University of Maryland Extension

Invasive Plants Cause Ecosystem-level Changes

 Why are Invasive Plants a Problem?

 Invasive plants displace native plants, reducing both the amount of native plant cover and the number of native species present in an ecosystem. This decline reverberates up the food web, causing, for example, losses in insect and songbird diversity. This type of damage can usually be reversed by removing the invasive plants and allowing natives to re-establish on their own, or if the seed bank is depleted, by planting nursery-grown natives. However, some invasive plant species alter the very structure or function of the ecosystems they invade, so that those ecosystems no longer provide growing conditions suitable to their original flora. To restore these areas, it is usually necessary to address the ecosystem-level changes that have occurred before re-introducing native vegetation. Here we describe some of the plant species that have invaded and altered Maryland ecosystems.

Destruction of Physical Structure

English ivy climbing tree

     Invasive vines provide an extreme example of the destruction of the physical structure of an ecosystem. Kudzu, porcelainberry, wisteria, Japanese honeysuckle, English ivy, and oriental bittersweet are invasive vines that, given enough time, will kill trees. If intervention is early enough, such a forest can be restored by simply killing the vines. Once the canopy layer is destroyed, however, removal of the vines yields a site that is too sunny for forest plants. At that point, restoration requires establishment of a native meadow containing early successional trees, and a long-term monitoring and maintenance program. 

English ivy, shown at left, climbs into the canopy, ultimately killing trees and destroying forests.

Change of Fire Frequency

     Fire frequency is another important ecosystem characteristic. Cheatgrass is an alien, annual species that is adapted to very frequent fires, more frequent than any of our native plant communities. It dries out in late spring/early summer. This creates highly flammable material at a time of year when it would not be found in native ecosystems. Cheatgrass-invaded habitat is like dry tinder waiting for a spark. When fire does occur, it favors even more cheatgrass invasion. The increased fire frequency in the Western United States is partly due to cheatgrass. Cheatgrass also occurs in Maryland, where it invades native meadows, degrading valuable plant, pollinator, and songbird habitat. Thanks to our more humid climate, however, it does not cause large-scale fires and loss of human life. Controlled burning is a technique that is frequently and successfully used to restore native meadows that have been invaded by alien plants, however, this technique would be a poor choice if cheatgrass were present.cheatgrass growing on side of road

Cheatgrass, shown above in early June in Worcester County, MD. Notice that it is beginning to dry out, as shown by the browning at lower right.

Hijacking Natural Succession

     Successional stage is another important ecosystem characteristic. In our region, when a forest is disturbed by a storm or fire, the opening becomes a meadow, then a shrubland, and finally a forest again. This process, called natural succession, normally takes about 20 years. While the meadow gap is open, it provides much-needed meadow habitat to plant and animal species that cannot live in the forest. The invasive alien tree Callery (a.k.a. Bradford) pear cuts the meadow/shrub phase down to less than 5 years, depriving our region of meadow habitat. We do not yet know how the interruption of natural succession will affect native forests of the future.

endangered eastern firebells
Eastern featherbells, shown above, is a state-endangered species and a member of the trillium family. The meadow habitat it requires is being lost to invasives. The oval leaves at the top of the photograph are Callery pear, the oval leaves at the bottom of the photograph are Japanese honeysuckle.

Changing Soil Chemistry

     Invasive plant species excel at using nutrient-rich soils to support rapid and abundant growth. Many invasive plant species alter soil chemistry in a way that gives future generations of invasive plants a competitive advantage. Common reed, for example, has roots that go deeper than other marsh roots, collecting nutrients other plants can't reach. Each fall the decaying stems and leaves release those nutrients to the soil, creating the perfect medium for growing more common reed. Johnsongrass, listed as a noxious weed by the Maryland Department of Agriculture, also does this. Japanese stiltgrass and barberry take it a step further, changing the pH of the soil, too. The more amenable, nearly neutral (6.5 - 7.5) soil pH favors more barberry growth.

     Barberry's altered ecosystem has changed the animal community as well. Changes in soil chemistry are accompanied by higher densities of alien, invasive earthworms. The invasive worms rapidly break down forest floor leaf litter, causing higher rates of erosion and more sediment in local streams. Barberry also changes the microclimate, creating higher humidity which is ideal for blacklegged ticks (a.k.a. deer ticks), the hosts of the bacteria that causes Lyme disease (Ward and Williams 2012).

tick infested earlobe of a deer

Black-legged ticks infest the inside of this deer's earlobe. Image by Jim Occi, via BugPics at

Altering Hydrology

     Hydrilla is an aquatic plant that alters ecosystem structure by establishing dense surface mats that shade out the native vegetation below. The mats are so dense that they impede water flow, resulting in zones of low oxygen and accompanying fish kills. Surface areas of stagnant water provide ideal habitat for mosquito larvae. Hydrilla hosts a bacteria that poisons aquatic birds that consume it. This poison can move up the food chain, as documented when some bald eagles in Georgia ate poisoned water birds and died (Simberloff, 2013).

thick mat of hydrilla

Hydrilla forms thick mats that alter light and water flow in aquatic habitats. Photo by Leslie J. Mehrhoff, Univ. of Connecticut, via


Kourtev, P.S., W.Z. Huang and J.G. Ehrenfeld. 1999. Differences in earthworm densities and nitrogen dynamics in soils under exotic and native plant species. Biological Invasions 1:237–245

Maryland Invasive Species Council.

McGrath, Deborah and Meagan Binkley. 2009. Microstegium vimineum invasion changes soil chemistry and microarthropod communities in Cumberland Plateau forests. Southeastern Naturalist, 8(1) 141-156

National Public Radio. Sea of sagebrush disappears for fire-prone cheatgrass.

Rout, Melanie, et al. 2013. Bacterial endophytes enhance competition by invasive plants. American Journal of Botany 100(9): 1726–1737. 2013.

Simberloff, Daniel. 2013. Invasive species: What everyone needs to know. Oxford University Press.

Ward, Jeffrey and Scott Williams. 2011. Controlling an invasive shrub, Japanese barberry (Berberis thunbergii DC), using directed heating with propane torches. Natural Areas Journal 31:2 156-162.

By Dr. Sara Tangren, Sr. Agent Associate, University of Maryland Extension, Home & Garden Information Center,  May 2019.

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