Tag Archives: Conservation

Why Conservation? Communicating Applied Biodiversity Science Updated for 2026

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Applied Biodiversity Science Program – Texas A&M University

You might have a favorite science writer. Mine are David Quammen, Bill Bryson, Carl Sagan, and Tim Flannery. Others may be more inclined to read Pulitzer Prize-winning and nominated authors like Jonathan Weiner, Siddhartha Mukherjee, or James Gleick, MacArthur-fellow Atul Gawande, or consummate greats like E. O. Wilson, Richard Dawkins, Stephen J. Gould, and Oliver Sacks. Or perhaps books aren’t all you’re interested in. In that case you may be a fan of Carl Zimmer’s blogging or the stories and editorials from journalists/authors Malcolm Gladwell or Stephen J. Dubner.

It’s likely you’ve read at least one of these authors. Like most readers you were probably impressed by how well they articulated the complexities and subtleties of their topic: everything from astrophysics to evolution, cancer, neurology, chaos theory, economics, and psychology. If you find an author who draws you into a topic that wouldn’t otherwise gain your attention, particularly an unfamiliar scientific discipline, take notice. Take stock of what they have accomplished by gaining your interest and curiosity. As George Gopen and Judith Swan stated in their 1990 for American Scientific, “the fundamental purpose of scientific discourse is not the mere presentation of information and thought, but rather its actual communication.” Good communication requires gaining the reader’s attention. Attention requires garnering interest and curiosity.

In our ever-connected world with vast communication and social networking ability, we have the ability to do just that. We possess the tools to communicate science to a diversity of people in a diversity of ways.

As a member of the Applied Biodiversity Science Program (ABS) at Texas A&M University I find myself in a position where communicating science is an imperative for success. The ABS program is graduate program originally funded by the National Science Foundation as part of their Integrative Graduate Education and Research Traineeship (IGERT) program. The principle mission of ABS at Texas A&M is to achieve integration between biodiversity research in the social and natural sciences with on-the-ground conservation practices and stakeholders.

To that end, a foundational component of ABS is to communicate across scientific disciplines with various institutional actors to facilitate broader impacts across the realm of conservation. In essence, the ABS Program seeks to produce applied scientists who can communicate effectively across disciplines. A natural corollary of this goal is the ability to communicate science outside the realm of science. In this respect, our ABS Perspectives Series is intended to communicate more broadly and inclusively who applied biodiversity conservationists are, what we study, where we conduct research, how we conduct research, and why we are doing it. The current issue of the ABS Perspectives Series, features experiences from the Caribbean, the United States, Sénégal, Ecuador, Nicaragua, and Costa Rica. Contributions cover topics ranging from captive parrot re-wilding with pirates to blogging in the Nicaraguan forest with limited Internet access.

Perhaps more importantly, the ABS Perspective Series wants to reach out and share ABS student and faculty experiences with a diverse readership to raise awareness of biodiversity conservation issues. Outreach is an important axiom of actionable science, especially outreach that informs, improves and influences management and policy. I consider both the ABS Perspectives Series and BioDiverse Perspectives outreach initiatives to communicate the biodiversity conservation mission to the general public, communities where our research has been conducted, fellow academics and practitioners, and institutions that can provide logistics, infrastructure, and support. We must intend to make and practice making our research accessible and intriguing to everyone.

November 18, 2014

Five ways to stop the world’s wildlife vanishing Updated for 2026





Full marks to colleagues at the World Wildlife Fund and the Zoological Society of London for the Living Planet Report 2014 and its headline message which one hopes ought to shock the world out of its complacency: a 52% decline of wildlife populations in the past 40 years.

Over the summer I re-read Fairfield Osborne’s 1948 classic Our Plundered Planet – the first mass-readership environmental book that detailed the scale of the damage humanity wrought on nature.

Faced with the figures in this report it is easy to slip into despondency and to blame others. But this would be a mistake. At the time, Osborne’s report must have been equally alarming, but the eclectic conservation movement of which he was part responded with confidence, hope and vision.

Their achievements were huge: the creation of a reserve network that forestalled the extinction of African creatures such as the elephant and rhino; the creation of a nature conservation agency, the International Union for Conservation of Nature) (IUCN) within the UN; and a raft of international wildlife agreements.

But what can we do now?

Today, conservation-minded people will probably be wondering what can be done to reverse wildlife declines.

For me the question is: how can today’s conservationists leave a wildlife legacy for the 21st century? I think there are five ways we can change conservation to better fit the circumstances we face.

1. Decentralise and diversify

The effort to ensure that nature conservation became a policy area of the UN necessitated developing a strong international conservation regime.

This has served us well, but the world has changed: centralised authority has given way to messy, networked governance organised across many levels.

If the Balinese want to restore Bali Starling populations in coconut plantations I say applaud their vision and learn from their innovation.

What matters is that wildlife populations flourish, not that some institutionalised notion of a ‘wild species’ gains global consensus. It is time to nurture diversity in conservation practice.

2. View wildlife as an asset

Since the 1990s conservation has become overly technocratic, with nature framed as a natural resource and stock of capital available for human economic development. Given human self-interest this just leads to arguments over who gets what share.

I suggest a better way to frame environmental policy is in terms of natural assets – places, attributes and processes that while representing forms of value to invest in, are also at risk of being eroded and must be protected.

We’ve done this before – think of great national parks where wildlife conservation, natural beautification and outdoor recreation combine for the benefit of wildlife, while also emphasising regional or national identity, health and cultural and economic worth.

3. Embrace re-wilding

Re-wilding is gaining traction. I see re-wilding as an opening, an opportunity for creative thinking and action that will affect the future.

A key theme is restoration of trophic levels – in which the missing large animals at the top of the food chain are reintroduced, allowing natural ecosystem processes to reassert themselves.

We might ask whether today’s reported declines in wildlife are a symptom of the ecosystem becoming more simple and, if so, whether re-wilding will lead to more abundant wildlife. Ecological intuition suggests the latter but in truth we don’t know.

In my view we need large-scale, publicly-financed re-wilding experiments to explore and develop new ways of rebuilding wildlife populations as an asset for society.

4. Harness new technologies

It’s clear that wildlife conservation is moving from being a data-poor to a data-rich science. The methods that underpin the Living Planet Report are state-of-the art, but even so we have yet to capture the analytical potential of ‘big data’.

Recent rapid developments in sensor technologies look set to bring about a step change in environmental research and monitoring.

In ten year’s time, I predict that the challenge for indexing the planet will shift from searching out and compiling data sets to working out how to deal with an environmental ‘data deluge’.

Despite this, wildlife conservation lacks a coherent vision and strategy. There are plenty of interesting technological innovations, but they are fragmented and individualistic in nature. We need leadership and investment to better harness them.

5. Re-engage the powerful

Like it or not, the wildlife conservation movement was at its most influential – as a policy and cultural imperative – when it was filled with active members drawn from the political, aristocratic, business, scientific, artistic and bureaucratic elites.

This was between 1890 and 1970. Over the past 40 years conservation organisations have become more professional, building close working relations with bureaucrats, but approaching other elites simply as sources of patronage, funds and publicity.

Conservation organisations must open-up, loosen their corporate structures and let leaders from other walks of life actively contribute their opinion, insight and influence to the cause.

But above all, keep caring

These are five starting points for discussion rather than prescriptions. Perhaps the greatest asset we have is the deep-rooted sense of concern for wildlife found across cultures, professions and classes.

It’s time to open up the discussion, to put forward new ideas for debate, and to ask others to suggest new and novel ways to save wildlife.

 


 

The report: Living Planet Report 2014.

Paul Jepson is Course Director, MSc Biodiversity, Conservation and Management at the University of Oxford. He does not work for, consult to, own shares in or receive funding from any company or organisation that would benefit from this article, and has no relevant affiliations.

This article was originally published on The Conversation. Read the original article.

Also on The Ecologist

 

The Conversation

 




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Deconstructing Defaunation Updated for 2026

Many species globally are threatened by numerous biotic and abiotic stressors, resulting in declining population and shifts in ecosystem functioning.

Many species globally are threatened by numerous biotic and abiotic stressors, resulting in declining population and shifts in ecosystem functioning.

Science recently released a special issue on defaunation, which spanned seven articles detailing the recent decline in animal species diversity and abundance.  Among others, the issue included two peer-reviewed articles, an opinion piece, and an analysis of national policies tied to global and local conservation strategies.  The statistics associated with defaunation are sobering, but the issue presents a few solutions to help us curb this global environmental crisis.

First, a damage assessment.  According to Defaunation in the Anthropocene, between 11,000 and 58,000 species go extinct each year.  At least 16% of all vertebrate species are endangered or threatened, and there’s been a 28% decline in their abundances since the 1970s.  Approximately 40% of invertebrate species are considered threatened, though less than 1% of described invertebrates have been assessed.  There is data to suggest that invertebrate species’ abundances are also decreasing, but it’s difficult to put an exact number on that decline since they are not as well monitored as vertebrates.  On a global scale, these statistics may be underestimated because our monitoring practices bias our data toward specific taxa.  Groups of large and charismatic organisms, like mammals and birds, get most of the attention because they are easier to monitor and more sympathetic than invertebrates, amphibians, and reptiles.  In some systems this is beneficial, where large mammals and birds are the most threatened and contribute significantly greater function to an ecosystem than smaller organisms.  However the opposite can be true in other instances, so it is critical that we prioritize greater sampling of underrepresented groups.

Additionally, there is concern that such measures of declines in species and abundance may not reflect the true extent of our ecological troubles.  Shifts in ecosystem compositions may not be reflected in a given measurement of biodiversity, yet are nonetheless indicative of environmental change.  The primary goal behind many conservation strategies has been to restore a species or population to a certain number.  While population viability is critical for any species, the authors argue that ecosystem functionality is a useful yet underutilized goal for conservationists.  With this goal, the composition of an ecosystem (i.e. the identity and abundance of resident species) can be more flexible, as long as the ecosystem functions in a similar way.  The issue with this then becomes how to measure ecosystem function, or rather, against what do we compare it?  Do we set an arbitrary time in history that we would like to restore it to, or do we attempt to maintain its function while integrated with a unique environment managed by humans?  Some proponents of the latter strategy see historical comparisons as unrealistic and uninformative, especially given our changing climate.  Regardless, restoring the functionality of ecosystems is a key predictor of the future success of not only animal and plant populations, but the human population as well.

One of the strongest arguments this issue makes derives from its use of specific economic values of animals and ecosystems.  According to the article Wildlife decline and social conflict, the harvest of land and sea animals accounts for $400 billion annually around the world.  Defaunation in the Anthropocene claims that pest control by native U.S. predators is worth approximately $4.5 billion annually, and that the decline in North American bat populations (a specific type of pest controller) has cost the agriculture industry $22 billion in lost productivity.  Insect pollinators are required for about 75% of the world’s food crops, and are therefore responsible for approximately 10% of the economic value of the entire world’s food supply.  According to the World Bank, food and agriculture represents about 10% of global GDP, which in 2012 was estimated at $72 trillion.  If we take total food supply to be approximately $7.2 trillion (again, estimating), then insect pollinators are worth around $72 billion dollars.  These estimates apply tangible figures to a broad and occasionally overwhelming issue, and may be good starting points to unite many different stakeholders under a common currency.

The article Reversing defaunation: Restoring species in a changing world details the different strategies conservationists use to preserve species abundances and their associated ecosystem functions.  These strategies can broadly be grouped into two categories, translocations and introductions.  Translocations involve moving individuals within their indigenous range to either reinforce a local population or to reintroduce them following a local extinction.  Introductions, on the other hand, move species outside of their indigenous range to prevent a global extinction of a species or to replace a lost ecosystem function.  Though planning a conservation strategy in terms of these labels can be useful for setting long-term goals, they are not mutually exclusive.  Certain strategies can incorporate aspects of both translocation and introduction, or can introduce a species both to preserve its numbers and to restore ecosystem functionality.  Therefore, it’s best to use these terms as guidelines for how to measure the success of any plan rather than as constraining requirements.

These losses in biodiversity, and their associated shifts in ecosystem functioning, are primarily driven by a combination of over-hunting, habitat destruction, impacts of invasive species, climate change, and disease.  The Defaunation articles make a point of addressing national policies aimed at preventing species extinctions, namely those regarding over-hunting and poaching.  Many of these policies simply impose penalties for illegal hunting rather than address the underlying causes of the issue, poverty and starvation.  While it’s unrealistic to expect a conservation plan to alleviate world hunger and income inequality, it may be useful to consider animal overexploitation as an unintended side-effect of the economic cycle caused by scarcity.  Supply and demand states that as a species becomes less common, its value on the market rises.  However, this scarcity also leads to a reduction in the amount caught per unit effort.  The rise in price drives a greater hunting effort by the sellers, further decreasing the population, and the cycle begins again.  Since many of these hunters are using their profits to feed themselves or their families, simply enacting penalties for poaching may not have the intended effect.  Overhunting is not a simple problem, and most likely will not have a simple solution.  However, the only way we can begin to address it is by determining its causes.

September 30, 2014

Botswana government lies exposed as $5bn diamond mine opens on Bushman land Updated for 2026





A $4.9bn diamond mine opens tomorrow in the Central Kalahari Game Reserve (CKGR), the ancestral land of Africa’s last hunting Bushmen – exactly ten years after the Botswana government claimed there were “no plans to mine anywhere inside the reserve.”

The Bushmen were told they had to leave the reserve soon after diamonds were discovered in the 1980s, but the Botswana government has repeatedly denied that the illegal and forced evictions of the Kalahari Bushmen – in 1997, 2002 and 2005 – were due to the rich diamond deposits.

It justified the Bushmen’s evictions from the land in the name of “conservation”.

In 2000, however, Botswana’s Minister of Minerals, Energy & Water Affairs told a Botswana newspaper that the relocation of Bushmen communities from the Central Kalahari Game Reserve “is to pave way for a proposed Gope Diamond Mine.”

And in 2002, the Bushmen told Survival International: “Foreign Minister General Merafhe went to the reserve and told us we had to be moved because of diamonds.”

The mine opening has also exposed Botswana’s commitment to conservation as window dressing. The government falsely claims that the Bushmen’s presence in the reserve is “incompatible with wildlife conservation” – while allowing a diamond mine and fracking exploration to go ahead.

Khama’s government has also been heavily promoting tourism to the CKGR while driving the Bushmen off their land.

Half the CKGR opened up to fracking

Botswana has opened up large parts of the CKGRto international companies for fracking, it was revealed last year in the documentary film The High Cost of Cheap Gas.

A leaked map shows that exploration concessions cover half of the CKGR – a reserve larger than Switzerland – raising fears of land grabbing, a drop in water levels, water pollution and irreparable damage to a fragile ecosystem essential for the survival of the Bushmen and the reserve’s wildlife.

Licenses have been granted to Australian Tlou Energy and African Coal and Gas Corporation, without consulting the Bushmen.

While Botswana’s government has denied any fracking in Botswana, Tlou has already started drilling exploratory wells for coalbed methane on the traditional hunting territory of the Bushmen.

CKGR Bushman Jumanda Gakelebone said: “The government is doing everything it can to try to destroy us … Fracking is going to destroy our environment and if the environment is destroyed our livelihoods are too.”

Hypocrisy personified: Botswana’s President Ian Khama

Botswana’s dash to develop extractive industries in the Kalahari, and its abuses the the indigenous Bushmen, are plenty bad enough in their own right.

But adding insult to injury, Botswana’s President Ian Khama is widely feted as a great conservationist. In 2010, the UK’s Princes William and Harry paid Khama a visit in Botswana in support of the Tusk Trust, which supports various African conservation projects.

And Khama is a board member of Conservation International, the US-based NGO. CI and other conservation organizations have heralded Khama’s conservation efforts – while remaining silent on the persecution of the Bushmen and mining and fracking in the CKGR.

A Bushman whose family was evicted told Survival, “This week President Khama will open a mine in the Central Kalahari Game Reserve. Do those organizations who have been awarding President Khama for his work with the flora and fauna still believe he is a good example to the world?

“The residents of the Reserve are not benefitting anything from the mine. The only benefits go to communities living outside the reserve, while our natural resources are being destroyed. We strongly oppose the opening of the mine until the government and Gem Diamonds sit down with us and tell us what we will benefit from the mine.”

‘Poaching’ on their own land

The government continues its relentless push to drive the Bushmen out of the reserve by accusing them of “poaching” because they hunt their food.

The Bushmen face arrest, beatings and torture, while fee-paying big game hunters are encouraged. The government has also refused to reopen the Bushmen’s water wells, restricted their free movement into and out of the reserve, and barred their lawyer from entering the country.

Survival’s Director Stephen Corry said: “When the Bushmen were illegally evicted from their ancestral homelands in the name of ‘conservation’, Survival cried foul play – both we and the Bushmen believed that, in fact, diamond mining was the real motivation for kicking the tribe off their territory.

“Forced evictions of Bushmen from the CKGR have nothing to do with conservation and everything to do with paving the way for extractive industries to plunder Bushman land. Why does President Khama continue to receive prizes for his ‘conservation’ efforts?

“It’s an absolute scandal that Conservation International accepts on its board a man who has opened up the world’s second biggest wildlife reserve to fracking, whilst persecuting the Bushmen whose home it is in the name of conservation.”


Diamond mine timeline

Early 1980s – A diamond deposit is discovered in the Central Kalahari Game Reserve within the territory of the Bushman community of Gope.

12 October 1986 – Botswana’s Minister of Commerce and Industry, Mr Moutlakgola Nwako, announces the government’s decision to relocate the Bushmen.

1996 – A formal evaluation of the mine is completed.

May 1997 – First evictions of Bushmen from the Central Kalahari Game Reserve take place.

1997 – Anglo American drills two exploratory holes in the reserve.

31 August 1997 – Anglo American (the majority shareholder in diamond company De Beers) “denied any knowledge of its activities within the reserve” to South African paper ‘Sunday Independent’.

1999 – Mineral exploration camps are set up a few miles from the Bushman community of Molapo.

July 2000 – Botswana’s ‘Midweek Sun’ reports that Botswana’s Minister of Minerals, Energy & Water Affairs, Boometswe Mokgothu, told Ghanzi District Council that “the relocation of Basarwa (Bushman) communities from the Central Kalahari Game Reserve is to pave way for a proposed Gope Diamond Mine.”

2001 – In its draft management plan for the Central Kalahari Game Reserve, Botswana’s Government Department of Wildlife and National Parks (DWNP) writes, “DWNP should continue to point out that mining is incompatible with the Game Reserve’s objectives.”

2002 – Bushmen tell Survival, “Foreign Minister General Merafhe went to the reserve and told us we had to be moved because of diamonds.”

2002 – A second wave of Bushman evictions from the reserve. The Bushmen’s water borehole is destroyed.

7 November 2002 – President Festus Mogae claims, “the program of assisted relocation of Basarwa (Bushmen) from areas of the Central Kalahari Game Reserve … was in no way related to any plan, real or fictitious, to commence diamond mining in the reserve.”

2004 – The Botswana government releases a statement which claims: “There is no mining nor any plans for future mining anywhere inside the CKGR as the only known mineral discovery in the CKGR, the Gope deposit, has proven not commercially viable to develop the mine.”

2005 – Third wave of Bushman evictions from the Central Kalahari Game Reserve.

2006 – The Bushmen win their historic case against the government. High Court Judge Justice Dow states that the Bushmen were evicted “forcibly, unlawfully and without their consent.”

May 2007 – De Beers sells its deposit at Gope to Gem Diamonds, for $34 million. Gem Diamonds’ chief executive calls the Gope deposit “a problematic asset for De Beers” because of the Bushman campaign.

5 September 2014 – Gem Diamonds’ official opening of the Ghaghoo (formerly Gope) mine worth an estimated $4.9 billion. The mine lies within the territory of the Gope Bushmen and just 3.2 kilometers from their community in the Central Kalahari Game Reserve.

 


 

Oliver Tickell edits The Ecologist.

Principal source: Survival International.

 




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Diverse Introspectives: a conversation with John Harte Updated for 2026

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Some may know UC Berkeley professor John Harte from his work developing the MaxEnt Theory of Ecology (check out July’s TREE for an accessible pedagogic overview), others may be more familiar with his long-term research on the effects of climate warming. Older readers likely recall his 1988 classic book on environmental problem solving named after an improbably shaped bovine. I had the opportunity to meet and chat with John at the recent Gordon Research Conference on Unifying Ecology Across Scales, where he and Mike Sears gave very interesting and divergent opening talks on how ecologists might bridge the problem of scale for a more productive science.

The very most important thing to me, being a scientist, is to seek out unification- to look for simplicity where initially we see nothing but complexity, and to see the underlying general principles that govern the phenomena of interest. In ecology we have a wealth of phenomena… everywhere we look we see uniqueness, but being a scientist I refuse to accept that and I look for what general underlying patterns and principles govern this wealth of phenomena. And so, to seek that, I love looking at huge databases and I love walking in the woods and observing patterns and the details. But, my major approach to seeking unification is to develop fundamentally-based theory.

I know a lot of people in ecology love to make models of phenomena. You see some behavior, you see a particular species dwindling in numbers on the edge of extinction and so you make a model of that phenomenon. Or, you see a funny pattern where you see some sort of regularity in who’s associating with whom, and so you build a very mechanistic process-based model to explain that behavior. Out of the thousands of possible traits and mechanisms that might be working, we use our intuition and pick two or three that we think are important and then we build a mathematical model and it’s got parameters so we show that if we pick the parameters right we can explain the behavior. I find that totally uninteresting. That is not what I do. But it does characterize a lot of good and important work in ecology. It’s just not personally what turns me on. What does turn me on is seeking out very general principles that must be true from which very general conclusions can be based, which can be tested, which are falsifiable, and which potentially, if the theory is right, can explain a huge amount of information.

As an example, I’ve always been very interested in species-area relationships. I think they encapsulate a huge amount of information. Now, if you look at all the known species-area curves in the world, of everyplace where somebody’s gathered species-area data, and you plot them all on one big piece of graph paper- log species vs. log area, you will find that the data points fill the graph almost completely. You get every possible behavior when you just do a plot of log S vs log A. There’s no regularity. I didn’t really think that had to be the case. What I learned from developing the theory of macroecology based on the maximum-information entropy principle, is that the theory makes a very startling testable prediction about the shape of the species-area relationship. It says that if you take any species-area curve and you plot the local slope of the log-log plot, what we call ‘z’, at any scale against a certain scaling variable that the theory identifies, namely, the number of individuals at that scale divided by the number of species at that scale, all species-area curves should collapse onto a single universal curve. And it turns out that they do. If you look at every species area curve in the world, there are no exceptions. Even ones that involve microbial species-area relationships like the one my former student Jessica Green developed. So we think we understand the species-area curve. It’s not a power-law- it obeys a universal scale-collapsed behavior which theory, not a model, predicts. To me that was a significant break-through, to be able to see that all species-area curves fall onto one universal curve if you re-plot it correctly. And the neat thing is, it’s not just something we guessed. The theory told us we had to re-plot this way.

It’s been a theme. When I was a kid, my major interest was bird-watching and natural history. I collected everything I could collect. My bedroom as a kid was a museum. It was extraordinarily overstuffed with fascinating little things I would find. I would catalog them and arrange them and study them. But even then I remember thinking, “where’s the simplicity behind all of this detail?” I went into physics partly because I thought that that was a branch of science where you could freely exercise this desire to seek universality, generality and unification. Physicists are very open to that goal- that’s what they do. My first faculty position was at Yale University and I realized 6 or 7 years after my PhD that I really wanted to go back to what I loved the most, which was biology and especially ecology. So I left the physics department and took a job as an ecology professor at Berkeley in the early 1970s and I’m very glad I did it. But, I’ve been pursuing that same theme, that same interest, all the way through, from childhood birdwatching to physics and back to ecology.

No, it was a very specific thing. During the Vietnam War, I co-organized a day of teach-in’s about the war, where we shut down all the science classes at Yale and we brought in speakers to educate ourselves, the faculty and the students, about the war. At that event one of the people I invited was a very famous physicist, a Nobel laureate who had gone to Yale as an undergrad, and at the dinner of the teach in, he asked me if I would be interested in joining a small group of physicists who were going to try to do something about environmental issues- take a summer or a year off from regular physics and see if we could make some headway. So we did. We studied a problem in the everglades of Florida, where there was a proposed super-sized jetport being planned to land the super-sonic planes that we thought we were going to build. So we studied the Everglades. We took 3 months and did nothing but immerse ourselves in the problem. I ended up writing a paper with a colleague that looked at what would happen if you drained all the marshes in central south Florida where the big jetport complex would be. We were able to show with a little bit of physics that it would lead to salt intrusion into the water supplies of over half a million residents of the Gulf Coast of south Florida. That reached the desk of the secretary of transportation who said to Nixon, who was president at the time, “We can’t build this jetport- we can’t throw away Florida in the election, and you will if you destroy the water supply of half a million voters.” So they canceled the jetport. So I actually got back into ecology with the major goal of doing very practical applied work to prevent other disasters, like wrecking the Everglades. But then as time went on I got more and more interested in big theoretical questions.

Great question! I have a post-doc, Justin Kitzes, a brilliant guy, who is doing exactly that (see ‘Continuing the Conversation with Justin Kitzes’). His main interest in conservation biology, but he’s really a good theorist too. So he’s been taking the predictions of maximum entropy theory and applying them to very practical questions. Questions like, ‘What is the magnitude and origin of this ‘so-called’ extinction debt?’, and ‘How many species do we lose if we deforest a portion of the Amazon?’ People have realized from way back that the species-area relationship has something to do with that, but now that we know the true behavior of the species-area curve, we can very accurately estimate species loss under habitat destruction, or under loss of climatically suitable habitat. Another question that Justin and I have been looking at that is not exactly a conservation issue, although people have been fascinated by it, is ‘How many species of beetles are there in the Amazon?’ All we know is that we’ve labeled about 1.8 million species total, but we think there are way more than that. We have a paper in review right now that projects out from small plot data using the species-area prediction, what the species richness is at very large spatial scales. So we make predictions and they may or may not be of conservation value, but I think it is useful to have a measure, to have a sense of how diverse our planet is.

I think science progresses from failure not from success. It’s failure that drives science forward. For example, when there’s a discrepancy in something that we always thought we understood and then realize our theory is incompatible with some new phenomena, and we say, “That theory is not correct!” And that’s what make science move forward. That’s how progress happens. So, my view is that, there is nothing more important, nothing we should look forward to more than discrepancies between our favorite theories and reality. Because then we improve. We figure out what the next step is.

A very famous example in physics was the ideal gas law, PV = nRT. It’s a very basic idea from thermodynamics and it’s a beautiful law, but it actually fails at very high pressure and very high temperature. Its failure led physicists to realize that there was something called dipole-dipole forces between molecules, a very important thing in physics. And it was only from the failure of a prediction that they were led to discover this mechanism. Openness to failure and being willing to revise, upgrade, and form the next-generation theory is very very critical. So that’s what not marrying your theory means, don’t get so wedded to it that divorce looks impossible. As far as how that idea helps connect people to biodiversity, I’m not sure it does because we are in a sense all married to biodiversity. Biodiversity is what drives the human economy. Ecosystem services are dependent on diversity and the human economy is dependent on ecosystem services, and we should think of that as a catholic marriage that you can’t get out of. You can’t divorce yourself from the natural world. Unfortunately, civilization acts as if it’s trying to divorce itself from biodiversity and nature.

Oh boy, don’t get me started… It’s actually appalling how little math and physics ecology students have. Not all, some come in very well prepared. But, I firmly believe that departments of ecology and evolution should be requiring more of their students to take at least one theory course with mathematical methods, stochastic modeling, more than just the basic Lotka-Voltera equations, which is about all most ecologists ever learn. I mean, those equations are sort of a good laboratory for introducing oneself to quantitative reasoning, but stopping there is not adequate. We require a good deal of statistics on the part of our students, but that’s not the most important kind of math. Students should also be learning stochastic mathematics and probability theory, using differential equations to study things like stability. There’s so much confusion about these things and if students were better educated it would make for better grad students.

I see a couple of risks on the horizon. One of them is the ease with which we can simulate numerically and handle massive data sets. There is a risk that this will divorce people from what really matters, which is the natural world. Ecologists who are incredibly adept at manipulating data and running simulations, but who never just walked in the woods, observed and in their minds sorted and catalogued the things that they are seeing, those students have a great handicap in the long run. Separation from the natural world because the silicon world is so easy to enter- that’s very dangerous. The other dangerous thing is that we get obsessed with mechanistic tinker-toy models and do not look beyond to the broad fundamental theory, which doesn’t require computer adeptness or capacity to manage big data sets or simulate numerically. Fundamental theory really is more a matter of thinking through things than running amazingly complicated programs. Think of three vertices on the triangle. There’s the real world, nature, there’s what I call theory, and there’s the silicon world. I’d like to see people spend most of their time on the leg between the theory vertex and the real world vertex and only when you are forced kicking and screaming, go to the silicon world and simulate.

From general laws flow absolutely bullet-proof insights and this is what we most need. To the extent that ecology can be based on broadly applicable laws, not models based on arbitrary choice of dominant mechanisms (which everybody will argue about until the cows come home), if you can base insights and predictions on laws, they are irrefutable and that’s how science can best influence policy. Ecology is not in good shape when it comes to influencing policy. For example, if an asteroid is going to hit the planet, congress will call upon and believe the physicists who can calculate the likelihood of impacting when, and maybe even what to do about it, because those physicists can base their statements on fundamental laws. Ecologists don’t get called or listened to when it comes to any big issue. We don’t have respect in policy circles because we haven’t figured out the laws of ecology. Instead we have a gazillion models of ecology, stories, and intuitions. Some of them are right, some of them are wrong, some of them aren’t even right or wrong, they’re not even testable, which is even worse than being wrong. The need for developing fundamental theory is just huge. If we’re going to save the planet, I think it’s critical that we do.

Besides theory, I like to do field work. I hate lab work- my students won’t even let me in the lab. I spend summers at the Rocky Mountain Biological Laboratory and this is my 38th consecutive summer. Twenty-seven years ago, I had this idea that everybody tried to talk me out of, which was to set up an outdoor climate warming experiment. We set up this big bank of overhead electric heaters that radiate heat down onto the ground to simulate the climate of the year 2050, roughly give or take. We have been running this now for 25 years. The heaters are on summer and winter, day and night. It’s the longest running experiment of its kind. But, when I set it up I got all kinds of arguments that this was a stupid thing to do. The first proposal to NSF, I got a review back that said “It won’t work because as the heat radiates down to the ground the wind will blow the radiant heat away.” So they rejected the proposal. I wrote back to the program manager and I said, sarcastically, “Oh, so that explains why when I go out at night with my flashlight and it’s windy the light beam doesn’t hit the ground, it blows away.” And the program officer wrote back and said “Oh. I see what you mean”.  They had rejected the proposal by taking the word of a reviewer that it wasn’t going to work and they didn’t know enough physics to understand that electromagnetic radiation doesn’t blow away. So by persevering, there have been 33 journal papers that have come out of this one experiment, 9 PhD theses, and over 100 undergrads have gotten their field training with me doing this. It certainly is the single biggest field experiment I’ve ever done. I’m glad I persevered- that opened up so many doors for me and for my students especially.

Well let me ask you a question. What do you think are the similarities and differences between ecosystems and physical systems? Some people say physical systems are really basically simple and ecosystems are intrinsically complex. Does that resonate with you?

Well I’ve been thinking about this a little bit. That there is a system in physics that everybody agrees is mind-bogglingly intractable, and that’s turbulence. Now the thing about turbulence that makes it interesting is that it’s a phenomenon that occurs at all scales. Little turbulent eddies become bigger, become bigger, BECOME BIGGER, and finally become huge atmospheric vortices. It’s why climate is so hard to model in detail- because you can’t make clean scale separations. Now my view is that complex systems are systems where you can’t make clean scale separations. So, the question is, can you in ecology? This is what we’ve been trying to demonstrate with workable theory. That you can think of the trees and the forest. The forest is the macroscale, the trees are the microscale. You could go to a lower microscale like cells, but let’s stop with the individual trees as the simplest unit in ecological theory. If you do that, you can apply ideas from statistical physics and scale separation works. It’s a simplification, because there are phenomena within a forest that are smaller than the forest but bigger than the tree, associations between trees and so on, but, to a first approximation you can make that macroscale-microscale separation. You can’t do it with turbulence. So if that is a correct way of thinking, it suggests that we’ll have an easier time with ecological theory than we would with a theory of turbulence.

August 31, 2014

Continuing the Conversation: The Role of Theory in Conservation, a follow-up with Justin Kitzes Updated for 2026

justin_kitzes_crop

In my conversation with John Harte, he mentions work by his post-doc, Justin Kitzes, who is interested in how ecological theory can be used in conservation. Two weeks after the Gordon Conference, where I interviewed John, I found myself at ESA, where Justin was coincidentally hosting a symposium on “Advancing Ecological Theory for Conservation Biology. I snagged a quick 10-minute conversation with Justin after what turned out to be a fascinating symposium. Here is, in his own words, why theory is important for conservation:

I’ll start with a more general answer to your question, why theory is relevant for conservation. In some sense, without theory ecology is a collection of stories. We can go to individual systems and we can study them very deeply. We can understand a lot about how they work and what makes them unique, but what fundamentally makes ecology a science is that we believe that there is some deeper order and deeper pattern underneath all of these individual observations of species and systems. In conservation, we’re often in a situation where we don’t have all of that deep information. We need to take what we’ve learned somewhere else and apply it in a context where we don’t have a lot of data, where we need to make a decision rapidly, and in those situations it’s often the case that theory offers some of the best information that we’re going to get in practice in order to be able to make decisions. In a broad sense, I think that the role of theory in conservation is filling in the gaps. When we don’t have time or money to study everything to the extent that we want to, we use theory to do the best we can.

The particular type of theory that I work with and that John works with is macroecology, which is, generally speaking, the focus on statistical patterns. If we have evidence that there are some sort of general universal underlying patterns that govern how communities structure themselves, we can use that information to make decisions where we don’t have a lot of time or a lot of money. Probably the canonical example of this is the species-area relationship, which tells you as area grows and shrinks, how the number of species goes up and down. That pattern has been used in conservation for probably 40 years or more by now. It’s a good way at providing a first pass estimate of something like extinction risk when you really don’t have much else to go on.

The species area relationship is a really interesting case. Arrhenius in the 1920’s was probably the first one to put a number on it, and pretty early on it was thought that it was a power law. So on a log-log plot it comes out to a straight line and the slope of that line was about 0.25. There was some early work, for example Jared Diamond’s paper on land bridge islands, that showed empirical fits close to 0.25. Frank Preston and Robert May followed that up in the 60s and 70s with some great work showing that a particular form of the species abundance distribution, the canonical log-normal, would lead precisely to a power law of a slope of 0.25. So for a while there everyone was happy. Of course there was always some scatter, but maybe that was just noise. Rosensweig comes along in 1995 with his book and really hits home the fact that, no, it’s not just scatter, there are patterns in how systems deviate from that traditional model. Over time, people like my PI, John Harte, start to look and see, there’s not just scatter. There’s curvature on a log-log plot. It’s concave downward. It bends over. And that seems to be pretty consistent. So it’s not just that the slopes are bouncing around. There’s something systematic going on here. One of the most interesting outcomes of MaxEnt, which was really not realized until after the original theory came out, is that it makes a prediction for the slope of the species-area relationship. What we normally take to be constant at 0.25, is actually decreasing as the number of individuals per species increases. So basically, as plots get large, the slope of the relationship is predicted to decrease. It turns out that really works well so long as you’re not crossing major habitat boundaries. It does an amazing job of collapsing what looked like an enormous shotgun blast of scatter down to something that follows a predicted curve, pretty darn closely, for what we consider close in ecology.

You never know what the right answer is until the future happens. When we’re talking about global change we’re in the business of predicting the future. So you have a couple choices. You could do nothing, that’s always one choice, right? You could look at the data qualitatively as best you can and try to decide what to do, and that can be a very reasonable option. Or you can rely on what, in the best case scenario, we’ve been spending 100 years trying to do, which is figure out how ecosystems work and to try to apply some of that knowledge to try to figure out what might happen in future. The embodied knowledge of how ecosystems work has shown up in the body of theory that underlies ecology. It’s also important to recognize that theory is not just mathematical theory. A lot of theorists work with mathematical theory, but things like the intermediate disturbance hypothesis or trophic cascades, those can be qualitative theories and those can play a role in trying to make predictions.

I do think that theorists and conservation biologists don’t talk to each other enough. I think there’s a cultural divide there in addition to differences in the backgrounds of the different communities. But if there was one thing I could say, it is that I really believe that theory is underutilized in conservation. I think across the board, not just type of theory I do, we’re not taking advantage of that body of knowledge that we put into our equations when it comes time to actually make decisions on the ground. And that’s not to say that theory is going to answer our questions and we’re going to have a technocratic world where we can predict exactly what to do. But there’s information there that is missing from the applied conversations that we should try to do a better job of bringing in.

August 30, 2014

Flump – Frozen microbial ecosystems, Primary forests, meta-analysis of genetic diversity studies, maps and more Updated for 2026

UNEP's recent publication includes maps of natural capital, providing a great visual of what and where nature provides humans with resources and services.

It’s Friday and that means that it’s time for our Friday link dump, where we highlight some recent papers (and other stuff) that we found interesting but didn’t have the time to write an entire post about. If you think there’s something we missed, or have something to say, please share in the comments section!

Nature published a study yesterday that provides the first evidence for microbial ecosystems beneath the Antarctic ice sheet.  Genetic data suggests that the microorganisms discovered are a mix of chemosynthetic autotrophs and heterotrophs, and therefore likely influence the geochemistry of the surrounding Southern Ocean.

Mackey et al., in a recent article in Conservation Letters, paint a dire picture of the state of primary forests worldwide. – Nate Johnson

Etienne Low-Décarie and colleagues show that, over the past years, ecological models have become much more complex and that their explanatory power have decreased steadily, in their new paper “Rising complexity and falling explanatory power in ecology“.

The last issue of Science features three letters about animal population declines:

At last, SCALES, a research project aiming to bring  the issue of sac ale into biodiversity conservation, ha just released a free ebook: “Scaling in Ecology and Biodiversity Conservation“. – Vinicius Bastazini.

August 22, 2014