
Exotic Plant Control Strategy
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High priority is given to the management of invasive exotic plant
species that can harm park resources or people and can be controlled.
Priority depends upon two independent factors:
- Degree and kind of biological, ecological, economic, or
health threat.
- Cost and expectation of control, based on current
distribution of the invasive species.
To be effective, the exotic plant manager seeks sound, scientifically
based knowledge of the biology of potentially harmful exotic plant
species, and networks with others regionally to learn the whereabouts
of invasive plants. Insofar as possible, prevention is the most cost
effective management approach. The park's Exotic Plant Management Plan
links four categories of population distribution and density to
corresponding appropriate strategic responses:
- Present in region but not in park.
- Ask whereabouts from cooperating agencies and landowners.
- Place on a Watch List --
Educate park staff to seek and report.
- Track spread if near park.
- Prevent establishment inside park.
- Avoid need for later control.
- Present in park as individuals or small, localized
populations.
- If infestation is new, alert cooperating agencies and landowners.
- Remove by hand.
- Maintain a record of actions.
- Monitor removal sites.
- Follow up as needed.
- Diligence keeps costs low.
- Present as large infestations in parts of park. Native
plant communities are disrupted and native species
displaced from infested areas.
- Remove outliers first.
- Eliminate seed bank in outlier areas after
removing plants.
- Map large infestations. Plan larger attack
projects. Cost permitting, implement one or more
large-scale projects, as follows:
- Contain spread to within infested areas.
- Reduce the number and size of infestations.
- Restore native species to bared sites.
- Minimize dispersal and re-infestation.
- Treat smallest, furthest outlying areas. first.
- Eliminate larger infestations, moving from
fringes toward the source of seed dispersal.
- Present as continuous infestations within and beyond
park boundaries. Displaces many or all native plants in
areas of infestation.
Complete control may be possible, but only by a
coordinated, comprehensive effort between parks and
neighboring agencies and land managers. Extensive
planning and provision for public comment are needed. New
and applied research may be required before control is
possible or cost effective. Ways to share costs of
eradication on a regional scale will be pursued. If costs
are unreasonable, it may be possible only to restore and
protect certain critical park areas from infestation.
Control steps will be similar to 3.