Transcript Document
Exotic Herbivore Species
Grazing Effect On Plant Life
Module 5
SEE-U 2001 Biosphere 2 Center, AZ
Yuko Chitani
Adam Nix
Mei Ying Lai
Eli Pristoop
Lily Liew
J.C. Sylvan
Asma Madad
Prof. Tim Kittel, TA Erika Geiger
Introduction
A community is all associated species
within a given area. A variety of factors act
to structure communities — factors as
varied as weather fluctuations and natural
disasters, to exotic species introductions, to
the natural tension between producers and
consumers. Whether or not the plant is
killed, however, herbivory has the potential
to dramatically alter plant and animal
communities.
In this study the question at hand was,
how grazing effects a community? What is
the effect of herbivory on plant community
diversity and species abundance? It is
important to find out the influences that
cattle grazing has on sonoran desert land.
Understanding the functioning of
communities is essential to conserve
endangered ecosystems and the species
therein. The only way to accumulate data
on this is to measure the percent of plant life
forms.
Site Locations
Methods
Three different sites were chosen to represent the varying intensity of herbivory
on plant communities: area 1 experienced little or no grazing by cattle. Area 2,
which was fenced off, experienced moderate grazing by cattle; 64 head of cattle
ranged this area for a period of 3 months prior to this study. Area 3, also fenced
off, was highly utilized by neighboring ranchers as rangeland. Observation
indicated that this area had experienced a high intensity of cattle grazing. The
line intercept sampling was used to determine the aerial cover of species (as
oppsed to basal cover) on a 50-meter line within the three sites. The distance of
the line to the fence of each respective site was also recorded. The line was then
divided into 10-meter sections. Working in pairs, we identified each
intersecting species and their coverage.
Sample bags were labeled with: site, location on the 10-meter sections from which it was collected,
specie name, and lifeform. 6 GPS readings were taken at the three sites, at the beginning and end of the
line. The data was then put into Excel.
We selected four other species that were representative of the changes in the percent cover over the
three areas: Boraginaceae Family #1, Calliandra eriophylla, Hilaria belangeri, Opuntia engelmanni
Absolute percent cover measures the specie’s proportion in respect to the length of the line sampled
(50m).
Relative percent cover measures the specie’s proportion in respect to the total length of all species
sampled (>50m).
Plant Lifeform Classification
Herbacious
Grass
Annual
Perennial
Woody
Forb
Annual
Perennial
Tree
Succulent
Shrub
Broadleaf
Microfyllous
Boradleaf
Microfyllous
Bunch
grass
Draught
deciduous
Draught
deciduous
Draught
deciduous
Draught
deciduous
Sodforming
Cold
deciduous
Cold
deciduous
Cold
deciduous
Cold
deciduous
Evergreen
Evergreen
Evergreen
Evergreen
Sarcostemma cynanchoides sp. Hartwegii, a vine, was classified as a perennial forb.
RESULTS
Results
1) Plant coverage: Area 1 (ungrazed) > Area 2 (moderately grazed) > Area 3 (heavily grazed). The
percent coverage of annual forbs dropped from 55% relative coverage in Area 1 to 52% in Area 2 to
only 14% in Area 3 (see fig. 1, 2, 3).
2) As total plant coverage diminished, relative and absolute % values achieved parity (see fig. 3).
3) Overall bare ground increased from Area 1< 2 < 3 (see fig. 4, 9).
4) Four species represent the changes in the percent cover over the three areas: Boraginaceae Family
#1, Calliandra eriophylla, Hilaria belangeri, Opuntia engelmanni. While some species displayed a
decrease in percent cover, others tended to increase (e.g. succulents increases from Area 1 (9.2%) to
Area 2 (16.5%) and Area 3 (24.2%)) (see fig. 9).
5) Species diversity remains constant over three areas (see fig. 10).
6) Lifeform diversity also remains constant over three areas (see fig. 10).
Fig. 1
Relative vs. Absolute Percent Coverage by Lifeforms in Area 1
60%
Percent Coverage
50%
40%
relative %
30%
absolute %
20%
10%
0%
Annual Grasses Perennial Bunch
Grasses
Annual Forbs
Perennial Forbs
Lifeform
Microphyllous
Deciduous
Shrubs
Microphyllous
Deciduous
Trees
Succulents
Fig. 2
Relative vs. Absolute Percent Coverage by Lifeform in Area 2
60%
Percent Coverage
50%
40%
relative %
30%
absolute %
20%
10%
0%
Annual Grass Perennial Bunch
Grass
Annual Forbs
Perennial Forbs
Lifeform
Microphyllous
Deciduous
Shrubs
Microphyllous
Deciduous
Trees
Succulents
Fig. 3
Relative vs. Absolute Percent Coverage by lifeform for Area 3
16%
14%
Percent Coverage
12%
10%
Relative (%)
8%
Absolute (%)
6%
4%
2%
0%
Annual Grass
Perennial
Bunch Grass
Perennial
Annual Forbs
Sod-forming
Grass
Perennial
Forbs
Lifeform
Microphyllous Microphyllous
Deciduous
Deciduous
Shrubs
Trees
Succulents
A
nn
ua
l
fo
rm
in
g
Fo
rb
s
G
ra
ss
G
ra
ss
G
ra
ss
M
ic
r
Lifeform s
Ba
re
ul
en
ts
G
ro
un
d
Su
cc
Pe
re
nn
op
ia
hy
lF
llo
or
us
bs
De
ci
du
M
ou
ic
ro
s
ph
Sh
yl
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us
De
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s
Tr
ee
s
Pe
re
nn
ia
lS
od
h
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ua
l
Pe
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lB
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A
Percent Cover
Fig. 4
Com parison of Absolute % Cover by Lifeform in Areas 1,2,3
60%
50%
40%
Absolute % (1)
30%
Absolute % (2)
20%
Absolute % (3)
10%
0%
Fig. 5
Com parison of Relative % Cover by Lifeform Areas 1,2,3
60%
Percent Cover
50%
40%
Relative % (1)
30%
Relative % (2)
Relative % (3)
20%
10%
0%
Annual Grass Perennial Bunch Perennial SodGrass
Annual Forbs
Perennial Forbs Microphy llous
forming Grass
Lifeform
Microphy llous
Deciduous
Deciduous
Shrubs
Trees
Succulents
ris
tid
a
ca
ci
a
te
rn
ip
es
A
gr
eg
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i
Bo
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th
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rio
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nt
ilis
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od
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=
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Percent Coverage
Fig. 6
Relative vs. Absolute Cover Percentages in Area 1
25.00%
Relative Cover (%)
20.00%
Absolute Cover (%)
15.00%
10.00%
5.00%
0.00%
Species
m
br
os
ia
Bo
co
ra
nf
gi
er
na
tif
ce
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Bo
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Fa
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#1
ae
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am
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a
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pe
Da
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Percent Coverage
Fig. 7
Relative vs. Absolute Percent Coverage in Area 2
25.00%
20.00%
Relative Cover (%)
Absolute Cover (%)
15.00%
10.00%
5.00%
0.00%
Species
Species
LITTER,
BARE GROUND
Sarcostemma
Plantago
Opuntia
50.00%
Machaeranthera
Lepidium
Gilia sp.
Eragrostis
Elymus
Daucus pusillus
Bromus rubens
Bouteloua
Boraginaceae
Aristida ternipes
Ambrosia
Percent Coverage
Fig. 8
Relative vs. Absolute Percent Coverage in Area 3
60.00%
Relative Cover (%)
Absolute Cover (%)
40.00%
30.00%
20.00%
10.00%
0.00%
Fig. 9
Comparison of Absolute Percent Coverages of 5 Selected Species for
Areas 1,2,3
Absolute Percent Coverage
60.00%
50.00%
40.00%
Area 1
Area 2
30.00%
Area 3
20.00%
10.00%
0.00%
BARE GROUND
Boraginaceae Family
#1
Calliandra eriophylla
Species (excluding "Bare Ground")
Hilaria belangeri
Opuntia engelmanni
Fig. 10
Total Number of Collected Species and Total Lifeforms Present Under
Different Grazing Treatments
Num ber of Species/Lifeform s
35
Species
Lifeforms
30
25
20
15
10
5
0
Area 1: Ungrazed
Area 2: Moderately Grazed
Grazing Treatm ent
Area 3: Heavily Grazed
Plant Species Found at Sites
•
•
•
•
•
•
•
•
•
•
Acacia greggii
Ambrosia confertiflora
Androsace occidentalis
Aristida ternipes var. gentilis
Boraginaceae Family #1
Boraginaceae Family #2 = Species K
Boraginaceae Family #3
Bothriochloa barbinodis
Bouteloua curtipenbula
Bouteloua hirsuta
•Hilaria belangeri
•Lepidium lasiocarpum
•Leptochloa dubia = Species B
•Lupinus concinnus(?)
•Machaeranthera tagetina
•Microseris linearifolia = Species D
•
•
•
•
•
•
•
•
•
•
•
•
•
Bromus rubens
Calliandra eriophylla
Chenopodium sp.
Daucus pusillus = Species H
Descurainia pinnata = Species E
Echinocereus
Elymus elymoides
Eragrostis curvula
Eragrostis intermedia
Erigeron divergens = Species A
Eriogonum wrightii
Gilia sp.
Gnaphalium
•Opuntia spinosior
•Opuntia chlorotica
•Opuntia engelmanni
•Opuntia phaeacantha
•Plantago patagonica
•Prosopis velutina = Mesquite
•Sarcostemma cynanchoides ssp. Hartwegii
•Sisymbrium irio L.
•Tridens muticus = Species J2
•Triodanis perfoliata = Species J1
•Viguiera longifolia = Species F
•Species I
•BARE GROUND
•DUNG
•LITTER
Discussion
How Does Grazing Affect Plant
Community Diversity and
Species Abundance?
To answer this question, we studied three different sites: Area 1 an ungrazed range, Area
2 a moderately grazed range, and Area 3 a heavily grazed open range. From general
observation, it was clear that the heavily grazed site had the least abundance of plants
and a lot of bare ground between markings. It also took us considerably less time to
sample the heavily grazed site than it did for the other two sites.
We measured the plant community’s overall richness of species by analyzing the number
of species found and collected in each of the three areas. The possible sources of error
include: misidentification of plants, inconsistency and inaccuracy in measuring
technique, uncertainty in whether the lines sampled were representative of the different
areas.
Conclusion
•Intense herbivory has an effect on the lifeform
composition of the plant community.
•However, herbivory does not necessarily affect
the biodiversity of the community.
In this exercise we learned:
• Plant identification and classification
• Relative and absolute percent coverages
References
Epple, Anne Orth. A Field Guide to the Plants of Arizona. Lew Ann Publishing Company,
Mesa, Arizona. 1995.
Gould, Frank W. Grasses of the Southwestern United States. University of Arizona Press,
Tucson. 1993.
Kearney, Thomas H. and Peebles, Robert H. Arizona Flora. University of California Press,
Berkeley. 1960.
Niehaus, Theodore F. A Field Guide to Southwestern and Texas Wildflowers. Houghton
Mifflin Co., New York. 1984.
Robbins, Travis, David Lancaster, Janna Lancaster and Dr. Tony Burgess. Biosphere 2
Centre Plant Field Guide. (Unpublished).
Thanks to Tim and
Erika for their
expertise in plant
identification.