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Lecture 21: Competition Experiments

Reading: None.

Experimental Methods for Studying Interspecific
Competition
Removals and Enclosures
Starfishes on Island Reefs (Menge, 1972)
Pisaster and Leptasterias
are two starfish species (Echinodermata) that have very similar diets
and both occur on three tropical island reefs. There is little migration
by adults between reefs.
If these two species are competing, we
would predict that remove of one species would have a positive effect
on the remaining species, and addition of more individuals of one species
would have a negative effect on the other species.
| Treatment |
Response
in Leptasterias |
| Remove
all Pisaster |
weight
increases |
| Add Pisaster
|
weight
decrease |
| Control
(no manipulation) |
no weight
change |
Responses in Leptasterias are
based on mean weight of individuals measured at the beginning and end
of the experiment. The density of Leptasterias was constant at
all three sites.
Wild Oats and Flax (Bell and Nalewaja,
1968)
Flax is an agricultural seed crop and
wild oats is a weed species in the northern Great Plains of the United
States.
If these two species are competing, we
would predict that as the density of the wild oats increases, the yield
of flaxseed would decrease.
Flaxseed yields were evaluated on fields
with varying densities of wild oats. The application of fertilizer was
also a variable. Comparisons were made to plots containing no wild oats.
Flaxseed yield reductions occur with increased
wild oat densities (after Krebs, 1994, p 253).
|
Wild Oats Density
|
Flaxseed Yield (Bu/acre)
|
|
number/m2
|
Fertilized
|
Unfertilized
|
Mean Reduction%
|
|
0
|
19.5
|
17.9
|
--
|
|
10
|
13.4
|
14.3
|
26%
|
|
40
|
6.7
|
8.0
|
60%
|
|
70
|
4.3
|
6.3
|
72%
|
|
100
|
3.5
|
4.2
|
80%
|
Flour Beetles (Park, 1962)
Two species of flour beetle, Tribolium
confusum and T. castaneum have very similar habitats.
Competition occurs along with cannibalism and reciprocal predation by
adults and larvae on eggs and pupae.
Climate and chance influence the outcomes
of competition between these two species, but one species always excludes
the other in culture experiments. This is very suggestive of a Lotka-Volterra
unstable equilibrium with ultimately leads to competitive exclusion (after
Begon, Harper, and Townsend, 1996, p 281, Table 7.2).
|
Culture Conditions
|
Competitive Exclusion
(percentage) by
T. castaneum
|
Competitive Exclusion
(percentage) by
T. confusum
|
|
Cold-dry
|
0
|
100
|
|
Temperate-dry
|
13
|
87
|
|
Hot-dry
|
10
|
90
|
|
Cold-moist
|
29
|
71
|
|
Temperate-moist
|
86
|
14
|
|
Hot-moist
|
100
|
0
|
Complete Competitors Cannot Coexist
Organisms with similar requirements
in nature compete most severely.
Exceptions:
1. Environmental patchiness, heterogeneity
2. Non-equilibrium conditions, both
species below carrying capacity
3. Species not resource limited, shared
resources not limiting, abiotic factors or predation dominate
4. Constant immigration
5. Fluctuating conditions, direction
of competition changes before one species is excluded (for example
food harvest vs. food digestion)
6. Shifts in resource requirements
by one or both species
Just because resources are shared does
not mean competition is occurring.
Gauses Principle or The Competitive
Exclusion Principle
If two competing species coexist in
a stable environment, then this must result from niche differentiation
(differentiation of realized niches). If there is no niche differentiation,
or if it is precluded, then one species will eliminate (exclude) the
other.
Finding niche differentiation is often
difficult even though competition with coexistence can be clearly
documented.
The competitive exclusion principle
is widely accepted because:
1. there is much evidence to support
it
2. this concept makes intuitive good
sense
3. theoretical models (Lotka-Volterra)
point to this principle
Examples of Exceptions to Competitive Exclusion
Heterogeneity, Patchiness, and Ephemeral
Environments (spatial, temporal, and individual)
Gaps of unoccupied space may be most
rapidly colonized by a species that is a poor competitor, but if gaps
regularly appear, coexistence is possible.
Paine (1979) studied an intertidal
brown algae called sea palm, Postelia palmaeformis and
the bivalve mussel, Mytilus californianus in the Pacific
Northwest. Sea palms are annuals that are only able to attach to bare
rock, and must do so each year. Bare rock gaps are gradually filled
by mussels. However, the two species coexist where gap formation is
7% of rock surface area per year or greater.
Temporal variation in the colonization
of gaps can also make coexistence possible. The timing of a competitively
superior species entering a site can influence the outcome of competition.
Harper (1961) studied two annual grass
species, Bromus madritensis and Bromus rigidus.
When grown together from seeds started at the same time and in equal
densities, Bromus rigidus represents more than 70% of
the total plant biomass after 126 days of growth. The contribution
to total biomass by Bromus rigidus declines as the introduction
of Bromus rigidus seeds is delayed (after Begon, Harper and
Townsend, 1996, p 283, Fig. 7.10).


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