With intermittent funding (much of it out of my own pocket) and the help of a small army of colleagues and assistants from 1962 through 2008, I have gathered and analyzed extensive data on ecological relationships of lizard faunas of some 32 desert study sites, which lie at roughly similar latitudes on three continents: western North America, southern Africa, and Western Australia. A series of 10-12 representative flatland desert areas were selected for investigation on each continent. Study sites are homogeneous and continuous, extensive enough to facilitate sampling, and generally well suited for ecological analyses. Study areas vary in size from about half a square kilometer to several square kilometers. Study sites exhibit a variety of habitat types, ranging from simple vegetation to more complex structure. Five lizard families are represented in the Kalahari, and seven occur in North Anerica and Australia. Australian deserts have 21 lizard genera and 69 species, African deserts 14 genera and 22 species, and North American deserts 12 genera and 14 species. Together, these three continental desert-lizard systems support 16 of the currently recognized 37 different lizard families.
In 1986, I published a synthesis "Ecology and Natural History of Desert Lizards" (Princeton Univ. Press) with extensive summaries of data collected from 1962-1979. Since then, I have been fortunate to collect many more data on Australian lizards (12,634 new specimens) from 3 study sites. Many of these species are uncommon but I have managed to acquire adequate sample sizes for most. Understanding the ecology of rare species constitutes a major challenge for ecologists (Main 1982; Thompson et al. 2003; Pianka 2014). Some North American study sites have succumbed to urbanization, making my 1960's records of substantial historical and scientific interest. Essentially they represent a recent fossil record of what was there before humans usurped the habitat. Humans are bent on erasing the very signature of the evolution of life on this Earth making it urgent that we read the vanishing book before it is destroyed -- of course, we must also do our utmost to save it for future generations to study.
I often receive requests for raw data, but I have seldom been able to provide them. Originally, these data were collected primarily to elucidate niche segregation and diversity, but many more innovative analyses should be undertaken. For example, we offered an informative analysis of how frequently lizards had empty stomachs (Huey et al. 2001). Another analysis used dietary niche breadths to test food web theory (Winemiller et al. 2001). Still another study demonstrated that deep history has had a profound impact on present day diets (Vitt and Pianka 2005).
When I die, I want my huge unique data set to be available to the next generation of frustrated lizard ecologists (Pianka 2016). This website constitutes my attempt to pass on these data. My goal is to preserve for posterity as much information as possible for each individual lizard (about 28,000 of them!). Accordingly, I have organized these data into a mySQL relational database format. Data have been collated, organized and cross checked for accuracy. These data are in a wide variety of formats: of those that have been digitized, some are still simple text files, others are in MS Word or Excel format, while others are Cricket Graph and Statview files. A substantial amount of data on microhabitats for about 14,000 lizards have not yet been digitized but were analyzed and summarized by hand -- these should be entered into digital computer files. Lizards collected are summarized in the following two tables.
Data acquired up until 1979 (first table) were summarized with totals and means as appendices in Pianka (1986), but will now be made available in much greater detail for each individual lizard. Ecology has changed dramatically in the past couple decades, with much greater emphasis now being placed on conservation biology, rare species, and phylogenetically corrected analyses of evolution using modern comparative methods. Whereas data collected before 1979 were intended for studying niche partitioning and community structure, data collected since 1989 using pit traps (second table, above) were designed to study rare species, fire succession, long-term change, habitat and microhabitat requirements, adaptive radiations, and phylogenetic constraints. Thus, these new data complement the older data and are qualitatively different than those collected earlier. These new data have not yet been published and will be organized and mined for new insights before they are put into the public domain and made freely available and easily accessible to all.
The text below explains some of what is available on this website. Essentially, it contains mySQL tables with everything I know about each individual lizard, including locality and date of collection, time of activity, body and air temperature, snout-vent length (SVL), tail length plus tail condition, fresh body weight, other head size and leg length morphometric variables, microhabitat location or pit trap number, sex, reproductive condition, stomach contents, and parasite load. Auxillary supporting data on climate, snakes, birds, mammals, GPS coordinates of pit trap locations, high-resolution aerial photographs with precise pit trap locations plotted on them are also be included. These data should be useful to a wide variety of biologists, including conservation biologists, physiologists, and zoo biologists.
In western North America, deserts form a continuous and enclosed series, uninterrupted by major physical barriers, over a latitudinal range of 1500 km, from southern Idaho and Oregon through Sonora and Baja California (Mexico). Three distinct regions are generally recognized within this region: a northern Great Basin Desert, a southern Sonoran Desert, and an intermediate area in southern California and southern Nevada known as the Mojave Desert. The Great Basin desert is structurally simple, with predominantly a single perennial plant life form (low "microphyllous semi-shrubs" including Atriplex confertifolia and Artemesia tridentata). Vertical heterogeneity is minimal. Because these small shrubs in northern deserts are usually very densely packed and uniformly spaced, horizontal spatial heterogeneity is also low.
transect in the three North American deserts.
The Great Basin Desert is a very repetitive and rather monotonous landscape. In contrast, the Sonoran is an arboreal desert with several species of trees and, in addition to small semi-shrubs such as Atriplex, many large woody shrubs (the most conspicuous of which is creosote bush, Larrea divaricata). As a result, the vertical component of spatial heterogeneity is considerably greater than it is in the Great Basin Desert. The Mojave Desert is also dominated by Larrea, but is virtually treeless, except for a few Yucca brevifolia "trees." The diversity of different plant life forms reaches an apex in the Sonoran Desert. The addition of perennial plant life forms in southern U.S. deserts is often accompanied by fewer plant individuals per unit area and much greater horizontal heterogeneity in their distribution in space. Rivulets and dry washes along bajadas are lined with different species of plants than intervening areas.
North American lizard species with family and 4-letter species codes.
Saurofaunas in the flatland deserts of western North America consist of a basic "core" set of four ubiquitous species (the whiptail Aspidoscelis (formerly Cnemidophorus) tigris, the side-blotched lizard Uta stansburiana, the leopard lizard Gambelia wislizeni, and the desert horned lizard Phrynosoma platyrhinos) to which various combinations of other species are added, with the total number of species increasing from 4 or 5 in the north to 9-10 in the south (Pianka 1967). Three Great Basin areas were studied (areas G, I, and L), four sites were selected in the Mojave Desert (areas M, P, S, and V), along with a further three Sonoran sites (areas C, T, and W). Incidental observations were also made at two Sonoran desert sites in northern Mexico (areas A and B). North American fieldwork was undertaken primarily during 1962 through 1964, but a few observations were also made in Mexico during the summers of 1966 and 1969. Censuses of North American lizards collected on each of these study sites were compiled, as follows.
In the southern Kalahari, major physiognomic and vegetational changes take place along an east-west precipitation gradient: the more mesic eastern region consists of flat sandplains with a savanna-like vegetation, whereas stabilized sandridges characterize the drier western "sandveld" or "duneveld." These red sandridges, which average about 10 m in height, generally parallel the direction of prevailing winds; sandridges are frequently as long as a kilometer or even more and support a characteristic grassy dune vegetation. Interdunal flats or "streets" average about 250 m in width, but occasionally may be much more extensive, sometimes as wide as several km, with a vegetation consisting of various grasses, laced with large bushes and scattered small trees. Two common woody shrubs of Kalahari flats are Rhigozum trichotomum and Grewia flava, both of which are vaguely reminiscent of the North American Larrea divaricata. Detailed descriptions of Kalahari vegetation, with photographs, are provided by Leistner (1967). Ten study areas were selected representing the full range of habitats and conditions prevailing across the southern part of the Kalahari (Pianka 1971).
is the "sandveld" of the Kalahari as delineated by Leistner (1967).
Typical Kalahari sandveld desert. Sandridge in background.
Four eastern sites are all on fairly flat terrain, but vary in their vegetation: area G is a chenopod shrub desert with Atriplex semibaccata, area R is a nearly pure Rhigozum flat, whereas area D supports a more diverse mixture of small to large shrubs, including Rhigozum, Grewia, and the thorny bush Acacia mellifera. Area T, in southern Botswana, is a mixed open forest and savanna site with a substantial number of trees (this site was still quite wild at the time of our initial study in 1969-70 with Spotted Hyaena, but with the advent of bore water, it has since become cattle-grazing country); the savanna and forest sections of the T-area can be treated separately as sub-areas. Most Kalahari observations were made during the 1969-70 Austral season, supplemented on a second trip in 1975-76. Most Kalahari specimens are lodged in the Los Angeles County Museum of Natural History but the 1975-76 specimens are lodged in the Museum of Vertebrate Zoology at the University of California at Berkeley. From 11 to 18 species of lizards in five families were found on Kalahari sites. Censuses of Kalahari lizards collected on each of these study sites were compiled.
Kalahari lizard species with family and 4-letter species codes.
Red Sands study area. Sandplain with spinifex grass tussocks in foreground.
"Red Sands" (area R) and area E are sandridge sites with marble gum trees (Eucalyptus gongylocarpa), a few desert bloodwood trees (Eucalyptus sp.), extensive spinifex (Triodia), and a variety of sandridge perennials (Acacia, Grevillea, and Hakea). On area D, a few scattered smaller sandridges and sand dunes support a lower and more open vegetation with fewer trees. Sandplain habitats also occur on these three study sites between sandridges. Two other areas, G and L, consist solely of such flat or gently rolling sandplains, with large marble gum eucalypt trees, spinifex and some scattered bushes. Areas B and N are "pure" spinifex flats (treeless grass desert), whereas area Y is a relatively pure (nearly treeless) shrub desert site in a dry lakebed. The last site was chosen because the structure of its vegetation was comparable to that of North American Great Basin Desert areas as well as that of Kalahari area G. Comparisons of numbers of lizard species present on these structurally similar chenopod shrub sites from 3 continental-desert lizard systems reveals 4-6 species in North America, 13 species in southern Africa, and 18 species in Australia.
Species codes and family identities for Australian lizards are here (Australian species codes).
I continued to monitor the Australian saurofaunas at the L-area and Redsands during 1989-1991 when I set up extensive pit trap lines. In 1992-94, dual funding from NSF and NASA allowed me to undertake a detailed satellite imagery remote sensing study of wildfires as agents of disturbance promoting habitat diversity in the Great Victoria desert of Western Australia (Haydon et al. 2000a, 2000b). An Australian field assistant ran pit trap samples for 3 months during the Austral Spring of 1992. A new study site, the B-area (Lat. 28° 13' 26.2"S, Long. 123° 35' 30.4"E), with pit trap lines was set up in 1992 and monitored before a controlled burn -- it was burned in October 1995 and monitored for 13 years following the fire during 1995, 1998, 2003 and 2008 to assess changes in community structure. B-area aerial photo showing locations of pit traps. Fire is increasingly recognized as a major contributor to species density and ecology, but what is the length of the recovery phase for desert lizard communities? My long-term census data provide insights into how individual species respond (species composition, relative abundance, dietary flexibility, and reproductive tactics). A total of 2846 individual lizards representing some 46 species were collected at the B-area from 1992 through 2008 (B-area Censuses). Stomach contents of these lizards reflect how arthropod prey resources changed during the fire succession cycle (Pianka and Goodyear 2012).
To gather data on ecological relationships of these lizard faunas, my assistants and I walked transects of many thousands of kilometers through study sites observing lizards. Between 1962 and 1979 we spent five full years in the field and nearly twelve man-years collecting data on lizards (sites were visited repeatedly over essentially the full seasonal period of lizard activity). Microhabitat and time of activity were recorded for most lizards encountered active above ground.
Early on (1962-68, 1970, 1978-79), lizards were hunted and captured during their normal daily course of activity, providing data on time of activity, microhabitat, ambient air temperature, and active body temperature. These data suffered, however, from collector bias and did not provide reliable estimates of relative abundance.
I changed my research protocol in 1989, since then most lizards have been pit trapped. Although trappability varies from species to species, this technique provides a standardized collecting method that allows relative abundances to be compared across space and time. It also allows informative estimates of point diversity, which can be used to infer habitat requirements.
The East pit trap line at Redsands, showing locations of pits. A sandridge
runs diagonally accross the scene. Large green areas are Marble gum trees.
Thousands of lizards and dozens of species have been collected from these
pits over the past two decades. I have similar data for 3 other pit trap lines
During two decades from 1989 through 2008, I made six expeditions down under (in 1989-91, 1992, 1995-96, 1998, 2003, and 2008) concentrating my efforts on several Australian study sites and began extensive pit trapping (over 62,000 trap days, and 12,634 specimens) in the Great Victoria Desert. Pit traps were located precisely on high-resolution aerial photos (part of one shown above) of study areas for a GIS analysis of habitat and microhabitat requirements. A census was taken in 1992 on a long unburned site to obtain pre-burn data, which was burned in 1995, with subsequent post-burn censuses in 1995, 1998, 2003, and 2008. Pit locations have also been plotted on a high resolution aerial photo of this site shown below.
Stomach contents of these lizards were exploited to evaluate how arthropod prey resources change during the course of the fire succession cycle. Snakes, birds, and mammals observed on study areas were recorded, and, in some cases, collected. Whenever possible, lizards were collected so that their stomach contents and reproductive condition could be assessed later in my laboratory. Resulting collections of some 3,974 North American specimens, 5,378 Kalahari animals, plus 20,599 Australian ones, representing nearly 100 species in nine extant families of lizards, are lodged in the Los Angeles County Museum of Natural History, the Museum of Vertebrate Zoology of the University of California at Berkeley, the Western Australian Museum, and soon, I hope, the Texas Memorial Museum.
In all three continental desert-lizard systems, the same 15 basic microhabitats were recognized: subterranean (for unknown, presumably largely historical, reasons, no subterranean lizards exist in North American deserts), open sun, open shade, grass sun, grass shade, bush sun, bush shade, tree sun, tree shade, other sun, other shade, low sun (within 30 cm. above ground), low shade, high sun and high shade (over 30 cm. above ground). For some purposes, finer microhabitat resource categories were used. Lizards at an interface between two or more microhabitats were assigned fractional representation in each. Only undisturbed lizards were used in these analyses. Considerable fidelity in microhabitat utilization is evident. Many species separate out using just these 15 very crude microhabitat categories: for example, some species frequent open spaces between plants to the virtual exclusion of other microhabitats, whereas other species stay much closer to cover. Microhabitat data summaries can be found here (Link).
Google Map showing Study Areas
For analyses of stomach contents, the same 20 basic prey categories were distinguished on all continents: centipedes, spiders, scorpions, solpugids, ants, wasps, locustids, blattids, mantids and phasmids, neuroptera, coloptera, isoptera, heimiptera and homoptera, diptera, lepidoptera, insect eggs, insect larvae, miscellaneous unidentified insects, vertebrates (including shed skin and reptile eggs), and plant material (both floral and vegetative). Prey items were counted and their volumes estimated. As is true of microhabitat utilization, considerable consistency in diets are evident among species. For example, some species eat virtually nothing but termites, whereas others never touch them. Moreover, diets of many species change little in space or time. For some purposes, much finer prey categories could be used. Termites were identified to species and caste for Kalahari lizards. Similarly, I was fortunate to get a competent entomologist to identify prey to the finest possible categories for the 1978-79 Australian data set resulting in over 200 prey categories.
A major virtue of these data is that identical methods and resource categories were used by the same investigator for each of three continental desert-lizard systems, enabling meaningful intercontinental comparisons. This unique body of data has thus allowed detailed analyses of resource utilization patterns and community structure in these historically independent lizard faunas (Pianka 1974, 1975, 1986). Moreover, both dietary and microhabitat niche breadths and overlaps can be estimated as well as species diversities and the spectra of resources actually exploited by entire lizard faunas varying widely in number of species. Another dimension that can often be profitably interpreted is variation in species utilization patterns (niche shifts) through time and between areas. Still another analysis that should be performed is to look forlong-term changes in reproductive cycles in response to climate change. To date, I have done relatively little with ontogenetic changes, variation, or sexual dimorphisms but these data can and should be examined from those perspectives.
In any undertaking of this magnitude, errors inevitably arise. These range from transposed numbers to misplaced decimals to other typographic errors. Quality control is necessary to assure data accuracy. Data that cannot be verified will have to be discarded. Next, I briefly describe various types of data.
Fresh snout-vent length (SVL), tail lengths, and weights were measured for all lizards in the field before preservation. Regressions of whole unbroken tail lengths on SVL allowed estimation of tail lengths for lizards with broken or regenerated tails. Nine morphological measurements were made on a subset of preserved specimens of each species: snout-vent length, head length, head width, head depth, jaw length, foreleg length, hindleg length, forefoot length, and hindfoot length. Preserved tail length can be estimated from fresh tail lengths.
Some of these morphological measurements have been digitized and have been collated with other files to associate sex with anatomy. Many more morphological measurements remain to be digitized and most specimens collected since 1995 have not yet been measured. These data will be checked for accuracy by plotting each morphometric against SVL and looking for outliers. This will be a time consuming and tedious task, requiring assistants. For a preliminary analysis, see Towards a Periodic Table of Lizard Niches (Power Point Presentation, View in Safari).
My Ph. D. research took place in the early 1960's when data were entered on to mainframe computers using punched 80 column computer cards. I wrote my own programs to analyze these data. Information on each individual lizard was input on two 80 column fields using a continuation card, with study site, a unique specimen ID number, species identity, sex, date, time of collection, length of fat bodies, gonad condition (testis lengths for males, number of eggs and average egg diameter for females), weight, fresh field-measured snout-vent length, fresh tail length, tail condition, body temperature, ambient air temperature at chest height, where the lizard was when first sighted, where it ran to, how many times it ran, total number of prey items and total volume of prey in the stomach. Items in stomach contents were scored by number and volume using the above-mentioned 20 basic prey categories. These data files for almost 4,000 lizards were originally in simple text file format, they have been converted into files with a single line of data for each individual lizard. Most of my information on North American lizards has now been imported into mySQL tables -- I have written queries to extract various subsets of information, such as diets by species and sex, study site, and time. However, much more can still be done. For example, sex has been cross-linked accurately to separate data sets with preserved morphometrics to allow analyses of sexual dimorphisms in anatomy, thermal relations, diet and microhabitat.
Data for almost 4,000 North American lizards are summarized in six SQL Tables: NAkey, NAanat, NAdiet, NAdietfreq, NAfemales, and NAtestes. Field notebooks were scanned and made into pdf files (available here).
I also made up some prey size data files for North American lizards. All snakes were collected and small mammals were trapped (these are deposited in the Burke Memorial Museum at the University of Washington in Seattle). Bird lists were also assembled (Pianka 1967).
Data collected for each Kalahari lizard (N = 5375) in the field were as follows: unique ID number, species identity, sex (if possible), ambient air temperature at chest height in °C, active body temperature in °C, time of collection, date, latitude, longitude, where the lizard was when first sighted, and where it ran to, fresh field measured snout-vent length, fresh tail length and condition, and weight in grams. All of this information has been digitized and converted to mySQL Tables. Later, in the lab, lizards were dissected, stomachs were removed and their sex and reproductive state was determined. Protocols of these raw data sheets, one for five individual lizards, have never been digitized, but were summarized by hand, and need to be entered into electronic format and cross checked. In addition to using the same 20 different prey categories that were used for North American desert lizards, another more detailed Kalahari dietary data set identified termites to species and castes based on 68 prey categories. Snakes were collected and bird lists were assembled (Pianka and Huey 1971).
Data for over 5,000 Kalahari lizards are also summarized in six SQL Tables: KLkey, KLanat, KLdiet, KLdietfreq, KLfemales, and KLtestes. Kalahari field notes were scanned and made into pdf files (available here).
For every lizard collected, the following information was collated in field notebooks (all of these have been scanned and saved as pdf files): unique ID number, genus, species, sex (if possible), date, time of collection, active body temperature in oC, ambient air temperature at chest height in °C, where the lizard was when first sighted, and where it ran to, fresh field measured snout-vent length, fresh tail length and condition, and weight in grams. On sandridge sites, positions where each lizard was found were recorded (flat, base, slope, or crest). For many thousands of lizards collected from 1992 through 2008, pit trap numbers were also recorded. High resolution color aerial photos show precise locations of pit traps on three study sites (B, L, and R).
As in North America and the Kalahari, Australian lizards were dissected and sex and reproductive condition ascertained. Stomachs were removed and stomach contents identified into the same basic list of 20 different prey categories, most insect orders, only 19 of which occurred in Australia (solpugids are present in North America and the Kalahari, but absent in Australia). All snakes were collected and bird lists were assembled for both the Kalahari and Australian study sites (Pianka and Pianka 1970).
In 1978-79, a Guggenheim Fellowship allowed me to focus attention on two study areas: the L-area (N = 1567 lizards) and Redsands (N = 1436 lizards), to better characterize resource utilization by rare species. I hired a competent entomologist Dr. Thomas D. Schultz to go through stomach contents of these lizards identifying prey to the finest resolution possible. Ants and termites were placed into size and/or color categories by family to generate some 97 ant and 58 different termite resource states. Over 200 different prey categories were recognized, not all of which were present at either site alone. These data have been digitized but need to be linked to other files, cross checked against original data sheets, and imported into mySQL tables.
The Australian Bureau of Meterology reports that long-term average annual precipitation in the region of the Great Victoria Desert is less than 200 mm (map shown below).
Moreover, whereas average annual rainfall over the past decade has fallen in eastern Australia and coastal areas, precipitation has increased in the interior of Western Australia. During the last 40 years, rainfall in this part of the GVD has increased by 20-30mm per decade above the long-term average (Australian Bureau of Meterology map of deviations in precipitation from 1970 to the present). This striking change in rainfall regime is indicative of global climate change.
In 2003, I was stunned that I did not recognize my long-term study areas and actually drove right past them because shrubs had increased so greatly in abundance! Spinifex, a vital microhabitat for many lizard species, has diminished with the increased abundance of shrubs. As a result of this increased rainfall, shrub encroachment seems to have changed these ecosystems profoundly. The changing vegetation appears to have affected both avian and lizard populations, and most likely has also impacted arthropod populations upon which birds and lizards depend for food. Old photographs of study sites will be compared with recent ones to document these changes in the vegetation. Changes in the relative abundances of lizard species and in their diets over this decade will constitute further evidence of global climate change as well as reveal its impact on insect and lizard faunas.
Because lizards are sedentary terrestrial ectotherms, they are very sensitive to temperature -- they respond rapidly to climatic change and can be used to monitor global warming. A recent study suggests that behavioral thermoregulation may enable ectotherms to adapt to global warming by shifting their seasonal patterns of activity and reproduction (Kearney et al. 2009; Huey and Tewksbury 2009). My extensive data on day and time of activity, microhabitat, ambient air temperatures and active body temperatures for thousands of desert lizards (82 species) will allow tests of the assumptions and predictions of their energy-mass balance models. In addition, my long-term (1966-2008) data on reproduction in Australian desert lizards will allow me to detect any such temporal shifts in reproductive cycles over a 42-year time interval.
Climate change appears to have altered the fire regime in the GVD as well: during the last two decades, fires have been more frequent and much more extensive than they were during the 1970's to the 1990's (Haydon et al. 2000a, 2000b). This new fire regime may result in a more homogeneous landscape, which could reduce habitat heterogeneity and species diversity, and might even lead to local extinctions.
Understanding rarity constitutes a major challenge for ecologists. About one-third of the species studied here are relatively abundant 'core species,' and the other two thirds are uncommon 'occasional species' (Magurran and Henderson 2003), some of which are extremely rare. Over the last 42 years, I have captured migrants of a number of species (Ctenophorus fordi, Ctenophorus scutulatus, Ctenotus leae, Ctenotus leonhardii, Lophognathus longirostris, and Nephrurus vertebralis) dispersing through habitats that they do not normally occupy. I have also witnessed metapopulation-like local extinctions and colonization in a few species. See also Rarity in Australian Desert Lizards.
Rarity has proven to be exceedingly difficult to study, but rare species could well be very important to community function (Main 1982, Morton and James 1988; Thompson et al. 2003, So far, inadequate sample sizes have prevented me from doing much with uncommon species, but I have now finally managed to acquire large enough samples to understand the ecologies of most of them. Of 67 Australian species studied, sample sizes are now less than 10 for only 6 species and samples exceed 30 for 48 species. For each uncommon species, I intend to determine whether rarity is due to mere dispersal into alien habitats or whether it is associated with scarce resources such as limited food or microhabitat availability.
These lizard populations can be viewed using a metaphor: their relative abundances are analogous to 3-dimensional waves in as many dimensions as there are species: the vertical coordinate represents the abundances of each of the various species moving up and down and around in space and time. At any given time, some species are abundant while others may be scarce. These abundance surfaces are relatively placid for some species, but very rough for others. Some species like Ctenophorus clayi and Ctenophorus nuchalis boom and bust, whereas others like Ctenophorus isolepis have more stable populations. These waves of relative abundance respond to fire and precipitation, both of which drive habitat changes through time and space. One of my goals is to describe this multi-dimensional spatial-temporal wave-like landscape.
Pit trap line on the B-area.
MacArthur (1965) identified several different types of species diversity based on the size of the area sampled. He named two of these within-habitat diversity and between-habitat diversity. In the limit, as space is collapsed down to a single point, he suggested that "point diversity" might be an informative measure as it avoids sampling area. Relatively few efforts have been made to estimate point diversity, but pit traps allow their measurement.
Pits were first installed on the L-area and at the R-area in September 1989. Five gallon plastic buckets were buried with their lips flush with the ground surface with drift fences about 20-25 cm high between pits. Individual pits were numbered. Additional pits were added in subsequent years, culminating in a total of 100 pits on the L-area, 100 pits at the R-area, and 75 pits on the B-area. Thousands of lizards have now been pit trapped at these 3 sites in the GVD from hundreds of pits arranged over a spatially heterogeneous landscapes. A total of 62,226 pit trap days, most during Austral Spring (September-November) from 1989-2008 has yielded 12,634 specimens.
Numbers of individuals of each species trapped in each pit have been tallied up. Some species are associated with sand ridges, others with flat sand plains between sand ridges, and still others with litter under marble gum trees. I have summed up the proportions of each species that were collected on flat sand plains, the base of sand ridges, the slopes of sand ridges, and the crests of sand ridges. Some species are specialized to only one of these habitats, while others have broader habitat niches.
Plot showing number of species versus the number of individual lizards
captured in pit traps located on flats and various positions on sandridges,
Pit trap data provide replicated estimates of point diversity through time. Pit traps vary widely in the numbers of individuals and species captured, as well as their relative abundances. Some pits are "hot" and catch many more individuals and species than others. For example, some pits captured hundreds of individuals of dozens of species whereas others, open at the same time and in apparently similar habitats nearby, captured only dozens of individuals of just a few species over the same time interval.
As explained above, some habitat-specialized species are found only on flat sand plains between ridges, while others occur only on sand ridges. Still other species have more flexible habitat requirements. I will categorize what features of the landscape various lizard species respond to, and then classify pits by what species they catch using multivariate analysis. Sand ridge pits should clump together based on what they captured. Strong positive and negative correlations between pairs of species will be identified (i.e., is species A likely to be captured in the same pits as species B, or are they unlikely to be captured together but found in different pits). In a preliminary analysis, of 26 strong correlations between such pairs of species, only 4 are negative. Understanding exactly why such correlations occur is a prime objective.
Low-level, high-resolution aerial photographs of these three areas were acquired at considerable personal expense. Precise positions of pit traps have been plotted on these aerial photographs. Using a geographical information system (GIS), as explained above, we are assessing habitat requirements of various species, as well as whether species are positively or negatively correlated with each other over space and time. Habitat requirements of Australian desert lizard species will be analyzed in detail using these extensive pit trap records of many thousands of individual lizards of dozens of species over a 20-year period.
We are looking for correlations between how far each pit is from various features such as sand ridges, marble gum trees, acacia bushes, termitaria, etc., all of which can be seen on the aerial photographs. Appropriate sizes of the neighborhoods for each lizard species must be estimated. Some, such as monitor lizards move over great distances, whereas others, especially small species such as litter-specialized skinks, are much more sedentary. We will begin with the most abundant species and work towards less abundant ones, which might not provide much signal and will obviously be harder to understand. This effort will contribute to understanding rarity.
When I was invited to write "The structure of lizard communities" for the Annual Review of Ecology and Systematics early in the 1970's, I assembled resource matrices for diets and microhabitats for what I called the "merged decks" which represented all the lizards of each species collected at all study sites within each continental-desert lizard system (Pianka 1973). These were updated and published as appendices in Pianka (1986). Later for my chapter in the MacArthur memorial volume, I performed a comparable site-by-site analysis, assembling resource matrices for diets and microhabitats for all the lizards from each study site. These data have not yet been published. A computer program read these as input files and generated overlap matrices as output. These files are useful because they provide concise summaries of utilization of prey and microhabitats by various species at a given site. Such resource matrices allow quantification of niche breadth and overlap.
Lizards have proven to be ideal subjects for ecological studies: work on them has revealed many basic ecological principles (Milstead 1966; Huey et al. 1983; Vitt and Pianka 1994). These model organisms are abundant, easily observed and captured, low in mobility, extremely hardy in captivity, and can be marked and monitored for many years. Moreover, they eat their prey whole which greatly facilitates stomach content analyses and quantification of diets. Because lizards are ectotherms, they respond rapidly to climatic change and can be used to monitor global weather change as explained above. Phylogenies have now been constructed for many lizard clades, allowing application of modern comparative methodology to elucidate the probable actual course of evolution of many traits (see below).
Lizards have evolved in response to desert conditions independently within each of these 3 continental desert systems. Intercontinental comparisons reflect the extent to which interactions between the lizard body plan and desert environments are determinate and predictable. Convergences observed between such independently evolved ecological systems provide important insights into the operation of natural selection and underscore general principles of community organization.
I have made major advances in understanding the ecology and diversity of Australian desert lizards. I have undertaken a series of phylogenetic analyses elucidating probable evolutionary pathways for a wide variety of important traits including functional anatomy, activity times and temperatures, foraging tactics and diets, reproductive tactics, habitat and microhabitat utilization, and relative abundances. I have made progress towards understanding the ecology of rare and uncommon species as well as why they are uncommon. I have documented long-term ecosystem changes due to global climate change as well as those occurring during the fire succession cycle.
Also, I will undertake pioneering studies on point diversity and habitat requirements, and map the ever-changing multidimensional spatial-temporal waves of relative abundances. I have organized invaluable old 'fossil' data as well as a large amount of new data so that they can be safely preserved for use by future generations.
For those who only find value in how something can serve humans, I submit that as we complete our domination of this planet, and enter into the final phase of human population growth and resource limitation, we will desperately need to know how natural ecosystems work in order to manage our own artificial systems. Unfortunately we still understand precious little about how natural ecosystems function. If we are ever to know our own impact on the planet, we must preserve data like these for the future. We must study vanishing natural ecosystems before they are completely gone if we are ever to gain the understanding we need for our own persistence. That is about as anthropocentric as one can get!
1. Lizard faunas and foods eaten on the B-area have been examined at six different time intervals in the fire succession cycle from original long unburned to 13 years post-burn to better understand the dynamics of this ecosystem. These long-term census data provide insights in to how individual species respond to fires (species composition, relative abundance, dietary flexibility, and reproductive tactics). See also Fire Succession on the B-area.
2. Habitat requirements of Australian species can be analyzed using extensive pit trap records of many thousands of individuals of dozens of species over two decades. Precise positions of pit traps plotted on low-level, high-resolution aerial photographs should be analyzed using a geographical information system (GIS) to assess habitat requirements of various species, as well as whether species are positively or negatively correlated with each other over space and time. See also Point-Diversity and Habitat Requirements.
3. About two thirds of the species are uncommon -- these can now be better characterized and I have finally been able to begin to attempt to understand rarity (a major challenge facing ecologists). See also Pianka 2014 and Rarity in Australian Desert Lizards.
4. Changes in relative abundances of species from site to site and through time at two long-term study sites should be compared and related to fires, climate change, and shrub encroachment.
5. Ecological and anatomical changes during ontogeny and sexual dimorphisms between males and females should be examined. See also Gender Differences.
6. Diets of diurnal species should be compared to those of nocturnal species.
7. Phylogenetically informed analyses of evolution of body and head size and shape, as well as head and tail proportions among these desert lizards should be undertaken. Some species are fossorial, others terrestrial, and still others are arboreal. Tail length varies widely among species, with relatively short tails in fossorial species (in some, the tail is shorter than snout-vent length, SVL).
For example, among pygopodids, terrestrial species like Pygopus have tails about twice as long as SVL, whereas most Delma have tails about 3 times SVL, but exceedingly long tails up to 4 times SVL occur among two closely-related arboreal pygopodid species (Delma concinna and Delma labialis). Among the six pygopodid genera, heads vary from shovel-like in fossorial species (Aprasia, Ophidiocephalus) to blunt snouts (Pygopus) to various degrees of long slender pointed snake-like noses (Delma, Lialis and Pletholax). Head morphologies can be related to ecologies (diets and microhabitats). We will exploit the phylogeny reconstructed by Jennings et al. (2003) but will include new sequences from additional slowly evolving nuclear genes (such as Rag-1) to clarify deep phylogenetic relationships. Heads have been scanned in Dr. Timothy Rowe's Digimorph laboratory using 3-dimensional high-resolution digital catscans. Similar phylogenetically informed studies should be undertaken for other species, especially for the species-rich Australian genus Ctenotus, but also among North American and Kalahari species.
Catscans of skulls of Pygopus and Lialis (from Digimorph web site).
Heads have been scanned in Dr. Timothy Rowe's Digimorph laboratory using 3-dimensional high-resolution digital catscans. See also Phylogenetic Reconstruction of Ancestral Traits.
No-one will ever be allowed to replicate Pianka's monumental efforts to understand the ecology and diversity of the world's desert lizards. Such invaluable data will never again be assembled. He is now organizing his massive data set to preserve them for use by future generations.
Almost 28,000 specimens from three continents representing more than 100 different species in 22 families of lizards have been safely deposited in major museums (DNA samples of Australian species were also deposited in the Evolutionary Biology Unit collection at the South Australian Museum in Adelaide.). Each specimen has its own unique number with accompanying information on locality, date, habitat and microhabitat, time, air and body temperature, fresh body weight, snout-vent length, and tail length and condition. These data are lodged with each museum as copies of field notes (link to pdfs here).
Lizard specimens were also dissected and their sex and reproductive condition assessed. Stomach contents were analyzed and summarized. Ten body measurements were made on preserved specimens. Many of these supplementary data remain at risk and will be lost with Pianka's demise unless he can finish getting them digitized and entered into a data base.
The culmination of Pianka's life and work is now at stake -- as much information as possible for each individual lizard should be preserved for posterity. These data need to be organized in a relational database format describing different types of data with queries to extract particular subsets. These data constitute an invaluable resource for a wide variety of future studies, including seasonal and long-term changes, ontogenetic changes, variation and sexual dimorphisms in morphology and ecology (gender differences), microhabitat and habitat requirements, thermal biology, reproductive biology, differences between diurnal vs. nocturnal species, within-versus between-phenotype components of niche breadth, dietary and microhabitat niche breadth and overlap, and point diversity.
Goodyear, S. E. and E. R. Pianka. 2011. Spatial and temporal variation in diets of sympatric lizards (genus Ctenotus) in the Great Victoria Desert, Western Australia. J. Herpetology 45: 265-271. Read On Line. Download pdf
Haydon, D. T., J. K. Friar, and E. R. Pianka. 2000a. Fire Driven Dynamic Mosaics in the Great Victoria Desert I: Fire Geometry. Landscape Ecology 15: 373-381. Abstract, Download pdf.
Haydon, D. T., J. K. Friar, and E. R. Pianka. 2000b. Fire Driven Dynamic Mosaics in the Great Victoria Desert II: A spatial and temporal landscape model. Landscape Ecology 15: 407-423. Abstract, Download pdf.
Huey, R. B. and J. J. Tewksbury. 2009. Can behavior douse the fire of climate warming? Proc. Nat. Acad. Sci. 106: 3647-3648. Download pdf.
Huey, R. B., E. R. Pianka, and T. W. Schoener (eds.) 1983. Lizard Ecology: Studies of a Model Organism. Harvard University Press. 501 pp.
Huey, R. B., E. R. Pianka, and L. J. Vitt. 2001. How often do lizards "run on empty?" Ecology 82: 1-7. Download pdf.
Jennings, W. B., E. R. Pianka, and S. Donnellan. 2003. Systematics of the lizard family Pygopodidae with implications for the diversification of Australian temperate biotas. Systematic Biology 52: 757-780. Download pdf.
Kearney, M., R. Shine, and W. Porter. 2009. The potential for behavioral thermoregulation to buffer "cold-blooded" animals against climate warming. Proc. Nat. Acad. Sci. 106: 3835-3840. Download pdf.
Leistner, O. A. 1967. The plant ecology of the southern Kalahari. Botanical Survey of South Africa, Memoirs 38: 1-172.
Magurran, A. E. and P. A. Henderson 2003. Explaining the excess of rare species in natural species abundance distributions. Nature 422 (6933): 714-716.
Main, A. R. 1982. Rare species: precious or dross? Graves, R. H. and W. D. L. Ride (eds): Species at risk: Research in Australia, pp. 163-174. Australian Academy of Science, Canberra. Download pdf.
Milstead, W. W. (ed.). 1966. Lizard Ecology: A Symposium. University of Missouri Press, Columbia. 300 pp.
Morton, S. R. and C. D. James 1988. The diversity and abundance of lizards in arid Australia: a new hypothesis. American Naturalist,132: 237-256. Download pdf.
Pianka, E. R. 1966. Convexity, desert lizards, and spatial heterogeneity. Ecology 47: 1055-1059. Download pdf.
Pianka, E.R. 1967. On lizard species diversity: North American flatland deserts. Ecology 48: 333-351. Download pdf.
Pianka, E.R. 1969. Habitat specificity, speciation, and species density in Australian desert lizards. Ecology 50: 498-502. Download pdf.
Pianka, E.R. 1971. Lizard species density in the Kalahari desert. Ecology 52: 1024-1029. Download pdf.
Pianka, E. R. 1973. The structure of lizard communities. Annual Review of Ecology and Systematics 4: 53-74. Selected as "This Week's Citation Classic" in Current Contents (Agriculture, Biology & Environmental Sciences) (1988), volume 19 (number 35): page 18.) Download pdf.
Pianka, E. R. 1974. Niche overlap and diffuse competition. Proc. Nat. Acad Sci. 71: 2141-2145. Download pdf.
Pianka, E. R. 1975. Niche relations of desert lizards. Chapter 12 (pp. 292-314) in M. Cody and J. Diamond (eds.) Ecology and Evolution of Communities. Harvard University Press.
Pianka, E. R. 1986. Ecology and Natural History of Desert Lizards. Analyses of the Ecological Niche and Community Structure. Princeton University Press, Princeton, New Jersey.
Pianka, E. R. 1996. Long-term changes in Lizard Assemblages in the Great Victoria Desert: Dynamic Habitat Mosaics in Response to Wildfires. Chapter 8 (pp. 191-215) in M. L. Cody and J. A. Smallwood (eds.) Long-term studies of vertebrate communities. Academic Press. Download pdf.
Pianka, E. R. and S. E. Goodyear. 2012. Lizard responses to wildfire in arid interior Australia: Long-term experimental data and commonalities with other studies. Austral Ecology 37: 1-11. Download pdf.
Pianka, E. R. and R. B. Huey. 1971. Bird species density in the Kalahari and the Australian deserts. Koedoe 14: 123-130. Download pdf.
Pianka, H. D. and E. R. Pianka. 1970. Bird censuses from desert localities in Western Australia. Emu 70: 17-22. Download pdf.
Thompson, G. G., P. C. Withers, E. R. Pianka, and S. A. Thompson. 2003. Assessing biodiversity with species accumulation curves: Inventories of small reptiles by pit-trapping in Western Australia. Austral Ecology 28: 361-383. Download pdf.
Thompson, G. G., S. A. Thompson, P. C. Withers and E. R. Pianka. 2003. Diversity and abundance of pit-trapped reptiles of arid and mesic habitats in Australia: Biodiversity for Environmental Impact Assessments. Pacific Conservation Biology 9: 120-135. Download pdf.
Vitt, L. J. and E. R. Pianka (eds.) 1994. Lizard Ecology: Historical and Experimental Perspectives. Princeton University Press. 403 pp.
Vitt, L. J. and E. R. Pianka. 2005. Deep history impacts present day ecology and biodiversity. Proc. Nat. Acad. Sci. 102: 7877-7881. Download pdf.
Winemiller, K. O., E. R. Pianka, L. J. Vitt, and A Joern. 2001. Food web laws or niche theory? six independent empirical tests. American Naturalist 158: 193-199. Download pdf.