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Bythotrephes is a species
native to Europe and Asia. It was first discovered in the Great Lakes
in 1982 and is now spreading into inland lakes in Ontario (about 55 lakes,
including at least 4 during 2003) and bordering United States (Michigan,
Minnesota, Ohio). The species is important both economically and
ecologically, and therefore assessment of its rate and pattern of spread
is important. It can be a nuisance to anglers because its long
caudal appendage (tailspine) fouls on fishing lines, creating a knot
which prevents anglers from reeling their lines in.
Hypothesis:
The progression of the spiny waterflea
(Bythotrephes) through inland lakes in Ontario can be tracked using
a combination of 'gravity' and GIS models. This Geographical Information
System (GIS) model will be based upon information gained through surveying
boaters in Ontario (gravity model).
Procedure:
According to past studies, the spiny waterflea
is mainly spread by boaters and anglers attached to equipment such as fouled
fishing lines, boat anchor lines and downrigger cables. Other possible
reservoirs for the species which could facilitate its spread include infected
bilge water and live well water, live minnow bait that have consumed waterfleas
and hold their eggs in the digestive system, fouled waterski or tubing
lines, and SCUBA diving equipment. All these factors were taken into
consideration, and a short boater survey was devised. Questions asked
on the survey pertained to the habits of boaters (i.e. do they clean their
fishing line), where they travel (i.e. the lakes they normally visit),
and if individuals have ever encountered the spiny waterflea.
After devising the survey, marinas, lake
associations and hunter and angler clubs, in and around areas containing
lakes invaded by Bythotrephes all over Ontario, were contacted.
For locations far from Windsor, we mailed copies of the survey, along with
self-addressed stamped envelopes, to the various clubs. For locations
within driving distance (i.e. within 8-9 hours away from Windsor), a
team of researchers visited various marinas and docks and performed surveys
with boaters in person. Once surveys were returned to the University,
the information was entered into a database. Tables based on this
information were then constructed for input into a GIS.
Results:
The gravity model predicted spread of
Bythotrephes
based upon seven identified risk factors (e.g. use of contaminated fishing
or boat anchor line) that may allow dispersal of either live individuals
or their resting eggs from invaded to noninvaded lakes, as well as based
on the spatial arrangement of invaded and noninvaded lakes in Ontario.
Discriminant analysis of lake gravity scores successfully identified invasion
status for 74% of 170 inland lakes. A retrospective analysis of 31
invaded lakes revealed that the order in which lakes were invaded was directly
related to the magnitude of vector inflows from invaded sources.
Analysis of the dominant vector inflow to each invaded lake revealed a
‘stepping stone’ pattern in which at least five lakes were sequentially
invaded from the source population in Lake Huron. One invaded lake
(Muskoka) apparently served as an invasion 'hub', resulting in up to 18
additional direct and 17 indirect invasions. Species spread occurred
via a combination of dominant, local diffusion (median distance 12.5km)
and rare, long-distance (>100km) dispersal. Eleven of 131 lakes that
were not invaded in 2000 were reported invaded in 2001. Gravity scores
of these lakes were significantly higher than those of other noninvaded
systems, indicating that susceptibility to invasion can be related to the
magnitude of vector inflows. A GIS model based on gravity scores indicated
that Bythotrephes’ distribution is expected to expand to eastern
and northwestern Ontario, although most new invasions are expected to occur
in the central region of the province. Our results indicate that
quantitative analysis of human dispersal vectors provides a robust starting
point with which to assess vulnerability of discrete ecosystems to invasion.
Management efforts focused on reducing the number and magnitude of human-mediated
dispersal vectors may reduce the rate of invasion of new ecosystems.
This work is now in press (2003) in the journal Ecological Applications.
Jim Muirhead, a PhD student, is currently
expanding our work on Bythotrephes to include new lakes that have
been invaded, and to assess spread of this species against patterns of
other species (e.g. zebra mussel). Jim has utilized our survey data
to model individual invaded lakes as threats to other lakes. His
Michaelis-Menton type assessments of vector outflows from invaded lakes
to other invaded lakes or to other noninvaded lakes allow usto determine
which invaded lakes will be most important in future spread of the species.
For example, while Lake Muskoka was very important to initial spread of
the wateflea in Ontario, most of the lakes with which this lake has contact
have been invaded (i.e. most vector outflow is to other invaded lakes).
On the other hand, Kash Lake, Lake Simcoe and Lake Nipigon all have outfloes
predominately to noninvaded lakes, and vector flow is substantial in each
case. So, we anticipate that these three lakes will be very important
to future spread. During 2003, three of the newly invaded lakes have
their strongest vector inflows from Kash Lake, consistent with our model.
Red dots indicate pre-2001 invasions, blue dots represent
reports of new invasions in 2001.
Green isobars indicate vulnerability to invasion based
upon vector outflows from invaded lakes.
The sequence by which we think lakes in Ontario were
invaded based upon the dominant
vector only. Lake Muskoka was central to the initial
spread of the species, while vector
data indicate Lakes Simcoe and Nipigon will be central
to future spread.
Model of Bythotrephes spread based upon vector
flows (all vectors included). The pattern is much more
complicated than that of the dominant-only vector model.
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