Although this course does not focus on behavioral ecology, this laboratory exposes you to one aspect of that field which directly relates to population and community ecology. We take advantage of ongoing research on fire ant biological control at Brackenridge Field Laboratory to develop this project for the course.
The imported fire ant, Solenopsis invicta was introduced into the Southern US about 7 decades ago. Since that time, this insect has spread across the entire Southeastern US and in the last two decades has established in Arizona and California. It is now known that U.S. Gulf Coast populations of this ant are the source for recent global expansion [@ascunce2011]. Ecologists believe that the lack of natural enemies in the introduced range is a major reason this species can increase its populations faster than native counterparts such as the native fire ants, S. geminata, S. xyloni, and other native ants.
Candidates for controlling fire ant populations include tiny parasitoid flies called the ant-decapitating flies, of the family Phoridae. This family of >20,000 species is generally characterized by scavengers and fungus feeders. However, a few genera focus on ants, and some (such as the genus Pseudacteon) specialize on a single species or a small species group of within a genus.
In the late 1970's, Don Feener, a graduate student working at BFL (now Professor at University of Utah) discovered that phorid fly females have an amazing effect on their host species as they attempt to inject eggs into worker ants [@feener1981]. Although Feener studied ants in the genus Pheidole and not fire ants, the observation that food foraging in ants could be inhibited by the mere presence of a tiny fly immediately suggested that one reason for the imported fire ant's success relative to the native Texas fire ant could be that it is free of such things as phorid fly attack in its introduced range. The native fire ants, S. geminata and S. xyloni, are attacked by several species of Pseudacteon phorids, which show no interest in S. invicta.
With these facts in mind, Dr. Gilbert and his colleagues have been studying 16 species of Pseudacteon from Brazil and Argentina in the hopes of introducing one or more species for the control of S. invicta. One aspect of such studies involves the documentation of how these flies alter fire ant food gathering behavior in S. invicta, since it is thought that the "control" of fire ant populations may be via reducing food to offspring rather than via direct mortality [@orr1997; @porter1995a].
Fire ant workers, like those of all ants, are sterile females who assist their queen (or queens, in the case of polygynous species or genotypes) in raising more workers or winged reproductive ants called alates. Fire ants are very effective competitors because they possess many sizes of workers and thus can compete well for many sizes of food particles. We term this attribute caste polymorphism. Most ants have one size of worker and are termed monomorphic.\ Note that "polygynous" in the context of ants refers to colonies with multiple queens, not to a polygamous form of mating.
An ant colony that is well supplied with food will eventually reach a size at which it can "afford" to produce winged alates for a mating flight. The number of alates produced and the frequency with which a colony of a species can produce mating flights determines the rate at which that species increases its density in an area. Phorids are thought to reduce the reproductive rate of fire ant colonies through several related effects on food foraging ability:
With either or both of these responses, less food will be taken to the mound than would occur in the absence of phorids. How will this decrease in food gathered due to parasite avoidance affect colony size and the ability of the colony to reproduce itself (i.e. start another colony)?
The goal of the exercise is to give you insight into the types of questions and approaches that define behavioral ecology.
The basic set-up consists of white tiles or cards upon which we ant bait. Worker fire ants will recruit from a nearby colony and begin harvesting the food. Once fire ants have recruited and formed a stable foraging line, we will cover the bait with a clear plastic shell that will allow you to control the exposure of each foraging trail to phorid flies. This is necessary to contain flies and to exclude other species naturalized and present outdoors at BFL. This setup forms our "arenas."
Each group will monitor two arenas: experimental and control. Phorids will be introduced to experimental area once ant numbers have become stable for a five-minute interval. Paired control arenas will be identical but not contain phorids. The two arenas should be within about two to three meters of each other. If there are too many phorids arriving from the resident populations, we will actively remove them from controls and add to experimental arenas. A tiny species, P. curvatus, is currently present at BFL along with P. obtusus.
A circle drawn on the tile or card around the bait is one good way to count foraging workers (number of ants crossing the line / unit time) but you can devise equally effective methods. The white tile or bait card helps the observer visualize the tiny, fast-flying phorids. It also helps if you can find a neat foraging trail so that most or all ants coming and going can be easily counted. On the previous day, Dr. Gilbert will choose likely sites and clear obstructing grass and weeds and to improve visibility of ants and flies. Baits will be placed out about 45 minutes prior to initiating the experiment. Hand counters and stop watches will be needed for these timed counts.
Temperature, light, and humidity might vary considerably between sites. You will record temperatures near the baits with HOBO data loggers. Shade cloth will be used to reduce solar heating of covers exposed to full sun (because fire ants cease foraging at high body temperatures). These covers will be gently removed to make observations. Try to make conditions in the experimental and control as similar as possible.
The effects of attacking female phorids on the foraging rates of S. invicta at food items will be assessed as follows:
For initial setup:
To view the data that's been collected, click the "Live Data" tab at the top.
Exporting your data:
In your methods section, be sure to identify the model of HOBO logger used (MX2303), manufacturer, and the interval at which the data were collected. For example, "We collected the temperature of each arena every 15 seconds with HOBO MX2303 data loggers (Onset Computer Corporation)."
Due to variable weather conditions, phorids may not be abundant enough in the environment to run this experiment. In previous semesters, we would supplement this with phorids raised in the BFL fire ant lab; however, shifting research priorities and budgetary conditions have resulted in the phorid program's termination. We will instead attempt to collect wild phorids using a series of baiting stations. These stations aim to attract phorid flies by concentrating a large number of mostly dead fire ants in a small area. This is the first time we have attempted this procedure, so if it does not work we will analyze a previous semester's data for this lab.
Your first question is whether phorids flies affect the rate of foraging in S. invicta. The goal is to compare ant activity before and after the introduction of the phorid parasitoid. We'll use the rate at which ants left tile as our measure of activity.
If you inspect the data, you will likely find that different groups had different recruitment rates to start with. Accounting for this is one challenge of the analysis (this is a methodological choice that may be worth talking about in your discussion). One solution to the problem is to standardize your counts. Each count (per time step, group, and treatment) needs to be divided by some baseline value. Since you should have three baseline values per area, you could choose to either standardize by the average of all three or by the final baseline value. This can be done with pivot tables, Excel formulas, or through R. This will express your data as a proportion of original "leaving" rates. This standardization will allow you to compare "leaving" rates between controls and experimentals across colonies.
To compare leaving rates, you'll need to do an analysis of covariance (ANCOVA), which tests whether the regression between time and proportion of ants differs between the two treatments. Create a figure to accompany this. See section \@ref(r-stats-ancova) for more details.
Does temperature affect foraging behavior? Does this effect change based on the presence of phorid flies?
Create a scatter plot with temperature on the x-axis and number of ants leaving on the y-axis; separate control and experimental data into different panels.
For all of these, run a linear regression; be sure to include the regression line in the plots and report the appropriate statistics
Your discussion should address the following points & questions:
I've been looking at the data and trying to begin the Analysis, but I don't understand what you mean about standardizing counts. What number would I divide by and would it be the same number for all groups, or do I have to analyze the data of each group individually and compare it?
Each colony (team/group * treatment combo) should be standardized by a different number, which represents the number of ants present before the treatment began. There are a number of ways to do this, but I would recommend either standardizing by the colony's number at baseline 3 (i.e., right before fly introduction), or by the average count for all three baselines at that colony. Once you have done this, you can then compare the relative counts across different colonies.
Once the leaving rate values are calculated after dividing by baseline values, what are the units? I'm a little confused. Is it ants/time step, ants/second, ants/minute? I know each time step is 2 minutes long, so saying 1.14 ants/time step seems incorrect. Is there something I'm totally missing?
Also I noticed that some of the data is very asymmetrical, so would you rather us talk about its median/range when describing asymmetrical center and spread (in the results), or would you still prefer mean and standard deviation?
It's a relative value, so it would be unitless.
If you decide to avoid mean/sd (which is your choice), I would recommend inter-quartile range over range, since it's a more robust measure.
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