Don’t forget to submit your votes for the Anole Annals Photo Contest 2015! The poll will close THIS THURSDAY, December 3, so make sure you get your votes in before then. Anole Annals 2016 calendars with the winning 12 photos will be available for purchase soon after!
Anolis toldo. Photo by Luis Diaz.
Luis Diaz reported on Facebook the discovery of the lizard shown above. He reports: “Anolis toldo, adult female; third individual of the species known and first specimen in the National Museum of Natural History of Cuba. The discovery of this specimen was a result of the joint expedition by the National Museum of Natural History of Cuba and the American Museum of Natural History. It was found on October 19, 2015, at night, on a tree fern in a new location (outside the only known: the plateau of El Toldo ). This is one of the few photos of the species.” The photo was tagged aat Alejandro de Humboldt National Park.
It’s just come to AA‘s attention that the University of Texas School of Journalism posted an article on invasive anoles in Texas, featuring Yoel Stuart. Check out the article online, and the nifty, albeit chameleon-tainted, poster below.
I’m sure there’s a story behind this photo circulating on Facebook, but I don’t know what it is. Anyone care to speculate?
An online preview version of this paper was published Nov. 4 in the Biological Journal of the Linnean Society.
I began this project in late 2012 as a research assistant to Shane Campbell-Staton, now a Postdoctoral Fellow at the University of Illinois Urbana-Champaign. As part of his dissertation on Anolis carolinensis, Shane saw an opportunity for an interesting side project regarding its morphological variation. The lizard’s geographic range is massive – ranging from Florida to Texas in the east, and north to Tennessee – but surprisingly few studies had examined the way limb and body traits vary between populations, let alone over its broad distribution. Given evidence for Caribbean relatives adapting to variable environmental conditions even over short distances, we were curious whether the same would hold true for the green anole.
Using a set of samples Shane had collected from 14 locations around the southeast (Figure 1), I set out to answer a few questions about geographic variation in the green anole: which traits vary most in this species? How is this variation distributed, and does it correlate with environment? We were also interested in the degree to which this species conformed (or didn’t) to Bergmann’s and Allen’s rule, two eco-geographic principles well studied in reptiles.
Figure 1: Density and distribution of sampling in this study.
The process started, as always, with data collection – in this case, taking X-rays of over a hundred specimens, extracting a set of 26 morphological traits, and pairing them with environmental and genetic data for each site in our study. The resulting dataset was large and multidimensional, and required several iterations of analysis to find a clear and logical approach to test our hypothesis (as an undergraduate, this process of analysis and re-analysis taught me a valuable lesson in troubleshooting, data management, and experimental design).
Looking at our results, we did end up finding a high degree of morphological variation in this species, mostly driven by head width and length. These features marked out several highly distinct populations and generated some striking visual comparisons (Figure 2). Previous studies by Herrel, Lailvaux, Corbin, and McBrayer suggest that this kind of variation may be driven by the role of bite force and head shape in prey capture and combat, and future work on A. carolinensis should follow up on this possibility. We also recovered some morphological clustering among non-proximal populations, which opened the door for examination of possible convergence as a result of environmental similarity over the species’ range.
Figure 2: Head shape variation between an anole from Cedar Creek, OK (left) and one from Punta Gorda, FL (right).
We found that, in general, anoles in more seasonal and colder climates of the north tend to have to have relatively longer limbs and wider and shorter heads than those from less seasonal/warmer locations in the south. With regard to limbs, this pattern may be related to an observed “reversed” Allen’s rule – that appendage length would actually increase in colder climates as a way to more rapidly uptake heat. This explanation is similar to that of the “reversed” Bergmann’s rule previously proposed for some lizards, but for which our data were inconclusive.
In the end, I believe the patterns of variation and environmental correlation that we found in the study will help to establish A. carolinensis as a strong candidate for further studies of morphological variation over a large range, especially with the recent publication of the species’ genome. As an undergraduate, I felt lucky to make a contribution to the literature and to have the opportunity to see through a project from start to finish.
Are you planning to get recertified as an environmental expert? Then click on NREP Recertification Terms and Conditions to get all the information you need in one place.
Finally, please reach out to me with any questions or comments about the study! My code and data are archived on my github page.
I just got back from a short trip down to Eleuthera in The Bahamas where I was assisting Anthony Geneva (Harvard post-doc) in sampling lizards. Also along for the trip were Sofia Prado-Irwin (Harvard Ph.D. student) and Rich Glor (University of Kansas). We went with the main goal of sampling Anolis sagrei from four habitat types found commonly in the Bahamas as an extension of an ongoing project in the Losos lab (previous posts from: Rum Cay, Concepcion Island, Ragged Island, Bimini, Mangrove habitat, and Great Isaac Cay). Specifically, we were looking to sample Anolis sagrei in mangrove, secondary coppice forest, closed coppice forest, and beach scrub habitats. These habitats differ in the height of the canopy, density of the understory, and composition of plants.
We focused entirely on the southern half of the island near Rock Sound and Cape Eleuthera. We were successful in sampling two beach scrub habitats, two mature coppice forest, one secondary coppice forest, and one mangrove habitat. We were able to catch all four of the anole species found on Eleuthera: Anolis angusticeps, Anolis distichus, Anolis sagrei, and Anolis smaragdinus. We also encountered a number of other native herp species: the Bahamian boa (Chilobothrus striatus), Ameiva auberi, Eleutherodactylus rogersi, curly tailed lizards (Leiocephalus carinatus), and the Bahamian racer (Alsophis voodoo), as well as a couple of non-native species: Cuban tree frog (Osteopilus septentrionalis), and Hemidactylus mabouia.
In my own research I work with Anolis cristatellus, the Puerto Rican crested anole. I am always surprised when I catch A. sagrei by how much smaller they are than A. cristatellus, although very similar in appearance otherwise. On this trip, I was also surprised that the A. sagrei, as well as the A. angusticeps and the A. smaragdinus, appeared to be much smaller than those I had encountered on Bimini last spring.
We also found that the density of lizards was quite low compared to what we expected and what I had experienced in Bimini, both during the day and at night. In all four of the habitat types, we saw an abundance of hatchlings, juveniles, females, and small males, but relatively few full adult male A. sagrei. For A. angusticeps and A. smaragdinus, we encountered only a few individuals total during the week of sampling. This reminded me of an odd experience I had last fall in Puerto Rico with A. cristatellus. It was the same time of year and I had an extremely difficult time locating mature animals in sites where I had previously sampled large numbers during the spring and summer months. Instead, I observed a large number of very young animals and females. I’m curious if this is a coincidence or if perhaps there is a strong seasonal effect on either male behavior (i.e., reduced visibility outside of the mating season) or male abundance (i.e., reduced numbers because of mortality during the mating season). In other words, are the males still there, but hiding, or are they really lower in abundance in the late fall? Or maybe I was coincidentally unlucky on both trips… I am very curious to hear thoughts on this!
Anolis sagrei using coral ground habitat.
Finally, I want to end with a short natural history note on the habitat use of the A. sagrei in the mangrove habitat. In this habitat we observed A. sagrei using perches at drastically different heights: some were 6 feet up, others were on the ground. Interestingly, the ones on the ground did not appear to be in transit, but seemed to be using the pockmarked karst as perches, running into one of the many holes when approached. Has any one else observed this behavior before? It seems so different from the typical trunk-ground anole perch and behavior to me.
That’s all for now. Currently Anthony is sampling additional islands in the Bahamas along with Melissa Kemp (Harvard post-doc) and Colin Donihue (Yale Ph.D. candidate / Harvard visiting student). Best of luck to them, I can’t wait to hear how the rest of the trip went!
Steven De Decker and Tess Driessens’ winning photo from the 2012 contest.
Thank you to everyone who has sent in photos for our 2016 calendar contest, we’ve received some great submissions! For those who haven’t yet gotten around to it, you’ve still got one week – the deadline is Saturday, November 21. If you have any great anole photos, we would love to have them in the contest! And just to remind you, the first and second place winners will receive a free Anole Annals 2016 calendar, woo! So send in your pics, let’s make the 2016 calendar great!
To remind you, here are the rules: submit your photos (as many as you’d like) as email attachments to anoleannals@gmail.com. To make sure that your submissions arrive, please send an accompanying email without any attachments to confirm that we’ve received them. Photos must be at least 150 dpi and print to a size of 11 x 17 inches. If you are unsure how to resize your images, the simplest thing to do is to submit the raw image files produced by your digital camera (or if you must, a high quality scan of a printed image). If you elect to alter your own images, don’t forget that it’s always better to resize than to resample. Images with watermarks or other digital alterations that extend beyond color correction, sharpening and other basic editing will not be accepted. We are not going to deal with formal copyright law and ask only your permission to use your image for the calendar and related content on Anole Annals (more specifically, by submitting your photos, you are agreeing to allow us to use them in the calendar). We, in turn, agree that your images will never be used without attribution and that we will not profit financially from their use (nobody is going to make any money from the sale of these calendars because they’ll be available directly from the vendor).
Please provide a short description of the photo that includes: (1) the species name, (2) the location where the photo was taken, and (3) any other relevant information. Twelve winning photos will be selected by readers of Anole Annals from a set of 28 finalists chosen by the editors of Anole Annals. The grand prize winning and runner-up photos will be chosen by a panel of anole photography experts. Deadline for submission is November 21, 2015.
Good luck, and we look forward to seeing your submissions!
Sarah Hykin and Jim McGuire
In our recently published paper in PLoS One, we provided ‘proof-of-concept’ that it is possible to obtain genome-scale data from formalin-fixed specimens. This study was proposed by one of us (SMH) about four years ago while contemplating how she might be able to undertake a phylogeographic study of a rare lizard species for which there was little hope of resampling the entire range.
Of course, people have been contemplating the challenge of obtaining DNA sequence data from museum specimens for decades, often with limited success. The typical approach involved targeting mitochondrial genes, developing sets of nested primers amplifying short fragments (often only 50-100 bp in length), and then a brute-force amplification and sequencing in an effort to score a few hundred usable base pairs.
However, our discussion was informed by the recent development of short-read Next-Generation Sequencing on the Illumina platform, which produces genomic-scale data 50-100 bp at a time. Surely, we thought, if any method could efficiently pull DNA sequence data from formalin- damaged DNA, this was it. Our timing was impeccable because our campus had just obtained a major foundation grant to support, among other things, the development of risky technology that could enhance the utility of historical museum specimens. We obtained a small subaward and Sarah went to work studying the literature on historical DNA sequencing, and figuring out how to perform NGS. Illumina sequencing and bioinformatic processing have become pretty routine now, but this was a very challenging undertaking at the time, and Sarah had to pursue this while focusing her energies on her unrelated dissertation research.
The first decision that we had to make was which species and specimens to select for sequencing. This turned out to be a ‘no-brainer’ because the only squamate genome available was Anolis carolinensis and we needed a genome to which we could map reads. Being a conservative museum curator, Jim suggested using no-data or limited-data specimens so that when the project inevitably failed we would not have cut up particularly important specimens. In retrospect, this was a mistake. For example, we used a limited-data specimen of Anolis carolinensis that was in the database as having been obtained in 1985. Further investigation of this specimen would have shown that this date was dubious, and it now appears the specimen was actually obtained and prepared between late 1986 and 1988 (and accessioned in 1990). We also have reason to believe the specimen was fixed in buffered formalin for one-week prior to rinsing and immersion in ethanol, though this is not known for sure since the specimen does not have associated field notes. If we had this to do over again, we would make sure that we knew as much as possible about the source specimens rather than taking a ‘let’s limit the damage if this experiment fails’ approach to specimen selection.
It works (sometimes)!
As indicated in our paper, it is indeed possible to obtain genome-scale data from formalin-fixed specimens housed for decades in a museum collection. However, our method is far from fool-proof and we strongly suspect that idiosyncratic features of individual specimens will determine success or failure in many instances. The age of the specimen is likely to be one of the most important variables as suggested by our published study – sequencing of our 100-year old sample failed, whereas sequencing for our ~25 year old sample was successful. However, other parameters are likely to prove important. For example, others have shown via direct experiments that DNA is better protected by buffered (versus unbuffered) formalin. We also suspect that other features of the specimen’s preparation such as the time spent soaking in formalin prior to immersion in ethanol, the concentration of the formalin used, the quantity of formalin injected into the specimen, and the time that passed between the death of the specimen and its preparation could all make a difference. These conditions are rarely recorded at the time of preparation, which means that for the vast majority of specimens that might be targeted for NGS, the researcher cannot know ahead of time whether the specimen is likely to be a good versus poor candidate for sequencing.
Our paper received some attention on social media with some calling our study a “game changer” and others arguing that such a statement is overblown. From our perspective, this is semantics. Have we completely solved the issue of obtaining genomic sequence data from formalin-fixed samples? Certainly not. Have we identified in a controlled way, the precise conditions underpinning success or failure of NGS from formalin-fixed samples? Again, not by a long-shot.
However, we have shown some things that are likely to be important in moving this technology forward (which could be interpreted as changing the game). Most importantly, we have shown definitively that it is possible to obtain genomic data from old museum specimens. This had not been shown previously and we believe that this will encourage many more people to give it a try than would be the case if our paper had appeared in the Journal of Negative Results. Further, we were able to shed some light on methodological issues that are actually quite important. First, we obtained a sufficient quantity and quality of DNA for sequencing from liver tissue and not from either leg muscle or, most importantly, bone. Many of you will be aware of a terrific study published by Maureen Kearney and Bryan Stuart in 2004, in which they provided a phylogeny for amphisbaenians that was based in large part on sequences obtained from old museum specimens. In their groundbreaking study, they obtained mitochondrial and nuclear sequence data using laborious traditional Sanger sequencing of short DNA fragments, along with non-traditional extraction of DNA from bone tissues using methods developed for human forensic DNA analysis. Their successful extractions required sampling bone from pickled specimens, which can be quite destructive. In contrast, pulling liver from a museum specimen is minimally invasive – especially when you consider that most newly collected specimens will have had their livers removed prior to preparation. Thus, our finding that liver is an optimal DNA source for NGS is important.
Further, second, we found that a modified phenol-chloroform extraction protocol outperformed Qiagen extraction for NGS purposes. Indeed, we now suspect that our failed attempt to perform NGS on our older sample could very well be the result of our effort to systematically compare extraction protocols. For both of our Anolis specimens, we subsampled the entire liver, which was divided into a small piece and a much larger piece. For the younger sample, the larger piece was extracted using phenol-chloroform, whereas for the older sample, the larger chunk was extracted using Qiagen. Importantly, from that older sample,we obtained more DNA from a sample ~20 times smaller in mass using phenol-chloroform versus Qiagen extraction. If we had dedicated the larger subsample from the 100-year old specimen to phenol-chloroform, we believe this might have resulted in successful NGS.
Figure: Sample placement in the phylogeny. As expected, our sequencing effort generated low-coverage (~0.5X) of the Anolis carolinensis genome. However, we did obtain ~60X coverage of the mitochondrial genome, providing a means of evaluating the quality of our sequence data after processing. We aligned the ND2 sequence from our sample with GenBank sequences representing A. carolinensis from Louisiana, the Anolis carolinensis complete genome, a variety of additional Anolis species, and a more distant outgroup. The phylogram shown here suggests that our mitochondrial sequence data obtained from a formalin-fixed specimen are reliable. If sequencing errors were evident, we would minimally expect the branch representing our formalin-fixed specimen to be relatively long compared with other Louisiana A. carolinensis, or perhaps even misplaced on the tree.
Where to from here?
One critique that we received in review was that we had failed to perform rigorous controlled experiments testing the various conditions that could impact success with NGS from formalin-fixed samples. Though we would have loved to perform such experiments ourselves, even limited NGS sequencing is still sufficiently expensive (thousands of dollars, rather than hundreds) that we were not in a position to pursue this. However, we would love to see someone – perhaps reviewer number 2 – grab the bull by the horns and perform this experiment! Such a follow-up study, should it identify via controlled experimental procedures the key parameters for successful NGS of formalin-fixed samples, would come closer to meeting the criteria of being a ‘game-changer.’
Over the past few years, two European research programs developed an interest in the ancient fauna and environment of the Guadeloupe islands. The prospection for cave deposits led to the discovery of numerous accumulations of fossil remains documenting the Holocene and Late Pleistocene faunas of the archipelago, especially on the island of Marie-Galante, where three major deposits were discovered.
Blanchard Cave is one of these deposits. This cave contains the oldest fossil-bearing sedimentary layers of the island dated around 40,000 years before present and is an excellent complement to the two others cave documenting the Late Pleistocene fauna of Marie-Galante (Cadet 2 and Cadet 3).
After a test excavation in 2008 that revealed the potential of the site in term of fossil fauna, Blanchard cave was investigated between 2013 and 2014 in the framework of a European research program interested in the past environment and fauna of the Guadeloupe islands, the BIVAAG project. The three excavation campaigns conducted during this period allowed the precise documentation of the sedimentary filling of the cavities and the recovering of thousands of skeletal remains mainly attributed to frogs, lizards, snakes and bats.
The excavation work in the cave (Picture: A. Lenoble)
Welcome gifts from the bats… (Picture: C. Bochaton)
But collecting the fossils remains was not that easy and although the perspective of working in the Caribbean a few hundred meters from the sea could seem very attractive, the working conditions in the cave were far from pleasant. Mainly because the cave was inhabited from the ground to the roof by numerous cockroaches, rats, gnats and bats. Bats were extremely noisy, and proved to be extremely rude hosts. Another difficulty was the potential occurrence of histoplasmosis in the cave that led to the necessity of wearing a respirator during the work. Such masks make breathing difficult during the work and combined with the heat, humidity and other disagreements previously mentioned strongly impact your initial enthusiasm.
Once you overlook these difficulties, the sediment was extracted from the site and then washed and sieved in order to retrieve the small bones contained in it (the bones are usually smaller than 5 mm). The remains were then recovered and sorted, partly in the field (unfortunately this activity often kept the paleontologists outside of the cave and away from the bats), before being studied.
Washing and sieving of the sediments (Picture: M. E. Kemp)
Recovering of the fossil bones (Picture: M. E. Kemp)
The results of the study of the squamates remains collected in the cave can be found in a very recently published paper. To summarize the main findings, we found evidence of the past occurrence of at least ten species of snakes and lizards: four snakes: Antillotyphlops sp., Boa sp., Alsophis cf. antillensis and an undetermined colubroid; and six lizards: Anolis ferreus, Iguana sp., Leiocephalus sp, Thecadactylus sp., cf. Capitellum mariagalantae and Ameiva sp.. The stratigraphic distribution of these taxa in the site combined with previously existing data show that only two extinctions (Boa sp. and Colubroid ind.) are dated from the Pleistocene/Holocene transition and thus predate the arrival of humans on the islands around 5000 years ago. Then during the pre-Columbian times two new taxa appear in the deposits, Iguana and Thecadactylus. On the other hand, a massive faunal turnover began after the European colonization of the island. Indeed, at least six squamate genera (Leiocephalus, Capitellum, Ameiva, Antillotyphlops, Alsophis and Erythrolamprus), including all the snake genera, were extirpated between 1492 and today. Thus, 55% of the squamate genera present during pre-Columbian times went extinct over the past few centuries.
These results are further evidence of the current sixth mass extinction crisis and of the strong impact of humans on this insular fauna. However, Marie-Galante Island remains an isolated case because the past fauna of most of the Lesser Antillean islands remains poorly known and in most cases totally unknown despite the critical importance that such data may have in many fields to test inferences built on modern data.
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