| USING VOLUNTEERS TO CREATE INVASIVE PLANT MAPS OF LAKE GASTON. B.R. Lassiter,
R.J. Richardson, G.G. Wilkerson, M.C. Sturgill, and R.E. Austin; Department
of Crop Science, North Carolina State University, Raleigh.
Lake Gaston, located on the border of Virginia and North Carolina, is
colonized by several aquatic invasive species including hydrilla which
cover over 15% of the lake. Hydrilla forms dense mats, and restricts swimming,
boating, and suppresses property values. Hydrilla also displaces natural
vegetation, reduces habitat quality for fish, provides breeding habitat
for mosquitoes, impedes commercial navigation, reduces drainage and increases
flooding, and blocks intakes for hydroelectric turbines and potable water.
Few management tools are available for aquatic weeds. Proper selection
and integration of management techniques requires accurate vegetation
surveys. In Lake Gaston, private contractors are hired yearly to generate
vegetation maps at a cost of $30,000 to $40,000. The accuracy of these
maps could be increased or the cost of production decreased by utilizing
trained volunteers. Volunteer scouts (Lake Gaston residents) were trained
in the identification of seven aquatic plant species, (including hydrilla)
and the use of handheld GPS units. Fourteen volunteers worked alone or
in groups of two to scout weeds during the months of October and November.
Scouts sampled in areas of their own choosing, and used their own boats
(both motor boats and kayaks). Volunteers recorded GPS coordinates using
a specialized computer program written by one of the volunteers. The scouts
measured water clarity and depth, as well as presence or absence of hydrilla
and 6 other aquatic weeds. Over 97 man-hours of labor were spent scouting
an estimated 57 miles of shoreline (approximately 17% of total lakeshore)
from at least 1,180 distinct sampling points. Data points were overlaid
on existing topographic maps for relatively detailed documentation of
hydrilla presence or absence in certain areas. Volunteers recorded the
locations of floating mats of hydrilla, grass carp sightings, length of
hydrilla shoots, whether the area had been treated with herbicides, and
condition of the plants collected. Current efforts will be extended through
2008 with additional volunteers expected. Volunteers will be surveyed
to determine time investment of each volunteer. The data collected from
this research may serve as a complement (to ground-truth) data collected
by the independent contractors. Future efforts could include assigning
part of the lake to contractors in an effort to reduce scouting costs.
It is also expected that the location of hydrilla growth could be tracked
using the GPS data and comparing growth from year to year to determine
long-term spread or control. |