Cottonmouth Moccasins: Adapting to the Beach and Beyond

Could some pit vipers evolve the capacity to invade the world’s oceans?


Last Thursday, while doing some fieldwork in Levy County, I came across this Florida cottonmouth as it was sunning itself after an early morning swim:

The warning behavior being demonstrated in the last photo is how the ‘cottonmouth’ earned its common name; trespassers and would be predators can be caught off-guard and intimidated when the snake curtly flashes the white interior of its mouth. The warning was certainly well received by me – I’ll take being startled over enduring a venomous bite any day of the week!

The Florida cottonmouth Agkistrodon piscivorus conanti is one of three subspecies of water moccasin native to the United States; the other two varieties include the Eastern cottonmouth (Agkistrodon piscivorus piscivorus) and the Western cottonmouth (Agkistrodon piscivorus leucostoma). These three subspecies of semi-aquatic pit vipers are renowned for their exceptional swimming ability and their associated preference for habitats in and around the freshwater lakes, streams and swamps of the Southeast U.S. They have adapted to be masters of wetlands; well, masters of freshwater wetlands anyway…

Even though their preferred range places them in proximity to the Atlantic Ocean and the Gulf of Mexico, the conquest of marine ecosystems by the cottonmouths has been - as it has with most aquatically inclined reptiles - blockaded. The physiological demands of maintaining adequate hydration in a high-saline environment has constrained the Agkistrodon genus to a landward life. But things could change.

Could cottonmouths evolve to live in the sea, like kraits or sea snakes?

As mentioned previously, the above images show a cottonmouth from Levy County, Florida. Levy County is located in West Central Florida and boasts an impressive coastline along the Gulf of Mexico. The coastline even has barrier islands. In fact, one such barrier island, called Seahorse Key, has its very own population of cottonmouths - cottonmouths that have found a niche in the intertidal zone.

Generally considered opportunistic carnivores, the bulk of the average cottonmouth’s diet is derived through consumption of its wetland neighbors - frogs and fish - however, they have been known to occasionally snack on insects, lizards, birds, rats, or even other moccasins. The cottonmouths of Seahorse Key have taken their tastes for fish from the freshwater to the saltwater; there they eat marine fish scavenged from the intertidal zone or haphazardly dropped from the Key’s bird rookeries. In addition to marine fish, the cottonmouths of Seahorse Key will even eat SEAWEED if it has the odor of fish on its leaves.

So, the cottonmouths of Seahorse Key have a proven ability to eat, digest and process marine food resources. They posses elongate lungs to provide buoyancy and streamlined bodies capable of eel-like swimming locomotion. As with other pit vipers they have venom to aid in capture of fast moving fish. And, in regards to reproduction, cottonmouths give birth to live young, so there’s no need to go to shore to lay eggs…

It seems that the only other major factor restricting the cottonmouths’ sea-ward invasion is a limited tolerance for high-salinity…

If only there was a selective pressure for improved salt water tolerance; for instance, a selective pressure something like being stuck on an island that is subject to rising sea levels. What are the chances of that happening?

The behavioral and physiological adaptations required in order for a land animal to successfully undertake a conquest of the sea are undoubtedly both varied and numerous; but, with sufficient selection pressure, ample time, and an incremental, step-wise process it can and has happened.

For example, consider all of the behavioral and physiological changes that must have occurred in order for a few Devonian lobe-finned fish to find their way to shore as fully terrestrial tetrapods! Or, viewing the scenario in reverse, imagine the adaptations that permitted Eocene land mammals to re-enter the sea as a line of cetaceans!

Subtle cumulative changes over time can alter a lineage’s dietary preferences, reproductive rituals and even bodily mechanics.

Lillywhite, H., Sheehy, C., & Zaidan, F. (2008). Pitviper Scavenging at the Intertidal Zone: An Evolutionary Scenario for Invasion of the Sea BioScience, 58 (10) DOI: 10.1641/B581008

Tree Plantations as Biological Deserts

If I had a nickel for every time a biologist told me that tree plantations are nothing but “biological deserts” I’d be a rich man!

Well, at least a rich-er man anyway…

Industrial tree plantations can be ugly places for those with an eye for the natural beauty offered by mature and diverse forested ecosystems. Plantations are more-often-than-not composed of crowded, densely spaced trees, predominantly of the same species, age, size and condition. The soil surface on which these monocultures stand is heavily disturbed, rutted, bedded & rowed, and laden with fertilizers and herbicides. The compounding effect of these characters alters hydrology, impedes the advance of recruiting plants and strongly restricts use by wildlife.

When compared to pristine natural forests, plantations are like ‘biological deserts;’ but what about when they’re compared to a sprawling urban landscape or an agricultural pasture? What if the plantation’s location in the landscape serves as a corridor for wildlife between a developed residential area and more pristine habitat at a distance?

Plantations do offer important ecosystem services and can often maintain critical ecological functions…

Replace natural forests with plantations? – No, I’ll fight you to my last breath!


Replace agricultural pasture, or a sprawling city-scape with plantations? – I’ll help you plant the trees!


A recently published review by Alain Paquette and Christian Messier has just found its way into a stack of papers I keep as ammunition against the overly broad characterization of plantations as worthless biological deserts (a claim usually made by biostitutes hired to devalue a chunk of land for the financial gain of the owners).

Check it out:
Paquette, A., & Messier, C. (2010). The role of plantations in managing the world's forests in the Anthropocene Frontiers in Ecology and the Environment, 8 (1), 27-34 DOI: 10.1890/080116

The Splendor of a Saprotrophic Stinkhorn

While in field last week, I encountered a species of fungus with a rather unique set of morphological and ecological characteristics. The aptly named ‘stinkhorn’ fungus (Clathrus columnatus) belongs to the Phallaceae Family of fungi and produces a distinctive gelatinous spore mass that gives off a lovely perfume. Well, lovely to insects anyway, to me it reeked of rotting meat and dung. The stinkhorn’s ‘aroma’ serves as an attractant for flies and other insects vital to the fungus’s lifecycle. In the process of munching on the glebra (spore mass) insects gather the fungus’s reproductive spores on their bodies and in their digestive tracts, these spores are then transported and dispersed once the insects have gotten their fill and part ways. Although my nose took offense to the odoriferous bouquet produced by the stinkhorn’s gleba, the fungus’s appearance was really pretty cool.

The orange and spongy columnar structure of Clathrus columnatus emerges from an "egg" on the ground and grows upward forming an arch-like receptaculum at the top. The underside of the ‘arch’ forms from the joining of the stinkhorn’s multiple columns and anchors the foul-smelling glebra.

The "Egg"

View from above - Intersection of Columns

Fungi play major roles in the nutrient cycling of terrestrial ecosystems. Clathrus columnatus itself is a saprotroph that decomposes organics, and in process of doing so frees-up important resources for it and the other organisms sharing its ecosystem.

Energetically, saprotrophic fungi utilize extra-cellular digestion to acquire nutrients from dead and decaying organic material. Extra-cellular digestion is the process in which an organism, such as a fungus, releases tissue degrading enzymes into its surrounding environment. The enzymes break down nearby organics into their more easily metabolized constituents, such as simple sugars and fatty acids. In the case of the wood specialist Clathrus columnatus, its enzymes catalyze cellulose into simple sugars which are in turn engulfed by the fungus’s cells (endocytosis). In addition to freeing simple disaccharides from wood, the enzymes produced by C. columnatus also liberate valuable carbons from the wood’s lignin stores. The ability of lignin to store atmospheric carbon makes it an important component of the Carbon Cycle, and antagonistically, the capacity of the stinkhorn’s lignin-modifying enzymes to oxidize and release these sequestered carbons represents a significant ecological contribution.

As a consequence of Clathrus columnatus’s affinity for dead wood, the fungus is often associated with anthropogenically disturbed habitats. It can often be found growing in and around gardens and residences where areas of cultivation have resulted in accumulations of mulch, woodchips or other cellulose laden landscaping materials. Interestingly, the photos displayed here were taken adjacent to a brownfield that previously held a paper mill. As a part of the mill’s past wood-processing, the otherwise nutrient poor sandy soils include high quantities of wood chips - a virtual stinkhorn buffet.


Tuno, N. (1998). Spore dispersal of Dictyophora fungi (Phallaceae) by flies Ecological Research, 13 (1), 7-15 DOI: 10.1046/j.1440-1703.1998.00241.x

Wetland Plant of the Week #33

Hypericum fasciculatum “Peelbark St. Johnswort”

Peelbark St. Johnswort, also known as ‘marsh St. Johnswort,’ is a Florida native and widely distributed member of the Hypericaceae Family that can commonly be found in swamps, marshes and just about any locality having sufficient water to satisfy its Obligate lifestyle. The multi-branched growth pattern of this upright shrub gives it a very bushy appearance, and provides ample structure for numerous arthropods species to nest and hide (including ticks, take caution).

Though typically about four feet tall, the woody stems of Hypericum fasciculatum can push the plant upwards to reach heights of over two meters (6ft). In an effort to increase available surface area for oxygen absorption, the reddish-bark of the stems is exfoliated giving it a soft and crumbly look and feel.



The needle-like leaves of the plant grow in bundles and average about 2.6cm in length with slightly longer leaves at the top of the stem. The flowers, although not pictured here, display five petals arranged in a whorled pattern and can be found spring-through-summer at the terminal ends of the branches.

The abundance of Hypericum fasciculatum, when combined with its multi-branched physiognomy and its habitat preference for plentiful water, make the plant an integral component of aquatic ecosystems here in Florida. As mentioned previously, the structure provided by the plant’s branches, branchlets and leaves attract a myriad of arthropod species. Once attracted by the ‘peelbark,’ these same arthropods will, in turn, move to occupy niches in proximity to the plant. There they’ll take on roles as pollinators, predators and prey for other organisms. Through such species interactions, the trophic effects of seemingly unconnected organisms become intertwined and bound.

As an example of how complex life histories can become tangled, consider for a moment a hypothetical swamp in which a hypothetical fish is swimming around the exfoliated base of a hypothetical Hypericum fasciculatum …

As with many fish, the hypothetical one feeds on aquatic insects like water beetles, mayflies and larval dragonflies. Examining dragonflies in particular, the loss of dragonfly larvae via fish predation ultimately results in the emergence of fewer adult dragonflies than would be predicted in the absence of the fish. Compounding the process further, the presence of fewer adult dragonflies in nearby ecological communities translates to less aerial predation of flying insects. Flying insects, in addition to being food-stuffs for dragonflies, also pollinate plants; from this relationship it can be inferred that with fewer dragonflies, more insect pollinators find the nectar-rich flowers they seek… The end result of this hypothetical situation is that the Hypericum’s proximity to the fish allows the plant to host a greater number of pollinators, and thus to experience a greater level of reproductive success itself.

Image from Cited Article, interaction web showing the pathway by which fish facilitate plant reproduction. Solid arrows ndicate direct interactions; dashed arrows denote indirect interactions. The sign refers to the expected direction of the direct or indirect effect.

As is characteristic of most ecosystem dynamics, the above scenario can also be run in reverse to show that the presence of the common Hypericum fasciculatum could lead to increased fitness in the hypothetical fish species.


Knight, T., McCoy, M., Chase, J., McCoy, K., & Holt, R. (2005). Trophic cascades across ecosystems Nature, 437 (7060), 880-883 DOI: 10.1038/nature03962

Adapting to Climate Change, the Uphill Pursuit of the Shifting Niche

This post represents the final in a three part series discussing Joseph Grinnell, climate change and ecological niches. The initial post can be found here: Joseph Grinnell, Climate Change and the Legacy of the California Thrasher, and the second here: Tracking the Niche, a Project of Grinnellian Proportions.



Having adopted Joseph Grinnell’s vision as their own, the current Director of the Museum of Vertebrate Zoology at Berkeley and his colleagues have taken on the challenge of following in Grinnell’s footsteps – quite literally. The group, headed by current Director Craig Moritz, has begun the process of resurveying the 700-plus localities that were originally surveyed by Grinnell in the early 20th Century. Their goal is to compare the newly collected data to that inherited from Grinnell in aspirations of gaining insight into how a century of environmental change has impacted California’s avian, mammalian and herpetological faunas. Through application of carefully recalibrated Grinnellian field-methods, and the employment of modern techniques, the group is expanding biology’s understanding of the ecological niche.

As discussed during the first post on this topic (available HERE), the effects of average changes in global climate can be dramatically amplified at local levels. As a case in point, consider the region of California that was originally surveyed by Grinnell between the years 1914 and 1920. Over the past 100 years an approximate one-degree rise in global temperatures has resulted in a 3.7°C increase in minimum monthly temperature! A four-degree change in temperature has undoubtedly altered the ecology of this region - Yosemite National Park – in substantial and quantifiable ways. Such quantification has been precise goal of Grinnell’s successor.

Pulling data from Grinnell’s field-notes and DNA from his collected specimens, Craig Moritz has used climate models, modern genetics and biodiversity informatics to decipher and compare the demographies of mammals, birds, reptiles and amphibians of past and present. The analysis rendered from this research clearly indicates that the link between environment-and-species has remained true since its inception in Grinnell’s 'The Niche-Relationships of the California Thrasher'. More specifically, as the 3.7°C increase in minimum monthly temperature pushed Yosemite’s available habitats towards new equilibriums its fauna followed suit.

Yosemite’s geologic and geographic setting entails a range of elevations that extend from about 50 meters to well over 3000 meters above sea level. As is typical for diverging elevations, as altitude increases average temperatures decrease. So, if moving towards the top of a mountain one could anticipate encountering bands of cooler micro-climates. The relationship that exists between a specific temperature range and its corresponding physical components allow for identification of specific ‘life zones’. For example, the hydrology found on a mountain’s glacial peaks will differ in type and quantity to that located near the base of the mountain. In considering this natural phenomenon of elevational transition with specific regard to an overall increase in temperature across the mountainous region as a whole, an upward shift in ‘life zones’ could be predicted. In other words, as a temperature increase reaches a certain threshold, the glaciers capping a mountain will recede as to reduce the total area occupied by ice, and to increase the availability of liquid water. With increased access to water, life zones that had been previously locked in a frozen state will become biologically available to plants formerly bounded to lower glacier-free altitudes.

Moritz’s comparison of the life zones documented by Joseph Grinnell to those surveyed by his research group demonstrated that as Yosemite’s temperature increased over the past century, its life zones moved upwards. Significantly, the research showed that the uphill advance of life zones induced pursuit by those avian and mammalian faunas found below. The general pattern discovered by Moritz was that as temperatures increased in the park, the majority of wildlife populations found at high elevations contacted upwards, abandoning previously occupied portions of their lower habitat range. Correspondingly, those animals occupying lower altitudes shifted their habitats uphill.

The ability of Yosemite’s wildlife to confront ever-shifting environmental attributes with resilience and flexibility is critical to maintaining lineages with the capacity to undergo the morphological and behavioral modifications required for their continued survival. The study of the processes driving this evolution, provides more than just a greater understanding of natural history, it also imparts the tools to ensure species conservation as global climate change accelerates environmental fluctuation. Luckily, field scientists such as Joseph Grinnell have, and will continue, to provide insight into the plasticity of adaptation.


See: The Grinnell Project's website.



Moritz, C., Patton, J., Conroy, C., Parra, J., White, G., & Beissinger, S. (2008). Impact of a Century of Climate Change on Small-Mammal Communities in Yosemite National Park, USA Science, 322 (5899), 261-264 DOI: 10.1126/science.1163428

Tingley, M., Monahan, W., Beissinger, S., & Moritz, C. (2009). Colloquium Papers: Birds track their Grinnellian niche through a century of climate change Proceedings of the National Academy of Sciences, 106 (Supplement_2), 19637-19643 DOI: 10.1073/pnas.0901562106

Joseph Grinnell (1917). The Niche-Relationships of the California Thrasher The Auk, 34 (4), 427-433

Joseph Grinnell (1924). Geography and Evolution Ecology, 5 (3), 225-229

Tracking the Niche, A Project of Grinnellian Proportions

This post is the second in a mini-series discussing Joseph Grinnell, climate change and ecological niches. The previous post is available here: Joseph Grinnell, Climate Change and the Legacy of the California Thrasher



Joseph Grinnell was THE quintessential field biologist. From the time of his birth in 1877 (or, roughly thereabouts), until his to death in 1939 he marveled at the natural world. He reveled in nature’s aesthetic splendor, and he contemplated its immense mystery. He dedicated his entire life to the field of biology; birds, reptiles, mammals and amphibians – he studied them all, and he did so with great detail.

Grinnell’s philosophy of scientific inquiry focused intently on the task of accumulating as much raw data as possible. For example, during the biological survey he carried out in Yosemite National Park between the years 1914 and 1920, Grinnell and his field crews collected 817 photographs, nearly 3000 animal specimens and more than 2000 pages of notes! Being organized and detail oriented is one thing, but Grinnell’s drive for thoroughness approached the obsessive.

As testimony to Grinnell’s view on taking accurate field notes, consider the following precept that he was known for continuously repeating as a mantra for meticulousness;

“Put it all down. You might not think it’s important, but somebody else may.” (1)

It may very well have been the sheer bulk of his available data that guided Joseph Grinnell to develop the concept of the ‘ecological niche’ discussed during the last post in this series (Available HERE). After all, he collected information on everything from the individual behavioral characteristics and morphology of observed animals to the daily weather patterns of Yosemite; all of these informational axes have been incorporated into the ecological niche concept. Even if the ‘niche’ wasn’t born of the data directly, the huge quantity of collected information would certainly have been useful during the writing of Grinnell’s numerous research papers and species descriptions, which are more than 500 in number.

Yet greater evidence to Grinnell’s tenacity can be found in the fact that despite his time spent collecting, he still managed to teach and perform administrative duties as the first Director of the Museum of Vertebrate Zoology at Berkeley. An absolutely astonishing scientist!

In considering Grinnell’s knack for field work, another of his now famous quotes comes to mind. This one (from 1910) relates to the long-term value of the data that he and his colleagues were collecting.

“This value will not, however, be realized until the lapse of many years, possibly a century, assuming that our material is safely preserved. And this is that the student of the future will have access to the original record of faunal conditions in California and the West, wherever we now work.”

This quote would turn out to be very prophetic…

What possible value could be reaped in modern times for century-old data collected during Grinnell’s survey of the ‘Yosemite Tract’? What would comprehensive and weather-correlated descriptions of wildlife niches tell us about contemporary linkages of climate-and-niche?

A few steps are required in order to assess the above questions. As an initial step, there would be a need to quantify the climate-to-niche relationships of current systems. Once such modern data was in-hand, comparisons could be made between the ‘old’ and the ‘new’ to identify any patterns or inconsistencies. In other words, to gauge change compare Grinnell’s data with what is exhibited by Yosemite’s ecosystems today.



This is precisely what the present Director of the Museum of Vertebrate Zoology at Berkeley has done. He and his colleagues went to field, and using Grinnell’s notes and methods collected new data for the purpose of comparison. Their resurvey - The Grinnell Project - and findings will be discussed during the next post...


UPDATE: The 3rd and final installment of this series is available HERE.


1-As told to Ward Russell during a field survey; an audio recording of Ward’s 1992 interview can be found at the MVZ @ Berkeley website – HERE



Joseph Grinnell (1917). The Niche-Relationships of the California Thrasher The Auk, 34 (4), 427-433

Joseph Grinnell (1924). Geography and Evolution Ecology, 5 (3), 225-229

Moritz, C., Patton, J., Conroy, C., Parra, J., White, G., & Beissinger, S. (2008). Impact of a Century of Climate Change on Small-Mammal Communities in Yosemite National Park, USA Science, 322 (5899), 261-264 DOI: 10.1126/science.1163428

Joseph Grinnell, Climate Change and the Legacy of the California Thrasher

Adaptive plasticity is a predictor of future reproductive fitness. The ability of an organism to confront ever-shifting environmental attributes with resilience and flexibility is critical to maintaining lineages with the capacity to undergo the morphological and behavioral modifications required for continued survival. Regardless if such elastic traits are realized through major swings in ontogenic development, or through the advent of novel life-history strategies, the ability of an organism to accommodate ecological variability is essential. This biological tenet is certainly true today as anthropogenically incited climate change is forcing accelerated rates of ecological alteration.

The Intergovernmental Panel on Climate Change has reported that mean global temperatures could increase by more than six-degrees over the course of the next century. Six degrees of global change translates to extremely dramatic transformations of biotic and abiotic conditions at the local level. Even if the ‘worse case scenario’ of six-degrees doesn’t come to pass changes in hydrology, periodic weather, seasonal patterns, emigration, extinction and in the availability of resources at regional and local levels are almost certainly inevitable during the next century. To cope with these changes it will be necessary for organisms to adjust their tolerances to environmental variability, they may need to more-efficiently utilize the resources on-hand, or they may need to physically relocate to habitats for which they are better suited. To better understand how these impending organism-to-environment adjustments will occur, it's important to seek understanding as to how organisms fit into their ecosystem. It is the relative position of an organism in its environment and the way in which it behaviorally responds to its surroundings that is referred to as the organism’s ‘niche’.

With respect to etymology, the word ‘niche’ is derived from the French word ‘nicher’ which literally means ‘to nest,’ as in a bird going to nest. In regards to the word’s use in biology – broadly defined above - this literal translation is very appropriate, because the term was first introduced by an ornithologist in a publication describing the distribution of a bird - the California thrasher (Toxostoma redivivum).

The California thrasher is the largest member of the Mimidae Family and can grow to be uupwards of 30 cm in length and weigh as much as 85 grams. The bird’s coloration is fairly non-descript; its body is brown and it has a tan or buff-colored ventral side. There are however a couple of characteristics that make T. redivivum especially unique. One is the bird's restriction to a very narrow geographic range in California, and another is its habitat preference for densely vegetated brushlands. It was the thrasher’s limited distribution and fondness for the concealment offered by shrubs that first attracted the interest of the celebrated naturalist and scientist Joseph Grinnell.

In the October 1917 issue of The Auk, Joseph Grinnell published his work 'The Niche-Relationships of the California Thrasher'. In that enduring contribution Grinnell explained that the reason for the thrasher’s

“…restricted distribution is probably to be found in the close adjustment of the bird in various physiological and psychological respects to a narrow range of environmental condition.”

In other words, Grinnell clearly recognized that the bird’s morphological and behavioral traits linked it to the specific ecosystem that it inhabited. Furthermore, Grinnell identified that

“[t]hese various circumstances, which emphasize dependence upon cover, and adaptation in physical structure and temperament thereto, go to demonstrate the nature of the ultimate associational niche occupied by the California Thrasher.”

In Grinnell’s mind, the relative position of the thrasher in its environment, as well as its distinctive behaviors, established a general rule that could be extrapolated and used as a tool for detailing and predicting the spatial and temporal relationships held between organisms and their environments. The ‘niche’ would quickly become a tool for not only itemizing individual life-history traits, but also for interpreting the evolutionary and adaptive implications of the organism-to-environment dynamic.

Building on his idea of an ecological niche, in July of 1924 Grinnell went on to publish ‘Geography and Evolution,’ a work in which he fathered what are contemporarily known as the competitive exclusion principle and the concept of ‘vacant niches.’

“Some of us have concluded that we can usefully recognize, as measures of distributional behavior, the realm, the region, the life-zone, the fauna, the subfauna, the association, and the ecologic or environmental niche. The latter, ultimate unit, is occupied by just one species or subspecies; if a new ecologic niche arises, or if a niche is vacated, nature hastens to supply an occupant, from whatever material may be available. Nature abhors a vacuum in the animate world as well as in the inanimate world.”

The competitive exclusion principle is the idea that two species occupying the same habitat and fighting for the same resources will not obtain equilibrium until one species overcomes, or out-competes, the other. These ideas are front-and-center to modern biology and are both credited to Grinnell.

Serving as the founding father of the ‘niche’ was but one of Joseph Grinnell’s numerous contributions to science. Over the next couple of days I hope to post more of Grinnell’s work, as well as that of his modern counterparts that are – literally – following in Grinnell’s footsteps in hopes of gaining insight into how the observations of an early 20th Century scientist can be used to decode the effects of climate change in a 21st Century world.


UPDATE: The second part of this post available HERE.

Joseph Grinnell (1917). The Niche-Relationships of the California Thrasher The Auk, 34 (4), 427-433

Joseph Grinnell (1924). Geography and Evolution Ecology, 5 (3), 225-229

Dead Zones, Conservation and Commercial Fishing

I’ve just read in the local news that Kevin Craig from the Florida State University’s Coastal and Marine Laboratory will be heading-up a collaborative four-year project funded by NOAA's Northern Gulf of Mexico Ecosystem and Hypoxia Assessment Program. The project’s goal is to assess the impact of the Gulf of Mexico’s ‘dead zone’ on marine ecosystems with a particular focus on shrimp and the shrimping industry.

It has long been known that agricultural run-off carrying excesses of fertilizer from the ‘bread basket’ of the United States are finding their way into the tributaries of the Mississippi River, and in turn, into the Gulf of Mexico. Once in the Gulf they consequently spawn explosions of algae growth resulting in hypoxic conditions and the conception of massive Dead Zones. Surges in the growth of algae and other noxious plants as a product of fertilizer facilitated Nitrogen and Phosphorous loading is called eutrophication. Eutrophication leads to de-oxygenated environments, and the resultant death of those organisms that require oxygen - of which there are many. The loss of oxygen-dependent organisms leaves vacant important positions in long established food-webs, potentially leading to the total breakdown of ecosystem function. To make matters worse, far from being stationary the dead zones move or “creep” from their epicenters corrupting ecosystems both far and wide. For Florida, the Gulf of Mexico Dead Zone may contribute to “Red Tide” and the death of everything from phytoplankton to manatees in the State’s coastal waters.

Kevin Craig is certainly the person for the job; back in 2005 he wrapped-up a research project that examined the effects of hypoxia on the abundance and distribution of Farfantepenaeus aztecus - the Gulf of Mexico’s ‘brown shrimp’. In that study, Craig, Larry Crowder, and Tyrrell Henwood used shrimp trawl surveys to compare the distributions of shrimp between hypoxic and non-hypoxic areas. What the team found was that the spatial distribution of shrimp in hypoxic regions was substantially different that those associated with non-hypoxic areas. The researchers also concluded that the effects of hypoxia contributed to as much as a 25% loss in F. aztecus’s available habitat.

The new NOAA funded project will undoubtedly have implications for both the science of ecology and in that of conservation. Shrimping is a major industry in the United States, and as such the participating fishermen and other commercial industries hold considerable economic and political clout. I'm eerily reminded of the warnings from biologists that were left unheeded and initially overthrown by rule-makers during the collapse of the Northern Cod Fishery…


Craig, J., Crowder, L., & Henwood, T. (2005). Spatial distribution of brown shrimp (Farfantepenaeus aztecus) on the northwestern Gulf of Mexico shelf: effects of abundance and hypoxia Canadian Journal of Fisheries and Aquatic Sciences, 62 (6), 1295-1308 DOI: 10.1139/f05-036

Fire Ecology Marathon; Nature Red in Tooth and Flame Part-4

The savannas of the southeastern United States are inimitable natural communities that have undergone ecological assembly in the presence of seasonal fire cycles and, as discussed during the first three installments on this topic (available here; Part-1, Part-2, Part-3), are rich in organisms capable of manipulating the regularity, movement and intensity of these wildfires. During the preceding post (Part-3) the phenotypes of two such fire-born species, the longleaf and slash pines, were detailed as exemplars of organisms with traits that not only aid in defending against heat and flame, but also as species that exhibit specific physical structures, chemicals and behaviors that could intrinsically promote fire. In closing that previous discussion, consideration was given to the possible motives behind the longleaf and slash pine’s ability to deliberately provoke fire.

Though it may initially seem to be counterproductive or even a hindrance to survival, through promoting fires the savanna pines obtain benefits that directly enhance their inclusive fitness. Because of the processes that drove the organismal evolution of the longleaf and southern slash pines in geological time, and the processes that propelled community assembly in savannas, the presence of wildfires effectively created a duality in the character of potential pine competitors and that of would-be savanna inhabitants - either they can tolerate fire, or they can’t tolerate fire.

In the absence of wildfires over extended periods of time (i.e. fire suppression) several ecological changes can occur in savannas. Most profoundly, without regular wildfires not only would the already present fire-tolerant plant species survive, but in addition, fire-intolerant species would experience greater fecundity. Without the deterrence provided by fire, resource-rich savannas can quickly become the envy of plants from surrounding hammocks and mixed hardwood forests, thus encouraging invasion and recruitment from these neighboring communities. Such movement of new species into the savannas would contribute to substantial ecological alteration of the natural processes that maintain the system’s predictable boundaries, ecotones and makeup.

Recall from Part-1 of this post that the plants found in hammocks have undergone selection for initial rapid growth and direct competition for sunlight. Just as the natural history of the pines has been shaped by fire, the history of dense-canopy species have evolved to fight for radiance. If unobstructed access to the abundant savanna sun is tantalizingly flaunted, these species would quickly invade, rapidly recruit and hurriedly regenerate to overtake all biologically available space. What was initially a patchwork of invasive species would spread to encompass and overcrowd the savanna, in the process reducing the diversity of appropriate groundcover plants, and adversely impacting the reproductive success of the native inhabitants – slash and longleaf fitness would decline.

In addition to increasing interspecific competition in the savannas, invasive species also create positive feedbacks in the wildfire cycle - magnifying fire suppression. The presence of abundant shrubs and woody species in a normally open savanna formulate densely vegetated landscapes that reduce fine fuel loads on the ground and decrease the likelihood of fire propagation. The lack of fire - in turn - facilitates further invasions, which increases vegetative densities even more, which reduces fire even more, which allows for yet greater invasive proliferation, etcetera…

With continued fire suppression, what was once a savanna, characterized by thinly distributed trees, would transition towards a densely canopied hammock with an impenetrable thicket understory. Growing populations of invasive species would amplify competition for resources, thus pushing the fitness experienced by the longleaf and southern slash pines to dangerously low values. This is precisely why the ‘fire gene’ is so critically important to the pine’s genotype. As crowding increases in this scenario, and essential resources dwindle, hormonal stress responses within the pines intensify. The hormones drive physiological changes in the trees causing leaves to drop and internal hydrocarbon chemistry to move toward increased combustibility. The probability for fire is increased. And, when fire does return, the stems, branches, leaves and roots from newly arrived invasives will serve as kindling for augmented wildfire intensity - to such extremes that only the hardiest of the fire-tolerant will be able to survive.

For clarification, conceptual genes (like the ‘fire gene’) aren’t confirmed as actual chromosomal localities for which variable alleles compete. Rather, conceptual genes are offered as thought-tools for understanding the premise that natural selection operates on phenotypical traits that are the products of genotypical coding. In regards to the ‘fire gene’ specifically, it is a hypothetical genetic compliment that is expressed in such a manner that the physical presence of fire improves the likelihood of that genotype being passed on to future generations. In other words, if a population of trees exist in which some members have a genotype that provides increased fitness in the presence of fire, AND that population is then exposed to fire - ultimately killing a certain percentage of the population - those trees with fire gene advantage will experience higher survivability and greater measures of fecundity compared to those not possessing a fire gene.

Returning to the savanna pines expressly, irregardless or not if there is literally a single gene that provides for all of the phenotypical adaptations to fire described throughout this post, or if these traits are the result of a cooperative epistasis, or if the characters are disparate and independent, it remains likely that their occurrence and continued propagation through evolutionary time has provided a significant advantage.

Through 300 million years of natural selection, wildfires have propelled the savanna defending pines to levels of adaptation in which they are capable of wielding fire. ‘Nature, red in tooth and flame’ has fashioned a true ecosystem engineer, one that is capable of establishing and defending the ecotonal boundaries between natural communities.


Beckage, B., Platt, W., & Gross, L. (2009). Vegetation, Fire, and Feedbacks: A Disturbance‐Mediated Model of Savannas The American Naturalist, 174 (6), 805-818 DOI: 10.1086/648458

Stevens, J., & Beckage, B. (2009). Fire feedbacks facilitate invasion of pine savannas by Brazilian pepper New Phytologist, 184 (2), 365-375 DOI: 10.1111/j.1469-8137.2009.02965.x

Ecosytem Engineering and Fire Ecology, Part 3

The closing paragraph of ‘Nature, Red in Tooth and Flame Part-2’ mentioned how extrinsic factors in the environment, such as the presence of increased atmospheric oxygen and an abundance of herbaceous plants to serve as fuel, collectively worked to generate frequent and intense wildfires during the Pennsylvanian Period approximately 300 million years ago. It was the presence of these Carboniferous wildfires that positively selected fire-tolerant gymnosperm species for continued development, and initiated their adaptive radiation towards the representative pine trees that occupy the modern-day savannas in the southeastern United States. It is within contemporary savannas that the longleaf pine (Pinus palustris) and the southern slash pine (Pinus elliottii var. densa) express their fiery ancestry; however, the fire ecology observable in these natural communities isn’t limited to wildfires born of purely extrinsic factors. Through, evolution the longleaf and slash pines have developed the ability to intrinsically influence the movement of fire, and they have learned to use this powerful tool as an instrument for customized ecosystem engineering.

During the description of savanna communities in Part-2, it was detailed that the canopies of these systems exist in an open condition that allows for ample access to sunlight by a diverse range of groundcover plants. Ample sunlight, water and soil nutrients can all be found in savannas. So, considering the occurrence of these botanical prerequisites, compounded with the highly competitive, almost war-like, tendencies of nature (as elaborately described in Part-1), one might wonder why trees from the hammocks don’t advance to occupy the promising and resource-rich savannas… The reason for the limited progress of hammock trees in moving to the savannas is that invasions are tightly controlled by the few trees already inhabiting the systems – the few trees usually being longleaf and slash pine.

An open canopy is a characteristic physiognomy of savannas precisely because the ground gaining charge of closed-canopy trees is impeded by the heirs of the Carboniferous gymnosperms. Said differently, the trials-by-fire endured by the antecedents of the modern-day conifers have shaped the phenotypes of the savanna-defending longleaf and southern slash pines. Furthermore, the phenotypes shown by the longleaf and slash pine reach outward to encompass the savanna as a whole, where these phenotypes serve as catalysts for engineering ecosystem towards one purpose – making more pine trees.

The longleaf and southern slash pine exhibit a host of morphological features that facilitate their continued manipulation of fire. For instance, both of these trees have thickly armored plates of bark on the exterior of their trunks; like fire-retardant shields, the plates guard the tree's interrior tissues against excessive heat and all but the most intense of wildfires. Similarly, the undifferentiated cells (meristematic cells) found within the trees, the ones that make-up the growth tissue found in meristems, are safeguard by a casing of heat resistant scales. And, as opposed to a pattern of wide lateral spreading, the roots of the slash and longleaf trees penetrate perpendicularly downward, where they are sheltered from harsh surficial temperatures. These are but a small number of the morphological – anatomical – traits displayed by the fire-scaping pines; their reproduction and growth habits give additional clues as to their natural history.



The reproductive cycle of the longleaf and southern slash pine include strategies that take into account the recurring spring fires described in Post-2; by germinating in the fall and occasionally producing periodic mast crops, young pines are afforded several months of growth before the first ravages of wildfire arrive. In spite of the head start gained through fall germination, the longleaf and slash pine don’t approach growth from a mere lackadaisical standpoint, quite the contrary, both trees posses the ability to quickly establish themselves. Just as the most successful plants of a closed canopy hammock battling for access to solar radiation (see the ‘competition for sunlight’ example provided in Part-1), the savanna pine trees – in addition to a ‘fire gene’ – also hold in their genetic arsenal a ‘rapid growth gene.’ Slash pine, for instance, has a genetic compliment that permits the tree to take advantage of every opportunity to seize real estate; once germinated, it rapidly shoots upward expressing secondary needles in less than six month’s time, and by the time it is two-years old, it is able to survive a wildfire of ‘average' intensity.

The above characteristics depict but a few of the intrinsic phenotypes that improve the survivability and reproduction of the savanna dwelling pines in the presence of fire; but what is truly remarkable is the trees’ ability to channel fire directly – the trees’ ability to shape their ecosystem through offensive tactics.

In addition to the defensive phenotypes of the savanna pines, the chemistry of their leaves (i.e. pine needles) have undergone adaptation such that while on the tree, the leaves produce flame resistant chemicals, but when the leaves are shed, their chemical consistency changes to achieve an altogether different effect - they become flammable and easily ignited. As the leaves are shed from branches, they fall to the ground where they accumulate around the circumference of the trees. The piled pine needles are composed of cellulose-laden fibers, which unlike the fire-resistant lignin that evolved during the Paleozoic, serve as excellent fuel for fires. So when on the tree, the pine needles are similar to the armored plates found on the trunks, they help defend against tissue damage when exposed to wildfire; but, in the absence of recurrent fire, the leaves are quickly dropped and their chemistry changes to promote fire. Moreover, pine leaves aren’t the only fire stoking property of the savanna pines. The very structure of the pine’s thin and supra-numerous branches can facilitate the spreading of fire (horizontally and vertically) through increasing the surface area of exposed tissues to flame. And, the flammable hydrocarbons produced in the plant’s resins can incite wildfires or encourage lightening strikes to take hold (for example, the terpenes produced by the conifers in question; think ‘turpentine’).

Though it may initially seem to be counterproductive, or a hindrance to survival, through promoting fires the savanna pines obtain benefits that actually enhance inclusive fitness….

[Continue HERE, PART-4.]


Beckage, B., Platt, W., & Gross, L. (2009). Vegetation, Fire, and Feedbacks: A Disturbance‐Mediated Model of Savannas The American Naturalist, 174 (6), 805-818 DOI: 10.1086/648458


Stevens, J., & Beckage, B. (2009). Fire feedbacks facilitate invasion of pine savannas by Brazilian pepper New Phytologist, 184 (2), 365-375 DOI: 10.1111/j.1469-8137.2009.02965.x

Fire Ecology and Cutthroat Ecosystem Engineering, Part 2

The phrase ‘ecosystem engineer’ refers broadly to the ability of an organism to change or modify the physical characteristics of its surroundings. When these environmental modifications resultantly impact the fitness of the engineering organism itself, the feedbacks created can be thought of as functioning like an extended phenotype. In other words, the feedbacks generated between the engineer and the ecosystem contribute to the reproductive success of the organism, and often (directly or indirectly) affect the life history of nearby competitors. In the closing line of ‘Nature Red in Tooth and Flame - Part 1’ the organisms adapted to use fire are personified as ‘cutthroat’ because they possess a genetic compliment that facilitates the shaping of their environment through a two-fold process that could easily be categorized as self-interested. Firstly, through harnessing fire these engineers are able to create a pattern of ecological disturbance that promulgates increased fitness; and secondly, the application of fire eliminates resource pilfering opposition via direct incineration. But, prior to detailing the precise methods in which ecosystem engineering plants employ fire, it is important to set the stage with a description of the battlefield – the savanna community.

In the southeastern United States savannas are typically found on relatively low topographical gradients with poorly drained soils and ample soil nutrients. Similar in biological composition to hydric flatwoods communities, savannas characteristically differ in regards to tree abundance and exhibit a relatively open canopy with a thin understory and a lavish herbaceous groundcover. Both savannas and hydric flatwoods rely on seasonal rain and fire cycles in order to maintain their soil chemistry, floral diversity and faunal components. Yes, these communities depend on fire cycles…

Prior to modern anthropogenic intervention, and the suppression of natural, seasonally occurring fire cycles, the forests, prairies and savannas of the southeastern United States experienced regular ecological disturbance by means of fire. Using Florida as an example, the annual climate cycle here is punctuated by alternating periods of relatively dry and wet weather. More specifically, the months of November through February represent the dry season and accordingly receive comparatively little precipitation. This dry season is followed by dramatically increased amounts of precipitation during summer with heavy rains and thunderstorms (particularly near the coasts) for the period including June, July and August. The spring season, February-through-May represents a transitional period from dry to wet; however the forthcoming summer brings with it thunderstorms; during this period lightening-strikes often ignite wildfires. The wildfires feed on the parched condition of desiccated plants – the wildfires thrive on the fuels remaining behind from the departing dry season. The regularity of this annual climate has resulted in a cyclic ‘fire season’ that has been recurrent for several millennia. The persistence of the fire cycle has thus contributed greatly to the structuring of local natural communities; however to understand the organismal biology of some of the fire adapted plant species a deeper gaze into evolutionary time is required. So, now that a cursory look at the battlefield has been made, a review of the actual players is in order.



Two exemplars of the fire wielding and ecosystem engineering life style are the longleaf pine (Pinus palustris) and the southern slash pine (Pinus elliottii var. densa). These trees both maintain genetic compliments – fire genes – that enable them to prosper in the flame frequented savannas of the southeastern United States. In order to appreciate the natural history of these organisms, a look at their evolutionary past is obligatory.

The longleaf pine (Pinus palustris) and the slash pine (Pinus elliottii) are two species of the genus Pinus (pine tree) which branched from genus Picea (spruce tree) during the Cretaceous Period, somewhere between 87 and 193 million years ago.


NOTE: There are two distinct varieties of slash pine, variety elliotti and variety densa, both of which can be found in southeastern U.S. and although there are several important distinctions, for purposes here both varieties can be considered one and the same, though the southern slash pine (var. densa) displays slightly greater levels of adaptation to fire.



Pine and spruce trees are grouped together with cycads, gnetophytes and ginkgo as gymnosperms, which had an initial start back in the Pennsylvanian Period of the Carboniferous more than 300 million years ago. The long history of the pine trees, and the slash pine in particular, is significant because these trees have one of the largest and most complex genomes of any organism on the planet today – a result of varied evolutionary forces. Of specific interest in regards to evolutionary history is that gymnosperms arose from the Carboniferous swamps during a period of rapid plant adaptation. In addition to the advent of the bark fiber “lignin,” plants during that period underwent a multitude of morphological changes - many of these changes were adaptations to wildfire. This was the case because unlike the 21% atmospheric oxygen present today, the carboniferous boasted 35% oxygen content, this in conjunction with an abundance of herbaceous material resulted in frequent – and intense – wildfires. Here, ‘intensity’ can be interpreted as being the ratio of a wildfire’s maximum temperature and duration; both of which can vary. The wildfires positively selected for those plant traits that phenotypically exhibited fire-tolerance, and the wildfires also actively worked to eliminate those plants that displayed fire-intolerant characteristics. Through this dualistic mechanism of natural selection, a long passed Paleozoic ecosystem worked to shape and mold the longleaf and the slash pines into masters of pyrogenic manipulation.


[This blog post continues here with installment Number 3.]



Beckage, B., Platt, W., & Gross, L. (2009). Vegetation, Fire, and Feedbacks: A Disturbance‐Mediated Model of Savannas The American Naturalist, 174 (6), 805-818 DOI: 10.1086/648458


Stevens, J., & Beckage, B. (2009). Fire feedbacks facilitate invasion of pine savannas by Brazilian pepper New Phytologist, 184 (2), 365-375 DOI: 10.1111/j.1469-8137.2009.02965.x

Nature Red in Tooth and Flame: Fire Ecology and Cutthroat Ecosystem Engineering

Renowned journalist, publisher and geologist Robert Chambers spent the majority of his 19th Century life actively engaged in two - often antagonistic - worlds, the world of science and that of the high-society Scottish elite. It may have been his struggle to maintain balance between these two worlds, one that valued rationality and meticulous observation, the other preferring political correctness and adherence to theological dictates, which helped guide him to the decision to anonymously publish his 1844 work ‘Vestiges of the Natural History of Creation.’ The work was truly progressive by almost any measure and it would go on to influence such diverse individuals as the scientifically minded Charles Darwin and the poetically endowed Alfred, Lord Tennyson.

It was a combination of Vestiges’ theological implications and the loss of a dear friend that motivated Lord Tennyson to pen the following stanza:

Who trusted God was love indeed
And love Creation's final law
Tho' Nature, red in tooth and claw
With ravine, shriek'd against his creed
(In Memoriam A.H.H., Canto 27)

‘Nature, red in tooth and claw’ is an often quoted metaphor for natural selection, and as such, it has been a recurrent theme here at Ecographica. During several previous posts, a harmonious – ‘all is in balance’ - view of nature was contrasted with the perspective of nature as a series of oppositional organisms struggling to gain a competitive edge over rivals. During these comparisons, the ‘red in tooth and claw’ view was the hands-down victor in all cases; being both more analytically accurate, and the more observationally sound perspective. As a case in point, two recently published articles, one appearing in the December edition of The American Naturalist, the other in the July New Phytologist have compelled the issuance of an update to a post made back in April; a post that emphasized the above described contrasting views of nature. Both of the published articles lend further credence to the conceptual “fire gene,” an idea coined in the April blog. One article supports the fire gene concept through development of ecological disturbance feedback models; the other tells the story of an invasive plant with a contrasting and adversarial phenotype to the one detailed in the original post, a phenotype that suppresses fire – it bears what can be called an “anti-fire gene.” As with the original blog post, the re-write begins in the Big Cypress Preserve, with a somewhat overly embellished lead-in…

Nature Red in Tooth and Flame
Gazing across the tranquil landscape of the Big Cypress Preserve, nature seems to be in balance, unchanging and at peace - picturesque beyond any poetic description. Within this serene setting, anthropogenic throngs of sharply angled concrete and glass edifices suspend their battle for roadside commercial dominance and yield themselves to a sea of sparsely treed savannas, rolling prairies of grass, and randomly scattered islands of thickly vegetated hammocks. It’s the perfect environment for a relaxing stroll, a picnic, or, an inquiry into the natural world...

All may appear calm within this enchanting panorama with its diverse array of plants, animals and abiotic ornamentation; however, this perceived tranquility is but a chimera. It is a mere illusion of serenity resulting from shortfalls in the ability of the observer’s photoreceptors to see beyond that narrow range of the electromagnetic spectrum called visible light, an inability to hear sound outside of 22000 Hertz, and the failure of the human olfactory system to nose its way into the vast chemo-landscape of pheromones and other volatile chemicals in which it is continuously assailed. Indeed, if only the sensory apparatus of Homo sapiens was keener – if only it was more finely calibrated – the landscape of the Big Cypress would be seen for what it truly is… How very different it would seem.

Picture taken from Turner river Rd - Big Cypress Preserve

Very different indeed; imagine the ecological interplay that could be interpreted if humans could see ultraviolet light through the eyes of a bee, smell pheromones from six-miles’ distance like a moth, or interpret chemical stimuli through soil like a plant… Far from serene, if viewed through time, adaptive maneuvers, survival strategies and arms races would be manifest in every action undertaken by the immense diversity of organisms in the landscape. If these actions could be viewed more directly, if they could be seen in greater detail, the landscape would appear saturated with war; from the birds in the sky to the millions of soil bacteria underfoot, mortal conflict - not harmony - would be identified as the prime mover. Even the distribution of the apparently benign flora, the very plant community boundaries that demarcate prairie-from-savanna-from-hammock in the above described landscape, is maintained by way of fierce battles waged over evolutionary time. These ecosystems, which appear stable and so pleasingly haphazardly scattered, are in fact hordes of competing plants, all struggling for limited resources and their continued existence. It is in these contested boundaries that conflicts incessantly rage, and it is within these envied ecotones that one species has honed a new weapon – it has undergone adaptation to exploit the power of fire.

Before getting to the exploitation of fire, it is important to understand that natural plant communities exist in a continuum of environments and have adapted to inhabit almost every available niche on the planet; from “box thorns” in Death Valley to fully aquatic hyacinths floating around the lakes of Brazil, genetic plasticity in plants is clearly evidenced as a product of natural selection. And although the conquest of diverse habitats represent a surmountable challenge, a multitude of both biotic and abiotic factors conspire to determine the overall abundance (density), composition (diversity) and ultimate success of plant communities at any given location.

For example, looking across the landscape of the Big Cypress, densely concentrated hardwood trees form hammocks which, due to the broad area of their collective canopies, limit the amount of sunlight available to underlying herbaceous groundcover. This is a straight forward relationship, no sunlight reaching the ground means fewer plants on the ground. Following this rationale, if the tree canopy should be opened, say by a storm, hurricane or by the death of older trees, this would permit sunlight to temporarily penetrate to the floor and a rapid emergence (recruitment) of both herbaceous plants and new saplings would be predicted. This is precisely what happens; in this example sunlight is the limiting resource and once made available those plants best able to take advantage of the situation through rapid growth will be able to quite literally overshadow their competitors. Stated differently, plants with genetic compliments favoring a period of ‘initial rapid growth’ are at an advantage and will be positively selected if positioned to compete for sunlight with a species lacking such a genetic compliment.

Similar to the botanical quarrels described for wooded hammocks - those in which plants have undergone selection for rapid growth - plants also engage in conflict to secure access to the resources offered by prairies and savannas. And, just as with the battles for sunlight on the forest floor, contenders occupying hammock-savanna ecotones have evolved specific defensive and offensive phenotypes to aid in their advance; as alluded to earlier, a few have even acquired the ability to harness the power of fire. Like the genetic compliment that allows a plant to undergo a period of initial rapid growth when a break in the hammock’s canopy becomes manifest, some plants possess a genetic compliment that allow for direct modification of local ecology. In short, the genetic compliment allows the plant to apply heat and flame in a cutthroat effort to destroy competitors, and to assert themselves as ecosystem engineers.


[The second installment of this post is available HERE.]



Beckage, B., Platt, W., & Gross, L. (2009). Vegetation, Fire, and Feedbacks: A Disturbance‐Mediated Model of Savannas The American Naturalist, 174 (6), 805-818 DOI: 10.1086/648458


Stevens, J., & Beckage, B. (2009). Fire feedbacks facilitate invasion of pine savannas by Brazilian pepper New Phytologist, 184 (2), 365-375 DOI: 10.1111/j.1469-8137.2009.02965.x

Poor Conservation or Good Business?

(This post has been temporarily removed for revision)

Reiss, K., Hernandez, E., & Brown, M. (2009). Evaluation of Permit Success in Wetland Mitigation Banking: A Florida Case Study Wetlands, 29 (3), 907-918 DOI: 10.1672/08-148.1

The Future of Biodiversity Research

I decided to take a short break from scratching my chigger bites to recommend a paper on ecology. The paper reviews the links between biodiversity and ecosystem function, and does an excellent job of clarifying some of the commonly held misconceptions about species diversity.

For instance one of the diversity flavored misconceptions that I encounter on a regular basis centers on the notion that species richness (the count of the different species present at a given location) is the preeminent indicator of ecological stability, quality or “value.”

Yes, richness is absolutely an important measure of a system’s health, however it is just one metric, and even if – during an assessment - one is able to identify a species list two-miles long, there are other factors that need to be considered prior to making a “value – based” determination. After all, the study of ecology should center on evaluating the processes, cycles and organismal traits that drive the actual functionality (energetics, nutrient processing, trophic interactions, etc…) of the system at hand.

It’s all about the interactions.

In other words, although having a large variety of species in an ecosystem is generally a good thing, there is always going to be some redundancy built in; some species have a higher “value” than others, some contribute less to the foodweb, some more…

So, is diversity important - yes! But not only diversity in nominal place holders, what’s important is a diversity of ecological functions. Do the traits of those present facilitate the system? Are there traits lacking in the system that, if present, would bring enhancement? What are these traits, and how can they be measured?

The recommended paper:
Reiss, J., Bridle, J., Montoya, J., & Woodward, G. (2009). Emerging horizons in biodiversity and ecosystem functioning research Trends in Ecology & Evolution, 24 (9), 505-514 DOI: 10.1016/j.tree.2009.03.018

NOTE: I don’t intend the above to deride any particular species; all have ecological “value” beyond the aesthetic. My point is simply that the concept of species diversity and its associated measure, species richness, can sometimes be mishandled.

Sort of a minor pet peeve of mine, like ecologists that think of ecological succession as a predetermined, unavoidable “potential” towards which all communities strive. This, despite the conflicting and limiting physical conditions in which the community currently resides; but that’s another rant...