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Invasive Plants in Murrysville, PA

AUG 06   SEP 06   OCT 06   JAN 07  APR 07

Pirate tickets for August 29 and August 30.
 
2 pairs of excellent Pirate tickets will be raffled off on August 23 among all people who volunteer more than 40 hours in the Murrysville parks eradicating the invasive plants. For more information, call Pia
van de Venne, Volunteer Coordinator Parks at 724 733 2770

 

Callery pear
Pyrus calleryana Decne.

SOURCE: The following information on this species is taken from the Delaware River Invasive Plant Partnership, Invasive Plant Fact Sheets at http://www.paflora.org/DRIPP.html. Modifications include additional pictures (from www.invasives.org) and resource information.

DESCRIPTION: Callery pear is a medium-sized deciduous tree, it grows to a height of 35-40 feet with upright branches and a very dense, symmetrical crown.

Stem - Callery pear trees have scaly gray-brown bark and branches with numerous short lateral twigs. Twigs ending in thorns are typical of the species, but the Bradford cultivar is thornless.
Leaves - The leaves are simple, 2-3 inches long, broadest near the rounded base and tapering to the tip. They are light to dark green and glossy with a wavy edge. The leaves remain green late into the fall and finally turn a deep red color before falling.
Flowers - Callery pear is one of the earliest trees to flower in the spring, well before the leaves appear. The flowers are white, about ¾ inch in diameter, with five white petals.
Fruit and seed - Callery pear fruits are small, ¼-½ inch in diameter, and hard and brown when ripe; each fruit contains 2-4 shiny black seeds. Birds and small mammals eat the fruits.

Callery pear

Photos: (clockwise from top left): Britt Slattery, U.S. Fish and Wildlife Service, www.forestryimages.org;
(2) Chuck Bargeron, The University of Georgia, www.forestryimages.org; from Fact Sheet

DISTRIBUTION AND HABITAT: Callery pear is native to China; in 1918 seed was brought to the United States for potential use as rootstock for cultivated pears. Of the initial batch of 100 pounds of seed that was planted at the Plant Introduction Station at Glen Dale, Maryland , one vigorous, non-spiny seedling was selected and named "Bradford". The 'Bradford' callery pear proved to be an attractive landscape specimen with a neat growth form, attractive flowers and foliage, and no pests. Furthermore Bradford was not self-pollinating and thus no fruit or seeds were produced. The landscape industry popularized it and before long it was being planted in urban and suburban settings from parking lots and streets to home landscapes. In 1982 the National Landscape Association voted 'Bradford' callery pear the second most popular tree in America.

However, with time other callery pear cultivars were developed and introduced into the nursery trade. With several cultivars in circulation, cross-pollination could take place and the trees began to produce fruits and seeds.

The spread of callery pear along roadsides, rights-of-way, and in successional old fields was first noticed in southern Maryland and around Washington, DC. In Pennsylvania naturalized populations are known in Bucks and Montgomery Counties. Naturalized populations generally exhibit characteristics of the species including wide-spreading branches and thorniness. Fruit size may vary from ¼ inch to nearly 1 inch in diameter.

EFFECTS OF INVASION: Naturalized callery pear competes with native early successional trees in old fields and hedgerows.

Callery pear

REPRODUCTION AND METHODS OF DISPERSAL: The spread of callery pear is by seed, apparently dispersed by birds, and perhaps also small mammals, that consume the small hard fruits and excrete the seeds when they defecate.

NATIVE ALTERNATIVES FOR LANDSCAPE USE: Native small, flowering trees such as shadbush or juneberry (Amelanchier arborea, Amelanchier laevis), alternate-leaved dogwood (Cornus alternifolia), blackhaw (Viburnum prunifolium), or cockspur hawthorn (Crataegus crus-galli) are suitable for landscape use.

AUTHORS: Ann F. Rhoads and Timothy A. Block, Morris Arboretum, University of Pennsylvania.

For more information on callery pear, please contact:
Delaware River Invasive Plant Partnership, http://www.paflora.org/DRIPP.html.
Mid-Atlantic Exotic Pest Plant Council, Inc., http://www.ma-eppc.org
National Invasive Species Information Center, http://www.invasivespeciesinfo.gov
Plant Invaders of Mid-Atlantic Natural Areas, http://www.nps.gov/plants/alien/pubs/midatlantic/
The Bugwood Network, MA-EPPC Plant List, http://www.invasive.org/maweeds.cfm
USDA Forest Service, Northeastern Area, http://www.na.fs.fed.us/fhp/invasive_plants/weeds/.
USDA-NRCS PLANTS Database, http://plants.usda.gov

REFERENCES:
Rhoads, A. F. and T. A. Block. 2000. The Plants of Pennsylvania, An Illustrated Manual. University of Pennsylvania Press, Philadelphia.

 
Winged Burning Bush
USDA, NRCS

Winged Burning Bush
Euonymus alata

Origin: Northeastern Asia, Japan and Central China

Background
Introduced for use as an ornamental plant for landscaping beginning about 1860. Widely planted by landscape professionals and homeowners for its fall color, dark green leaves, winged stems and other characteristics.

Distribution and Ecological Threat
In the United States, winged burning bush is found from New England to northern Florida and the Gulf Coast and also in Illinois. It threatens a variety of habitats including forests, coastal scrublands and prairies where it forms dense thickets, displacing many native woody and herbaceous plant species. Hundreds of seedlings are often found below

Winged Burning Bush
Britt Slattery, USFWS

the parent plant in what is termed a "seed shadow."

Description and Biology

  • Plant: multiple stemmed, angular branching shrub with conspicuously winged stems, normally 5 to10 feet high but mature plants can grow to 20 feet.
  • Leaves: deciduous, dark green, in pairs along stem, turn brilliant red-purple in autumn.
  • Flowers, fruits and seeds: inconspicuous, greenish flowers occur in late spring and red-purple fruits mature during summer.
  • Spreads: expands locally through vegetative reproduction and to new areas through bird dispersal of seeds.
  • Look-alikes: may be confused with other species of euonymus, including our native strawberry bush, or 'hearts-a-bustin' (Euonymus americana), which does not have winged stems. Saplings of native sweetgum (Liquidambar styraciflua) with winged stems may also be mistaken for winged burning bush.

Prevention and Control
Do not plant winged burning bush. Manual, mechanical and chemical means are available to control established plantings. Seedlings can be pulled by hand. Shrubs can be repeatedly cut to the ground to control re-sprouts, or cut and treated with systemic herbicides like glyphosate and triclopyr.

Native Alternatives

red chokeberry (Aronia arbutifolia)
Red ChokeberryRed Chokeberry
Both photos Britt Slattery, USFWS
Virginia sweetspire (Itea virginica)
Virginia Sweetspire
Britt Slattery, USFWS
mapleleaf viburnum (Viburnum acerifolium)
Mapleleaf Viburnum
USDA
highbush blueberry
(Vaccinium corymbosum)

Highbush Blueberry
Britt Slattery, USFWS
silky dogwood (Cornus amomum)
Silky Dogwood
Chris Miller, NRCS
 
fragrant or shining sumac
(Rhus aromatica or copallina)

Fragrant or Shining Sumac
Britt Slattery, USFWS
 

 
Japanese Barberry
Britt Slattery, USFWS
Japanese Barberry
Berberis thunbergii

Origin: Japan

Background
Japanese barberry was introduced to the United States as an ornamental in 1875. Seeds were sent from Russia to the Arnold Arboretum in Boston, Massachusetts. In 1896, it was planted at the New York Botanic Garden. It was eventually promoted as a substitute for Berberis vulgaris, an exotic plant introduced and used by early settlers from Europe for hedgerows, dyes and jams, and later found to be a host for the black stem rust of wheat.

Japanese Barberry
John M. Randall, TNc

Distribution and Ecological Threat
In the United States, Japanese barberry occurs throughout much of New England and the Northeast, south to North Carolina and west to Michigan and Missouri. Barberry forms dense stands in a variety of habitats, including closed canopy forests and open woodlands, wetlands, pastures, meadows and wastelands. This highly shade-tolerant exotic shrub displaces a variety of native herb and shrub species in areas where it is well established.

Description and Biology

  • Plant: a dense, deciduous shrub that grows 2 to 8 feet high. The branches are deeply grooved, brown and usually have simple spines.
  • Leaves: 1/2 to 1 1/2 inches long and shaped like small spatulas or narrow ovals, with a color ranging from green to bluish-green to dark reddish purple.
  • Flowers, fruits and seeds: flowering occurs from mid-April to May in the Northeast and the fruits mature from July to October and will persist through the winter. The abundant pale yellow flowers occur along the entire length of the stem. Flowers are in clusters of two to four and produce bright red berries about 1/3 inch long.
  • Spreads: by seeds eaten by small mammals and birds (e.g. turkey and grouse) and through vegetative means.

Prevention and Control
Do not plant Japanese barberry. Small plants can be pulled by hand, using thick gloves to avoid injury from the spines. A weed wrench ® can be used to uproot older shrubs when soil is moist. Shrubs can also be mowed or cut repeatedly. Treatment with systemic herbicides like glyphosate and triclopyr has been effective.

Native Alternatives

sweet pepperbush (Clethra alnifolia)
Sweet Pepperbush
USFWS
spicebush (Lindera benzoin)
Spicebush
Chris Miller, NRCS
highbush blueberry
(Vaccinium corymbosum)

Highbush Blueberry
Britt Slattery, USFWS
northern bayberry (Myrica pensylvanica)
Northern Bayberry
Chris Miller, NRCS
swamp rose (Rosa palustris)
Swamp Rose
Chris Miller, NRCS
pasture rose (Rosa carolina)
Pasture Rose
R. Harrison Wiegand

 
 

Tree of Heaven

Ailanthus altissima

 

Origin: Central China

 

Background

Introduced bu a Pennsylvania gardener in 1748 and into California by immigrants during the gold rush years, Tree of Heaven, also called stinking sumac, was available commercially by 1840.

 

Distribution and Ecological Threat

Widely distributed across the United States, Tree of Heaven occurs in 42 states, from Maine to Florida and west to California. It is an extremely common tree in urban areas where it can cause damage to sewers and structures but poses a greater environmental threat because of its invasiveness in cultivated fields and natural habitats. A prolific seeder, Tree of Heaven grows vigorously, establishing dense stands that displace native plants. It produces chemicals that kill or prevent other plants from growing in its vicinity.

Description and Biology

  • Plant: a rapidly growing, deciduous tree in the mostly tropical quassia family (Simaroubaceae). Mature trees can reach 80 feet or more in height. Ailanthus has smooth stems with pale gray bark, and twigs that are light chestnut brown, especially in the dormant season. Tree of Heaven is dioecious, meaning plants are either male or female. The wood of  Ailanthus is soft, week, coarse-grained and creamy white to light brown in color. All parts of the tree, especially the flowers, have a strong, offensive odor, which some have likened to cat urine, or rotting peanuts or cashews.

  • Leaves: large compound leaves, 1 to 4 feet in length, composed of 11 to 25 smaller leaflets and alternate along the stems. Each leaflet has one to several glandular teeth near the base.

  • Flowers, fruits and seeds: large clusters of small greenish flowers are produced during June; in the late summer, female trees produce flat, twisted, papery fruits called samaras that may remain on the trees for long periods of time; an individual tree can produce up t0 325,000 seeds per year.

  • Spreads: reproduces by seed and by vigorous re-sprouting, especially in response to injury such as cutting or breaking.

  • Look-alikes: staghorn sumac (Rhus typhina), ash (Fraxinus species) and black walnut (Juglans nigra). The sumac has fuzzy, reddish-brown leaves and stems. All ash species have opposite leaves. Black walnut leaves are toothed, large green fruits fall from the tree.

Prevention and Control

Correct identification of Tree of Heaven is essential. Native shrubs are often confused with it. Elimination of Ailanthus requires diligence, due to its abundant seed production, high seed germination rate and vigorous vegetative reproduction. Targeting female trees for control will help reduce spread by seed. Young seedlings may be pulled or dug up, preferably when soil is moist. Care must be taken to remove the entire plant including roots and fragments as these will almost certainly re-grow. Extensive research has been conducted on herbicidal methods of control of Tree of Heaven and include leaf, bark and cut stem applications.

 

NATIVE ALTERNATIVES

 

box elder

(Acer negundo)

smooth sumac

(Rhus glabra)

black walnut

(Juglans nigra)

green or white ash

(Fraxinus pennsylvanica or americana)

fringetree

(Chionanthus virginicus)

staghorn sumac

(Rhus typhina)

 

 

Japanese Stilt Grass

Microstegium vimineum

 

Origin: Japan, Korea, China, Malaysia and India

 

Background

Japanese stilt grass was first introduced into the United States in Tennessee around 1919 and likely escaped as a result of its use as a packing material for porcelain.

 

Distribution and Ecological Threat

Japanese stilt grass is currently established in 16 eastern states, from New York to Florida. It occurs on stream banks, river bluffs, floodplains, emergent and forested wetlands, moist woodlands, early successional fields, uplands, thickets, roadside ditches, gas and power-line corridors, lawns and gardens. Japanese stilt grass threatens native understory vegetation in full sun to deep shade. Stilt grass readily invades disturbed shaded areas, like floodplains that are prone to natural scouring, and areas subject to mowing, tilling and other soil-distributing activities including white-tailed deer traffic. It spreads opportunistically following disturbance to form dense patches, displacing native wetland and forest vegetation as the patch expands. Japanese stilt grass appears to be associated with moist, acidic to neutral soils that are high in Nitrogen.

 

Description and Biology

  • Plant: an annual in the grass family (Poaceae) resembling a small, delicate bamboo; mature plants are 2 to 3 feet in height.

  • Leaves: pale green, lance-shaped, asymmetrical, about 3 inches in length, with a shiny midrib

  • Flowers, fruits and seeds: delicate spikes of flowers emerge from slender tips in late summer and early fall. Fruits are produced shortly after flowering and then the entire plant dies.

  • Spreads: vegetatively by rooting at joints along the stem (a new plant can emerge from each node) and by seed. A single plant can produce 100 to 1,000 seeds that remain viable in the soil for at least three years, ensuring persistence. Stilt grass seed germinates readily following soil disturbance. Although dispersal is not fully understood, seeds are probably transported by movement of water e.g., (surface runoff, streams, and floodwaters), soil, plants and on the feet of animals including people.

  • Look-alikes: Virginia cutgrass (Leersia virginica), hairy jointgrass or small carpetgrass (Arthraxon hispidus), and possibly other delicate grasses and wildflowers like Pennsylvania knotweed (Polygonum persicaria)

Prevention and Control

Because it is similar in appearance to several native grasses, it is important to know how to recognize and differentiate stilt grass from look-alikes. The shiny midrib and asymmetrical leaves help to distinguish stilt grass. Early attention to new infestations should be a priority. Because it is shallow-rooted, stilt grass may be pulled by hand at any time. Late summer [September] large accessible areas  can be cut with a weed whacker or lawn mower at very low setting. Stiltgrass is an annual and when we cut it right before the seed sets, the plant will die back. If you cut the stiltgrass too early, the plant will keep growing and produce seeds very low to the ground. If hand pulling or mechanical methods of control are not practical, systemic herbicides such as glyphosate [Round-Up or Rodeo for wetlands], imazameth [Plateau], herbicidal soap [Scythefir] or grass killers may be used. No biological controls are currently available for Japanese Stiltgrass. Flowering plants can be cut back using a mower or weed whip prior to seed production. For extensive infestations, contact and systemic herbicides may be more practical and effective.

 

Native Alternatives

Following disturbance to an area susceptible to stilt grass, stabilize with native vegetation suitable to site conditions.

Internet resources - http://www.paflora.org/,
http://www.invasivespeciesinfo.gov/,
http://tncweeds.ucdavis.edu
For more information or if you need help with invasive plants, call Pia van de Venne at 724 733 2770