Friday, July 31, 2015
Fundamental Theorem on the Prairie
R.A. Fisher, foundational 20th-century figure in statistics and in evolutionary biology, famously (famously among evolutionary biologists, anyway) developed an idea he called the Fundamental Theorem of Natural Selection: "The rate of increase in fitness of any organism at any time is equal to its genetic variance in fitness at that time." To grasp this idea requires understanding evolutionary fitness, the nature of a biological population (Fisher didn't mean an individual organism, of course, because individuals don't evolve.), variance as a statistical concept, and what genetic variance is. Even scientists who understand those things (or think they do) have argued about exactly what Fisher meant in the 85 years since he proposed it. A simple take on the idea is that it explains, in mathematical terms, why natural selection is responsible for adaptation (Grafen 2003), something Darwin (1959) knew, though he couldn't do the math. A more nuanced (and sassier) take on the Theorem goes like this: "Sure. Genetic variance in fitness limits how fast adaptation by natural selection occurs, but, given all the things Fisher neglected (such as the facts that environments don't stay constant from generation to generation, and that chance events matter), how fast does adaptation really happen?"
The answer to this sassy question isn't just "academic." It's essential to understanding how wild organisms might respond to changing climates and other circumstances.
With apologies to Laura Ingalls Wilder, that's where Grinnell comes in. At Grinnell's Conard Environmental Research Area, my MAP students (Sam Sokolsky and Greg Margida, below, left and right, respectively) and I are carrying out an experiment to answer that question. Working with researchers from Professor Ruth Shaw's lab at the University of Minnesota, we're going to compare "Fisher-predicted" increases in evolutionary fitness to the actual changes that occur in complex natural environments, using the native prairie plant Chamaecrista fasciculata ("partridge pea") as a model.
Stay-tuned. We're just starting.
Friday, December 12, 2014
Cats Helping Birds: Introduced Species Impact Trophic Cascades
Invasive
species commonly modify native communities of plants and animals, sometimes in drastic
and unexpected ways. Through competition, habitat destruction, and predation,
vertebrate invasive species are a major threat to communities across the globe.
One way invasive species impact communities is through altering the ecosystems’
feeding structure. Increased predation by the invasive on a particular group of
prey times, termed trophic level, can modify the number of species and their
relative population sizes in ways that ripple through the entire community.
Ecologists call such rippling effects a trophic cascade. Consider the
simplified food web:
If a new top predator begins to feed on the 3rd
trophic level predator, the original top predator’s population would decrease. In
response, the mid-level predator would experience decreased levels of predation
and its population would increase. This increased mid-level predator population
would then intensify predation on the prey species, whose population would
experience a decline. Such patterns describe a trophic cascade; these changing
community compositions often accompany the invasion of new species.
Understanding trophic level interactions and trophic cascades is essential for
understanding the intricacies and connections within biological communities
increasingly altered by human actions, including the introduction of new
species.
In “Cats
protecting birds: modeling the mesopredator release effect,” Frank Courchamp,
Michel Langlais, and George Sugihara (1999) investigate the effects of
introducing new species to island communities by modeling a particular type of
trophic cascade, mesopredator release. Invasive species particularly threaten
endemic island natives, species found in only one island locale, because these
isolated species are highly susceptible to extinction due to lack of genetic
diversity or lack of new immigrants to resupply a declining population. Both
invasive rats and feral cats have been unintentially introduced by humans to a
number of islands across the globe. Rats and cats both prey on birds; rats
commonly steal eggs and kill juveniles while cats kill adults. A number of
rare, endemic songbirds and seabirds have gone extinct due to predation by both
or either invasive species. Courchamp et
al. (1999) studied the interactions between the three species through
trophic cascades. In this system cats serve as the top trophic level predator,
rats as the mid-level predator, and birds as the prey species. The major
modification to the previously introduced trophic structure is that the cats
prey on both rats, the mid-level predator, and birds, the prey species.
The mid-level predator is commonly called the mesopredator;
trophic cascades within this system can lead to mesopredator release. If the
top predator’s population declines or is removed, the mesopredator’s population
is “released” from predation and intensifies its predation on the prey species.
Mesopredator release, then, is a trophic cascade that results in decreasing
prey populations due to the decline of the top predator. In this system,
mesopredator release would cause the decline of songbirds if cats were removed
from the system. If cats, though, are not removed from the system and prey more
commonly on rats, the mesopredator’s population should decline. In this way,
higher populations of cats indirectly help to increase bird populations by
suppressing rat populations.
Courchamp
et al. (1999) created a mathematical
model to investigate whether mesopredator release could occur in island
communities containing cats, rats, and birds. Their model indicates that a
mesopredator release effect would be likely if cats were removed; in other
words, they found that rats and birds could not coexist without the presence of
cats because rats would hunt birds to extinction. The authors suggest that the
high probability of trophic cascades demonstrates the necessity of understanding
the indirect effects of species’ interaction. Furthermore, their findings
suggest that the top predator of systems often have extremely important roles
in maintaining the stability of biological communities. Courchamp et al. (1999) explain that these
findings should caution conservation plans that eradicate cats to protect bird
populations because such plans may actually cause further decline of bird
species through increased predation by rats.
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| https://c2.staticflickr.com/4/3212/4562537127_3247924143.jpg |
Courchamp
et al. (1999)’s results indicate that
ecological conservation must understand the complex interactions of
communities. Invasive species, though, can greatly modify such interactions,
causing trophic cascades that damage the stability of the community. The ability to
model trophic interactions is an important tool for conservation biology
because such mathematical models generate predictions that help to minimize the
negative impacts of trophic cascades. Courchamp et al. (1999)’s research focused on island populations, but the
trophic interactions among birds, rodents, and cats undoubtedly occur in urban
areas as well. Urban yards are an important habitat for many songbirds; both
cats and rodents are common invasives that threaten bird populations in urban
and suburban areas. Therefore, expanding Courchamp et al. (1999)’s investigation to urban areas would be beneficial to songbird
conservation efforts. Finally, while mathematical models are quite useful,
investigating trophic level interactions such as mesopredator release through
fieldwork is important for testing mathematical predictions against natural
systems. While difficult, such field studies are essential to increase
knowledge of the effects of invading species on communities.
References:
Courchamp, F., M. Langlais, and G. Sugihara. 1999. Cats protecting birds: Modelling the mesopredator release effect. Journal of Animal Ecology 68: 282-292.
Courchamp, F., M. Langlais, and G. Sugihara. 1999. Cats protecting birds: Modelling the mesopredator release effect. Journal of Animal Ecology 68: 282-292.
Since when are leaves magnetized?
![]() |
A close up of U. carpinifolia leaves
https://www.portlandoregon.gov/parks/article/479621?
|
Since when are leave magnetized?
By: Andrea Semlow
Air pollution is a prominent concern in urban areas around the world. Dry regions in particular have higher particulate matter air pollution in high traffic areas. These high traffic areas are usually areas near streets with high vehicle density that kick-up dust containing heavy metals from brake systems and industrial facilities. These tiny airborne particles are highly hazardous because they can lead to lethal respiratory and cardiovascular diseases. Due to these pressing concerns, researchers have been searching for inexpensive, rapid air pollution monitoring techniques. Over the past twenty years, studies on tree leaves' ability to proxy as a bio-monitoring systems have resulted in a variety of new techniques. Tree leaves in urban and roadside areas have been proven to be good accumulators of atmosphere dusts. Recent studies have even shown that along with dust particles, leaves also accumulate magnetic particles. So leaves are magnetized, so what?
Mohammad
Mehdi Sadeghian conducted a study in 2011 that utilized this magnetized quality
of leaves to find out the quantity and quality of vegetation in different areas
of Isfahan, Iran, specifically looking at the magnetic properties of Elm (Ulmus carpinifolia) leaves. His goal was
to determine if magnetic material on leaves could be a possible proxy to
monitor regional distribution of air particulate matter (PM) pollution. A close
up of the magnetic particles on a leaf surface is depicted on the right. The magnetic
particles associated with atmospheric particles arise from domestic heating,
vehicle exhaust and brake systems, and industrial facilities (Sadeghian et al
2011).This method is non-destructive, inexpensive, easily detected, and rapid. Sadeghian
collected from four spaces, a park, square, street, and control station, in
order to determine urban landscape areas with the highest density of air
pollutants. This method is unique because he has accounted for the leaf surface
composition change due to rain as well as water evaporation (Sadeghian et al
2011). Leaves from each site were collected and a magnetometer, an instrument
used for measuring magnetic forces, measured magnetized susceptibility with a
pulsed field (Sadeghian et al 2011). The study found the highest concentration
of magnetic properties were trees found in squares and streets. Streets had the
highest concentration of particles most likely because high traffic roads re-suspend
road dust resulting in higher magnetization of the U. carpinifolia leaves (Sadeghian et al 2011).
Future
use of this method will hopefully allow for cities to develop less expensive
monitoring systems; however, it appears this particularly approach would be quite
labor intensive. My potential future project would be in a similar vein utilizing
tree leaves as a bio-monitoring system, only a little closer to home in
Phoenix, Arizona. If you have never heard of a COTS monitoring system, it
stands for commercial off the shelf monitoring system. Basically a miniaturized
version of the really expensive air pollution monitor currently in place in
urban areas around the world. These devices will allow for more localized air
pollutant detection, increasing our knowledge of on the ground conditions in
cities. This will be extremely beneficial to updating the urban landscapes of
not only Phoenix, but numerous dry urban areas.
Reference: Sedeghian, M.M. (2011) “Biomonitoring of
particulate matter by magnetic properties of Ulmus carpinifolia leaves” African
Journal of Biotechnology 11 (73): 13827-13830.
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