Any plant that grows outside of its natural range is considered exotic. If it responds to its new environment with rapid growth, and if it can quickly establish itself over large areas of land then it is considered invasive.
When humans were introduced into North America we brought plants with us from our country of origins. Plants have
been introduced for agricultural purposes, horticultural purposes, and in some cases, purely by accident. However, when
a plant species is introduced outside its natural range, it is also outside the natural range of its natural controls that can
include any herbivores, parasites and diseases. Free from these natural controls, some exotic plants experience rapid
and unrestricted growth, become invasive in their new environments, and reduce ecosystem diversity and function.
The primary factors which contribute to a plant’s ability to invade include its life cycle, annual or perennial; how it
spreads, as a vine or by seed; its capacity for abundant seed production; its high seed germination rate; how long-lived
its seeds are; and how rapid it can mature to its seed-producing stage. The quicker it can reproduce itself, the quicker it
can invade and overwhelm the native plant species which previously occupied the land.
Invasive plant species are the second greatest threats to the natural ecosystems of the world today. Only direct habitat
destruction poses a greater threat to the future of biological diversity. Invasive species disrupt the ecology of natural
ecosystems by displacing native plant and animal species and reduce biological diversity by reducing the amount of light,
water, nutrients and space available to native species.
Targeted Species |
||
1 |
Garlic mustard |
Alliaria petiolata |
2 |
Autumn olive |
Elaeagnus umbellata |
3 |
Japanese honeysuckle |
Lonicera japonica |
4 |
Amur honeysuckle |
Lonicera maackii |
5 |
Morrow honeysuckle |
Lonicera morrowii |
6 |
Tatarian honeysuckle |
Lonicera tatarica |
7 |
Purple loosestrife |
Lythrum salicaria |
8 |
Reed canary grass |
Phalaris aurundinacea |
9 |
Common reed grass |
Phragmites australis |
10 |
Japanese knotweed |
Polygonum cuspidatum |
11 |
European buckthorn |
Rhamnus cathartica |
12 |
Glossy buckthorn |
Rhamnus frangula |
13 |
Multiflora rose |
Rosa multiflora |
Well-established Species |
||
1 |
Quack grass |
Agropyron repens |
2 |
Tree-of-heaven |
Ailanthus altissima |
3 |
Japanese barberry |
Berberis thunbergii |
4 |
Smooth brome |
Bromus inermis |
5 |
Flowering-rush |
Butomus umbellatus |
6 |
Asian bittersweet |
Celastrus orbiculatus |
7 |
Common thistle |
Cirsium arvense |
8 |
Poison hemlock |
Conium maculatum |
9 |
Field bindweed |
Convolvulus arvensis |
10 |
Crown-vetch |
Coronilla varia |
11 |
Queen Anne's lace |
Daucus carota |
12 |
Air-potato |
Dioscorea batatas |
13 |
Cut-leaved teasel |
Dipsacus laciniatus |
14 |
Common teasel |
Dipsacus sylvestris |
15 |
Russian olive |
Elaeagnus angustifolia |
16 |
Hairy willow-herb |
Epilobium hirsutum |
17 |
Small-flowered hairy willow-herb |
Epilobium parviflorum |
18 |
Winged euonymus |
Euonymus alatus |
19 |
Wintercreeper |
Euonymus fortunei |
20 |
Meadow fescue |
Festuca pratensis |
21 |
Day-lily |
Hemerocallis fulva |
22 |
Dame's rocket |
Hesperis matronalis |
23 |
Yellow flag |
Iris pseudacorus |
24 |
Common privet |
Ligustrum vulgare |
25 |
Moneywort |
Lysimachia nummularia |
26 |
White sweet-clover |
Melilotus alba |
27 |
Yellow sweet-clover |
Melilotus officinalis |
28 |
Eurasian watermilfoil |
Myriophyllum spicatum |
29 |
Lesser naiad |
Najas minor |
30 |
Water-cress |
Nasturtium officinale |
31 |
Curly pondweed |
Potamogeton crispus |
32 |
Lesser celandine |
Ranunculus ficaria |
33 |
Bouncing Bet |
Saponaria officinalis |
34 |
Johnson grass |
Sorghum halepense |
35 |
Narrow-leaved cattail |
Typha angustifolia |
36 |
Hybrid cattail |
Typha X glauca |
37 |
European cranberry-bush |
Viburnum opulus var.opulus |
38 |
Periwinkle |
Vinca minor |
Watch List Species |
||
1 |
Porcelain-berry |
Ampelopsis brevipedunculata |
2 |
Nodding thistle |
Carduus nutans |
3 |
Spotted knapweed |
Centaurea maculosa |
4 |
Leafy spurge |
Euphorbia esula |
5 |
Border privet |
Ligustrum obtusifolium |
6 |
Showy pink honeysuckle |
Lonicera X bella |
7 |
Nepalgrass |
Microstegium vimineum |
8 |
Chinese silvergrass |
Miscanthus sinensis |
9 |
Star-of-Bethlehem |
Ornithogalum umbellatum |
10 |
Mile-a-minute weed |
Polygonum perfoliatum |
11 |
Giant knotweed |
Polygonum sachalinense |
12 |
Kudzu |
Pueraria lobata |
13 |
Dog rose |
Rosa canina |
14 |
Black swallow-wort |
Vincetoxicum nigrum |
For more Information:
The introduction of exotic plant species have resulted in the escape of plant pathogens that have greatly impacted our local flora, such as Dutch Elm Disease, Beech Bark Disease, Chestnut Blight and Dogwood Anthracnose. Introduced insects that have impacted Holden include European Beech Scale, Gypsy Moth and Emerald Ash Borer.
White-tail Deer were extirpated from Ohio in the late 1800s but were re-introduced to Ohio in the late 1920s. Browsing by white-tail deer has a negative impact on all Holden collections. Deer browse destroys specimens propagated or purchased for the designed landscape. Browsing severely limits ecological function of natural areas when whole age classes and layers of woody species disappear from the landscape. Holden has protected a landscape matrix of woodland and grassland that is coincidentally optimal habitat for whitetail deer. Deer exclosure studies within the natural landscape produce quantifiable data on the impact of whitetail deer on the landscape. Infrared aerial surveys document the population density of whitetail deer in and around the Holden landscape. Historical density for whitetail deer in northeastern Ohio is eight deer per square mile. Current whitetail deer density is 29 deer per square mile. Whitetail deer are one of the strongest negative pressures on Holden landscape and require management plans to reduce population density.
Did you know that there are no native earthworms in glaciated North America? For many of the same reasons that earthworms are useful in a vegetable garden, they are harmful within our native woodlands that evolved with earthworms. Studies conducted by the University of Minnesota show that at least seven species of earthworms are invading Minnesota’s hardwood forests and causing the loss of tree seedlings, wildflowers, and ferns. Invading earthworms eat the leaves that create the duff layer and are capable of eliminating it completely. Big trees survive, but many young seedlings perish, along with many ferns and wildflowers. In areas heavily infested by earthworms, soil erosion and leaching of nutrients may reduce the productivity of forests and ultimately degrade fish habitat. For more information on invasive earthworms visit the Minnesota Department of Natural Resources web site.