By now, many—probably most—serious striped bass anglers have
heard that
Maryland has released its juvenile abundance index for 2026, and that such
index recorded a very uninspiring 5.5.
While that is the best Maryland JAI since 2018, it is still
barely above the long-term average of 10.8, and helps entrench the
period 2019 through 2026 as the eight years with the lowest average JAI, 3.15,
in the 70-year history of the Maryland juvenile abundance survey. The next-lowest eight-year average, 3.57,
occurred in the period 1979-1986; the fact that those years encompassed
most of the stock collapse of the late 1970s and 1980s provides some context as
to just how dire the current striped bass recruitment situation really is.
To put that in perspective, if we replaced the period used
to calculate Virginia’s long-term average JAI with the
years 1992 through 2006, which the Atlantic States Marine Fisheries Commission
uses to determine whether the “recruitment trigger” in the fishery management
plan is tripped, we’d find that the 2026 JAI was just a bit over Virginia’s
recruitment trigger value of 8.22.
We’d also find that such recruitment trigger, which marks the 25th
percentile of all JAIs in the 1992-2006 period, is already above the long-term
average of 7.77, so the simple fact that Virginia’s 2026 JAI is above the state’s
long-term average doesn’t provide much reason to celebrate.
At the same time, there were some mildly hopeful details
underlying the overall bad news. The
Maryland press release that announced the 2026 JAI also noted that, although
“the fish were more widely distributed than in recent years,”
“[t]he highest performing areas were the upper Bay and
Choptank River.”
No explanation was given as to why there was a greater
concentration of juvenile striped bass in the upper Bay. It is very possible that higher water flows
and lower water temperatures, attributable to snowmelt and runoff in the
Susquehanna River watershed, particularly those portions of the watershed located
in Pennsylvania and New York, made conditions in the upper Bay more favorable
for juvenile survival. If that was, in
fact, the case, the greater number of fish in the upper Bay might portend
greater numbers of juvenile bass throughout the Bay in the future, should
winter and early spring bring conditions—including
water flows, temperatures, and zooplankton availability—more favorable to
striped bass reproduction.
While such favorable conditions might occur as early as this
upcoming winter—right
now, the National Oceanic and Atmospheric Administration is predicting that, at
least during December, January, and February, the Chesapeake Bay region will
see above-normal temperatures, above-normal precipitation, and no drought
conditions at all—that’s not guaranteed, and might not even be likely. When
the striped bass population last collapsed in the late 1970s and 1980s, it took
14 years, from 1975, when the JAI began its decline at 6.69, until 1989’s dominant
year class, with a JAI of 25.20, was produced; during those 14 consecutive
years, the JAI averaged 4.35.
It’s not at all impossible that we might have to again wait
that long before we see another dominant year class emerge.
“Maybe we need to have a conversation about new reference
points and new expectations. I don’t think
that we should expect the population to be where it was in the early
2000s. We have a different Chesapeake Bay. We have a different planet than we had in the
early 2000s.”
And maybe she’s right.
Maybe climate change has seriously wounded the Chesapeake
Bay, and rendered it physically incapable of producing the sort of big striped
bass year classes that it produced as recently as 2011, 2015, 2017, and 2018,
the sort of year classes that, with proper conservation and management, might
help to rebuild the striped bass stock to the current spawning stock biomass
target.
Mr. Luisi’s efforts to increase striped bass landings has
been a consistent feature of Management Board meetings ever since then. So has his
continuing effort to change the reference points used to gauge the health of
the striped bass stock, so that the spawning stock biomass target would be
lower, which would allow for higher annual landings. As early as October 2017, he argued that
“I’ve always been one who has thought that the current
targets that are set for spawning stock biomass, or [sic] set to a point
where they’re unachievable. They may be
achievable, but we’re unable to maintain them.
“It sets a false expectation for fishermen along the coast…”
It seems that the only reason that the spawning stock
biomass target appeared “unachievable” or that managers were “unable to
maintain” it was that the same managers never made a serious effort to get
overfishing under control.
“I do not support the removal of reference points as a
discussion point. I think 1, I think
fishery goals and objectives is the fundamental basis for what we do.
“If you don’t have the appropriate goals and objectives, none
of the other elements and the other components make any difference. I would like to see us go forward with goals
and objectives, reference points, triggers, stock rebuilding and schedule…”
Mr. Luisi lost the debate back then, but we would be foolish
to believe that he has given up trying to skew the fishery management plan toward
greater exploitation.
Thus, when we hear a Maryland fisheries manager talk about
revisiting the reference points, and about how we shouldn’t expect to see the
spawning stock biomass reach the level it did in the early 2000s—another way to
say that the current SSB reference point is unrealistically high—it is only reasonable
to wonder whether that manager is expressing a legitimate concern about
changing conditions in the Chesapeake Bay, or whether that manager is merely
setting the stage for another attempt to increase striped bass landings.
Whatever the motivation, giving up on striped bass
rebuilding right now—or, more precisely, immediately after the 2027 benchmark
stock assessment is released--would be a serious mistake.
Right
now, the stated goal of the striped bass management plan is
“to perpetuate, through cooperative interstate fishery
management, migratory stocks of striped bass; to allow commercial and
recreational fisheries consistent with the long-term maintenance of a broad age
structure, a self-sustaining spawning stock; and also to provide for the
restoration and maintenance of their essential habitat.”
In order to achieve that goal, the management plan’s
objectives include, among a number of other things, to
“Manage fishing mortality to maintain an age structure that
provides adequate spawning potential to sustain long-term abundance of striped
bass populations,”
and
“Establish a fishing mortality target that will result in a
net increase in the abundance (pounds) of age 15 and older striped bass in the
population, relative to the 2000 estimate.”
The current reference points are, at least in part,
calculated to achieve such goal and the objectives of sustaining long-term
abundance and a broad age structure that includes a reasonable abundance of
fish that are at least 15 years old.
Changing the goals and objectives, and so the reference
points, to allow higher landings, at the cost of reduced abundance, increased
long-term risk, and fewer older, larger females, would be a mistake,
particularly in the face of current poor recruitment, as it may well be those
older, larger females that hold the key to rebuilding the stock.
“Through a moratorium on Maryland State harvests in the Chesapeake
Bay the 1982 year-class [which was the key to rebuilding the striped bass stock
after it had collapsed] was effectively protected and became a dominant
one. Ironically, most egg production in
1982 was attributed to striped bass >10 years in age. Old remnant females produced during the 1960s
were a hedge against a long period of recruitment overfishing which occurred
during the 1970s. Striped bass epitomize
periodic strategists, spreading risk of failed replacement through variability
in spawning behavior over many spawning seasons. This life history tactic indicates that a truncated
age structure would result in stock abundance being more closely linked to annual
changes in year-class strength.”
In other words, doing what Mr. Luisi has suggested in the
past—changing the goals, objectives, and reference points to allow higher
annual landings, while compromising a broad age structure, reducing the number
of age 15+ fish, and reducing long-term abundance—could remove the very old
fish from the population that might be needed to spearhead the current recovery
of the striped bass stock, as older fish spearheaded the recovery forty-plus
years ago, and so make that recovery much harder to achieve.
As I noted before, it’s possible that Ms. Kennedy is right,
and that long-term changes in the Chesapeake Bay will make rebuilding to the
current spawning stock biomass target impossible. But that has not yet been established, and there
is no reason to hurry to change the reference points now.
If changes in the Bay have truly made the current spawning
stock biomass target unachievable, that will be revealed to be true over time, but
it would be a serious mistake to rush to give up on the striped bass’ recovery,
and change the reference points before the data conclusively demonstrates that
such recovery cannot and will not occur.
To give up too soon would potentially deprive striped bass
fishermen, recreational and commercial, of the benefits that accrue from a
healthy and abundant stock, and put the long-term sustainability of the striped
bass population at risk.
We can, and without a doubt should, wait at least another
decade or so before condemning the bass to such fate.
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