Below is the Discussion portion of the 2010 Population Assessment of Lake Sturgeon in the Lower St Croix River.
At the bottom of this post you’ll find a link to the full report.
Discussion
The present population of lake sturgeon in the
Lower St. Croix River consists of a large
proportion of immature fish. Given the
migratory nature of this species and the fact that
the Lower St. Croix is an open system to the
Upper Mississippi River, an estimate of the
present population with any degree of accuracy
will be difficult to attain (Knights, et.al. 2002).
Because of these factors, the present calculated
population likely underestimates the actual
population that is present at any given time
significantly. To date, no movement patterns or
habitat preferences can be determined from
reported recaptures.
Project data indicates the lake sturgeon in the
Lower St. Croix River exhibit a slower growth
rate than fish from more fertile river systems. It
is also evident that lake sturgeon in the study
area exhibit a poorer condition than fish in other
river systems. We’re finding that the sturgeon in
the Lower St. Croix average over 12 percent
less in weight than fish of the same length from
other heavily studied populations in North
America. Our data even reflects an overall
relative weight (as determined from a length –
weight regression) of approximately 6 percent
less than that observed by the WDNR in 1986-
87 in these same waters.
Sampling results to date have also yielded very
few fish that are likely mature females
(approximately 1397 mm or mid-50 inches). It
is well documented that individual male lake
sturgeon spawn every 2 to 3 years, and
individual female lake sturgeon spawn once
every 4 to 6 years after reaching sexual
maturity. There is also some speculation that
females may not even spawn the first year that
they become mature. Given these spawning
intervals, it is likely that less than 30 percent of
the adult fish in the population may be sexually
active in any given season.
Sampling efforts during this project indicate that
lake sturgeon are very vulnerable to targeted
angling pressure. Given that lake sturgeon are
long lived, slow growing, and require a long
time to reach sexual maturity; present
populations could be threatened by the growing
popularity of this species as a sport fish.
From 1992 through 2008, regulations on the
Lower St. Croix River allowed the harvest of
one lake sturgeon 50 inches (1270 mm) or larger
(total length) per angler per year during a
limited angling season extending from the first
Saturday in September through October 15th.
Since 2006, anglers wishing to keep a lake
sturgeon from these waters have been required
to purchase and possess a special harvest tag
prior to having a legal size fish in possession. A
total of 16 lake sturgeon have been reported
harvested since initiation of Minnesota’s tag
reporting system. Five of these fish have
measured 60-inches (1524 mm), or more, in
length.
Fisheries managers had been concerned that
given the slow growth and the below average
condition for fish observed during this project,
the 50-inch minimum harvest length (1270 mm)
may be too liberal for the lake sturgeon in this
system. Until more information is available,
both Minnesota and Wisconsin are in joint
agreement that the harvest regulations should be
made more restrictive to protect female lake
sturgeon until they have had the chance to
spawn at least once. Beginning with the 2009
season, a 60-inch minimum harvest size (1524
mm) for lake sturgeon has been enacted on the
Lower St. Croix River. The harvest limit will
remain 1 fish per year for anglers who have
purchased a harvest tag in advance. The harvest
season has been shortened from the first
Saturday in September through September 30th.
An additional 15-day catch-and-release only
season was established that runs from October
1st through October 15th for anglers possessing a
Minnesota fishing license.
Ideally, data from this project should serve as a
foundation for biologically-based management
decisions to insure that lake sturgeon continue
to have strong presence in the Lower St. Croix
River. Given that we are working with a long-
lived and slow growing species, it will be
necessary to collect information for a long
period of time to do a thorough and proper
evaluation of this population. Future efforts
should also address the data gaps that are
evident in the present project that hinder more
informed management decisions. Besides the
need for data on growth rates of larger fish and
age of maturity for each of the sexes; telemetry
work is needed to better understand movement
patterns, preferred habitats and spawning
periodicity. Other issues that should also be
addressed are recruitment, natural mortality,
hooking mortality, and incorporation of PIT tags
on all marked fish to enable estimation of tag
loss.