Tomorrow, the Atlantic States Marine Fisheries Commission will be holding a webinar/hearing on the proposed “Recreational Harvest Control Rule.” I probably should listen in, and perhaps provide comment, but I haven’t registered for the webinar yet, and I’m still not sure that I will.
Usually, I comment on management proposals out of a
long-held belief that public input, if well-thought out and properly presented,
can have a meaningful effect on the management outcome. I’ll admit that, at times, trying to move the
management process feels a lot like banging my head against a brick wall. But over the years, I have also had regulators
ask for my thoughts on various proposals and mention testimony I made at hearings
some weeks after the fact, indications that public input was being heard
and valued.
That’s how the fishery management process is supposed to
work, with science shaping the management options and the public—the
ultimate owner of all the nation’s living marine resources—shaping the
policy decisions that determine which of the various science-based management
measures will ultimately be adopted.
Unfortunately, the fishery management process also has a
political component, and when politics ends up driving that process,
both good science and good public policy often end up riding in the back seat,
where they can be all too easily forgotten and ignored.
That seems to be what’s happening with the Recreational Harvest
Control Rule.
That’s what happens when politics takes control. And we should have no doubt that politics, and
representatives of the recreational fishing industry, rather than
representatives chosen by recreational fishermen, is driving the Control Rule
process.
The history of the Control Rule arguably dates back to federal legislation
called the Modernizing Recreational Fisheries Management Act of 2018—better known
as the “Modern Fish Act”—which was largely
an effort by various angling industry and industry-affiliated organizations to
find a way to kill more red snapper in the South Atlantic and Gulf of Mexico
than was possible under existing law.
In an effort to circumvent legally-mandated annual catch
limits that restrict recreational red snapper landings to sustainable levels,
the Modern Fish Act amended the
Magnuson-Stevens Fishery Conservation and Management Act by, among other changes, adding a finding that
“While both provide significant cultural and economic
benefits to the Nation, recreational and commercial fishing are different
activities. Therefore, science-based
conservation and management approaches should be adapted to the characteristics
of each sector.”
To further that finding, the Act added another amendment that
gave regional fishery management councils
“the authority to use fishery management measures in a
recreational fishery (or the recreational component of a mixed-use fishery) in
developing a fishery management plan, plan amendment, or proposed regulations,
such as extraction rates, fishing mortality targets, harvest control
rules, or traditional or cultural practices of native communities in
such fishery or fishery component.
[emphasis added]”
However, the Modern Fish Act also made it clear that the
existing provisions of Magnuson-Stevens that required regional fishery management
council actions to prevent overfishing, timely rebuild overfished stocks, establish
binding annual catch limits, and require fishermen to be held accountable for exceeding
their catch limits remained in full force and effect.
While the effort to undermine federal red snapper management
was unsuccessful, it probably isn’t surprising that many of the
same affiliated recreational fishing industry organizations—the American Sportfishing
Association, Center for Sportfishing Policy, Coastal Conservation Association,
Congressional Sportsmen’s Foundation, National Marine Manufacturers’
Association, and Recreational Fishing Alliance—sought another opportunity
to undermine Magnuson-Stevens’ disciplined, science-based management process,
perhaps hoping that if “alternative” management measures could be established
in any recreational fishery, anywhere in the country, that precedent might allow them to convince southern
fishery managers to place less emphasis on annual catch limits and excessive
recreational landings in the southeastern red snapper fisheries. Thus, such organizations proposed what has now
become the Recreational Harvest Control Rule in the Mid-Atlantic.
Mid-Atlantic fisheries were particularly vulnerable to such
an effort, as there was wide discontent, particularly among the party boat
fleet, with the Mid-Atlantic Fishery Management Council’s approach to black sea
bass management. While spawning stock
biomass was well over twice the target level, indicating a more-than-healthy
stock, recreational management measures were growing steadily more restrictive
due to the high level of recreational fishing effort and the resulting high landings,
a situation that was tailor-made for industry spokesmen who sought to inflame
opinion against the federal fishery management process.
“One really important issue that the [Mid-Atlantic Council’s
Fishery Management Action Team] highlighted was it doesn’t seem like this
approach as described would be necessarily feasible under the current Magnuson
requirements for catch limits and accountability measures.”
Thus, many of the traditional advocates of science-based
fishery management were lulled into complacency, believing that the Control
Rule was headed for a dead end. The industry,
however, worked with both the National Marine Fisheries Service and the
Atlantic States Marine Fisheries Commission to come up with revisions to its
original proposal that might, in theory, satisfy Magnuson-Stevens’ requirements.
It’s far from impossible that one or more of the
Recreational Harvest Control Rule proposals will fully meet the legal standards
imposed on federal fishery managers. The
problem is that, because the Control Rule effort has been hijacked by politics,
the process is being rushed toward completion before the scientific merits of
the Control Rule have been fully explored; the public is being asked to comment
on management proposals without being given the information needed to know how
such proposals will impact the long-term health of managed fish stocks.
Which is why I’m not sure that I’m going to
participate in tomorrow’s public hearing.
I lack the information that I need to make informed comment. It’s clear
that the only other comment that I could make—that the process ought to slow
down until the public can be fully informed, and is able to make intelligent
comment—would be completely ignored, overridden by the political desire to have
the Control Rule in place before the 2023 fishing season.
Neither state nor federal fishery managers want to adopt
regulations that would further restrict black sea bass fishermen, even if 2022 recreational
landings far exceed the recreational harvest limit for the year. That message came through loud and clear when
the Mid-Atlantic Council and the ASMFC’s Interstate Fishery Management Program
Policy Board met last February; members’ concerns about moving too quickly were
swiftly dismissed by other members’ deep reluctance to adopt more restrictive
2023 rules.
So, as I mentioned in the blog that I published in March,
both the Council and the ASMFC seem Hell-bent on approving the Control Rule for
the 2023 season, despite the fact that models
deemed “critical” to the Control Rule will not be ready by that time, with one
ASMFC representative justifying such haste by explaining—if that’s the right
word—that such models were
“critical, not required.”
That sort of attitude, which prioritizes getting the Control Rule done quickly, rather than getting the Control Rule right, has characterized the entire Control Rule process.
Tomorrow night, New York stakeholders will be asked to
comment on four possible approaches to the Control Rule. In making their comments, they will be relying
on the ASMFC’s Draft
Omnibus Addendum to the Summer Flounder, Scup, and Black Sea Bass Fishery Management
Plan and Bluefish Fishery Management Plan, which sets out the four
approaches in detail.
Such draft addendum informs stakeholders that one option,
the “Percent Change Approach,” differs from current management in that
“it includes additional consideration of biomass compared to
the target level (B/Bmsy) when determining if the recreational
management measures should be liberalized, restricted, or remain
unchanged. The amount of change varies
based on the magnitude of the difference between a confidence interval (CI)
around an estimate of expected harvest and the average [recreational harvest
limit] for the upcoming two years, as well as considerations related to biomass
compared to the target level (B/Bmsy).”
It then goes into more detail explaining how the approach
works.
The draft addendum then goes on to describe the “Fishery
Score Approach,” explaining
“The fishery score is a formulaic method that combines multiple
metrics into one value which is used to determine the appropriate management measures. Based on the score, the stock would be placed
in one of four bins with corresponding management measures. The fishery score would be based on four metrics:
biomass (B) relative to the target (Bmsy), recruitment (R), fishing
mortality (F), and fishery performance…Each metric has a weight assigned to it,
determined by the Technical/Monitoring Committee such that metrics with a
stronger relationship to harvest would have more weight in the fishery score
while still accounting for metrics that impact harvest but may not drive
harvest. Additional metrics may be added
and weighting schemes adjusted as more data become, [sic] based on the
recommendations of the Monitoring/Technical Committees.”
Again, more details of how the approach would work were provided.
Then there was the “Biological Reference Point Approach.”
“Under this option, the primary metrics of terminal year B/Bmsy
and F/Fmsy from the most recent stock assessment would be used to
guide selection of management measures.
Management measures would be grouped into seven bins…Each bin would have
a set of default measures which would be implemented the first time the stock
in placed in that bin.
“To define the bins under this option, fishing mortality (F)
would be considered in two states:
overfishing (F greater than Fmsy) or not overfishing (F equal
to or below Fmsy). B/Bmsy
would be further divided to provide more responsive levels of access based on
the following:
·
Biomass is greater than or equal to 150% of
target.
·
Biomass is greater than or equal to the target
but less than 150% of target.
·
Biomass is less than the target, but greater
than or equal to the threshold (the threshold is ½ the target).
·
Biomass is less than the threshold (the stock is
overfished).
“Recruitment and trends in biomass are secondary metrics
under this option which are used to fine tune the default measures only
when stock conditions (F/Fmsy and B/Bmsy) relative to the
categories above have not changed between the prior and most recent
assessments. In this case, biomass trend
and a recruitment metric…can be used to further relax, restrict, or re-evaluate
measures. As such, biomass trends and
recruitment would impact the management measures, but to a lesser extent than
F/Fmsy and B/Bmsy.”
I’m sure that, to most anglers and other stakeholders
planning to comment on the draft addendum, such explanation, and the details
that followed, made the merits of this approach perfectly clear…
Finally, there is the “Biomass Based Matrix Approach.”
“This option uses a matrix to set recreational measures based
on two factors: B/Bmsy and
the most recent trend in biomass (increasing, stable, or decreasing)…Using
these two factors and four parameters for each…provides a three-by-four matrix
to determine the appropriate management measure bin. Bin A represents the optimal conditions,
while Bin F represents the worst conditions.
Certain pairs of conditions (e.g., a healthy stock that is increasing or
an abundant stock with any biomass trend) are treated as equivalent to reduce
the number of bins to six.”
Based on those four descriptions, supported by pages of
additional details, do you believe that you could pick the best management approach
to use for the Control Rule? Do you
believe that the average stakeholder attending the hearing could do so?
I do my best to stay on top of the fishery management
process, and think that I have a pretty good layman's understanding of the science
underlying management issues, but I freely admit that I have no idea how to
compare the merits of each possible Control Rule approach.
I suspect that the people who developed the four approaches couldn’t
explain their relative merits, either.
I harbor that suspicion because I took the trouble to ask.
When I attended the Saltwater
Recreational Fishing Summit a couple of weeks ago, I happened to run into a
member of the Mid-Atlantic Council staff who was very familiar with the development
of the Control Rule, along with a NMFS staffer who was also involved with the development
process. Over the course of our
conversation, I expressed my view that the process was being rushed along far
too quickly, and asked a few questions that the other folks could not readily answer.
The NMFS staffer tried to justify the undue haste by parroting the Modern Fish Act argument that recreational and commercial fisheries are different, and should be managed differently.
I don’t disagree with the staffer’s assertion.
The problem is that the biggest difference between the two
sectors is that commercial landings are reported by every commercial fisherman, confirmed
by reports filed by the fish buyers, and can be tabulated in near real time,
making commercial data both accurate and timely. Recreational
landings data, on the other hand, are derived from the Marine Recreational Information
Program surveys, and thus necessarily contain a significant degree of uncertainty.
Because of such management uncertainty, recreational
fisheries should be managed more conservatively, to account for the inevitable
errors. But the Recreational Harvest
Control Rule does just the opposite, creating greater opportunities for the
recreational fishing sector to exceed its catch limits, while the commercial
fishing sector, despite its far less uncertain data, is held to hard quotas and
mandatory pound-for-pound paybacks of any overages.
“Government counsel conceded at oral argument that, to meet
its statutory and regulatory mandate, the [National Marine Fisheries] Service
must have a ‘fairly high level of confidence that the quota it recommends will
not result in [fishing mortality] greater than [the target fishing mortality].’ We agree.
We also hold that, at the very least, this means that ‘to assure’ the
achievement of the target [fishing mortality], to ‘prevent overfishing,’ and to
‘be consistent with’ the fishery management plan, the [total allowable
landings] must have at least a 50% chance of attaining [such fishing mortality
target]. [citations omitted]”
Yet when I asked the Council staff member whether the
Control Rule would allow such staff member to say, with confidence, that there
would be at least a 50% chance of preventing overfishing or exceeding the catch
limit, I couldn’t get a clear answer.
Instead, along with some hemming and hawing and talk of “challenges,” I
was told that the Control Rule represented a process, not a specific set of
management measures.
The ”process” part may be true, but it’s also true that the
end product of such process is a set of recreational management measures for
the species in question, and we have not yet received any assurance that such
management measures will be able to meet the NRDC v. Daley standard.
Nor have we received any information on the most important
consideration on any of the four “approaches” described in the draft
addendum: How any of them will affect
the health of fish stocks.
Remember that one of the key motivations behind the Control Rule,
and particularly behind the haste to implement the Control Rule by the end of this year, is political: A desire to increase the recreational black
sea bass harvest in order to please a faction within the recreational
community, along with a desire to avoid politically unpopular restrictions on
black sea bass landings.
And maybe that makes sense with black sea bass, at least so
long as spawning stock biomass soars will above the biomass target. With biomass as high as it currently is, even
severe overfishing for a couple of years probably wouldn’t reduce such biomass
below its target. There is plenty of
room for error.
But how will the Control Rule fare with stocks at more typical
levels of abundance, which hover somewhere between the biomass target and
threshold?
So far, no one has provided such information.
Which of the four approaches is more likely to see a
somewhat depleted stock rebuild to target?
Or, looking at it from the opposite perspective, which of the approaches
is more likely to maintain a currently healthy stock at its target level, and
which is more likely to push a healthy stock into decline?
So far, no one has provided such information.
Which of the four approaches is more likely to prevent
overfishing, and which is more likely to let overfishing occur?
So far, no one has provided such information.
Both the Council and the ASMFC have expressed concern about
the impact of the uncertainty in recreational fishing data on regulations,
perhaps forcing regulatory change when such change isn’t needed. Perhaps the Percent Change Approach, with its
consideration of the confidence interval surrounding the recreational data, helps to ease such concerns.
But no data is perfect; there is always some uncertainty
involved. And given that the other three
approaches—Fishery Score, Biological Reference Point, and Biomass Based Matrix—consider
more streams of data than does the current management practice, is it possible
that such Control Rule approaches will actually introduce more uncertainty into
the management process than currently exists?
So far, no one has provided such information.
Yet, without such information, it is impossible to provide
intelligent, informed comment on the draft addendum, and for that reason, there
is a good chance that I won’t attend the public hearing. I lack the
information needed to make a reasoned case for any alternative, including the
status quo.
Normally, I’d feel guilty about remaining silent. But in the case of the Recreational Harvest
Control Rule, I feel no guilt at all.
That’s because I know that the Control Rule effort isn’t
being driven by science. It isn’t driven
by well-considered public policy.
It is being driven by a political agenda, by an industry
that seeks to boost short-term profits by boosting the recreational kill of not
only black sea bass, but summer flounder and scup (and, in the future, bluefish
too, although being overfished, they are currently shielded by the rebuilding
provisions of Magnuson-Stevens).
And when politics is in the driver’s seat, there is little
point standing in the way and being run over.
We can only hope, when the dust clears and the Control Rule
is inevitably put into place, that Mid-Atlantic fish stocks aren’t run over, too.
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