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Quarter 2, 2001
by Miriam Wasserman
Fishing is the last commercial hunt on earth. While agriculture
long ago displaced hunting and gathering, providing a steady
source of food for cities and civilizations to expand, an
important share of the world’s population still depends on
the ability of fishermen to go out and catch fish in the wild.
And the prey are finding it harder to escape. Today’s fishermen
are equipped with global positioning satellite technology
that can help fishermen pinpoint and return to an especially
productive spot, fish finders that can help determine what’s
under the boat based on the fish’s swim bladders, and nets
made out of strong, synthetic materials that are invisible
to fish.
But fishermen are increasingly victims of their own success.
As more fishermen become more efficient, they can outstrip
the fish stock’s ability to replenish itself. The end result:
Greater and greater effort is required to catch a diminishing
number of smaller and younger fish. The combined effect, perhaps
together with other human activities such as those that generate
pollution, has led to flattening yields from ocean fishing.
As it is, over a quarter of the major marine stocks tracked
by the Food and Agriculture Organization of the United Nations
face diminishing catches or are showing very small yields
as they recover from near depletion.
At issue is not just humanity’s ability to catch fish. World
population growth has fueled demand. And technological innovations
ranging from the diesel engine to improved refrigeration have
facilitated trade and opened markets for fresh fish in areas
far from traditional coastal markets.
The oceans, which once seemed inexhaustible, have now shown
that their productivity has limits. After rising very rapidly
following World War II—in the face of increasing demand—the
growth of the world marine fish catch has leveled off at about
85 million tons per year since the 1990s.
This situation is having a deep impact on how we look at
our oceans and the right to fish. What used to be an open
field, where the adventurous and the skilled were free to
enter in pursuit of bounty, is increasingly regulated and
controlled. In particularly hard-hit areas, communities built
around fishing—where skilled fishermen passed their secrets
from generation to generation—have been left scrambling for
new ways to make a living. But, beyond the painful adjustments
made by any industry in transition, the matter touches on
vital costs that are harder to quantify, such as negative
impacts on marine biodiversity, and the health of ecosystems.
New England is ahead of the curve. In the early 1990s, the
collapse of several of the region’s principal groundfish—a
mixture of bottom-dwelling species including Atlantic cod,
haddock, and redfish—was one of the earliest signs of trouble.
The demise captured the imagination of many because cod fishing
is closely intertwined with the region’s history. (Those in
doubt should read Mark Kurlansky’s Cod: A Biography of
the Fish that Changed the World.) As members of the environmental
Conservation Law Foundation point out, “The threat of preventing
the spread of ‘another New England’ to other domestic fisheries
in the United States has been repeatedly used as a prod in
Congressional proceedings” on fishery legislation.
Today, New England offers a look ahead and a slightly more
optimistic outlook. After several years of draconian restrictions
imposed on the region’s fishermen, scientists see the beginnings
of a recovery. But difficult challenges remain. And, the ultimate
question facing the fisheries in New England and around the
globe is how to ensure that such painful collapses do not
happen again.
The common tragedy
(Chronicle of a tragedy foretold)
Fishing issues stir up heated debate. But in the collapse
of New England’s staple fish stocks, scientists, fishermen,
and managers now seem to agree on one thing: Too many boats
were chasing too few fish.
Distant-water fleets from Europe and Asia began working
the waters of the Northwest Atlantic after the Second World
War and landings of groundfish reached unprecedented heights
in the 1960s. By the late 1960s, the landings of cod from
foreign fishing vessels were close to triple those of Canadian
and American vessels combined. Fish stocks soon declined sharply
and, in 1977, Canada and the United States extended their
exclusive fishery rights to 200 nautical miles from their
shores. With the expulsion of the foreign fleets, the fish
stocks began to recover. But the domestic fleet exploded to
fill the void left by the foreign trawlers. As a result, in
the 1980s, far more fishing effort was being applied than
the stocks could support.
Finally, in the early 1990s, groundfish populations fell
to record lows and landings of the principal groundfish stocks
fell by 60 percent from the previous decade. These facts,
together with increasing pressure from environmental groups,
led to a halving of days at sea for all fleet sectors and
the closure of over 5,000 square nautical miles of prime fishing
areas.
Excessive fishing capacity is not unique to New England.
The rate of growth of the world’s fishing fleet during the
1970s was faster than that of fish landings. By the 1980s,
fishing fleets were about 30 percent greater than was needed
to catch the maximum sustainable level of fish worldwide,
according to researchers at the Worldwatch Institute. And
during the 1990s, the fishing fleet continued to grow in size
and sophistication, albeit more slowly.
The fundamental problem, according to economists, is that
fishing is an example of the “tragedy of the commons,” named
after the experience of fourteenth-century British villages,
which tended to have a common pasture for villagers to graze
horses, cattle, and sheep. In a pasture open to all, each
herdsman will try to keep as many animals as possible on the
commons. Each additional cow imposes costs on all the other
villagers whose cows must make do with less grass and who
jointly suffer the effects of soil erosion. But so long as
the price the individual herdsman receives by selling another
cow is greater than the costs he directly experiences, each
herdsman is likely to continue bringing additional cows to
the commons. And as the village grows in size and more and
more animals are placed on the commons, overgrazing ruins
the pasture.
Likewise, since no person or company owns the fish stocks
and, until recently, anyone who desired to was allowed to
fish, fishermen have the incentive to enter a fishing ground
so long as what they catch will cover the costs of their equipment.
The impetus is to catch as many fish as possible before other
fishermen get them—even if this undermines potential catches
in the future. Individual fishermen are not rewarded for self-restraint:
Any fish they leave in the water to allow the stocks to replenish
themselves are likely to be caught by someone else. This fierce
competition results in reduced incomes for fishermen as well
as in an inefficient use of capital for society: Money could
have been better invested in other industries.
The crux of the problem is that when fishing becomes excessive,
fish stocks shrink and their productivity diminishes. Fishermen
then have to scramble to catch the same number of fish that
they could have easily landed with a healthy stock.
The tendency toward overfishing has also been aggravated
historically by public efforts to build and sustain competitive
national fishing fleets. The growth and modernization of the
domestic fleet was encouraged in part by government subsidies.
Since the 1970s, for instance, fishermen have been able to
defer income tax on profits from fishing if the money was
set in a special account destined for the purchase or refurbishment
of a fishing vessel.
Some had hoped that fishermen and fish might be regulated
by a natural “predator-prey” cycle where a declining abundance
of fish would force some boats out of business until the reduced
fishing effort would permit stocks to grow, and fishermen
would reenter the industry. This may still be true in the
long term, but New England saw its groundfish stocks bottom
at levels far lower than ever expected, as rising prices helped
offset emptier nets. Moreover, while fishermen go out of business,
the boats may continue operating longer. “A steel-hauled trawler
has a lifecycle of about thirty years,” points out Steven
Murawski, chief of population dynamics at the National Marine
Fishery Service in Woods Hole, Massachusetts. Even when vessels
are repossessed by banks, they are likely to be resold at
lower prices and go right back to fishing.
Counting the fish in the sea
As the problems of overfishing have become evident, regulators
have used licenses to limit entry into most fisheries and
have furthermore imposed a variety of restrictions that aim
to match the level of fishing effort to the right number of
fish.
Any type of management regime must start with an estimate
of how many fish can be taken out of the ocean without harming
the future of the stock. And, for the most part, the fish
themselves are not particularly cooperative. Many of the species
migrate, disdainful of international or state borders and
other human jurisdictions, which complicates estimating populations
and exerting effective control over fishing activity.
“We have a task that is literally of biblical proportions—we
are trying to count how many fish are in the sea,” observes
Murawski, who is responsible for developing information on
marine fishery resources off the northeast coast of the United
States. Using the landings reported by the region’s fishermen,
information from scientific survey cruises, and other data,
his office puts together fish population estimates for New
England.
The specific details of each population and how it responds
to fishing vary widely from species to species. Some, like
the spiny dogfish—a small shark found in the North Atlantic
from Labrador to Florida—bear live young, with a gestation
period of about 18 to 22 months, producing an average of six
pups per female. This makes the dogfish population very vulnerable
to fishing—especially when effort is directed at the larger
females.
Others like cod, for instance, are incredibly prolific spawners.
A forty-inch female can produce three million eggs in a spawning.
Such fertility led people to think cod could not be overfished.
But, with experience, we have learned that very few cod eggs
reach maturity. Changes in currents and temperature, predators,
and a myriad other factors stand in the way of the eggs becoming
larvae, then juveniles, and finally adult fish. Because of
this, populations of cod can fluctuate widely from year to
year—which also complicates the estimation of the impact of
fishing on future populations.
Moreover, when it comes to fertility, not all fish count
equally. Managers try to ensure that young fish don’t get
caught so that they grow old enough to reproduce. But also,
they often want to protect some of the older, bigger fish
because they are more experienced and successful spawners,
as a higher share of their young seem to grow to adulthood.
In spite of the difficulties, scientists produce the best
picture they can of each fish population (with a margin for
error on either side), and they estimate the largest number
of fish that can be taken under existing conditions without
reducing the size of the stock.
In the case of New England, scientists were issuing warnings
of significant overfishing as early as the mid 1980s. According
to some experts, fishermen were taking up to six of every
ten adult fish each year, over twice the sustainable amount.
But misunderstandings and mistrust between scientists and
fishermen made it difficult to act on these warnings. Even
while scientists are issuing warnings of stock collapse, fishermen
may see increasing landings and healthy populations, notes
David Dobbs, author of The Great Gulf: Fishermen, Scientists,
and the Struggle to Revive the World’s Greatest Fishery.
Scientists may observe the abundance of females of a certain
size and age, for instance, or try to determine how many fish
are caught by a fixed level of effort; for their part, fishermen
will count the fish in their nets and use new technology to
catch fish—without taking into account how much increased
effort is being applied. The difficulties are, of course,
exacerbated by the fact that the scientific findings have
direct consequences for fishermen’s livelihoods.
In the midst of heated debates, managers and fishermen were
slow to heed the warnings. In the early 1990s, the experts’
pronouncements proved to be tragically accurate.
Matching boats to fish
Even when there is agreement on a target number of fish
that can be taken out, ensuring that this is the number that
winds up trapped in the nets is a difficult challenge. In
the United States, eight regional fishery management councils
are charged with developing plans to manage marine organisms
in their areas. The councils are composed of representatives
of commercial and recreational fishermen, as well as marine
scientists and state and federal fisheries managers. The different
regulatory regimes they have imposed run the gamut from fixed
limits on the amount of fish that can be taken out to limiting
licenses, to restrictions on vessels and gear, and even to
creating private ownership of fish quotas. However, each option
has its own costs and weaknesses.
With Alaska halibut, for instance, a decision was reached
in the late 1970s to set a total allowable catch and close
the fishery after this limit was reached. But this led to
a race to capture the largest share of the available quota.
Fishermen competed by building up their vessels and gear.
As a result, seasons became progressively shorter until by
the late 1980s fishing was limited to two 24-hour seasons
a year. “In a scene reminiscent of a horse race, fishing vessels
would line up, awaiting the opening of the season, and then
rush out, regardless of weather, to catch as much as they
could as quickly as they could,” observe Suzanne Iudicello,
Michael Weber, and Robert Wieland in Fish, Markets and
Fishermen: The Economics of Overfishing. In the mad frenzy,
accidents proliferated in an industry that already had the
highest number of work fatalities in the United States. Moreover,
as fish flooded the processing plants, consumers would see
short-term market gluts, and then face very high prices for
the rest of the year.
In contrast, fishery managers in New England have opted
for arriving at the desired level of catch indirectly, through
restricting the effort and gear that fishermen use. Managers
try to set regulations that reduce the efficiency of fishermen
to the level they think will approximate this catch by measures
such as limiting the number of days boats are allowed to fish,
limiting the areas available for fishing, and regulating mesh
sizes. This reduces somewhat the “derby” nature of fishing
and ensures that fresh fish are available more of the year.
But the regulations tend to become increasingly restrictive
as fishermen find new ways to increase their efficiency. If
vessels are restricted in their maximum length, for instance,
fishermen are likely to increase width or engine power. Furthermore,
adequate regulations may be slow in coming, particularly because
such actions can become highly politicized and end up pitting
different groups of fishermen against each other—say gillnetters
against trawlers, or big boats against small boats—as regulations
tend to hit some groups harder than others.
Alternatively, regulators could, at least in theory, design
a tax that would raise the costs of fishing to just the “right”
level to discourage an excessive catch. In this way, fishermen
would have greater freedom in choosing cost-effective gear,
while the government could collect and invest the tax revenues
productively. Yet, designing such a tax would be difficult,
especially in the face of continuously changing fishing technology
and widely variable fish populations. It would also be difficult
to implement in New England, where a large number of boats
and fishermen are already reeling from economic hardship.
A radically different approach is to address the ownership
problem that gives rise to the tragedy of the commons directly,
and grant fishermen the equivalent to private property rights.
This has been done in countries like Iceland and New Zealand,
as well as in some fisheries in Canada and the United States
(see sidebar). For instance, fishermen
are granted the right to a fixed share of the available quota;
these shares are tradable and their value depends on the health
of the fishery. Fishermen have less incentive to race each
other, as their catch is fixed. They can concentrate on finding
the most cost-effective way to harvest their allocation. And
they may also have an incentive to use gear that is more environmentally
friendly, or at least that minimizes the impact on the habitat
for the fish stock they have a stake in. Property rights will
also allocate wealth to fishermen by granting them, at zero
cost, a right that can be sold.
Nonetheless, this type of program is extremely controversial
because it dramatically alters the open approach to the oceans.
Opponents fear that these programs ultimately lead to consolidation
of quota shares, with big boats and businesses buying out
smaller mom-and-pop businesses and their traditional way of
life. This is especially of concern in New England, where
the fishing industry is currently composed of several thousand
independent boat owners. Creation of such property rights
could strain intricate social networks that go back for several
generations, and the special nature and attractive quaintness
of some traditional New England fishing communities could
be imperiled, points out anthropologist Madeleine Hall-Arber.
Private quota shares are also difficult to establish because
of the highly controversial questions of who is entitled to
quotas and how they should be allocated. And, once in place,
there is still a need for enforcement to ensure that no cheating
occurs. Of particular concern is the practice of “high-grading”
in fisheries where larger fish are more valuable and fishermen
could gain from dumping overboard smaller ones to maximize
the value of their quota.
Underwater parks
The difficulties in establishing or implementing the tried
policy options is feeding into the growing popularity of another
alternative—protecting marine areas in something akin to underwater
parks. Beyond frustrations with the current options, interest
in establishing such reserves stems from a recognition that
fish are parts of complicated ecosystems: While species are
managed individually, their fates are really interconnected.
For instance, managing species separately may not take into
account delicate predator-prey balances. Since the 1970s,
as the groundfish were being subjected to intense fishing
pressure, for example, the ratio of dogfish to groundfish
has doubled. This has caused some fishermen to worry that
dogfish would take over the niche of the groundfish and prevent
their recovery.
Also, managing each species independently makes it difficult
to take into account what impact regulations destined for
one species will have on others. When New England managers
drastically tightened regulations to protect groundfish, something
like a “domino effect” ensued: Boats turned their attention
to other species, including monkfish and dogfish, and soon
these came to be declared overfished as well.
In contrast, marine protected areas can help preserve entire
marine ecosystems and biodiversity, points out economist Priscilla
Brooks of the Conservation Law Foundation. A good example
is the barn door skate. Although the fish is not commercially
valuable, some thought it was destined for biological extinction
because its large size means that it gets trawled up as “bycatch”
before it reaches sexual maturity. However, this does not
look as likely now. Over 17,000 square kilometers in Georges
Bank and southern New England waters were closed to fishing
in 1994 as part of the drastic measures to protect groundfish.
Six years later, the barn door skate was showing greater numbers
than anybody had seen for a while.
Aside from the inherent (and unquantifiable) value to preserving
the variety of living organisms, species that are not commercially
valuable now may prove valuable resources for biotechnology
in the future.
Still, the extent to which marine protected areas can protect
stocks that are part of targeted fishing efforts is a current
topic of debate. Proponents argue that such reserves potentially
offer a hedge against management or implementation errors.
Some even claim that they may allow for larger stocks and
higher sustainable yields. But much remains to be studied.
The impact of protected areas will probably depend on, among
other things, their size; whether they cover a particular
type of habitat—such as a spawning ground of a particular
species; the types of species covered (the impact on scallops
would be very different from the effect on a highly migratory
species such as bluefin tuna); and what happens in the surrounding
area in terms of fishing effort and contamination or pollution.
New England offers a case in point: The areas closed in 1994
were aimed mostly at protecting groundfish. While, for the
most part, these are showing signs of recovery, it is difficult
to know how much of the improvements are due to area closures
and how much to other measures, such as halving available
days at sea, or the dramatically reduced fishing effort in
Canada.
Thinking long term
The collapse of some of the historically more important
fish stocks has left some clear and painful lessons. As fishery
scientist Murawski puts it, “The lesson about the hubris of
unlimited resources has been learned for this generation.”
And there are some hopeful signs of change.
What happened may be altering our way of responding to fishery
crises. One current example: Monkfish—a deepwater fish with
skin instead of scales that is prized for its sweet, firm,
white tail meat—was declared overfished by scientists in 1999
even as landings were at historically high levels. A monkfish
fishery was scheduled to be closed by May of 2002. But, fishermen
argued that the scientists run the fish surveys with equipment
that cannot accurately determine the state of the monkfish
population because it cannot reach as deep as is needed to
get to them. Now, instead of being locked in a self-defeating
argument, scientists and fishermen are collaborating in a
research project that is among the first of its kind. With
federal fishery disaster relief funding, fishermen and scientists
have jointly planned a survey of monkfish populations using
two chartered commercial vessels that can survey deeper waters
than the National Marine Fishery Service’s trawl vessels.
The project may lead to a reassessment of the status of the
monkfish stock. It may also aid scientists who will benefit
from the knowledge accumulated in fishermen’s experience and
help to improve the understanding between fishermen and scientists.
Similarly, while fishermen of old spent centuries designing
technology to hunt the very last fish, new developments are
more likely to focus on how to make fishing more precise and
less harmful to the fish’s habitat. Dolphin-safe fishing methods
for tuna and Nordmore grates used by shrimpers to allow unwanted
fish to escape their nets are already common. Still, much
remains to be learned about fish biology and the way in which
species interact amongst themselves and with fishermen.
But perhaps the greatest challenge lies above water: how
to get fishermen, managers, scientists, environmental groups,
and all who have a stake in the health of our oceans to come
up with a shared vision of what the fishing industry can look
like, in a way that ensures its long-term economic health
and protects marine biodiversity. Though there are many options,
there are no clear right answers at this point. What is certain
is that the days of the last unlimited commercial hunt are
probably over.
| The Collapse of the Groundfish |
| Landings of these groundfish
species peaked in the 1960s under intense fishing from
foreign fleets. After the foreign vessels left, catch
levels recovered slightly before plummeting to record
lows in the early 1990s. |
| 
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| Source: Murawski et al.,
Groundfish Stocks and the Fishing Industry. Updated
by Steven Murawski.
Note: Landings are for the Northwest Atlantic from Labrador
to North Carolina. |
| The Beginnings of a Recovery |
| As fishing restrictions have
taken effect, the share of fish populations harvested
each year has decreased, and the collective mass of all
the breeders in the population is beginning to increase.
|
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| Source: Murawski et al., Large-Scale
Closed Areas as a Fishery-Management Tool in Temperate
Marine Systems: The Georges Bank Experience. Updated
by Steven Murawski. |
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| Is Farming an Alternative?
Much as the development of agriculture reduced the
dependence on hunting and gathering and increased food
supplies for human societies, fish farming or aquaculture
can help ease some of the constraints on natural fish
supplies. Farming also eliminates altogether the issue
of “overfishing” the natural stock. And, having a private
owner allows fishing to be run as a regular business,
making it more likely that inputs and investment will
be commensurate with maintaining the long-term level
of fish production.
People have been farming fish for many centuries (fish
farming was invented in China over three thousand years
ago). But it wasn’t until the 1950s that the production
of fish at an industrial scale really started taking
off. Since then, inland and marine aquaculture has been
growing rapidly—about 10 percent per year in the 1990s,
according to the Food and Agriculture Organization of
the United Nations. Indeed, as the catch from wild marine
species has leveled off, the main growth in the supply
of fish has come from fish farming. Today, as much as
25 percent of the fish consumed worldwide is grown in
farms.
American consumers may be well acquainted with the
farm-raised salmon, catfish, and shrimp commonly served
in restaurants. Still, carp grown in Asia (especially
China) currently accounts for the largest share of farm-raised
fish.
But fish farming is not without problems. The farming
of salmon and shrimp in particular can pose a threat
to wild marine stocks. Unlike carp and catfish, salmon
eat other fish, so salmon farms do not reduce the pressure
on wild stocks. The diet of farmed salmon consists of
fishmeal from anchovies or herring, among others, and
it can take up to five tons of landed fish for each
ton of salmon produced, according to a report of the
Worldwatch Institute. In addition, since farmed salmon
are bred for fast growth and not for survival in the
wild, some worry that if they manage to escape and breed
with wild salmon they might weaken the wild stock’s
capacity to survive.
Likewise, shrimp—mostly farmed in developing countries
such as Thailand—are often produced by clearing coastal
mangrove forests that serve as nursery habitats for
local fish, and thus can end up leading to the decline
of wild stocks.
Greater efforts and attention are being placed on
addressing some of the negative environmental impacts
of aquaculture. Many have experimented with sterilizing
farmed fish so that they don’t breed with wild ones,
for instance. But fish farming remains controversial
in many places, and managing the concentrated refuse
produced is always a challenge.
Fish farming is expected to continue growing at the
same clip in the next couple of years. But, unless the
wild stocks become exceedingly scarce and greater technological
innovations in fish farming are made, our reliance on
wild fish stocks is not likely to go the way of hunting
and gathering anytime soon.
Of Chowder and Private Rights
How Individual Transferable Quotas Transformed Clamming
In 1990, the surf clam and ocean quahog fisheries became
the first in the United States to be managed through
individual transferable quotas (ITQs), a system in which
fishermen have private rights to a share of the catch.
Since these fishing shares can be traded, the most efficient
fishermen can buy shares from others who, in turn, are
able to receive compensation for exiting fishing—and
total fishing capacity can be reduced.
Well before the establishment of ITQs, in the early
1970s, surf clam fishing—particularly in the Mid-Atlantic—had
been rocked by wild boom and bust cycles driven by a
combination of overfishing and natural disasters. A
particularly bad period of low dissolved oxygen in the
waters off of New Jersey killed a large portion of the
surf clam stock and gave momentum to prevent the unregulated
industry from harvesting the remaining clams into economic
extinction.
Thus, in 1977, the Mid-Atlantic surf clam fishery
instituted a total allowable catch and became the first
in the nation to limit the entry of new vessels. Fishing
time limits per vessel also were instituted to spread
the catch over time.
Though the idea of allocating a share of the quota
to individual vessels was present from the beginning,
instituting such a system was stymied by arguments about
how to allocate the valuable shares, given large differences
in interest and power in the industry, according to
Sharing the Fish, a report by the National Research
Council.
Owner-operators and small fleet owners, for instance,
resisted an early proposal to allow fishermen to trade
and consolidate allocations of fishing time because
they feared that this would give unfair clout and advantage
to larger owners. “Everyone had a different point of
view and they were watching out for their own interests,”
explains David Wallace a former surf clam fisherman
and industry consultant. Also, the idea of allocating
quotas to vessels was problematic to many, as it was
tantamount to giving away a public resource.
While the debates raged, the capital invested in the
fishery steadily increased. Though the total number
of participating ships remained the same, the number
of small vessels decreased as they were replaced by
bigger and more powerful boats. As a consequence, allowed
fishing time steadily decreased until, in 1987, surf
clam boats were allowed to fish only eight hours out
of every month, even though the harvestable clam population
had greatly increased.
Finally by 1988, the Mid-Atlantic Fishery Management
Council created ITQs that could be freely sold and traded.
Quota shares were divided among the owners of vessels
that had harvested surf clams and ocean quahogs in the
previous decade, according to complicated formulas which
varied by region and were based on catch history.
Since the introduction of the ITQ program in 1990,
the surf clam and ocean quahog industries saw dramatic
change. The number of vessels active in both fisheries
has declined markedly—from 133 vessels harvesting surf
clams in 1988 to 48 by 1994 and, similarly, from 62
to 35 in the ocean quahog fishery over the same period.
About one-third of vessel owners stopped fishing and
leased out their quotas. At the same time, total employment
in the clam fishing industry declined, but full-time
employment became more common.
Thus, the ITQ program helped address the vexing issue
of excess capacity. But whether or not it is applicable
to other fisheries is not clear. The surf clam and ocean
quahog industries were much smaller and more concentrated
to begin with than say, the groundfish fleets, which
consist of more than 3,000 vessels distributed over
a much larger geographic area. The surf clams and ocean
quahogs are relatively easy to target, and their extraction
is more akin to mining than to fishing (they get dug
out of the ground with large dredges, in a way that
makes it less likely that other species get harvested
at the same time). In contrast, groundfish involve a
mix of several different species that share the same
habitat. The number of landing sites for the clams was
relatively small, facilitating enforcement of regulations.
And, the industry was not in direct competition with
other interest groups such as recreational fishermen
and environmentalists.
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