The Aquatic Plant Restoration Program in
Illinois
Gary W. Lutterbie
Illinois Department of Natural Resources 301 S. Date Street,
Gibson City, IL 60936 217/784-4730
Aquatic and wetland plant restoration is primarily needed for
larger impoundments and renovation of wetland. Illinois' larger
impoundments are generally void of aquatic vegetation. High wave
action caused by wind and recreational boating, and water level
fluctuations are believed to be the main reasons for the lack of
aquatic vegetation establishment. Other factors might include
turbidity, lack of an adequate seed bed and uprooting of plants caused
by carp and other fish species. Biologists have tried transplanting
aquatic vegetation from other lakes or purchasing plants and root
stock from private nurseries. Transplanting from other lakes is
discouraged due to introduction of unwanted species that might be
attached or come in with the plants (i.e. zebra mussels, the spiny
water flea, Eurasian milfoil, curlyleaf pondweed). The Department is
also concerned about genetic strains of plants and would prefer not to
buy plants, tubers or seed from private nurseries unless they can
guarantee the use of local seed for their nursery stock. The Mason
Tree Nursery in our Division of Forestry has undertaken a program to
try and furnish the needs of the biologist from the Divisions of
Natural Heritage and Fisheries. Nursery personnel have been
experimenting with the culturing of different aquatic and wetland
plants to meet the needs of the biologist. It is up to the requesting
biologist to furnish the seed, proper identification and location from
where the seed were obtained. The nursery will then raise the plants
in trays containing 45 tubes which can then be easily transported to
the biologist for planting at the appropriate time. Much of the work
has been conducted at Clinton Lake, a 5000 acre impoundment located in
central Illinois. Early (1990) attempts to plant sago pondweed (Potamogeton
pectinatus) and wild celery (Vallisneria sp) failed even
though they were protected with plastic snow fencing. The reason for
failure was thought to be due to high turbidity and possibly the late
planting date, July 2. Limited success was obtained with American
pondweed (Potamogeton nodosus). The American pondweed grew well
the first year though failed to come back the following year. Water
willow (Justica americana) was planted from 1991 through 1998,
except in 1994. In each year five to nine beds were established.
Evaluations conducted in July and August 1998 indicated that an
average of 70% (33 to 89%) of the beds planted between 1991 and 1998
were successful. Plantings from 1991 through 1995 were primarily along
the main shoreline in order to provide shoreline protection as well as
fish habitat. Average bed survival for these years was 56% (range
33-86%). Plantings from 1996 through 1998 occurred in protected coves,
or in the upper arms of the lake where wave action was less severe.
Average bed establishment was 88% (range 86-89%). Substrate type and
protection from wave action probably increased survival in these
areas. Planting clumps of water willow plants vs individual plants
increased survival greatly. From 1996 through 1998 15 beds of wild
celery were planted. Evaluations in August 1998 indicated that 53% of
these beds were still actively growing. Beds protected with geo-jute
and snow fencing planted in ambient water temperatures, in clear water
and where depth was at least 12 in deep in August performed the best.
The recent establishment of lizards tail (Saururus cermuus) and
water willow along stream banks is showing some promise. Recent
attempts to grow the wetland plants hardstem bulrush (Scirpus
acutus), three-square bulrush (Scirpus americanus), river
bulrush (Scirpus fluviatilus), deep-water duck potato (Sagittaria
rigida) and spadder dock (Nuphar Iuteum) have met with
mixed success. Wetland renovation is becoming a bigger part of
watershed management and will require more attention to determine
which plants will provide the best habitat in the various types of
wetlands.
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