Regular readers of this blog know that I am an enthusiastic
supporter of the Magnuson-Stevens
Fishery Conservation and Management Act, and more particularly, of the
conservation and management provisions of that act which prohibit overfishing
and require the timely rebuilding of overfished stocks.
Those regular readers also know that I am a frequent critic
of the Atlantic States Marine Fisheries Commission, and other state management systems,
largely because they don’t have such legally-enforceable requirements, and often
make decisions in which economic, political and social considerations are elevated
above the need to maintain and restore healthy fish populations.
To that end, it’s probably worth noting that ASMFC’s
former vision statement
“Healthy, self-sustaining populations for all Atlantic coast
fish species or successful restoration well in progress by the year 2015”
has been abandoned, and has been replaced by
“Sustainably Managing Atlantic Coastal Fisheries.”
All mention of “healthy”populations and “successful
restoration”, much less “by the year 2015”, has been deleted, which probably
makes sense from ASMFC’s standpoint, as the aspirations expressed its previous vision
statement, while certainly noble and worthwhile, were never matched by the
organization’s real-world accomplishments, largely because the lack of legally-enforceable
standards made it easy for ASMFC’s various species management boards to avoid
making the kind of hard, but always unpopular, decisions that are often needed
to successfully restore badly depleted fish stocks
ASMFC’s management process was criticized once again last November.
Prior
to that meeting, the Management Board had been deluged with comments from the
public, which overwhelmingly supported the adoption of interim biological
reference points, which would have required managers to consider menhaden’s
role as a forage fish, and not just fishing’s impact on the sustainability of
the stock, and opposed any increase in menhaden harvest. However, in the end, the Management Board
voted the other way, rejecting the interim reference points and increasing the
annual catch limit.
Such votes came as a surprise to many in the conservation
community, including both the professionals at various non-governmental
organizations and the many concerned individuals who thought that Management
Board failed to properly represent the public’s interest in a healthy menhaden
stock, and instead bent over backward to accommodate the demands of both the
Commonwealth of Virginia, which had previously been granted about 85% of the
overall menhaden harvest, and Omega
Protein Corporation, which harvests an overwhelming majority of the Virginia
allocation.
During the many post-mortems that took place after the
Management Board met and made its decisions, some folks blamed the outcome on ASMFC’s
legally unfettered approach to fisheries management, and argued that the outcome
would have been quite different had menhaden been managed under
Magnuson-Stevens.
It’s an interesting argument, and one worth a bit of thought.
Although Magnuson-Stevens is a long and complicated law, its
strength and effectiveness as a conservation tool can be boiled down to a few
key provisions.
One is the concept of “optimum” yield, which for purposes of
this discussion can be defined as
“…the amount of fish which will provide the greatest overall
benefit to the nation, particularly with respect to food production and
recreational opportunities, and taking into account the protection of marine ecosystems
[and] is prescribed as such on the basis of the maximum sustainable yield from
the fishery, as reduced by any relevant economic, social, or ecological factor…”
Such key provisions also include National Standards One and
Two, which require that
“Conservation and management measures shall prevent
overfishing while achieving, on a continuing basis, the optimum yield from each
fishery for the United States fishing industry,”
and
“Conservation and management measures shall be based on the
best scientific information available.”
Finally, to assure that healthy stocks are maintained at
sustainable levels and that depleted stocks are returned to health,
Magnuson-Stevens requires that each regional fishery management council
“develop annual catch limits for each of its managed
fisheries that may not exceed the fishing level recommendations of its
scientific and statistical committee or the peer review process…”
and that
“for a fishery that is overfished, any fishery management
plan, amendment, or proposed regulations…shall specify a time period for
rebuilding the fishery that shall be as short as possible…and not exceed 10
years, except in cases where the biology of the stock of fish, other
environmental conditions, or management measures under an international
agreement in which the United States participates dictate otherwise… [internal numbering omitted]”
ASMFC isn’t legally bound by any of those guidelines, so the
question to be asked is, had menhaden been federally managed rather than
managed by the states through ASMFC, would the outcome have been any different?
The
most recent benchmark menhaden stock assessment, accepted for management use in
2015, found that
“Based on the current adopted benchmarks, the Atlantic menhaden stock status is not
overfished and overfishing is not occurring. In addition, the stock is currently below the
current fishing mortality target and above the current [fecundity] target [an
estimate of the eggs produced by the stock, used in place of a biomass reference
point]. The fishing mortality rate is
currently at F65% which is the lowest [fishing mortality rate] in
the time series.”
That being the case,
even if the menhaden stock was federally managed, or if ASMFC was bound by the
language of Magnuson-Stevens, neither the overfishing prohibition in National
Standard One nor the 10-year rebuilding requirement would have prevented
managers from making the same decisions that were made in November.
However, that still leaves open the question of whether the
annual catch limit adopted by the Management Board would constitute “optimum”
yield as defined in federal fisheries law.
Arguments can easily be made that it would not. But those arguments would not reflect a
consensus on what the optimum yield ought to be; factions supporting either a
higher or a lower annual catch limit would each be able to cite language and
data that justifies their positions.
On
December 20, 2017, Virginia did, in fact, appeal the Management Board’s
decision, arguing in part that the annual catch limit was set too low. Virginia noted that
“the [Management] Board was presented with information
indicating that raising the [total allowable catch] to 220,000 metric tons
would result in absolutely no risk of the fishing mortality target being
exceeded and raising the [total allowable catch] even higher would result in
only a small risk of exceeding the target…The Board raised the [total allowable
catch] by 8%, setting it at 216,000 metric tons…
“In sum, the Board’s decisions on the [total allowable catch
and other, related matters]…are excessively restrictive and unnecessary for the
conservation of the menhaden fishery, should not be allowed to persist. Virginia believes that the Interstate Fisheries
Management Board should instead order that the total allowable catch be set at
220,000 metric tons…”
A
letter from ASMFC’s Chairman, James Gilmore of New York, made it clear that
ASMFC will not accommodate that request, although it is willing to hear an
appeal on the related, reduced cap on menhaden harvest in Chesapeake Bay. Would the catch limit have been any higher if
menhaden were federally managed?
Maybe.
The question is whether a higher catch limit would provide “the
greatest overall benefit to the nation,” and that’s a debatable question.
Certainly, a larger harvest would, at least
in the short term, provide a greater economic benefit to menhaden fishermen and
the menhaden industry, so in that respect, a 220,000 metric ton annual catch limit
would provide a greater economic benefit than one of
216,000 metric tons.
However, setting optimum yield requires that factors other
than just economic gains be considered.
In
determining “the greatest overall benefit to the nation,” managers are directed
to give particular consideration to “food production and recreational
opportunities.” Neither such factor is
directly relevant here, although the argument could be made that abundant
menhaden and other forage fish sustain and concentrate important food and
recreational fish species, and in that way enhances both food production and
recreation.
But ecological factors also come into play. In determining optimum yield, managers are
directed to “[take] into account the protection of marine ecosystems” and are
authorized to set optimum yield at some level below maximum sustainable yield
if justified by any “ecological factor.”
The conservation community and the vast majority
of those who submitted public comments made just those points: That interim ecological reference points were
needed, and no harvest increase should have been considered, because of
menhaden’s importance to the marine ecosystem as a forage fish.
Based on those arguments, had menhaden been federally
managed, there is good reason to believe that interim ecological reference
points would have been adopted, and the annual catch limit would not have been
increased—provided that the requirements of National Standard Two were
met: Such interim reference points, and such
lower catch limit, would have to be justified by the best available science.
And that’s exactly where things fell apart at the Management
Board.
While few fisheries managers seriously doubt the important
ecological role played by menhaden, and the effort to calculate
menhaden-specific environmental reference points received wide support, the
interim reference points preferred by most of the public, including me, turned
out to be badly flawed, in a way that we all originally missed.
The preferred interim points, designated “Option E” in a
draft document released by ASMFC, would have set a target menhaden biomass
at 75% of the biomass of an unfished stock, and set a threshold biomass
at 40% of a virgin population. Remedial
management action would only be required if biomass fell below the
threshold level.
The problem with those reference points is that biomass
includes all individuals in the population, immature fish as well as
spawning-age adults. And in the case of
relatively short-lived forage fish such as menhaden, which are eaten by just
about every larger predator that swims in or flies above the coastal sea, a lot
of the biomass is made up of individuals that are too young to reproduce, while
most of the fishing effort targets the sexually mature fish. As a result, as explained at the November
meeting,
“if you were to ramp up fishing mortality to the level that
would allow you to achieve that threshold level, the vast majority of the
biomass exists in [zero year old fish] and [one year old fish] and then as you enter the [two year old fish]
the population really starts to decay for fishing and natural mortality and all
of those reasons.
“That is why the foible of that particular part of the
[environmental reference points] exists, and that is you can really whack those
older ages and drive them down to near zero; but you still have enough biomass
in the zeros and ones and twos to meet that metric. But if you were to then compare it to your
fecundity metrics that you had been using that is where you would see the big
difference.”
Thus, had menhaden been federally managed, it’s possible—but
by no means certain or perhaps even probable—that the annual catch limit would
not have been increased.
On the other hand, the preferred interim ecological
reference points would still have been doomed. National Standard One prohibits overfishing,
and overfishing occurs when
“[the] level of fishing mortality…jeopardizes the capacity of
a fishery to produce the maximum sustainable yield on a continuing basis.”
And since, as explained at the November meeting, the level
of fishing mortality proposed in the favored interim reference point would have sharply reduced the fecundity of the stock, to a point where the spawning stock
biomass would be “driven down to near zero,” such
interim reference points would not meet the minimum standard established by
Magnuson-Stevens.
Thus, the fate of such interim reference
points would have been no different had menhaden been federally managed.
However, as this discussion demonstrates, what Magnuson-Stevens
would have brought to the table is an orderly set of standards that could have been used to evaluate the various management options, a sort of structured analysis
that is often absent at ASMFC.
While, with respect to menhaden, the result would probably
have been the same regardless of the management body, that is often not the
case, and it is difficult to argue that the ASMFC process would not be improved
and made more effective if the Atlantic States Marine Fisheries Commission was
bound by the same sort of objective legal standards that bind federal managers.
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ReplyDeleteThank you for this insightful post, Charles, and for planting a seed.
DeleteIt is probably time to look at the system as a whole to figure out a better way to manage ALL species under the ASMFC. Of the 27 species they manage, by my count, 17 of them are either "overfished" or "depleted," or their status is "unknown." (see: https://www.asmfc.org/files/pub/ASMFC_StockStatus_Jan2016.pdf)
And even this evaluation is generous since it's based on an antiquated "single species" construct of what constitutes effective management. As you point out, they do not consider "Optimum yield."
This is an unacceptable track record and Congress should either abolish the ASMFC, putting all fisheries under the Magnuson Act, or they should provide much stronger guidance for management. The ASMFC has no accountability and states appear to "horse trade" species.
I disagree with your conclusion that the best available science did not justify stronger action by the ASMFC on menhaden in November. In fact, the best available science justified much stronger action, with the implementation of Option C, a hockey stick control rule--and huge reductions in catch. Option D, leaving 75% of the unfished biomass was not bad either. And option E, which you highlight, was more justified by science than status quo management that allows for a 40% increase in catch. More than 100 scientists said so.
However, my interest at this stage is in how to build new accountability into the ASMFC management system. Something needs to change.
Thanks for the thoughts. I agree that ASMFC needs standards; the history of tautog management probably illustrates that better than anything else, with ASMFC kicking the can down the road for 20 years before taking some sort of hopefully effective action--and even then, allowing overfishing to continue in Long Island Sound because the for-hire fleet very noisily objected to needed restrictions.
DeleteAs far as the best available science goes, while I agree that it may have supported adopting some sort of interim ecological reference point last year--although I question whether ERPs based on Krill are necessarily appropriate for finfish--the key was basing such ERPs on overall biomass rather than SSB. If there was an SSB-based ERP, I think that it may well have been adopted, because even conservation-oriented commissioners who I know had concerns about the implications of using biomass that I described in my post
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