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Allegheny River Headwaters Watershed Conservation Plan

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<strong>Allegheny</strong> <strong>River</strong> <strong>Headwaters</strong> <strong>Conservation</strong> <strong>Plan</strong><br />

Chapter 4. Biological Resources<br />

germinates from seed in the fall, then grows into a seedling over winter, and primarily flowers in the<br />

spring. Seeds remain viable for two to five years in the seed bank.<br />

Cheatgrass typically invades pasture lands and other open areas, as it has done in McKean County. It<br />

crowds native species as it competes for resources, such as space, sunlight, and nutrients.<br />

Manual, chemical, and biological control methods are effective in reducing populations of<br />

cheatgrass. Control methods, such as fire, mowing, grazing, tillage, interseeding, and competitive native<br />

species, are examples of manual techniques that have been used to effectively reduce populations of<br />

cheatgrass. The use of herbicide, in addition to other control methods, increases the efficiency (USDA<br />

Forest Service, 2005a).<br />

Crownvetch<br />

Introduced into the U.S. in 1950 for erosion control purposes, the Europe, Asia, and African native is<br />

an herbaceous legume with creeping stems that can grow two to six feet long. It is used as a ground cover<br />

in areas susceptible to erosion, such as road banks and right-of-ways, because of its rapid growth. It<br />

spreads via seed dispersal and creeping root system. It has been known to invade woodland edges,<br />

agricultural fields, pastures, hayfields, streambanks, and gravel bars. Populations of crown vetch have<br />

been established in Potter County.<br />

Manual and chemical control options are available. Prescribed burning that is conducted in late<br />

spring and needs repeated annually for several years to effectively exhaust the seed bank. Mowing<br />

conducted in late spring or multiple mowing sessions in June and late August—to correspond with<br />

successive leaf-out periods—will reduce populations. Chemical control with herbicides can be applied in<br />

early spring following instructions on the selected herbicide.<br />

Garlic mustard<br />

Native to Europe, garlic mustard was introduced to the U.S. in 1868, when it was cultivated for food<br />

and medical use. It has been identified within Potter County, while no infestations within McKean County<br />

have been detected.<br />

This cool season biennial herb has stalked, triangular to heart-shaped, coarsely toothed leaves that,<br />

when crushed, give off an odor of garlic. Garlic mustard can reach two to three and a half feet in height,<br />

and produces button-like clusters of small white flowers, each with four petals in the shape of a cross. A<br />

single plant can produce 1,000 seeds. The seeds are produced in erect, slender pods that, when mature,<br />

become shiny black, beginning in May. By late June, the plants die, holding their seeds throughout the<br />

summer. The seeds remain viable for five or more years. Identification is critical, because it resembles<br />

several native species that grow alongside it, such as toothwarts, sweetcicely, and early saxifrage.<br />

Garlic mustard crowds out native species by aggressively utilizing needed resources, such as light,<br />

moisture, nutrients, soil, and space. This, in turn, affects wildlife, depriving them of the essential food<br />

source the displaced native species provided.<br />

For example, one rare insect species West Virginia white butterfly is suppressed by garlic mustard’s<br />

dominating presence and destruction of toothwarts, native plants that serve as the primary food source and<br />

habitat for West Virginia white caterpillars. Due to the lack of toothwarts, the West Virginia white lays its<br />

eggs on the garlic mustard, which produces a chemical toxin that affects the eggs’ ability to hatch.<br />

To effectively manage garlic mustard involves a long-term commitment. Management options<br />

involve a combined effort of mechanical and chemical treatments, and vary depending on size of the<br />

infestation. In small infestations and where desirable native species occur, manual removal is possible;<br />

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