Category: New Research Page 4 of 67

Muscle map on scapulocoracoid of Anolis insolitus

Morphology of the Scapulocoracoid of Anolis Ecomorphs

 

From the onset of my scientific career I have been fascinated by the pectoral girdle. In its structural and functional diversity it is barely rivaled by any other skeletal part of the tetrapod body. Anoles, in particular, employ their forelimbs not only in locomotion, but also in various routines of display, grooming, feeding, or mating. It is likely that the different functional roles fulfilled by the pectoral limb and girdle impose varying, and potentially opposing, selective pressures onto the evolution of its structural form.

Jane Peterson briefly alluded to the structural variance displayed by the different anole ecomorphs, relating them to specific locomotor requirements by providing brief descriptions in her thesis (1973) and the First Anolis Newsletter (1974). However, beyond this initial work, and a few qualitative assessments in papers regarding phylogenetically informative characters, very little is known about the variability of the anole pectoral girdle.

right scauplocoracoid of Jamaican anoles

Right scapulocoracoid of three anole species, representative of the Jamaican lineage. The arrow denotes anterior. (via Tinius et al. 2020)

In many ways, our recent publication in the Annals of Anatomy (Tinius et al. 2020) is a dream come true (at least for me), as it allowed us to finally visualise the patterns of morphological variation that Peterson (1974) could only communicate in descriptions. Because the shoulder girdle is comprised of multiple elements that are mobile with respect to one another, this paper only investigated one of its moieties: the scapulocoracoid. This paired structure spans the entire height of the body wall, is comprised of developmentally very different compounds, and directly connects the forelimb to a midline element, the presternal plate. These attributes made it a great starting point for our investigations of the pectoral girdle.

In describing the scapulocoracoid of two non-anoline iguanids, Polychrus and Pristidactylus, we anchored our comparisons in two well-studied and closely related lizards. We then expanded on this anatomical framework by comparing all representatives of the monophyletic Jamaican anole radiation to their respective ecomorph representatives on Puerto Rico and Hispaniola. We tried to take full account of the variability of the scapulocoracoid by examining it both qualitatively, in images and comparative description, and quantitatively, through geometric morphometric analysis.

CVA of the right scapulocoracoid of Anolis ecomorphs

Canonical Variate Analysis (CVA) of the right scapulocoracoid of Greater Antillean anoles, including warp image of the scapulocoracoid denoting shape changes along CV1 and CV2. (via Tinius et al. 2020)

We found that regardless of potential phylogenetic constraints on skeletal morphology, morphospatial occupancy differs markedly between ecomorph groups. Unexpectedly, twig anoles show the most distinctive shape of the scapulocoracoid, with a relatively tall scapula and anteroposteriorly short coracoid, similar to the situation found in chameleons (Fischer et al. 2010). But despite a significant overlap in morphospatial occupancy, the other three ecomorphs examined (trunk-ground, trunk-crown, and crown-giant) also exhibit trends towards a specialized scapulocoracoid morphology, such as a relatively wide/cylindrical scapulocoracoid in trunk-ground anoles.

These variations in form likely impact the size and vectors of muscles attaching to the scapulocoracoid. One muscle group that is likely particularly impacted by the differences in scapulocoracoid form is the M. serratus anterior. This muscle group originates laterally on the cervical ribs and inserts on the medial aspect of the suprascapula. The M. serratus anterior group stabilizes the scapulocoracoid during locomotion and protracts/retracts it along the body wall. The anteroposteriorly more extensive suprascapula of crown-giant anoles likely facilitates more forceful scapular retraction, through the relatively greater attachment area for this muscle and the anterior disposition of its insertion area. Contrastingly, the relatively tall scapula of twig forms likely allows for a greater moment arm acting through this muscle group, while the anteroposteriorly short suprascapula facilitates more precise protraction/retraction of the scapulocoracoid.

Muscle map on scapulocoracoid of Anolis insolitus

Right scapulocoracoid of Anolis insolitus in a) lateral, and b) medial view, showing the attachment sites of major muscle groups that act upon the scapulocoracoid. (via Tinius et al. 2020)

My only regret about this project is the exclusion of Cuban anoles, which markedly limited our ability to compare patterns in a wider phylogenetic context. Most of the crown-giant and trunk-crown anoles examined belong to their own ecologically homogenous clade, making it impossible to discern ecological from morphological signal.

The Jamaican Anolis clade provides a glimpse into what might be achieved with a phylogenetically broader sample, as it represents four major ecomorph groups (five, if you attribute A. opalinus to the trunk group) plus two non-ecomorph species within a seven-species radiation. Despite the relatively young age of the Jamaican clade, its ecomorph representatives exhibit a push towards specialized morphologies of the scapulocoracoid, even if this level of specialization is markedly smaller than in their Puerto-Rican and Hispaniolan relatives. A future widening of our sample should allow us to answer some intriguing questions regarding the retention and diversification of ecomorphologically specialized forms within distinct phylogenetic lineages.

Literature cited

Fischer, M.S, Krause, C. & Lilje, K.E. (2010): Evolution of chameleon locomotion, or how to become arboreal as a reptile.─ Zoology, 113:67-74.

Peterson, J.A. (1973): Adaptation for arboreal locomotion in the shoulder region of lizards.─ Ph.D. thesis, University of Chicago.

Peterson, J.A. (1974) [In:] Williams, E.E. (ed.) The First Anolis Newsletter. Cambridge, Massachusetts: Museum of Comparative Zoology, Harvard University.

Tinius, A., Russell, A.P., Jamniczky, H.A. & Anderson, J.S. (2020): Ecomorphological associations of scapulocoracoid form in Greater Antillean Anolis lizards.─ Annals of Anatomy, 231; doi.org/10.1016/j.aanat.2020.151527.

Sleeping Behavior of the Puerto Rican Twig Anole, Anolis occultus

In August, we published a paper in the Caribbean Journal of Science entitled, “Sleeping Behavior of the Secretive Puerto Rican Twig Anole, Anolis occultus.” Check out our new post on the Chipojo Lab blog about the paper!

Levi Storks, Manuel Leal. 2020. Sleeping Behavior of the Secretive Puerto Rican Twig Anole, Anolis occultus. Caribbean Journal of Science 50(1):178–87.

Morphology Does Not Distinguish Candidate Species of Anolis distichus

Photo by Richard Glor

Anolis distichus, the North Caribbean bark anole, is probably best known by readers of Anole Annals for its striking variability in dewlap color among populations. Primarily based on these differences in dewlap color, Albert Schwartz published a monograph with descriptions for 18 subspecies distributed across Hispaniola and the Bahamas (1968). The large number of subspecies and the question of their origin has helped establish Anolis distichus as one of the most intriguing cases for the study of speciation in anoles. Do the subspecies of Anolis distichus represent geographic patterns in dewlap color variation? Or, are the subspecies evolutionarily isolated lineages worthy of species status?

Molecular genetic data have revealed several genetically distinct populations of Anolis distichus that appear to be at varying stages of the speciation process. However, with the exception of A. d. ignigularis and A. d. favillarum, these genetically distinct groups did not align with the subspecies described by Schwartz, corresponding better to geography than patterns of dewlap color variation (Geneva et al. 2015). Most recently, using genome wide markers and multicoalescent species delimitation methods, MacGuigan et al. (2017) identified six candidate species within A. distichus. The authors, however, did not update the taxonomy because the boundaries among the candidate species remained unclear.

To clear up those boundaries, we tested if the candidate species identified by MacGuigan could be distinguished by morphological characters. Because Schwartz considered scale counts along with dewlap and body color pattern in his monograph and was not able to recover any diagnostic differences, we focused on morphometric characters and measured 13 traits from more than 500 animals (available on Dryad). We conducted univariate and multivariate analyses to test if (a) any of the individual characters distinguished candidate species; and (b) if characters considered in aggregate could distinguish the candidate species. Because the candidate species are parapatrically distributed across Hispaniola, locality information has the potential to aid diagnosis. To account for this, we carried out comparisons of all candidate species together and only the pairs of candidate species that potentially come into contact. 

Although ANOVAs recovered significant differences in mean character values, visual examination of violin plots showed that none of them were diagnostic for any of the candidate species.  Discriminant Function Analysis (DFA) revealed clustering of some of the candidate species, but there was still substantial overlap in multivariate space and candidate species were diagnosed with poor accuracy. DFA did prove to be more accurate when asked to classify individuals only between the pairs of potentially co-occurring candidate species instead of all of the candidate species together. Ultimately, we still rejected the hypothesis that candidate species could be distinguished on the basis of our morphometric dataset due to gaps in our sampling and overall similarity among the candidate species.

Univariate and multivariate results from Myers et al. (2020). (A) Example violin plots for two characters, snout-vent length and head width. (B) Multivariate plots of DFA results.

Because both univariate and multivariate analyses did not recover support for the hypothesis that the candidate species could be distinguished by morphometric characters, we decided to test how many species were supported by the data.  We tested alternative species delimitation scenarios with a model fitting approach that uses normal mixture models (Cadena et al. 2018). Normal mixture models consider morphological variation to consist of a mix of different normal distributions and, unlike DFA, does not require individuals to be assigned to different groups a priori. We tested the support for models specifying up to as many as 12 species and compared the support for these generic models to models specifying MacGuigan’s candidate species and Schwartz’s subspecies. The best supported normal mixture model specified two groups; however, the model specified a group containing 489 individuals and another with 24 individuals and followed no clear geographic trend. We scrutinized the principal components used to estimate these models and determined that longitudinal and vertical ear opening diameter were driving this result. We removed them and conducted the normal mixture model analysis with the reduced dataset and recovered a single morphological group.

Is Anolis distichus only one species? Do the candidate species lack distinguishing features? We weren’t comfortable making either conclusion. Our dataset of linear morphometric characters was not capable of distinguishing candidate species, but future datasets featuring other aspects of phenotypic variation e.g., geometric morphometrics, might. Larger, genome-scale datasets with more comprehensive geographic sampling than previous molecular genetic studies will also help address the question of species boundaries in A. distichus. We also discuss some possibilities for why we were unable to recover distinguishing morphological differences, including that local adaptation across Hispaniola’s environmentally heterogeneous landscapes has resulted in morphometric variation that does not align with candidate species boundaries. Ng et al. (2013) found that dewlap color in A. distichus is correlated with local environmental signaling conditions, which would explain why dewlap color does not correspond with putative evolutionary lineages in this group of lizards. Many of the morphometric traits we considered (e.g., limb length) affect ecological performance and may have responded similarly to selective pressures. 

We were not able to resolve the confounding taxonomy of Anolis distichus in this paper, but I enjoyed the project and found it to be a very rewarding first publication. I was able to travel to the Dominican Republic to catch lizards twice as an undergraduate for this project and we were able to amass a large and geographically comprehensive dataset. Working on the taxonomy of this confounding group of lizards helped me realize my interest in speciation, which I plan to pursue further in my PhD. A lot of friends and collaborators helped with this project by assisting with fieldwork and providing input on manuscript drafts. And, of course, this work wouldn’t have been possible without my co-authors and mentors, Pietro de Mello and Rich Glor

References

Cadena, C. D., F. Zapata, and I. Jiménez. 2018. Issues and perspectives in species delimitation using phenotypic data: Atlantean evolution in Darwin’s finches. Syst. Biol. 67:181–194.

Geneva, A. J., J. Hilton, S. Noll, and R. E. Glor. 2015. Multilocus phylogenetic analyses of Hispaniolan and Bahamian trunk anoles (distichus species group). Mol. Phylogenet. Evol. 87:105–117.

MacGuigan, D. J., A. J. Geneva, and R. E. Glor. 2017. A genomic assessment of species boundaries and hybridization in a group of highly polymorphic anoles (distichus species complex). Ecol. Evol. 7:3657–3671.

Myers, T. C., P. L. H. de Mello, and R. E. Glor. 2020. A morphometric assessment of species boundaries in a widespread anole lizard (Squamata: Dactyloidae). Biol. J. Linn. Soc. 130:813-825.

Ng, J., E. L. Landeen, R. M. Logsdon, and R. E. Glor. 2013. Correlation between Anolis lizard dewlap phenotype and environmental variation indicates adaptive divergence of a signal important to sexual selection and species recognition. Evolution 67:573–582.

Schwartz, A. 1968. Geographic variation in Anolis distichus Cope (Lacertilia, Iguanidae) in the Bahama Islands and Hispaniola. Bull. Mus. Comp. Zool. 137:255–309.

Anole Genomes Webinar

Tomorrow (30 June 2020) I will be presenting a webinar on our ongoing work assembling Anolis genomes. The webinar is hosted by Dovetail Genomics who provided the core technology we used to generate high quality genome sequences. The talk is at 11AM EST. If you want to watch live and have the chance to ask questions, you can register here. If you can’t make it but still want to hear what we are up to, Dovetail will post the video on their website alongside other speakers in the series.

Vasotocin and Chemical Communication in Anolis carolinensis

 

A male green anole basking on my porch in Atlanta, Georgia. (Photo source S. M. Campos)

Growing up in Texas, I often found Anolis carolinensis green anoles (my first love) basking on my front porch and developed an early obsession with studying their natural behavior. Green anoles are the only anole endemic to North America (but see Wegener et al. (2019) suggesting the Cuban green anole, Anolis porcatus, is the same species). Anolis carolinensis are often referred to as American Chameleons due to their ability to switch between green and brown skin colors, despite being a completely different family than true chameleons. In graduate school, I worked with a different lizard genus, Sceloporus (from Greek “skelos” meaning leg, “poros” meaning hole), named for the scent producing glands on their inner thighs called femoral glands. The realization that some lizards modulate their social behavior based on chemical information that is deposited by other lizards was pivotal in my research career. Here, I’ll discuss chemical communication in A. carolinensis and the serendipitous discovery that the neuropeptide arginine vasotocin (AVT) plays some role in stimulating this chemical communication.

Anolis is an important animal model for studying the neuroendocrine control of visual communication due to their hormonal modulation of  vibrant color displays and conspicuous push up displays. Large eyes and brain areas dedicated to processing visual information suggest that detecting and responding to the visual environment is very important to anole survival and fitness. In contrast, anoles do not have the femoral or precloacal glands described in other lizards, which are used to deposit scent marks. Their olfactory bulbs (the portion of their brains that responds to volatile and non-volatile chemical signals) are tiny structures that are nestled in front of their eyes and behind their nares, attached to the rest of the brain by a long narrow nerve tract. Therefore, it is not all that surprising that anoles have long been considered microsmatic, relying very little on their sense of smell.

A CT scan of Anolis sagrei showing the main and accessory olfactory bulbs (yellow and blue arrows, respectively). The main olfactory bulb responds to volatile chemicals detected by the olfactory epithelium in the nose (such as odors in the air) and the accessory olfactory bulb responds to non-volatile chemicals detected by the vomeronasal organ. (Source Photo by Ed Stanley, arrows added by S. M. Campos)

So what is the deal with this peptide hormone, AVT? AVT and its mammalian homologue vasopressin (AVP) regulate social behavior in animals and decades of research has shown that AVT works within the visual sensory system of green anoles to modulate competitive and reproductive interactions. In non-reptilian animals like fish and mammals, AVT/AVP plays a similar role in modulating social interactions through the chemosensory system. Whether AVT influences chemosensory behavior in reptiles is unknown, representing an important gap in our understanding of the evolution of social behavior.

Now, the serendipitous part of the story. My postdoc advisor, Walter Wilczynski, built his career studying how AVT impacts visual communication in social interactions of frogs and green anoles. Previous work showed that green anoles can differentiate between AVT-treated and saline-treated males during live social interactions, but found no obvious differences in visual display rates between AVT-treated and saline-treated males, suggesting differences in behavior may be due to available chemical information. In the present study, we asked  whether an untreated lizard responds to a live AVT-treated male by altering its rate of chemosensory behavior, which we would expect if AVT-males and saline-males emit different chemical signals.

From left to right: Study authors Stephanie M. Campos, Walter Wilczynski, and Valentina Rojas. (Photo source S. M. Campos)

While lizards breathe in odors in a manner similar to humans (olfaction), they also have a secondary sense of “smell” called vomerolfaction. The latter involves using their tongues to bring chemicals from the outside environment into their mouths and deliver those chemicals to the vomerolfactory organ (often referred to as Jacobson’s organ in snakes) located in the roof of their mouths. We can easily quantify chemosensory behavior involving the tongue by counting the number of licks (tongue touches to a substrate, such as a rock), tongue flicks (tongue extrusions into the air), and lip smacks (draws odors into the mouth) a lizard performs. Use of these behaviors give us an estimate of a lizard’s level of interest in the chemical information available in their immediate environment. Chin wiping, or jaw rubbing, is another chemosensory behavior that may either deposit chemical signals or help to detect chemical signals already on a substrate. We provide short video clips in the online version of our article to show each of these behaviors.

In our experiment, we gave adult male green anoles an intraperitoneal injection of either an AVT or saline (control) solution, then introduced an untreated lizard (male or female) into the home tank of the treated lizard for a filmed 30-minute interaction. We measured rates of chemosensory behavior and the latency to perform these different behaviors. Since lizards tend to use higher rates of tongue flick behavior for exploratory purposes as they move around their environments (Cooper et al. 1994; Mason 1992), we also counted short bouts of locomotion.

Untreated males that interacted with AVT-males performed more tongue flicks and lip smacks compared to males that interacted with saline-males. Interestingly, lizards that interacted with AVT-males tended to move around less compared to lizards that interacted with saline-males. This suggests that the higher rates of chemosensory behavior by untreated males that interacted with AVT-males was not simply due to an increase in locomotion. We also found that untreated males moved around more than untreated females, regardless of treatment, demonstrating a general sex difference in locomotion among green anoles. We found no significant differences between treatments in chemosensory behavior performed by untreated females.

Lizards in their home tanks. (Photo source S. M. Campos)

When we examined the behavior of treatment males (which received injections), we found that AVT-males were faster than saline-males to perform a chemical display and, more specifically, a tongue flick toward untreated males. This suggests that AVT increases the level of initial interest in chemical information that is available during asocial encounters.

What about visual displays? We found no significant differences in visual display rates of untreated lizards, but did find that as treatment males performed more visual displays, untreated lizards moved around more (Supplementary Materials).

These results collectively suggest that AVT impacts chemosensory behavior during social interactions in green anoles, even in untreated social partners. More broadly, the mechanisms used by AVT to impact chemosensory behavior may be evolutionarily conserved. Our results are consistent with previous work linking AVP in mammals and AVT in fish to chemosensory-mediated interactions, such that AVT in reptiles deserves more research attention in the future. Furthermore, even in microsmatic lizards like Anolis, the impact of chemical communication on social dynamics should not be ignored. This study examined social dynamics between two live lizards and did not isolate the chemical signal. Thus, further work is necessary to determine whether similar changes in chemosensory displays occur when isolated chemical stimuli are presented to untreated lizards.

Tolerance to Urbanization is Widespread in Anoles

From Winchell et al. (2020): Anoles throughout the Caribbean differ in their tolerance to urbanization. Red colors = urban tolerant, blue colors = intermediate tolerance, green colors = urban intolerant.

Seven years ago I asked for the help of Anole Annals readers as I started to think about how different species of anoles throughout the Caribbean tolerate urbanization. This question, it turned out, was a lot more complex than I had originally anticipated! The idea was simple, find out which species are in urban areas and to what extent they use urban habitat elements, then determine if there is an evolutionary signal in urban tolerance and what traits are correlated with urban tolerance. Many hours of troubleshooting and brainstorming with my coauthors Klaus Schliep, Luke Mahler, and Liam Revell (and years later) and this study is finally out in the journal Evolution: Phylogenetic signal and evolutionary correlates of urban tolerance in a widespread neotropical lizard clade.

Anolis lineatopus, one of many urban tolerant anoles (photo K. Winchell)

Inventorying urban species

To figure out which anole species are tolerant of urbanization, my initial plan was to survey researchers and the literature to score each of the 100+ Caribbean species based on their presence in different types of urban habitats and their habitat use. Although I got a lot of great feedback from this original survey, it left a lot of gaps in the dataset. I needed to find a more objective way to assess urban tolerance.

With the help of Klaus Schliep and Luke Mahler, we decided to examine location records in museum collections (via GBIF) to determine which species had been observed (collected) in urban environments. Because we suspected museum records might be biased towards non-urban habitats, we also examined location records from the citizen science database iNaturalist, which we suspected might be biased in the opposite direction (i.e., people photograph things where they live). For each record, we looked at satellite imagery and scored the observation as urban or non-urban, then tallied the total number of observations and the total number of urban observations per species.

Even with these two data sources, we noticed gaps in our data for some species. So we included a third source, Henderson & Powell’s (2009) book on the Natural History of West Indian Amphibians and Reptiles. This fantastic reference (highly recommended!) gives detailed natural history information and summarizes key features of every anole (and other Caribbean herps) in the Caribbean. Of course, this is more subjective than the location-based data, so Luke and I came up with a scoring system that assigned a set number of urban tolerant or avoid “points” based on key descriptors. For example, if a species was described as being common around houses and often observed on buildings, it would get points for being tolerant of urbanization. In contrast, a species described as having a restricted range and intolerance of anthropogenic disturbance, it would get points for being intolerant.

Analyzing urban tolerance in a phylogenetic framework

We combined these disparate data sources into a logistic model with parameters we set based on the number of urban observations we would need to be certain of urban tolerance and how many total observations we would need to be certain of our species assessment. This resulted in a probability of being an urban avoider or urban tolerant for each species, which we used as our prior probabilities for these states in our phylogenetic model. We then reconstructed ancestral states and missing tip states for urban tolerance in 131 species of Caribbean anoles.

Of course, we don’t mean to say that we attempted to reconstruct the evolution of urban habitat use — anoles are far older than urbanization! Instead, we wanted to understand the evolution of the behavioral, physiological, ecological, and morphological traits traits that influence whether a species will exploit or avoid urban habitat when it arises. The threshold model is well-suited for this type of complex trait. The threshold model assumes that a discrete trait is determined by a combination of continuously valued characteristics. These characteristics may be measurable, unmeasurable, or even unknown. As a taxon accumulates specific trait changes, the species is pushed incrementally closer and closer to the discrete state change (in this case urban tolerance), and the more recently this discrete character state has flipped, the more likely a reversal to the previous state could occur. From this model we can extract a single continuously valued trait, the liability, that underlies the complex trait of urban tolerance.

Urban tolerance in Caribbean anoles, from Winchell et al. (2020).

Traits of urban species

So what did we find? To start, urban tolerance appears to be widespread in Caribbean anoles and has a strong phylogenetic signal. Because of that, we suggest that our approach may be used to predict urban tolerance of species that either have yet to encounter urbanization or for which we are lacking information. This application could be particularly useful for determining which species are likely to be intolerant of urbanization and thus should be prioritized in conservation efforts. At the other end of the urban tolerance scale, we caution that our approach should not be used to predict species that are robust to anthropogenic habitat loss, but rather that it might be useful to identify species that are promising for future urban ecology and evolution studies.

Finally, we used the liability score for each species to try to get a better understanding of what those traits underlying urban tolerance are exactly. Using PGLS we looked for correlations between the liability and a suite of ecological and phenotypic traits. We found that species that are more tolerant of urbanization had higher field body temperatures, fewer ventral scales, more rear lamellae, shorter hindlimbs, and experience warmer and drier climates within their native range. These traits may be key “pre-adaptations” enabling species to colonize urban habitats as they arise and to take advantage of anthropogenic niche space (i.e., on and around buildings). For example, urban habitats tend to be hotter and drier than nearby forest sites, so it makes sense that species with larger ventral scales, higher field body temperatures, and which experience hotter and drier temperatures in their non-urban range would be predisposed to tolerate urban habitats. Similarly, lamellae are important for clinging to smooth surfaces, which may be particularly beneficial in urban habitats dominated by smooth anthropogenic surfaces.

Lastly, we found, somewhat to our surprise, that no one ecomorph seems to be best suited for urban environments. Based on our experience, we had thought that trunk-ground anoles would be more likely to tolerate urbanization, but it turns out that there are a lot of trunk-ground anoles that are intolerant of urbanization and a lot of species from other ecomorphs that are tolerant (think A. equestris or A. distichus)!

Salmonella in Japan’s Green Anoles

When I hear or read Salmonella, I think of my mom explaining to my 7-year-old self why I shouldn’t eat raw chicken (to be clear, I never expressed interest in doing this, but lesson learned nonetheless). According to the U.S. Centers for Disease Control and Prevention, most instances of Salmonella bacteria making people sick do in fact result from transmission by food. But Salmonella infection can come from other sources, including direct contact with living animals, particularly reptiles (including birds which, in case you haven’t heard, are reptiles). So I was only a little surprised when I came across a recent paper in the Journal of Veterinary Medical Science, based in Japan, documenting the prevalence of Salmonella in the green anole, Anolis carolinensis, on Okinawa Island, Japan.

Of the 706 green anoles from Okinawa Island whose intestinal contents were analyzed for Salmonella presence between 2009 and 2014, only 2.1% tested positive. That number is low compared with published results for green anole populations in Florida (7.5%), Chichi Island in Japan (34.2% – this study was highlighted here on Anole Annals when it came out in 2013), and Guam (76.2%). I’m struck by how much these percentages vary. Green anoles have been in Florida for millions of years, whereas populations in the other locations have only been established for tens of years. The authors hypothesize that infection rate in recently introduced populations should correlate with how long the population has been established. Testing this hypothesis will require data from more populations.  It also appears that we know little about whether anoles are affected by carrying Salmonella, although a quick search did reveal this study involving the brown anole, Anolis sagrei.

All told, we have a lot to learn about anoles and Salmonella. In the meantime, please protect yourself from Salmonella infection by following basic food safety precautions: refrigerate foods adequately, wash fruits and vegetables and cook meat and eggs thoroughly, and clean potentially contaminated cookware and utensils with soap and water. Most importantly, WASH YOUR HANDS, although I assume that like me, you are already doing this approximately a hundred times per day (for those of you reading this in the future, I’m not a weirdo. We’re in the middle of a pandemic).

For those who may be interested, green anoles became established in and around Japan several decades ago and are considered an ecologically disruptive pest. If you want to read more, here are links to some old Anole Annals posts on various topics related to the region’s green anoles: trapping efforts, population age structure, range expansion. Enjoy!

Anolis cristatellus Journal Cover!

Hot off the press — the latest anole journal cover! In this issue of Nature Ecology & Evolution, Shane Campbell-Staton and I led a team of researchers to explore the effects of urban heat islands on anoles. We found that not only can urban Anolis cristatellus tolerate higher temperatures than their forest counterparts, but also identified genomic regions associated with divergent thermal tolerance. Check out a summary of this work at the urban evolution blog I co-edit, Life in the City: Anoles Adapt to Beat the Urban Heat.

In the Eye of the Beholder: How Do Anoles Respond to Human Clothing Color?

Water anole (Anolis aquaticus), Costa Rica

Have you ever wondered how your clothing color affects how many anoles you see and catch on a given day? When we go out herping, a lot of us favor some sort of clothing color scheme – whether it’s conscious or subconscious, scientific or superstitious. Since anoles have such excellent color vision, and since they’re so sensitive to the signaling colors of the individuals they interact with, this makes sense, right?

(a) Water anole dewlap; (b) Orange and blue shirts; and (c) green shirts worn in this study.

Bree Putman (Cal. State San Bernardino), Andrea Fondren (an undergraduate researcher), and I teamed up to determine if there was any truth behind the superstition. In an effort to understand how anthropogenic colors affect the behavior of lizards, we designed a study to test whether researcher shirt color would influence the sighting and capture rates of water anoles (Anolis aquaticus). Male water anoles have large orange dewlaps, which is their most conspicuous sexual signal. Using a modified version of the species confidence hypothesis, we predicted that water anoles would be least fearful of anthropogenic colors that most closely resembled the color of their own sexual signals (orange). To test this, a group of us spent the summer surveying water anole populations wearing three different shirt colors: orange, blue, and green. We carefully allocated shirt colors to research teams and study sites, planning it out in advance so that all shirt colors were worn by all researchers and used at all sites evenly in the study.

Our results, published in Biotropica, may make you rethink your own field shirt color choices. Both our sighting rates and our capture rates of water anoles were significantly higher when wearing orange shirts – matching the color of water anole dewlaps. Lizards likely have sensory biases for colors used in their species-specific displays, and we found that this translates into clear differences in behavioral responses to anthropogenic colors. On some level, I think many of us expected that the green shirts, which camouflaged us beautifully in the forest, would have been the most successful. Not so. Looking more broadly, Bree Putman’s previous study on western fence lizards (Sceloporus occidentalis) helps to solidify the idea that lizards are biased toward anthropogenic colors that they themselves “wear.” Western fence lizards have blue sexual signals and – corresponding nicely to our water anole results – these lizards are less fearful of researchers wearing blue clothing. Taken together, these findings remind us that placing a human perspective on animal perception can sometimes lead to flat out wrong conclusions.

As ecotourism is on the rise, it’s worthwhile to consider how the anthropogenic stimuli that ecotourists bring into a species’ native habitat can affect species behavior and survival. Reducing a species’ exposure to more frightening stimuli (such as unfamiliar colors) can reduce stress and disturbance. Something for the ecotourism community to consider as researchers continue to explore ways to minimize disturbance of natural populations, while promoting sustainable use of natural areas.

As for me, it looks like I’ll be buying quite a few orange shirts this year.

 

SICB 2020: Artificial Light Keeps Green Anoles Hungry!

There are so many great anole talks at SICB 2020, I’d be remiss if I didn’t take this opportunity to shed some light on some of our fantastic undergraduate researchers, who turned out in force to Austin this year! As I’m sure Dr. Kristin Winchell will tell you, anole lizards make awesome model organisms for studying the effects of city life and urbanization on wildlife.

Cities can be dangerous though. A lot of different urban environments will present wildlife that have not lived in cities with numerous pressures they might not have faced before, such as different surfaces and substrates on which to run, different temperatures, and even new predators. One of the relatively new pressures that goes along with city life is light at night, and artificial light to boot. If you’ve ever been too disturbed by light during the moonlight hours to sleep and rest, imagine how small lizards feel!

To address the effects of this pressure on green anoles (Anolis carolinensis), Michelle D’Alessandro, an undergraduate student at the University of Scranton working in the lab of Dr. Chris Howey, measured the effects of artificial light at night (I’m just going to call it ALAN) They exposed anoles to ALAN and described the effects of artificial light on metabolism in green anoles. Initially, they did not find any differences between metabolic rates when lizards were exposed to ALAN, however after a sufficient time period, anoles exposed to ALAN increased their metabolic rates during the evening, but not during the day! During this experiment, they also found that ALAN anoles were far hungrier and ate more often than lizards that weren’t exposed to light at night. The term ‘midnight snack’ definitely comes to mind here! Michelle suggests that much like when humans get exposed to changes in sleeping patterns, anoles undergo some energetic changes, causing them to eat more and having to burn more energy. Maybe next time think twice about keeping that porch light on during the waning hours of the evening- give the wildlife some much needed rest.

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