Overview of Vegetation Management Guidelines
Volume 1, Number 3 through Volume 1, Number 27
PURPOSE OF THE MANUAL
This Vegetation Management Manual was developed by the Illinois Nature Preserves
Commission to provide volunteer groups, laypersons, natural area owners, wildland
owners, and other interested individuals with easy-to-understand methods for
controlling undesirable vegetation in natural areas.
The manual primarily consists of 25 individual guidelines, each describing the best
control techniques recognized to date for a given species. Because each natural area
is composed of a unique set of environmental factors, the recommended methods are not
guaranteed to work in every situation.
The first section of this manual presents a "philosophy" of vegetation management.
All persons should read this section before proceeding to recommendations for
controlling a specific plant. Every guideline was written with this philosophy in
mind, and this understanding is necessary to make best use of the guidelines.
Alien (Exotic) and Opportunistic Native Species
There are two kinds of troublesome plant species in natural areas. Members of the
first group are called aliens or exotics. These are plants that are not native to
the flora of the region in which they are found. Often, these plants were introduced
from Europe or Asia accidentally, or for horticultural or other purposes. Members of
the second group are called opportunists. They are plants that are native components
of the regional flora, but that have become overly abundant and/or aggressive due to
environmental conditions that are different than conditions before European
settlement (e.g., heavy grazing, lack of fire, or creation of disturbed habitats).
Healthy Ecosystems
Invasion or increase of alien and/or opportunistic species usually is the result of a
disturbance or degradation of a natural system. A healthy, well-managed system
usually will not experience problems with these species. Therefore, long-term
control of problem species ultimately depends on restoring the natural processes that
originally maintained the health of the system. In many cases, measures that
concentrate solely on control of problem species without restoring natural processes
will merely treat symptoms of the "disease". For example, lack of periodic fire
contributes to invasion of alien and exotic species in fire-adapted communities. In
these communities, fire must be restored to the site to ultimately achieve long-term
control of problem species.
Eradication vs. Control
The goal in protecting natural areas from exotic and opportunistic species is
maintaining or restoring ecosystem health and the native biodiversity of the natural
area. Eradication of non-native exotic plants is a preferred goal. Although
complete eradication of an undesirable plant may be ideal for the health and
aesthetics of an ecosystem, it can be difficult to achieve due to the labor and
resources required. Controlling an alien or opportunistic species by reducing
density and population size to low levels sometimes is a more practical goal than is
complete eradication.
Certain control measures, such as herbicides, can be harmful to native flora and
fauna, and the potential risks must be considered carefully. It rarely is desirable
to risk degradation of ecosystem health and diversity by using pesticides to
eliminate an alien species completely. Rather, herbicides could be used to control
(reduce the population size) an alien species, and then less risky measures (e.g.,
fire, cutting, or hand pulling) could be used to eliminate or further reduce the
problem species.
For opportunistic native plants, eradication usually is undesirable if these native
species belong in the ecosystems in which they are found, and have simply become
overly abundant and/or aggressive due to a change in ecosystem conditions since
presettlement times. For example, a species may have been held in check by very hot
fires. Because prescribed burns we use to manage many areas today are small tens or
hundreds as compared to ten-thousands of acres, prescribed fires may not achieve
temperatures needed to retard the expansion of such a species. In such cases, the
species should be managed to return it to presettlement abundances. Whether it is
desirable to control native opportunistic species on a site depends on what other
species are present on the site and whether these are rare or sensitive enough to
require special protection. For example, if a prairie is large enough to provide
refuge for grassland animals that need large treeless acreages for long-term
reproductive success, then complete removal of aggressive shrubs or trees to
eliminate edge habitat may be desirable. If a natural community is very small and of
high quality, it may be more important to preserve rare species or species
diversity. In most cases, native opportunistic species should be controlled and not
be eliminated.
Chemical vs. Mechanical or Natural Control
Use of herbicides to control exotics in a natural area should be initiated only after
critical consideration of the effects that pesticide use may have. Use of pesticides
should be avoided when natural (e.g., fire) or mechanical (e.g., cutting, girdling,
mowing) control measures exist. Chemicals should be used only when the consequences
of not using the chemical are worse than the risk of chemical use.
Herbicide use often is justified when labor available to manage alien or
opportunistic plants is severely limited, or when mechanical methods are ineffective
due to the extent of the infestation or to environmental limitations (too wet, too
rocky, etc.). Even so, non-chemical methods always should be given first
consideration when management of exotic species is undertaken. Chemicals should be
used only when the threatened spread of exotic species under non-chemical control is
more harmful than the risks posed by use of the chemical.
When using herbicides in natural communities, use of safety precautions is
imperative. By law, herbicides must only be applied in accordance with label
instructions and precautions. Extreme care should be taken to avoid contacting
nontarget species with the herbicide, and to minimize drift. When applying
herbicides, plants should not be sprayed to the point of runoff as this can harm
nontarget species. The minimum effective concentration of an herbicide should be
used, rather than higher concentrations. In natural communities, only closed
containers should be used for herbicides, as open containers can spill. In
state-designated nature preserves or state-owned natural areas, herbicides should
only be applied by a licensed pesticide applicator or operator.
Control May Take Several Years
The time needed to control exotic species by various methods is an important
consideration. Some exotic species gradually are displaced by native species once
presettlement conditions (such as fire or hydrology) are restored and native species
are given several years to compete under these new conditions.
In cases where native plants can outcompete exotic plants in the long-term, use of
herbicide or limited labor resources may be unwise. Sometimes managers may need
patience in controlling exotics in an area. While it can be satisfying to eradicate
a species in 1 year, it is sometimes more realistic, more resource-efficient, and
better for ecosystem health to consider a 3-, 5-, 10-, or 20-year time frame to
achieve desired results. Certain alien plant species, however, spread very rapidly.
These species (e.g., purple loosestrife, garlic mustard) are easiest to control when
control measures are taken as soon as the species is noticed.