Monthly Archives: April 2018

Too much of a good thing is killing Monarch butterflies

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There was a time in the mid-Pleisticine when a photo of an ecological event was an awesome novelty, and a movie of an ecological event even more so.  Dodderers of an ecological bent (myself included), can vividly recall viewing a series of photos or a movie, either in a seminar or in an ancient ecology text, of a blue jay consuming a monarch butterfly, Danaus plexippus.  Consumption is immediately followed by explosive vomiting, as the cardenolides within the monarch butterfly claim another victim.  The monarch sequesters these cardenolide toxins from its larval food (milkweed), and incorporates them into its tissues as a means of protecting itself from predators – presumably blue jays learn from this very aversive experience.  I should point out that the individual sacrificial butterfly enjoys no fitness from this learning event – which raises some evolutionary questions we will not explore at the present.

Karen Oberhauser

Five instars (stages of development) of monarch caterpillars on a milkweed leaf. Credit: Karen Oberhauser

Rather we turn our attention to the relationship between milkweed, monarchs, and climate change. In several places in this blog we’ve talked about how climate change has influenced the behavior or physiology of a single species. For example, my first blog (Jan 31, 2017) discusses how increasing temperatures create more females in a loggerhead turtle population. But there are fewer studies that explore how climate change influences the ecological landscape, ultimately affecting interactions between species.  Along these lines, Matt Faldyn wondered if increased air temperature would change the chemical constitution of milkweed in a way that might influence monarch populations.  As he describes, “With milkweed toxicity, there is a ‘goldilocks’ zone where monarchs prefer to feed on milkweed that produce enough toxins in order to sequester these (cardenolide) chemicals as an antipredator/antiparasite defense, while also avoiding reaching a tipping point of toxicity where feeding on very toxic milkweeds negatively impacts monarch fitness.” He expected that at higher temperatures, milkweed would become stressed, and be physiologically unable to sustain normal levels of cardenolide production.

Faldynnative

Monarch butterfly feeds on a native milkweed, Asclepias incarnata. Credit: Teune at the English Language Wikipedia.

For their research, Faldyn and his colleagues worked with two milkweed species.  Asclepias incarnata is a common, native milkweed found throughout the monarch butterfly’s range in the eastern and southeastern United States.  Asclepias curassavica is an exotic species that has become established in the southern United States.  In contrast to A. incarnata, A. curassavica does not die back over the winter months; consequently some monarch populations are no longer migratory, relying on A. curassavicato provide them with a year round food supply.

Faldynexotic

The exotic milkweed, Asclepias curassavica. Credit: 2016 Jee & Rani Nature Photography (License: CC BY-SA 4.0)

To protect against herbivory, milkweeds have two primary chemical deterrants: (1) the already-mentioned cardenolides, which are toxic steroids that disrupt cell membrane function, and (2) release of sticky latex, which can gum up caterpillar mouthparts and actually trap young caterpillars.

field_noborderii.jpgThe researchers wanted to simulate climate change under field conditions, so they created open-top chambers with plexiglass plates that functioned much like mini-greenhouses, into which they placed one milkweed plant that was covered with butterfly netting.  This setup raised ambient temperatures by about 3°C during the day and 0.2°C at nighttime.  Control plots were single milkweed plants with butterfly netting. Half of the plants were native milkweed, and the other half were the exotic species.

For their experiments, Faldyn and his colleagues introduced 80 monarch caterpillars (one per plant) and allowed them to feed normally until they pupated.  Pupae were brought into the lab and allowed to metamorphose into adults.

MattGood

Matt Faldyn holds two monarch butterflies in the laboratory. Credit Matt Faldyn.

At normal (ambient) temperatures, monarchs survived somewhat better on exotic milkweed.  But at warmer temperatures, there is a strikingly different picture. Monarch survival is unaffected by warmer temperatures on native milkweed, but is sharply reduced by warmer temperatures on exotic milkweed (top graph below). The few that managed to survive warm temperatures on exotic milkweed grew much smaller, based on their body mass and forewing length (middle and bottom graph below)

FaldynFig1

Survival (top), adult mass (middle) and forewing length (bottom) of monarch butterflies raised under normal (ambient) and warmed temperatures.  Error bars are 95% confidence intervals.

Both milkweed species increased production of both types of chemicals over the course of the experiment. But by the end of the experiment, the exotic species released 3-times the quantity of latex and 13-times the quantity of cardenolides than did the native milkweed species.

FaldynFig2

Average amount of latex released at the beginning and end of the experiment.  Error bars are 95% confidence intervals.

FaldynFig2

Average cardenolide concentration at the beginning and end of the experiment.

The researchers argue that the exotic milkweed, Asclepias curassavica, may become an ecological trap for monarch butterflies, in that it attracts monarchs to feed on it, but will, under future warmer conditions, result in dramatically reduced monarch survival. Interestingly, these results are not what Faldyn originally expected; recall that he anticipated that temperature-stressed plants would reduce cardenolide production. The tremendous increase in cardenolide production in exotic milkweed at warmer temperatures may simply be too much toxin for the monarchs to process. The researchers predict that as climate warms, milkweed ranges will expand further north into Canada, and lead to northward shifts of monarch populations as well.  They urge nurseries to emphasize the distribution of native rather than exotic milkweed, so that monarchs will be less likely to become victims of this ecological trap.

note: the paper that describes this research is from the journal Ecology. The reference is Faldyn, M. J., Hunter, M. D. and Elderd, B. D. (2018), Climate change and an invasive, tropical milkweed: an ecological trap for monarch butterflies. Ecology. doi:10.1002/ecy.2198. Thanks to the Ecological Society of America for allowing me to use figures from the paper. Copyright © 2018 by the Ecological Society of America. All rights reserved.

Fungi attack plants – insects respond!

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As she was preparing to do her dissertation research on the interactions between the Asian chestnut gall wasp, the chestnut blight disease and the European chestnut, Pilar Fernandez-Conradi read a lot of papers about fungal-insect-plant interactions.  She was impressed by the diversity of outcomes that resulted when plants were attacked by both insects and fungi, and wondered whether there were any generalities to glean from these research findings. She asked two basic questions. First, if a plant is infected by a fungus, is it more or less likely to be attacked by insects than is an uninfected plant?  Second, does an insect that attacks a fungal-infected plant perform better or worse than it would have on an uninfected plant?

D. Kuriphilus+Gnomo

Three-way interaction between the chestnut tree, the chestnut gall wasp, and the fungus Gnomopsis castanea. Female wasps induce the plant to create galls, which house developing larvae. Green globular galls (with a hint of rose-color) have not been infected by a fungus, while the very dark tissue is the the remains of a gall that was attacked by the fungus. Credit: Pilar Fernandez-Conradi.

Fernandez-Conradi and her colleagues thought they were more likely to discover a negative effect of fungal infection on the preference and performance of herbivorous insects.  Several studies had shown that nutrient quantity and quality of host plants is reduced by fungal infection, so it makes sense that insects would avoid infected plants.  But the researchers also knew that fungal infection can, in some cases, actually increase the sugar concentration of some plants, so insects might prefer those plants and also develop more rapidly on them. In addition, fungal infection can induce chemical defenses in plants that might make them less palatable to insects, or alternatively, fungal infection could weaken plant defenses making them more palatable to attacking insects.

To resolve this conundrum, Fernandez-Conradi and her colleagues did a meta-analysis, of the existing literature, identifying 1113 case studies based on 101 papers.  To be considered in the meta-analysis, all of the studies had to meet the following criteria: (1) report insect preference or performance on fungal-infected vs. uninfected plants, (2) report the Genus or species of the plant, fungus and insect, (3) report the mean response and a measure of variation (standard error, standard deviation or variance). The measure of variation allows researchers to calculate the effect size, which calculates the strength of the relationship that is being explored. The researchers found that, in general, insects avoid and perform worse on infected plants than they do on uninfected plants.

Fernandez-conradi-myfig

Mean effect size of insect preference and performance (combined) in response to fungal infection infection.  Error bars are 95% confidence intervals (CIs).  In this graph, and the next two graphs as well, a solid data point indicates a statistically significant effect.  You can also visually test for statistical significance by noting that the error bar does not cross the dashed vertical line that represents no effect (at the 0.0 value). The negative value indicates that insects respond negatively to fungal infection.

Fernandez-Conradi and her colleagues then broke down the data to explore several questions in more detail. For example, they wondered if the type of fungus mattered.  For their meta-analysis, they considered three types of fungi with different lifestyles: (1) biotrophic pathogens that develop on and extract nutrients from living plant tissues, (2) necrotrophic pathogens that secrete enzymes that kill plant cells, so they can develop and feed on the dead tissue, and (3) endophytes that live inside living plant tissue without causing visible disease symptoms.

Fernandez-conradiFig1

Effect of fungus lifestyle on insect performance.  k = the number of studies.  Different letters to the right of CIs indicate significant differences among the variables (lifestyles).

The meta-analysis showed an important fungus-lifestyle effect (see the graph to your left).  Insect performance was strongly reduced in biotrophic pathogens and endophytes, but not in necrotrophic pathogens, where insect performance actually improved slightly (but not significantly). The researchers point out that biotrophic pathogens and endophytes both develop in living plant tissues, while necrotrophic pathogens release cell-wall degrading enzymes which can cause the plant to release sugars and other nutrients.  These nutrients obviously benefit the fungus, but can additionally benefit insects that feed on the plants.

To further explore this lifestyle effect, Fernandez-Conradi and her colleagues broke down insect response into performance and preference, focusing on chewing insects, for which there were the most data. Insects showed lower performance on and reduced preference (i.e. increased avoidance) for plants infected with biotrophic pathogens. They also performed equally poorly on endophyte-infected plants, but did not avoid endophyte-infected plants (see graph below). This was surprising since you would expect natural selection to favor insects that can choose the best plants to feed on. The problem for insects may be that endophytic infection is basically symptomless, so the insects may, in many cases, be unable to tell that the plant is infected, and likely to be less nutritionally rewarding.

Fernandez-conradiFig2

Effects of fungal infection on preference and performance of chewing insects.  k = the number of studies.  Different letters to the right of CIs indicate significant differences among the variables. Variables that share one letter have similar effect sizes.

Many ecological studies deal with two interacting species: a predator and a prey, or a parasite and its host.  Fernandez-Conradi and her colleagues remind us that though two-species interactions are much easier to study, many important real-world interactions involve three or more species. Their meta-analysis highlights that plant infection by pathogenic and endophytic fungi reduces the performance and preference of insects that feed on these plants. But fungus lifestyle plays an important role, and may have different effects on performance and preference. Their meta-analysis also suggests other related avenues for research.  For example, how are plant-fungus-insect interactions modified by other species, such as viruses, bacteria and parasitoids (an animal that lives on or inside an insect, and feeds on its tissues)? Or, what are the underlying molecular (hormonal) mechanisms that determine the response of the plant to fungal infection, and to insect attack?  Finally, how does time influence both plant and insect response?  If a plant is recently infected by a fungus, does it have a different effect on insect performance and preference than does a plant that has suffered from chronic infection.  There are very few data on these (and other) questions, but they are more likely to get pursued now that some basic relationships have been uncovered.

note: the paper that describes this research is from the journal Ecology. The reference is Fernandez‐Conradi, P., Jactel, H., Robin, C., Tack, A.J. and Castagneyrol, B., 2018. Fungi reduce preference and performance of insect herbivores on challenged plants. Ecology, 99(2), pp.300-311. Thanks to the Ecological Society of America for allowing me to use figures from the paper. Copyright © 2018 by the Ecological Society of America. All rights reserved.

Saguaro survival: establishing an icon

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Having grown up in the New York metropolitan area, my only contact with the saguaro cactus, Carnegiea gigantea, was from several TV westerns, which dubiously placed these mammoth cacti in New Mexico, Texas and Colorado.  In fact, the saguaro is limited to the Sonoran Desert of northwestern Mexico, extreme southeast California and southern and central Arizona. You won’t find these cacti further north, because a freeze lasting more than 24 hours kills them.  I still remember my first real sighting of these cacti; I was amazed at how distinct they seemed in comparison to the other vegetation, and I delighted in their abundance.

Daniel Winkler - Saguaro Photo 1

Dense patch of saguaros. Credit: Daniel Winkler

Many others delight in their abundance as well.  The flowers, fruits and seeds feed many animals (including humans).  They were an important food for the Tohono O’odham and Pima Indians – eaten fresh or converted into numerous products including wine, juice, jam and syrup.

Daniel Winkler - Saguaro Photo 2

Large saguaro with many fruits emanating from the apex of its branches. Credit: Daniel Winkler

Woodpeckers and flickers excavate nests in the saguaro’s trunk, which are subsequently occupied by other animals such as snakes, arthropods and small mammals.

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Saguaro with nest cavity excavated near the top of its trunk. Credit: Daniel Winkler

Daniel Winkler also delighted in the saguaro’s awesomeness. As he describes “I fell in love with answering some basic ecology questions about the saguaro. I was surprised that scientists had been studying this wonderful plant for almost 100 years and there were still many basic questions about the species general biology and ecology that remained unanswered. Thus, I was hooked immediately and became obsessed with saguaro.”

Don Swann - Photo of D. Winkler with young saguaros

Daniel Winkler with young saguaros. Credit: Don Swann

Winkler and his colleagues wanted to know how moisture, temperature and habitat influence the establishment or survival of juvenile saguaro seedlings. Previous research had shown that saguaro height can be used to estimate saguaro age, given knowledge of previous rainfall in a particular area. So buoyed by an army of citizen scientists whom they recruited with the help of social media, student groups from schools and volunteers working at the Saguaro National Park, the research team estimated the age of every saguaro on 36 4-ha plots (1 ha = 10,000 m2).

Going into the study, the researchers knew that rainfall was a very important factor, with saguaros surviving better during wet periods.  But they also knew that historically, some areas located near each other showed different establishment trends, thus they suspected that other variables, particularly land use and other landscape factors, might be important.  They did their research in two different districts within the park: 21 plots in the Rincon Mountain District (RMD) on the east side of the park, and 15 plots in the Tucson Mountain District (TMD) to the west. They classified each plot as a particular habitat type based on slope, elevation and soil-type. Bajada was low elevation, flat and had gravelly porous soils.  Foothills were intermediate elevation and intermediate slope, while sloped habitats had highest elevation, steepest slope, and the coarsest rockiest soils.

Daniel Winkler - Saguaro Photo 4

Panoramic view of Saguaro National Park showing diversity of habitats. Credit: Daniel Winkler.

Winkler and his colleagues calculated the Palmer Drought Severity Index (PDSI) for the years 1950-2003. The PDSI quantifies the water balance between precipitation and evapotranspiration, taking into account not only rainfall but also other factors such as temperature and cloud cover.  The PDSI was estimated by assessing tree ring width for each year in nearby woodlands; wet conditions have wide tree rings (maximum PDSI value = +6), while dry years have narrow tree rings (minimum PDSI value = -6).

The researchers discovered a very strong association between the PDSI and seedling establishment. Low PDSI at the beginning and especially the end of the time frame was associated with low seedling establishment, while high PDSI (particularly in the 1980s was associated with high rates of seedling establishment (top graph below).  But other patterns emerged as well.  For example, establishment was higher in the TMD during the wettest years, but higher in the RMD during the most recent drought (bottom graph below).

WinklerFig1

Top. Total number of saguaros (left Y-axis) established per hectare from 1950-2003 in relation to PDSI (dashed line, right Y-axis). Bottom. Total number of saguaros established per hectare in the Tucson Mountain District (TMD – filled bars) and the Rincon Mountain District (RMD – open bars)  from 1950-2003 in relation to PDSI (dashed line, right Y-axis).

Saguaro establishment increased in all habitats when conditions were relatively wet (more positive PDSI values).  Under drought conditions, slopes had greatest saguaro establishment, while establishment increased more rapidly in foothills (and to a lesser extent in Bajadas) as moisture levels increased.

WinklerFig2

Model projecting number of saguaros established in the three major habitats in relation to PDSI.  Shaded regions are 95% confidence intervals.

The researchers were surprised at how tight the connection was between drought and saguaro establishment. But landscape features are also important.  The TMD is warmer and dryer than the nearby RMD, and had substantially lower establishment during the recent drought. The slopes in the RMD are steeper and rockier than sloped areas of the TMD, and may buffer saguaros from drought by capturing water in rock crevices and holding it for longer periods of time so it can be absorbed by saguaro roots. Nurse trees that provide shade to young saguaros may also be more common on the RMD slopes.

Winkler and his colleagues are concerned about the long-term impacts of climate change on saguaro populations, particularly in the drier areas of the TMD. They urge researchers to explore how long-term management of grazing and invasive species influences saguaro establishment across the landscape.  They also encourage researchers to gather some very basic data about saguaros, such as how they access water and how human water use patterns influence the water’s availability to this iconic species.

note: the paper that describes this research is from the journal Ecology. The reference is Winkler, D. E., Conver, J. L., Huxman, T. E. and Swann, D. E. (2018), The interaction of drought and habitat explain space–time patterns of establishment in saguaro (Carnegiea gigantea). Ecology 99: 621-631. doi:10.1002/ecy.2124. Thanks to the Ecological Society of America for allowing me to use figures from the paper. Copyright © 2018 by the Ecological Society of America. All rights reserved.