Halibut IFQ Program Resulted in Changes That Harmed Some 
Processors and Benefited Others: 

The Alaskan halibut IFQ program changed the environment in which 
traditional shore-based processors operated by extending the halibut 
fishing season from several days to 8 months. Before the IFQ program 
was implemented, fishermen had just a few days to fish the total 
allowable catch for the year. Consequently, they provided processors 
with large amounts of fish in a very short period of time, and 
processors organized their operations to process under these 
conditions. With the implementation of the IFQ program, the "race for 
fish" was eliminated because fishermen had more flexibility in 
choosing when to fish. As a result, processors received halibut in 
smaller quantities over a longer period of time. This extended fishing 
season enabled more halibut to be processed and sold as a fresh 
product. Consequently, the fresh halibut market, as figure 1 shows, 
increased from 15 percent of the total halibut market in 1994 to 46 
percent in 2001. 

Figure 1: Fresh Halibut as a Percentage of Total Halibut Production, 
1984 through 2001: 

[Refer to PDF for image: line graph] 

The graph depicts fresh halibut as a percentage of total halibut 
production, 1984 through 2001, with an indication that the IFQ program 
began in mid-1995. 

Source: GAO analysis of Alaska Department of Fish and Game, Commercial 
Operators Annual Report data. 

[End of figure] 

However, to take advantage of the fresh market and its potential for 
higher wholesale prices, processors needed ready access to highways 
and air transportation. As a result, processors with access to 
transportation systems may have been competitively advantaged, while 
those who were in more remote locations may have been competitively 
disadvantaged because transportation costs were higher for them. For 
example, one processor estimated that the costs of transporting fresh 
product from Kodiak Island, Alaska, to Seattle, Washington, was about 
20 cents a pound higher than from Seward or Homer, Alaska, which has 
ready access to a major road system to Seattle. Also, processors 
located near providers of fuel, ice, stores, and entertainment, said 
that fishermen were more willing to deliver fish to them than if these 
providers were not available. 

The shift toward fresh product in the halibut market led to the 
emergence of the buyer-broker, an intermediary who buys fish at a port 
and ships it fresh to market. Processors told us that the emergence of 
buyer-brokers, generally one-person operations with lower overhead 
costs, increased competition for fish and contributed to the increase 
in ex-vessel halibut prices. As table 1 shows, the percentage of 
halibut purchased by buyer-brokers increased from 3.7 in 1995 to 17.4 
in 1999. 

Table 1: Halibut Buyers, by Category, 1995 and 1999: 

Category: Buyer-broker; 
Percentage of halibut purchased 1995[A]: 3.7; 
Percentage of halibut purchased 1999[B]: 17.4. 

Category: Shore-based processors; 
Percentage of halibut purchased 1995[A]: 84.9; 
Percentage of halibut purchased 1999[B]: 73.8. 

Category: Other; 
Percentage of halibut purchased 1995[A]: 11.4; 
Percentage of halibut purchased 1999[B]: 8.8. 

Category: Total; 
Percentage of halibut purchased 1995[A]: 100.0; 
Percentage of halibut purchased 1999[B]: 100.0. 

Source: NMFS. 

[A] 1995 was the earliest year for which NMFS data were available. 

[B] 1999 was the most recent year we could analyze because, starting 
in 2000, buyers could identify themselves in multiple categories. 

[End of table] 

Along with an increase in buyer-broker halibut purchases, there was a 
net decrease in the number of individual shore-based plants that 
processed halibut. While some plants stopped processing halibut, 
others decided it was beneficial to start. Between 1995, when the IFQ 
program was implemented, and 2001, 68 plants stopped processing 
halibut and 56 started, resulting in a net decrease of 12 plants. Most 
of the shore-based plants that stopped and started processing were 
relatively small in comparison to other processors. About 80 percent 
of the shore-based plants that stopped processing halibut and 75 
percent of those that started purchased less than 100,000 pounds of 
halibut annually. 

The IFQ program alone did not necessarily cause a plant to stop 
processing halibut. For example, one processor with a freezing 
operation bought halibut, but its primary business was buying salmon 
from &oilers and then selling it. When the supply of farmed salmon 
increased, contributing to price decreases, the owners decided to sell 
the plant. According to industry and government officials, other 
plants stopped processing halibut because plant management made poor 
business decisions that were unrelated to the IFQ program, the plant 
burned down, or the plant was closed for personal reasons. 

In addition to changes in the number of plants processing halibut, 
companies experienced some change in their market share.[Footnote 4] 
Some processing companies lost market share, while others gained 
market share. Comparing market shares for 1995 and 2001, we found that 
of 28 companies that processed halibut in both years, 15 experienced a 
decrease in market share and 13 experienced an increase. 

Factors other than the IFQ program's implementation could also have 
contributed to changes in the economic well-being of processors. For 
example, according to NMFS officials and industry experts, most 
processors handled other species of fish in addition to halibut, and 
the relative proportion and value of these species will affect the 
economic condition of processors. According to our analysis of data 
from the Alaska Commercial Operators Annual Report, halibut 
represented a relatively small portion of the fish processed by shore-
based plants. Specifically, from 1994 to 2001, halibut represented, on 
average, 2.0 percent to 4.1 percent of all fish processed at a plant. 
In terms of value, as shown in table 2, halibut was 4.4 percent of 
total plant product value in 1994 and 7.9 percent in 2001. (These 
ranges are averages for all plants processing halibut and a particular 
plant may process a higher percentage of these fish.) In these 
circumstances the drop in salmon prices most likely had a larger 
effect on economic well-being of processors than the halibut IFQ 
program. 

Table 2: Average Product Value Percentage, by Species, for Plants 
Processing Halibut and Sablefish, 1994 and 2001: 

Species: Halibut; 
Percentage of product value, 1994: 4.4; 
Percentage of product value, 2001: 7.9. 

Species: Sablefish; 
Percentage of product value, 1994: 4.7; 
Percentage of product value, 2001: 5.3. 

Species: Cod; 
Percentage of product value, 1994: 5.7; 
Percentage of product value, 2001: 9.5. 

Species: Pollock; 
Percentage of product value, 1994: 12.6; 
Percentage of product value, 2001: 27.6. 

Species: Salmon; 
Percentage of product value, 1994: 46.7; 
Percentage of product value, 2001: 35.1. 

Species: Other species[A]; 	
Percentage of product value, 1994: 25.9; 
Percentage of product value, 2001: 14.6. 

Species: Total; 
Percentage of product value, 1994: 100.0; 
Percentage of product value, 2001: 100.0. 

Source: GAO analysis of Alaska Department of Fish and Game, Commercial 
Operators Annual Report data. 

[A] Other species include crab, flounder, greenling, herring, lingcod, 
octopus, perch, prowfish, rockfish, shrimp, skate, sole, and turbot. 

[End of table] 

To determine the IFQ program's effect on processors, Alaska's 
Department of Fish and Game commissioned a study to examine how 
halibut and sablefish processors were affected economically.[Footnote 
5] This was the only study we could find that attempted to quantify 
the economic effect the IFQ program had on halibut processors. Using a 
sample of halibut processors, the study assessed the change in 
processors' gross operating margins (revenues minus variable costs of 
processing). The study used the periods 1992-1993 for pre-IFQ margins 
and 1999-2000 for post-IFQ margins. According to the study's principal 
author, these years were chosen because they provided the longest 
possible length of time between the pre-and post-IFQ years for which 
data were available. The study estimated that halibut processors 
suffered a 56 percent, or $8.7 million, loss in gross operating 
margins because the IFQ program caused halibut prices to increase and 
processors' market shares to change.[Footnote 6] 

While we could not validate or replicate the study's results because 
the proprietary data used in the study were confidential, we 
identified a number of concerns with the study's assumptions, 
representiveness, and potential for participant bias that brings into 
question the reliability of the study's estimates. First, we 
identified several issues of concern about the assumptions used in the 
study. For example, the study assumes that all costs, except labor and 
material inputs, remained fixed from 1992 through 2000. However, as 
pointed out in a critique of the study,[Footnote 7] this assumption 
would not be appropriate for a period as short as a year, and is 
clearly unjustified for the 7-year period evaluated, because the 
longer the time period assessed, the more likely costs will change. 

Even if the study's assumption about costs were valid, the pre- and 
post-IFQ periods examined identify a greater negative change in gross 
operating margins than might have been identified if different or 
longer periods had been used. The changes in gross operating margins 
and the estimated economic effects are influenced by the fact that ex-
vessel halibut prices dipped in the period 1992-1993 and were near 
their peak in 1999-2000. (See figure 2.) Ex-vessel halibut prices in 
1999-2000 were 44.5 percent higher than they were in 1992-1993. 
However, when different base years, such as 1991-1992, are compared 
with 1999-2000, the price increase is 22.7 percent. If these different 
periods had been used in the study, the estimated loss in processor 
gross operating margins would have likely been much less. 

Figure 2: Ex-Vessel Halibut Prices, 1984 through 2001: 

[Refer to PDF for image: line graph] 

The graph depicts halibut prices per pound, 1984 through 2001, with an 
indication that the IFQ program began in mid-1995. 

Source: GAO analysis of Alaska Department of Fish and Game, Commercial 
Operators Annual Report data. 

Note: Ex-vessel halibut prices were adjusted to 1996 dollars using the 
Bureau of Economic Analysis's Gross Domestic Product implicit price 
deflator. 

[End of figure] 

The influence of the choice of base years and the corresponding ex-
vessel prices can also be demonstrated by looking at the difference 
between the price a processor pays for raw fish and the price a 
processor receives for the processed fish—the processor's price 
margin. We calculated a simplified version of the price margin to 
demonstrate the sensitivity of the margin to the choice of the time 
period examined. As table 3 shows, comparing the study's pre- and post-
IFQ price margins of 47.3 percent and 24.1 percent, respectively, 
shows a 23.2 percentage point decrease in margins. However, comparing 
the price margins for 1991-1992 with 19992000 shows a 13.0 percentage 
point decrease and comparing 1993-1994 with 1998-1999 shows a 1.1 
percentage point increase. Again, the Alaskan study's estimated loss 
in processor gross operating margins would have likely been less if 
different time periods had been used. 

Table 3: Price Margins in Selected Pre- and Post-IFQ Years: 
		
Pre-IFQ	Years: 1991-1992; 
Pre-IFQ	Price margin[A]: 37.1%. 

Pre-IFQ	Years: 1992-1993[B]; 
Pre-IFQ	Price margin[A]: 47.3%. 

Pre-IFQ	Years: 1993-1994; 
Pre-IFQ	Price margin[A]: 30.3%. 

Post-IFQ Years: 1998-1999; 
Post-IFQ Price margin[A]: 31.4%. 

Post-IFQ Years: 1999-2000[B]; 
Post-IFQ Price margin[A]: 24.1%. 

Post-IFQ Years: 2000-2001; 
Post-IFQ Price margin[A]: 23.3%. 

Source: GAO analysis of Alaska Department of Fish and Game, Commercial 
Operators Annual Report data. 

[A] The price margin is the percentage by which real wholesale price 
exceeds real ex-vessel price, excluding other variable costs. We did 
not incorporate recovery rates (the amount of raw product required to 
produce the finished product) or product mix in price margin 
calculations. 

[B] Years used in the Alaska study. 

[End of table] 

Second, the study's results may not be representative of the industry 
as a whole. Responses were used from processors representing only 52 
percent of all halibut purchased in the pre-IFQ years and 61 percent 
of all halibut in the post-IFQ years.[Footnote 8] The study does not 
provide the actual number of participants whose data were used. 
Without knowing the number of participants or the characteristics of 
the respondents whose data were used, we cannot determine whether the 
study's estimates are representative of the industry as a whole. 

Third, the survey the study's authors used to request economic 
information from processors may have biased participant responses. In 
the preamble to the survey, participants were told, among other 
things, that the purpose of the study was to test the theory that a 
harvester-only quota allocation transfers wealth from processors to 
harvesters and that the survey's results would be used to assist in 
designing future IFQ or other fishery rationalization programs. Such 
statements leave little doubt as to how responses could benefit or 
harm processors with economic interests in other fisheries. According 
to standard economic research practice, these types of statements are 
to be avoided when designing a survey because they can influence the 
results. 

Several Methods Are Available for Protecting Communities: 

We identified several methods that could be used to protect 
communities. First, allowing communities to hold harvesting quota is 
the easiest and most direct way under an IFQ program to help protect 
fishing communities. According to fishery experts and participants, 
fishery managers can give each community control over how to use the 
quota in ways that protect the community's economic viability, such as 
selling or leasing quota to fishermen who reside in the community. 
Community quota could be held by municipalities, regional 
organizations, or other groups representing the community—unlike 
traditional individual fishing quota, which is generally held by 
individual boat owners, fishermen, or fishing firms. 

Second, fishery managers can establish rules governing quota 
transfers, i.e., quota sales-to protect certain groups of fishery 
participants. We identified the following approaches used in foreign 
IFQ programs that were aimed at protecting communities: 

* Prohibiting quota sales. Fishery managers in Norway prohibited all 
quota sales to protect fishing communities in certain locations. 

* Placing geographic restrictions on quota transfers. Iceland and New 
Zealand fishery managers have set limits on where quota can be sold or 
leased to protect certain groups, such as local fishermen and the 
communities themselves. The Icelandic IFQ program, in which 
individuals own vessels with associated quota rather than the quota 
itself, adopted a "community right of first refusal" rule to provide 
communities the opportunity to buy vessels with their quota before the 
vessels are sold to anyone outside of the community. New Zealand's 
Chatham Islands community trust has, in effect, used residence in the 
Chatham Islands as a requirement to lease its quota. 

Finally, according to fishery managers and experts we spoke with, 
fishery managers can help protect fishing communities by (1) setting 
limits on the amount of quota an individual or entity can hold, (2) 
requiring quota holders to be on their vessels when fish are caught 
and brought into port, and (3) restricting the ports to which quota 
fish can be landed. 

However, in designing and implementing community protection methods, 
fishery managers face multiple issues/challenges. How these 
issues/challenges are met depends on the fishery's circumstances and 
the program's objectives. First, fishery managers face an inherent 
tension between the economic goal of maximizing efficiency and the 
social goal of protecting communities. According to fishery experts we 
spoke with, this tension occurs because a community often may not be 
the most efficient user of quota. For example, according to Icelandic 
fishery experts, some communities did not have the knowledge and 
skills to manage their quota effectively and eventually sold it, 
reducing the communities' economic base. Adopting rules that constrain 
the free trade of quota, such as those designed to protect 
communities, would likely limit the efficiency gains of the IFQ 
program. Therefore, fishery managers have to decide how much economic 
efficiency they are willing to sacrifice to protect communities. 

Methods for protecting communities may also raise concerns about 
equity. In the United States, community quotas or rules aimed at 
protecting certain groups may not be approved because they are not 
allowed under the Magnuson-Stevens Act. For example, National Standard 
4 of the Magnuson-Stevens Act prohibits differential treatment of 
states. A rule that proposes using residence in one state as a 
criterion for receiving quota may violate the requirements of National 
Standard 4. Furthermore, methods that propose allocating quota to 
communities can appear unfair to those who did not benefit and could 
result in legal challenges. Moreover, allowing communities to purchase 
quota may be considered unfair or inequitable because relatively 
wealthy communities would more readily have the funds needed to 
purchase quota, while relatively poor communities would not. 

Second, fishery managers face several definitional issues in allowing 
communities to hold and trade quota, and communities must decide how 
to best use the quota. 

* Fishery managers need to define the community. However, fishery 
managers and experts told us that communities can be defined 
geographically, such as island communities, and nongeographically, 
such as fishermen who use the same type of fishing gear (e.g., hook-
and-line or nets) for a particular species. 

* Once fishery managers define the community, they must then determine 
who represents it and thus who will decide how the quota is used. More 
than one organization (e.g., government entity, not-for-profit 
organization, private business, or cooperative group) may claim to 
represent the interests of the community as a whole. For example, 
rural coastal communities in Alaska, which are geographically 
distinct, could have several overlapping jurisdictions, including a 
local native corporation, a local municipality, and a local borough. 

* Fishery managers also need to define what constitutes economic 
viability, which is likely to differ by community because the fishery 
has different economic significance in each community. Some 
communities primarily rely on fishing and fishing-related businesses, 
while others may have a more diverse economic base. Moreover, the 
balance of industries making up a community's economy may change over 
time when the area becomes more modernized or a new industry enters. 

* Community representatives have to decide whether to keep their 
quota, sell it, or lease it to others. If they keep their quota, they 
also have to decide how to allocate it. Similarly, if they sell or 
lease their quota, they have to decide how to allocate the proceeds. 
Unless communities can decide how to allocate quota or the proceeds, 
the community quota may go unused and thus prevent the community from 
receiving its benefit. For example, the quota New Zealand's Maori 
people received from the government in 1992 has not been fully 
allocated to the Maori tribes, largely because the commission 
responsible for distributing the quota and the tribes could not agree 
on the allocation formula.[Footnote 9] 

Third, along with these definitional challenges, fishery managers and
communities have to consider issues associated with quota transfers. 

* Prohibiting quota sales may not allow fishing communities or 
businesses to change over time as the fishing industry changes. 
According to fishery experts we spoke with, rules that prevent change 
essentially freeze fishing communities at one point in time and may 
create "museum pieces." For example, prohibitions on quota sales 
prevent the fishery from restructuring, thus forcing less efficient 
quota holders and fishing businesses to remain in the fishery. 
Consequently, prohibitions on quota sales may actually undermine the 
economic viability of the fishing communities they were designed to 
protect. 

* Geographic restrictions on quota transfers can be easily 
circumvented. For example, Icelandic officials told us that in their 
IFQ program, where individuals own vessels with associated quota 
rather than the quota itself, companies holding quota easily avoided 
the "community right of first refusal" rule by selling their companies 
as a whole to an outside company, rather than just selling their 
vessels and associated quota. As a result, communities could not use 
this rule to prevent the sale. Furthermore, communities that could 
benefit from such a rule may not have the money to purchase the quota, 
while those communities that can afford to purchase the quota may not 
need the rule's protection. 

Finally, fishery managers also face challenges associated with (1) 
setting limits on the amount of quota an individual or entity can 
hold, (2) requiring quota holders to be on their vessels when fish are 
caught and brought into port, and (3) restricting the ports to which 
quota fish can be landed. Monitoring and enforcing quota accumulation 
limits can be extremely difficult when fishermen create subsidiaries 
and complicated business relationships that enable them to catch more 
than the quota limit for an individual quota holder. Requiring quota 
holders to be onboard their vessels can be impractical, especially for 
small businesses where the same person would have to be on board at 
all times. According to fishery experts we spoke with, an onboard rule 
would require so many exceptions, such as for emergencies and illness, 
that it would be meaningless. Requiring fishermen to bring their catch 
into ports in a particular geographic area may not be healthy for a 
community's economy in the long term. Such a requirement may subsidize 
inefficient local fish processors that cannot compete on the open 
market. With reduced competition, these processors may offer less 
money for the catch, thus reducing the fishermen's income and 
ultimately harming the community. According to Shetland Islands 
fishery managers we spoke with, had fishermen been required to land 
their catch in the Shetland Islands, they would have received a price 
far below the market value, and the processor would have had no 
incentive to restructure into the competitive business it is today. 

Mr. Chairman, this completes my prepared statement. I would be pleased 
to respond to any questions that you or other Members of the Committee 
may have at this time. 

Contacts and Staff Acknowledgments: 

For further information about this testimony, please contact me at 
(202) 512-9846. Keith Oleson, Susan Malone, Mark Metcalfe, and Tama 
Weinberg also made key contributions to this statement. 

[End of section] 

Footnotes: 

[1] Pub. L. No. 94-265 (1976) (codified as amended at 16 U.S.C. §§ 
1801-1883. 

[2] Individual Fishing Quotas: Better Information Could Improve 
Program Management, [hyperlink, 
http://www.gao.gov/products/GAO-03-159] (Washington, D.C.: Dec. 11, 
2002) and Individual Fishing Quotas: Methods for Community Protection 
and New Entry Require Periodic Evaluation, [hyperlink, 
http://www.gao.gov/products/GAO-04-277] (Washington, D.C.: Feb. 24, 
2004). 

[3] 50 C.F.R. § 600.345(b)(3). 

[4] The market share of a company is the amount of halibut purchased 
by that processing company as a percentage of total halibut purchased 
by all processing companies. Processing companies, in this context, 
are those companies that own one or more of the individual shore-based 
plants that process halibut. 

[5] Matulich, Scott C., and Michael Clark, Efficiency and Equity 
Choices in Fishery Rationalization Policy Design: An Examination of 
the North Pacific Halibut and Sablefish IFQ Policy Impacts on 
Processors, Washington State University, January 2002. 

[6] The study also estimated that gross operating margins for 
sablefish processors decreased by 75 percent, on average. However, we 
did not review the sablefish estimates because the methodology and 
adjustments used in the study were not clear to NMFS economists or us. 

[7] Halvorsen, Robert, Comments on the Matulich and Clark Report, 
"Efficiency and Equity Choices in Fishery Rationalization Policy 
Design," University of Washington, April 2002. 

[8] In total, 53 halibut processors, representing 88 percent of all 
halibut purchased in the study years, were asked to participate in the 
survey. 

[9] In December 2003, legislation was introduced in the New Zealand 
Parliament that, among other things, sets out the allocation formula 
to be used to allocate quota to the Maori tribes. 

[End of section] 

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