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Scientific name: : : : : Common Name: Information Sheet, Shawna Arsenault Country: USA Photographer: E. M. Barrows Identifier: E. M. Barrows Abstract The purpose of this study is to test the hypotheses that Ash-leaved Maples
and Trees-of-heaven on the Capital Crescent Trail in Washington, D.C., host a
different number of vine species and have different percent coverages by vines.
After examining 100 specimens of each tree species, my observations indicate
that though almost the same vine species can be found on each tree, Ash-leaved
Maples generally have a greater number of vine species per tree. Ash-leaved
Maples were also had a greater coverage by vines. Finally, it seems that not all
vines were present to the same amount, but that English Ivy was most common on
Ash-leaved Maples, and Asian Clematis was most common on Trees-of-heaven. Introduction In this study, I examined vine growth on Ash-leaved Maples (Acer negundo)
and Trees-of-heaven (Ailanthus altissima) along the Capital Crescent
Trail (CCT) in Washington, D.C. I tested the hypotheses that the trees were
hosts to different species of vines and that they have different amounts of vine
coverage, as well. The Capital Crescent Trail is an 11-mile path that stretches from
Lyttonsville, Maryland, in West Silver Spring, through Bethesda, Maryland to
Georgetown, Washington, D.C. It is a popular recreation area for joggers,
roller-bladers, bicyclists, and walkers and offers beautiful views of the
Potomac River and the Rock Creek Stream Valley. Many trees, shrubs, and other
organisms live and grow on each side of the paved trail (Phyillaier 2003). Ash-leaved Maples and Trees-of-heaven are large autotrophs that are common in
forests throughout the eastern United States. They are most often found in
forests, forest edges, successional areas, and yards, and both are important in
forest succession. Also, both provide food for many other kinds of organisms
(Barrows 2002a). Ash-leaved Maples and Trees-of-heaven can grow up to 70 feet tall and up to 4
feet in diameter (Athenic Systems 2003). Their large stature makes them prime
hosts for vines, plants with woody or herbaceous stems that climb up or over
other organisms or structures. Vines are unable to hold themselves upright and,
therefore, depend upon trees, such as the Ash-leaved Maple or Tree-of-heaven,
for support. Vines common on the CCT include Asian Bittersweet (Celastrus
orbiculatus), Asian Clematis (Clematis terniflora), English Ivy (Hedera
helix), Japanese Honeysuckle (Lonicera japonica), Japanese Wisteria (Wisteria
floribunda), Kudzu Vine (Pueraria lobata), Poison Ivy (Rhus
radicans), Porcelainberry (Ampelopsis brevipedunculata), and wild
grape species. Asian Bittersweet (AB) is an invasive, woody vine that lives in disturbed
areas such as abandoned homes, fence rows, roadsides, and forest edges, usually
in direct sunlight. It grows rapidly and covers other plant species, many of
them native, and harms them by weighing them down, blocking sunlight, and
reducing nutrients in the surrounding soil (Ohio Department of Natural
Resources). Asian Clematis (AC) is an invasive vine found throughout the eastern and
central United States. It can grow from 20 through 30 feet long and is used
widely as an ornamental vine in yards. However, it requires a large area to grow
and often grows over native species, blocking sunlight to the underlying plants
(The Plant Database 2000). English Ivy (EI) is a woody, evergreen vine that can grow up to 150 feet
long. It is a noxious, alien species that grows thickly on trees and other
structures. It can kill trees by blocking them from the sun or felling them with
its heavy weight (Barrows 2002b). Japanese Honeysuckle (JH) is a woody, semi-evergreen, invasive vine that can
grow up to more than 30 feet long. It is found primarily in disturbed areas,
such as yards, fence rows, roadsides, forest edges and abandoned fields in the
eastern and central United States. It kills native plant species by forming
thick canopies on them and reducing light availability (Virginia Native Plant
Society 1995). Japanese Wisteria (JW) is a deciduous, invasive vine from Asia that is common
throughout the eastern United States, although it is most abundant in southern
U.S. It is generally an ornamental vine used on walls, balconies, and trellises,
but it also grows over trees and other plants. It may kill other plant species
and is very poisonous to Humans (International Programme on Chemical Safety
2003). Kudzu Vine (KV) is an alien, invasive vine from Japan that is common from
Connecticut through northern Florida and as far west as Texas. It is a woody,
perennial vine that can grow up to 200 feet long and forms thick blankets over
other plants, often killing them in competition for sunlight (Barrows 2002c). Poison Ivy (PI) is a woody vine that grows in many forms, as a thick woody
vine, a thin vine, or a vine-like bush. It may grow on other plants and compete
for sunlight, but does not form thick mats that kill its host plants. It grows
in forests, forest edges, successional areas, yards, and fields and provides
food for many organisms, though it causes a painful dermatitis in many people
(Barrows 2002d). Porcelainberry (PB) is an alien, invasive woody vine that forms thick
blankets on other plants and compete for sunlight and kills covered plants. It
provides nectar and other food to many different organisms (Barrows 2001). There are several species of wild grape, which are in the family Vitaceae.
They can be found throughout the United States, most often by streambanks, sandy
soils, dry woods, or thickets. Wild grapes are native to North America and may
kill other plant species by forming thick blankets of vines over them (Rodenhouse
1998). Materials and Methods I collected data in the Georgetown section of the CCT in October 2003. I
walked approximately 2 mi, observing trees on the bank side, along the Potomac
River, and on the opposite side of the Trail. In a nonrandom manner, I selected
the first 100 Ash-leaved Maples and the first 100 Trees-of-heaven within 10 ft
of the path for study. For each tree, I recorded a number I assigned to each,
the location (opposite or bank), diameter at breast height (d.b.h.), vine
species present, and percent coverage of vines, estimating coverage to the best
of my ability. I measured the d.b.h. with a tape measure and identified any vine
species unknown to me with the help of Professor Edward Barrows, a professor of
biology at Georgetown University. To eliminate biases, I used a random-number table to randomly choose 50
Ash-leaved Maples and 50 Trees-of-heaven to study for this project. After
tabulating my data (Tables 1 and 2), I found means and performed Student’s
t-tests to compare the number of vine species present on each type tree and
percent coverage of vines. Finally, I graphically organized the vine species
found on each tree species (Figure 1) and performed a Chi-Square test to
determine if particular vine species had a preference for Ash-leaved Maples or
Trees-of-heaven. Results and Discussion I found nine different vines on Ash-leaved Maples on the CCT, including AB,
AC, EI, JH, JW, KZ, PB, PI, and WG (Table 3). Only seven trees out of 50 (14%)
had no vines (Table 1). Trees-of-heaven had all the same vines as
Ash-leaved Maples, with the exception of KZ and JW. Also, 15 of 50 trees
(30%) did not have vines (Table 2). These percentages suggest that vines
may have a slight preference for Ash-leaved Maples. However, this
preference may be explained by the size of the trees, as well. Ninety
percent of Trees-of-heaven were small (d.b.h < 5.5 in) (Table 2), while only
26% of Ash-leaved Maples were considered small (Table 1). This suggests a
positive correlation between tree size and vine presence. Ash-leaved Maples had 1.40 ± 0.88 SD (range 0–4, N = 50) vine species per
tree, while Trees-of-heaven had 0.980 ± 0.09 SD (range 0–3, N = 50) vine
species per tree. There is a significant difference in the means of the two
species (t = 2.4, d.f. = 98, P < 0.05), suggesting that while
most vine species are the same, Ash-leaved Maples generally have more vine
species per tree. There was also a significant difference between coverages of
vines in the two species (t = 2.58, d.f. = 98, P <
0.05). Ash-leaved Maples had a mean coverage code of 2.94 ± 1.13 SD
(range 1–4, N = 50), and Trees-of-heaven, a value of 2.34 ± 1.19 SD (range 1–4,
N = 50); thus, it seems Ash-leaved Maples are also covered to a greater degree
than Trees-of-heaven. The vines were not present to an equal degree in each tree species.
There was a significant difference in the vines on the Ash-leaved Maples (X2
= 199, d.f. = 7, P < 0.05). Seventy-two percent of trees
observed had English Ivy growing on them, while only 2% had Kudzu or Japanese
Wisteria. This indicates that Ash-leaved Maples are more likely to be host
to English Ivy than other vines on the CCT. Only 4% of Trees-of-heaven, on
the other hand, had English Ivy growing on them. Therefore, English Ivy
seems more likely to grow on Ash-leaved Maples than Trees-of-heaven. There
is also a significant difference between vines on Trees-of-heaven (X2
= 74, d.f. = 6, P < 0.05). Thirty-eight percent were host to
Asian Clematis, 30% had no vines, and none of the Trees-of-heaven were host to
Japanese Wisteria or Kudzu. These results indicate that Trees-of-heaven are more
likely to be host to Asian Clematis than other vines, and they are more likely
to have this vine than Ash-leaved Maples, of which only 10% had Asian Clematis. There are several biases in this project. First, I did not choose the trees
completely randomly. I studied only trees on the Georgetown end of the CCT,
which may have unusual features affecting vine growth. My using randomly
assigned transects of the trail would have allowed me to get a better idea of
the most common vines that associate with Ash-leaved Maples and Trees-of-heaven.
Also, I studied trees of all different sizes, with Trees-of-heaven generally
being smaller than Ash-leaved Maples. This difference in size between the two
trees may have affected the types, number, and sizes of vines growing on the
species. Finally, I approximated at percent coverage of vines on each tree,
which may have caused many errors in my data. In conclusion, it appears that Ash-leaved Maples and Trees-of-heaven on the
CCT do not have equal amounts of vines species present or equal coverage by
vines. Ash-leaved Maples seem to have more vine species and coverage. In order
to better understand the relationship between trees and vines, future studies
should examine the health of trees with and without vines and also possibly
remove vines from trees already covered. Other studies may also include
examining other tree species and studying other parts of the forest. Acknowledgements I thank Professor Edward Barrows (Department of Biology, Georgetown
University) for assisting me with this project and for making the time to visit
my site to help me identify vines. I also thank Daniel S. Kjar for helping to
format my report and put it online. Finally, I thank Megan E. Brooks for her
patience as we collected our data on the Capital Crescent Trail. Literature Cited Athenic Systems. 2003. The Tree Guide. Website. Barrows, E. M. 2001. Information Sheet, Porcelainberry. In Barrows, E. M and D.S. Kjar. 2002. Biodiversity Database of the Washington, D.C., Area (BDWA). Website. http://biodiversity.georgetown.edu (20 December 2003).Barrows, E. M. 2002a. Information Sheet, Ash-leaved Maple. In Barrows, E. M and D.S. Kjar. 2002. Biodiversity Database of the Washington, D.C., Area (BDWA). Website. http://biodiversity.georgetown.edu (20 December 2003).Barrows, E. M. 2002b. Information Sheet, English Ivy. In Barrows, E. M and D.S. Kjar. 2002. Biodiversity Database of the Washington, D.C., Area (BDWA). Website. http://biodiversity.georgetown.edu (20 December 2003).Barrows, E. M. 2002c. Information Sheet, Kudzu Vine. In Barrows, E. M and D.S. Kjar. 2002. Biodiversity Database of the Washington, D.C., Area (BDWA). Website. http://biodiversity.georgetown.edu (20 December 2003).Barrows, E. M. 2002d. Information Sheet, Poison Ivy. In Barrows, E. M and D.S. Kjar. 2002. Biodiversity Database of the Washington, D.C., Area (BDWA). Website. http://biodiversity.georgetown.edu (20 December 2003).International Programme on Chemical Safety. 2003. Environmental Health Criteria. http://www.inchem.org (20 December 2003).Ohio Department of Natural Resources. 2003. Invasive Plants of Ohio. Website. http://dnr.state.oh.us/dnap/invasive/ (20 December 2003).Phyillaier, W. 2003. Silver Spring Trails. Website. http://www.silverspringtrails.org (20 December 2003).Rodenhouse, N. 1998. Web of Species; Biodiversity in New England and at Wellesley College. Website. http://www.wellesley.edu/Activities/homepage/web/index.html (20 December 2003).The Plant Database. 2000. Website. http://plantsdatabase.com (20 December 2003).Virginia Native Plant Society. 1995. Invasive Alien Plant Species of Virginia. Website. http://www.vnps.org (20 December 2003).
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