It has been widely published that Anolis pogus is only found in high elevation on the island of St Martin. While it is true, it is very common and in high densities at these higher elevations and more mesic environments, however I observed this species at lower elevations and even only meters from the beach. I came across this species several times (by accident) while making my way around the island, even in downtown Phillipsburg. Mongoose certainly take their toll on this ground, bush, and trunk “generalist” and there were many areas on the island where neither A. pogus nor A. gingivinus are easily observed. I do not agree with the assumption that this species is excluded by competition by the larger species as both species were observed in great numbers in these areas where both are present. This species certainly deserves another look at its ecology.
Category: Notes from the Field Page 11 of 22
Juan Salvador Mendoza
Fundación Kamajorú para la conservación y educación ambiental Barranquilla, Colombia.
Anoles (genus Anolis sensu old taxonomy) are one of the most diverse neo-tropical vertebrate groups with more than 200 species. In continental Colombia more than 60 anole species have been registered, including 30 which are endemic (Sanchez et al. 1995). Three more endemic species are known from the insular portion of San Andres and Providencia in the Atlantic Ocean and Malpelo in the Pacific (Sanchez et al. 1995). One of this insular species is A. concolor (Cope, 1836) a relatively medium-sized anole (60-80 mm SVL) that inhabits mangroves and dry forests in the islands of San Andres and Providencia; on the latter island, this species is sympatric with a A. pinchoti which is endemic only to the island of Providencia. In the Pacific, the representative species is A. agassizi from Malpelo Island.
Anolis concolor is a very agile lizard that may use the ground, tree trunks and branches to forage and display courtship and territorial behavior. I observed and photographed several individuals in the “Jardin Botanico, Universidad Nacional de Colombia;” this garden holds more than two hectares of the natural vegetation of the island, tropical dry forest. This lizard can be found in the borders of roads on top of secondary vegetation and can be also found in conserved remnants of mangroves and dry forest. In San Andres this species shares its habitat with a gecko species (Aristelliger georgensis) that may be also found even during the day time in the tree trunks. This is the only anole species in San Andres Island and can be very abundant; I counted 35 individuals in a 1 km forest trail.
Photographs from Jaime Palacio Sierra. We are currently reviewing reptiles from our home department and have doubts on two specimens captured by Jaime. can anyone help us confirm their taxonomic identities?
For many of us, the academic summer has finished or is ending imminently. In Boston, the temperature is falling, and most in the Boston area woke up to temperatures in the low 50s this morning. At this point, I thought the timing would be good to revisit (with some nostalgia) the manner in which I started the summer – with a three week field trip to Puerto Rico.
In June I was in Puerto Rico primarily to help my first Ph.D. student, Kristin, start her thesis project on urban ecology and adaptation in anoles. The focal species of Kristin’s research is the ubiquitous Anolis cristatellus, which, as anyone who has visited Puerto Rico will know, is equally common (if not more abundant) in heavily urbanized habitats as it is in natural forests. One species that is not found in urban areas, and, in fact, is fairly difficult to find in most habitats, is the Puerto Rican crown giant anole, Anolis cuvieri. We were lucky enough to see a few of these anyway, including one that I happen upon entirely by accident on the 60 acre finca where we stayed in a rental cottage for a little more than a week.
At night I was searching for invasive boa constrictors which are known from this part of the island, so as dusk approached I thought I’d try and take some photos of the sunset over the island’s western coast. Always on the lookout for A. cuvieri, I nonetheless somehow missed this individual in this pre-dusk shot (highlighted here by the red arrow). A perfect “find the anole” photo, but one in which I had initially “missed the anole” in spite of seeing it in person!
When I did spot him, he was far too high to capture with my meager 14 foot noose pole, so we just kept an eye on him. As the sun continued to set he did something interesting – he started to descend the trunk.
On the 14th of July, 2002, I wanted to test the possibility of using a modified funnel-trap to collect Anolis sagrei. The first lizard to respond to my trap, though, was an adult male of the agamid, Japalura swinhonis, that was attracted by the movements of the crickets in the trap. The J. swinhonis attempted to prey on the prey items for about 30 seconds. When an adult male A. sagrei approached, the J. swinhonis moved up the trunk of the betelnut palm onto which the trap was secured. No further observations were made after the A. sagrei lost interest after about one minute and moved off.
This was to date the only instance I observed in which a J. swinhonis gave way to an A. sagrei, and I am quite convinced that the J. swinhonis actually just lost interest in the possible prey in the trap, and as it moved away the A. sagrei thought he could try his luck. And this is my point concerning A. sagrei in Taiwan.
In my study area in Santzepu, Chiayi County, southwestern Taiwan, J. swinhonis males (mean ± SD = 70.5 ± 8.4 mm) and females (mean ± SD = 58.2 ± 13.9 mm) are substantially larger than A. sagrei (males; mean ± SD = 46.2 ± 9.1 mm; females; mean ± SD = 38.2 ± 5.5 mm). In most other aspects, both species are quite similar; both are diurnal trunk-ground ambush foragers and are very territorial. In a paper I am currently preparing, I compared the diet of these species and found that A. sagrei has a much wider dietary niche breadth than J. swinhonis, and that in areas where J. swinhonis and A. sagrei are sympatric, there is a substantial dietary niche overlap, and competition for prey is very likely.
Although both species are human commensals, J. swinhonis is more shade tolerant, while A. sagrei reaches higher densities in open disturbed habitats. So, my view of A. sagrei in Taiwan is that this species is here to stay, and we have to accept that it is becoming part of local ecosystems.
With only two weeks left in El Yunque, Puerto Rico, the two projects that Travis Ingram and I are doing will soon come to a close. Travis has already written about one project, the enclosure experiment. The second is a diet survey of six species (Anolis evermanni, A. stratulus, A. cristatellus, A. gundlachi, A. pulchellus, and A. krugi) that are sympatric in the area around where we are staying. The goal is to quantify diet overlap between these species. To obtain the stomach contents, we use a nonlethal method known as gastric lavage. I chose this method unsure of how it would turn out because, before this trip, Travis and I had had very little practice performing gastric lavage. My hope was that we could take this technique that we had read about and practiced a few times in the lab and become good enough at it to do it potentially hundreds of times in the field.
I’m presently in the field in Puerto Rico working with my (first, brave) doctoral student, Kristin Winchell, along with two undergraduate assistants (Zack & Sofia). Although Kristin has been with me to Puerto Rico once previously (in January), this expedition is the first trip of Kristin’s doctoral research, which will focus on urban ecology and adaptation in anoles. In this trip she is collecting phenotypic, habitat use, and activity temperature (ambient and internal) data for Anolis cristatellus in urban and forested sites in the three major municipalities of Puerto Rico: San Juan, Mayagüez, and Ponce. For example, our forested field locality in San Juan is the diminutive but verdant state forest Bosque San Patricio. San Patricio is a small forest of no more than about 70 acres nestled well within the sprawling San Juan metropolitan area. In spite of this status as an island of green amidst concrete, at least three species of anoles can be found there (including Anolis evermanni, pictured above), along with Ameiva, the Puerto Rican racer (I found two), and (according to accounts) the endangered Puerto Rican boa.
My role in this expedition is mostly in a supporting capacity. In addition, I am visiting colleagues, scouting sites, looking for boas, and preparing for the tropical biology field course that I will be co-instructing with herpetologist Alberto Puente here in January. In fact, while Kristin & her crew finish up in San Juan, I have proceeded ahead to Mayagüez with my wife, Emily, and our two year old daughter, Cecilia, both of whom joined us on the island a couple of days ago. This leads me to the the second part of my post title. No doubt Zack & Sofia, who have never worked on anoles before, suffered their first anole bites (and perhaps inumerable additional bites) on this trip. It’s part of the job! However, it was to my considerable surprise when Cecilia suffered her first Anolis bite as well. Before you call Child & Family Services, this was a total accident, not some cruel rite of passage.
What happened was as follows.
Krysko et al. report in the March 2012 issue of Herpetological Review on a new element of Florida’s food-web: one species of diurnal, arboreal, and non-indigenous lizard eating another species of diurnal, arboreal, and non-indigenous lizard. Anole lovers will not be pleased to learn that this event involved a Madagascan day gecko (Phelsuma grandis) eating a bark anole (A. distichus) on Ramrod Key in Florida. Krysko et al. note that this it he first report of a non-indigenous gecko consuming a non-indigenous anole. This interaction ups the ante on the gecko/anole dynamics in Florida and Hawaii that have been reported previously here on Anole Annals and elsewhere.
Editor’s Update: Here’s a non-cell phone version of the same, courtesy of Ken Krysko.
Well, the 2012 Abaco Expedition is over. For almost a year, we’ve been wondering what effect Hurricane Irene had on our lizard populations. Now we know.
A little background: initially, we feared the worst. Hurricanes had destroyed several previous experiments. The culprit was not the high winds, but the high water, which put our tiny, lowlying islands underwater for up to six hours, drowning or sweeping away all lizardkind. But then word trickled in that this time, maybe things weren’t so bad. The storm had come at the best time possible–absolute low tide–and from a direction that minimized the amount of storm surge that could build up in the protected areas where most of our islands occurred. Maybe things weren’t so bad.
So, back we came to Abaco several weeks ago to find out. We have two experiments going on. The primary study focuses on the effect of anole-eating curly-tailed lizards. What effects do the curlies have on the population size and behavior of the brown anole, A. sagrei? And, in turn, how do these changes trickle down to lower levels of the food web? These studies occur on islands up to 300 square meters in area (that’s less than 1/2 the area enclosed by the bases in a baseball infield).
The result of the hurricane: mixed. Several islands lie in a very exposed position, and their populations were decimated, to less than 10 individuals on both. In case there’s any doubt about the culprit for this crash, the dried seaweed strung high in the bushes is clear evidence of the highwater mark of the storm. On most other islands, those not so exposed to the storm’s onslaught, A. sagrei populations are higher, even those with the curly-tailed lizards. It seems that it was a overall a good year for lizards, except for those islands exposed to the hurricane’s wrath.
Our founder effect experiment occurred on seven tiny–and very low-lying–islands. These islands were wiped lizard-free by the last hurricanes to pass through the region, Frances and Jeanne in 2004. We re-inoculated the islands with brown anoles in 2005, placing one male and one female on each island. As I reported previously, the genetic and phenotypic mark of these founder events were still evident four years later.
Given past history and the diminutive size of the islands, we were not optimistic. But here, too, the results were mixed. Three islands were almost exterminated: down to two adults (and, encouragingly, one recent hatchling) on one island, and 4-5 on two others. But as with the bigger islands, the results here, too, were mixed, as one population increased from 25 to 49 and several others held steady with large populations.
These results lead to an interesting situation. All populations were established by a founding event, but now only several of them have experienced a subsequent population bottleneck. How will that effect patterns of divergence among the island populations? And let’s not forget that those who have postulated the importance of founder effects for species divergence and even speciation suggested that it was serial founder events/bottlenecks that were particularly likely to lead to important changes. Who knows? Maybe next year we’ll return to find a couple of newly evolved species.
Ten days into my first field work experience, and I’m loving it. I am in Puerto Rico with Travis Ingram, and we are studying the interactions between Anolis gundlachi and Anolis cristatellus, which requires us to catch lots of anoles. I had never noosed anoles before, but I figured I could get the hang of it pretty quickly. Little did I know the challenges and adventures that were in store…