Gone with the birds

1 09 2011

ebaumsworld.com

Another great post by Salvador Herrando-Pérez.

Through each new species, evolution assembles a unique combination of genes. Ever since living forms have populated our planet (> 3 billion years), the number of combinations is incalculable. That is why evolution resembles a cocktail shaker. Contemporaneous biogeographers look for order in that shaker to explain the history of life, as much as historians look for monarchs and revolutions in a library to explain the history of humanity.

The ethnic diversity of our suburb, village or city obeys factors of different temporal extent. Recent factors such as wealth, politics (war, segregation), culture (tradition, religion), and technology (airplanes, bridges, tunnels) determine racial migration, mixing and extinction. On the other hand, pre-historical factors express the expansion of the earliest hominids from Africa to the other continents – what makes a bantu ‘bantu’, or an inuit ‘inuit’.

Present ecological conditions and the macro-evolutionary past stock the elements by which biogeography attempts to understand the mechanisms shaping the spatial distribution of species, e.g., why kangaroos are restricted to Oceania, or why you could believe you were in Spain while strolling through a Greek forest. Read the rest of this entry »





More than leftovers: getting marine parks right in Australia

7 08 2011
Taken by user Hossen27

Image via Wikipedia

A few weeks back I cosigned a ‘statement of concern’ about the proposal for Australia’s South West Marine Region organised by Hugh Possingham. The support has been overwhelming by Australia’s marine science community (see list of supporting scientists below). I’ve reproduced the letter addressed to the Australian government – distribute far and wide if you give more than a shit about the state of our marine environment (and the economies it supports). Basically, the proposed parks are merely a settlement between government and industry where nothing of importance is really being protected. The parks are just the leftovers industry doesn’t want. No way to ensure the long-term viability of our seas.

On 5 May 2011 the Australian Government released a draft proposal for a network of marine reserves in the Commonwealth waters of the South West bioregional marine planning region.

Australia’s South West is of global significance for marine life because it is a temperate region with an exceptionally high proportion of endemic species – species found nowhere else in the world.

Important industries, such as tourism and fisheries, depend on healthy marine ecosystems and the services they provide. Networks of protected areas, with large fully protected core zones, are essential to maintain healthy ecosystems over the long-term – complemented by responsible fisheries management1.

The selection and establishment of marine reserves should rest on a strong scientific foundation. We are greatly concerned that what is currently proposed in the Draft South West Plan is not based on the three core science principles of reserve network design: comprehensiveness, adequacy and representation. These principles have been adopted by Australia for establishing our National Reserve System and are recognized internationally2.

Specifically, the draft plan fails on the most basic test of protecting a representative selection of habitats within the bioregions of the south-west. There are no highly protected areas proposed at all in three of the seven marine bioregions lying on the continental shelf3. Overall less than 3.5% of the shelf, where resource use and biodiversity values are most intense, is highly protected. Further, six of the seven highly protected areas that are proposed on the shelf are small (< 20 km in width)4 and all are separated by large distances (> 200 km)5. The ability of such small isolated areas to maintain connectivity and fulfil the goal of protecting Australia’s marine biodiversity is limited. Read the rest of this entry »





生态学 = ‘Ecology’ in China

13 05 2011

I’m just heading home after a very inspiring workshop organised by Fangliang He at Sun Yat-sen University in Guangzhou, China (I’m writing this from the Qantas Club in the Hong Kong airport).

Before I proceed to regale you with the salient details of the ‘International Symposium for Biodiversity and Theoretical Ecology‘, I am compelled to state publicly that I offer my sincerest condolences to Fangliang and his family; unfortunately Fangliang’s brother passed away while we were at the workshop and so Fangliang wasn’t able to spend much time reaping the fruits of his organisational labour. If you know Fangliang, please send him a supporting email.

That sad note aside, I am delighted to say that the workshop was compelling, challenging and also rather fortuitous. I was one of many overseas invitees, and I must say that I was at times overwhelmed by the size of the brains they managed to pack into the auditorium. Many colleagues I didn’t know attended, and I hope that many will become collaborators. The international invitees were: Read the rest of this entry »





How fast are we losing species anyway?

28 03 2011

© W. Laurance

I’ve indicated over the last few weeks on Twitter that a group of us were recently awarded funding from the Australian Centre for Ecological Synthesis and Analysis – ACEAS – (much like the US version of the same thing – NCEAS) to run a series of analytical workshops to estimate, with a little more precision and less bias than has been done previously, the extinction rates of today’s biota relative to deep-time extinctions.

So what’s the issue? The Earth’s impressive diversity of life has experienced at least five mass extinction events over geological time. Species’ extinctions have kept pace with evolution, with more than 99 % of all species that have ever existed now gone (Bradshaw & Brook 2009). Despite general consensus that biodiversity has entered the sixth mass extinction event because of human-driven degradation of the planet, estimated extinction rates remain highly imprecise (from 100s to 10000s times background rates). This arises partly because the total number of species is unknown for many groups, and most extinctions go unnoticed.

So how are we going to improve on our highly imprecise estimates? One way is to look at the species-area relationship (SAR), which to estimate extinction requires one to extrapolate back to the origin in taxon- and region-specific SARs (e.g., with a time series of deforestation, one can estimate how many species would have been lost if we know how species diversity changes in relation to habitat area). Read the rest of this entry »





Webinar: Modelling water and life

27 08 2010

Another quick one today just to show the webinar of my recent 10-minute ‘Four in 40′ talk sponsored by The Environment Institute and the Department for Water. This seminar series was entitled ‘Modelling as a Tool for Decision Support’ held at the Auditorium, Royal Institution Australia (RiAus).

“Four in 40″ is a collaboration between The University of Adelaide and the Department for Water, where 4 speakers each speak for 10 minutes on their research and its implications for policy. The purpose is to build understanding of how best to work with each other, build new business for both organisations and raise awareness of activity being undertaken in water/natural resource management policy and research.

CJA Bradshaw





Tropical biology and conservation overview

28 07 2010

Last week I attended the 2010 International Meeting of the Association for Tropical Biology and Conservation (ATBC) in Sanur, Bali (Indonesia). I only managed one post on the real-world relevance of conservation research (that attracted quite a lot of comment) while there, but I did promise to give a conference overview as I did for the International Congress for Conservation Biology earlier this month. So here goes.

This was my first ATBC meeting despite having co-written ‘the book’ on tropical conservation biology (well, one of very, very many). I no longer live in the tropics but am still managing to keep my hand in many different aspects of tropical research. After all, tropical regions represent ground zero for conservation biology – they have the highest biodiversity (no matter which way you measure it), some of the greatest threats (e.g., most people, most rapid development, most corruption) and some of the most pressing human problems (disease, hunger, socio-political instability). Ironically, most of the world’s conservation ecologists work in temperate realms – it should really be the other way around. Read the rest of this entry »





Faraway fettered fish fluctuate frequently

27 06 2010

Hello! I am Little Fish

Swimming in the Sea.

I have lots of fishy friends.

Come along with me.

(apologies to Lucy Cousins and Walker Books)

I have to thank my 3-year old daughter and one of her favourite books for that intro. Now to the serious stuff.

I am very proud to announce a new Report in Ecology we’ve just had published online early about a new way of looking at the stability of coral reef fish populations. Driven by one of the hottest young up-and-coming researchers in coral reef ecology, Dr. Camille Mellin (employed through the CERF Marine Biodiversity Hub and co-supervised by me at the University of Adelaide and Julian Caley and Mark Meekan of the Australian Institute of Marine Science), this paper adds a new tool in the design of marine protected areas.

Entitled Reef size and isolation determine the temporal stability of coral reef fish populations, the paper applies a well-known, but little-used mathematical relationship between the logarithms of population abundance and its variance (spatial or temporal) – Taylor’s power law.

Taylor’s power law is pretty straightforward itself – as you raise the abundance of a population by 1 unit on the logarithmic scale, you can expect its associated variance (think variance over time in a fluctuating population to make it easier) to rise by 2 logarithmic units (thus, the slope = 2). Why does this happen? Because a log-log (power) relationship between a vector and its square (remember: variance = standard deviation2) will give a multiplier of 2 (i.e., if xy2, then log10x ~ 2log10y).

Well, thanks for the maths lesson, but what’s the application? It turns out that deviations from the mathematical expectation of a power-law slope = 2 reveal some very interesting ecological dynamics. Famously, Kilpatrick & Ives published a Letter in Nature in 2003 (Species interactions can explain Taylor’s power law for ecological time series) trying to explain why so many real populations have Taylor’s power law slopes < 2. As it turns out, the amount of competition occurring between species reduces the expected fluctuations for a given population size because of a kind of suppression by predators and competitors. Cool.

But that application was more a community-based examination and still largely theoretical. We decided to turn the power law a little on its ear and apply it to a different question – conservation biogeography. Read the rest of this entry »





Protecting Australian wilderness

1 10 2009

Today I highlight a new paper just out online in Diversity and Distributions by James Watson and colleagues: Wilderness and future conservation priorities in Australia. It’s certainly one for the Potential list.

KNP

Jim Jim Falls, Kakadu National Park

Australia has a pretty bad biodiversity conservation track record – we have some of the worst mammal extinction trends in the world, and we’ve lost at least 50 % of our forested area since European colonisation. Despite our relatively large system of parks and reserves, things aren’t going to well (even in the parks!).

Our rapidly expanding influence means that we have to start protecting larger and larger areas if we want to have any chance of slowing the modern extinction crisis. This means we have to go beyond dedicated biodiversity reserves and sequester more ‘wilderness’ (defined as “…large areas that have experienced minimal habitat loss“). Watson and colleagues therefore used Australia as a good example to determine the extent to which the national protected area network captures ‘wilderness’, and how Australia’s planned expansion of the reserve system will include ‘wilderness’ in the future.

Although there wasn’t much planning involved initially, Australia (like many other countries) started to take biodiversity conservation seriously in the mid-1990s, such that now we have about 11 % of our 7.7 million km2 land area within a National Reserve System. Planning didn’t feature heavily in the early years, but it has been embraced now by nearly all planning bodies within government.

© Wiley-Blackwell

© Wiley-Blackwell

Using estimates of the total wilderness area in Australia (Fig. a), Watson and colleagues determined how much was included in the Reserve System (Fig. b), and how this value changed between 2000 and 2006.

Of the 2.93 million km2 of wilderness (38 % of land area, mostly in northern and western Australia), only 14 % was protected in 2000. This value increased marginally to 19 % by 2006 as the size of the Reserve System itself increased by 37 % (i.e., from 652597 to 895326 km2).

Bottom line – our growth in reserve area didn’t really capture the necessary wilderness; instead, gains were made in areas largely modified by humans. Even where wilderness has been captured, it’s predominately in ‘multiple use’ regions (incorporating mining, forestry and grazing, for example).

This isn’t a bad thing really – by focussing on areas of high biodiversity value that are under relatively high threat embraces the biodiversity hotspot approach to conservation and emphasises restoration. This is, of course, needed. But not incorporating a wider component of the habitats within wilderness could bias conservation toward range-restricted species.

© Wiley-Blackwell

© Wiley-Blackwell

Watson and colleagues therefore make a number of recommendations:

  1. We should strive to quantify and map spatially the  important ecological and evolutionary processes that drive the distribution and abundance of biodiversity so they can be explicitly incorporated into reserve area prioritisations.
  2. We should focus on predicting the magnitude and distribution of future threats and incorporate them into the spatial prioritisation framework.
  3. We should incorporate realistic constraints (e.g., financial costs) into prioritisation.
  4. We need to map and analyse a range of social and economic factors that define opportunities for conservation in conjunction with information on conservation values, threats and costs.

The bottom line is that we need to find a better balance between planning that protects threatened species and ecosystems in already highly fragmented (threatened) landscapes, and planning that protects large areas of wilderness that still contains most of its conservation values (wilderness). We’re getting there, but slowly, and hopefully in time to save our remaining threatened species from extinction.

CJA Bradshaw

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ResearchBlogging.org

Watson, J., Fuller, R., Watson, A., Mackey, B., Wilson, K., Grantham, H., Turner, M., Klein, C., Carwardine, J., Joseph, L., & Possingham, H. (2009). Wilderness and future conservation priorities in Australia Diversity and Distributions DOI: 10.1111/j.1472-4642.2009.00601.x





Conservation Scholars: David Lindenmayer

10 09 2009

The Conservation Scholars series highlights leaders in conservation science and includes a small biography, a list of major scientific publications and a Q & A on each person’s particular area of expertise.

David LindenmayerOur fourteenth Conservation Scholar is one of Australia’s better known conservation ecologists: David Lindenmayer. David has been battling for landscape ecology and conservation science to be taken seriously in this country for over 30 years. I recently featured David here at ConservationBytes.com on the importance of incorporating ecological knowledge into Australian bushfire policy, but here’s a more comprehensive coverage of his legacy.

Biography

I am a Research Professor at the Fenner School of Environment & Society at The Australian National University (ANU). I have worked at the ANU for over 17 years and have developed a speciality for establishing and maintaining large-scale, long-term empirical studies. These span wet forests (in Victoria), plantation forests (at Tumut in southern NSW), temperate woodlands (throughout south-western NSW) and coastal heathlands (at Jervis Bay Territory, southern NSW). We examine the response of different groups of biota (birds, mammals, reptiles, frogs, invertebrates and plants) to human or natural interventions in these studies – e.g., logging, plantation development, agricultural and revegetation, fire (wildfire and prescribed burning). We also have projects that attempt to integrate data and ecological insights across these major projects. These major programs have many (> 75) live projects embedded within them, including an array of post-graduate students.radiotracking1

The work we do has some key themes. First, it needs to be underpinned by careful statistical design and we have 3 professional statisticians in our group that have critical experimental design roles in all of our studies. Second, we build significantly upon long-term datasets to quantify longitudinal responses of biota to agents of change. Third, we work closely with land managers and government agencies to increase the chances of our work being adopted on the ground. Fourth, and related to the previous point, we work very hard to communicate our empirical results to a broad audience by publishing semi-popular books and other kinds of communication products.

Our group currently comprises ~ 30 people and the younger scientists in the team are a truly exciting part of its dynamism. Indeed, the best research is usually done by post-graduate researchers!! Our hope is to maintain the research and teaching momentum that we have generated over the past decade to keep the group a vibrant, active and forward-thinking one for several decades to come.

Major Publications

It is difficult to choose some papers above others. But I do like the major empirical ones we have done because large synthesis of field data are not common these days – in an age where the emphasis is on short, ‘newsy’ pieces. I also like writing books and longer review articles because these are a chance to pull together a lot of information and make sense of the literature out there.

Questions and Answers

radiotracking21. You are probably best known for your work on vertebrate responses to forested landscape change. What kind of data and studies are needed to gauge how biodiversity responds to such changes?

It is clear to me that there is a paucity of large-scale, long-term datasets really to develop an empirical understanding of what is happening in a changing world. This is what our group does really well I think, so it is a real privilege to be able to do that.

2. Your book, Practical Conservation Biology, is a great introduction to applied conservation. Can you describe what you mean by ‘practical’ and how aspiring students need to approach conservation science?

The aim of the PCB book was to provide students with the thinking and some (and I stress just some) of the tools to tackle real world problems. I am not sure that we succeeded in doing this, but it was a good thing to attempt. I also think it was important to showcase Australian conservation biology because there are some many outstanding researchers and practitioners in this country.

3. Fire management is a ‘hot’ issue (excuse the pun) in Australia and beyond, yet there still seems to be little uptake of good fire disturbance ecology by policy makers. What do we need to be doing differently at the policy level, and how can we facilitate better uptake of landscape disturbance ecology?

This is a tough question because so often fire management issues are hijacked by the emotion that is associated with major natural disturbance events. The issue here is that the science of fire and the science of conservation and environmental management need to be better intersected to examine how to best tackle resource management problems. Policy somehow needs to remain cold to all the emotion that humans throw, often illogically at resource management problems. Otherwise I see that policy making in crisis mode will risk perverse outcomes that will be poor management practice and have negative effects on biodiversity.

4. In your opinion, what are the some of the best ways Australia can improve its poor environmental record and reclaim some of its dwindling biodiversity heritage?

Australian needs to get serious about properly resourcing environmental management and biodiversity conservation. We have endless reports about what to do, yet this rarely transfers to serious things on the ground. Nor does environmental legislation really protect the environment and biodiversity. We also need to get serious about long-term datasets to get somewhere sensible with understanding long-term changes in biota.

CJA Bradshaw

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The rarity of commonness

18 08 2009

I’m attending the 10th International Congress of Ecology (INTECOL) in Brisbane this week and I have just managed to find (a) an internet connection and (b) a small window to write this post.

I have to say I haven’t been to a good plenary talk for some time – maybe it’s just bad luck, but often plenary talks can be less-than-inspiring.

Not so for INTECOL this year. I was very pleased to have the opportunity to listen to biodiversity guru Professor Kevin Gaston of the University of Sheffield give a fantastic talk on… common species (?!).

clones

If you have followed any of Kevin’s work, you’ll know he literally wrote the book on rarity – what species rarity is, how to measure it and what it means for preserving biodiversity as a whole.

Now he’s championing (in a very loose sense) the importance of common species because it is these taxa, he argues, that provide the backbone to the persistence of all biodiversity.

Yes, we conservation biologists have tended to focus on the rare and endemic species to make certain we have as much diversity in species (and genetic material) as possible when conserving habitats.

There are a lot more rare species than common ones, and the most common species (i.e., the ones you most often see) tend to have the broadest distributions. We know from much previous work that having a broad distribution reduces extinction risk, so why should we be concerned about common species?

Kevin made a very good point – if you turn the relationship on its head somewhat, you can state that the state of ‘commonness’ is itself ‘rare’. In fact, only about 25 % of the most common species account for about 90-95 % of ALL individuals. He used an interesting (and scary) example to show what this can mean from an extinction perspective. Although very back-of-the-envelope, there are about 2000 individual birds in a km2 of tropical forest; we are losing between 50000 and 120000 km2 of tropical forest per year, so this translates into the loss of about 100 to 240 million individual birds per year; this is the sum total of all birds in Great Britain (a bird-mad country). Yet where do we have the best information about birds? The UK.

Commonness is also geologically transient, meaning that just because you are a common species at some point in your evolutionary history doesn’t mean you have always been or always will be. In fact, most species never do become common.

But it is just these ‘rare’ common that drive the principal patterns we see globally in community structure. The true ‘rare’ species are, in fact, pretty crap predictors of biodiversity patterns. Kevin made a good point – when you look at a satellite image of a forest, it’s not all the little rare species you see, it’s the 2 or 3 most common tree species that make up the forest. Lose those, and you lose everything else.

Indeed, common species also form most trophic structure (the flow of energy through biological communities). Take away these, and ecosystem function degrades. They also tend to have the highest biomass and provide the structure that supports all those millions of rare species. Being common is quite an important job.

Kevin stated that the world is now in a state where many of the so-called common species are in fact, “artificially” common because of how much we’ve changed the planet. It is these benefactors of our world-destroying machinations that are now in decline themselves, and it is for this reason we should be worried.

When you start to see these bastions of ecosystems start to drop off (and the drop is usually precipitous because we don’t tend to notice their loss until they suddenly disappear), then you know we’re in trouble. And yet, even though once common, few, if any, once-common species have come back after a big decline.

So what does this mean for the way we do biodiversity research? Kevin proposes that we need a lot more good monitoring of these essential common species so that we can understand their structuring roles in the community and more importantly, be able to track their change before ecosystem collapse occurs. The monitoring is crucial – it wasn’t the demise of small companies that signalled the 2007 stock market crash responsible for the Global Financial Crisis in which we now find ourselves, the signal was derived from stock data obtained from just a few large (i.e., ‘common’) companies. All the small companies (‘rare’) ones then followed suit.

A very inspiring, worrying and somewhat controversial talk. Watch out for more things ‘Gaston’ on ConservationBytes.com in the near future.

CJA Bradshaw

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Eastern Seaboard Climate Change Initiative

30 04 2009
© A. Perkins
© A. Perkins

I’ve just spent the last few days in Sydney attending a workshop on the Eastern Seaboard Climate Change Initiative which is trying to come to grips with assessing the rising impact of climate change in the marine environment (both from biodiversity and coastal geomorphology perspectives).

Often these sorts of get-togethers end up doing little more than identifying what we don’t know, but in this case, the ESCCI (love that acronym) participants identified some very good and necessary ways forward in terms of marine research. Being a biologist, and given this is a conservation blog, I’ll focus here on the biological aspects I found interesting.

The first part of the workshop was devoted to kelp. Kelp? Why is this important?

As it turns out, kelp forests (e.g., species such as Ecklonia, Macrocystis, Durvillaea and Phyllospora) are possibly THE most important habitat-forming group of species in temperate Australia (corals and calcareous macroalgae being more important in the tropics). Without kelp, there are a whole host of species (invertebrates and fish) that cannot persist. The Australian marine environment is worth something in the vicinity of $26.8 billion to our economy each year, so it’s pretty important we maintain our major habitats. Unfortunately, kelp is starting to disappear around the country, with southern contractions of Durvillaea, Ecklonia and Hormosira on the east coast linked to the increasing southward penetration of the East Australia Current (i.e., the big current that brings warm tropical water south from Queensland to NSW, Victoria and now, Tasmania). Pollution around the country at major urban centres is also causing the loss or degradation of Phyllospora and Ecklonia (e.g., see recent paper by Connell et al. in Marine Ecology Progress Series). There is even some evidence that disease causing bleaching in some species is exacerbated by rising temperatures.

Some of the key kelp research recommendations coming out of the workshop were:

  1. Estimating the value of kelp to Australians (direct harvesting; fishing; diving)
  2. Physical drivers of change: understanding how variation in the East Australian Current (temperature, nutrients) affects kelp distribution; understanding how urban and agricultural run-off (nutrients, pollutants, sedimentation) affects distribution and health; understanding how major storm events (e.g., East Coast Lows and El Niño-Southern Oscillation) affects long-term persistence
  3. Monitoring: what is the distribution and physical limits of kelp species?; how do we detect declines in ‘health’?; what is the associated biodiversity in kelp forests?
  4. Experimental: manipulations of temperature/nutrients/pathogens in the lab and in situ to determine sensitivities; sensitivity of different life stages; latitudinal transplants to determine localised adaption
  5. Adaptation (management): reseeding; managing run-off; managing fisheries to maintain a good balance of grazers and predators; inform marine protected area zoning; understanding trophic cascades

The second part of the discussion centred on ocean acidification and increasing CO2 content in the marine environment. As you might know, increasing atmospheric CO2 is taken up partially by ocean water, which lowers the availability of carbonate and increases the concentration of hydrogen ions (thus lowering pH or ‘acidifying’). It’s a pretty worrying trend – we’ve seen a drop in pH already, with conservative predictions of another 0.3 pH drop by the end of this century (equating to a doubling of hydrogen ions in the water). What does all this mean for marine biodiversity? Well, many species will simply not be able to maintain carbonate shells (e.g., coccolithophore phytoplankton, corals, echinoderms, etc.), many will suffer reproductive failure through physiological stress and embryological malfunction, and still many more will be physiologically stressed via hypercapnia (overdose of CO2, the waste product of animal respiration).

Many good studies have come out in the last few years demonstrating the sensitivity of certain species to reductions in pH (some simultaneous with increases in temperature), but some big gaps remain in our understanding of what higher CO2 content in the marine environment will mean for biota. Some of the key research questions in this area identified were therefore:

  1. What is the adaptation (evolutionary) potential of sensitive species? Will many (any) be able to evolve higher resistance quickly enough?
  2. In situ experiments outside the lab that mimic pH and pCO2 variation in space and time are needed to expose species to more realistic conditions.
  3. What are the population consequences (e.g., change in extinction risk) of higher individual susceptibility?
  4. Which species are most at risk, and what does this mean for ecosystem function (e.g., trophic cascades)?

As you can imagine, the conversation was complex, varied and stimulating. I thank the people at the Sydney Institute of Marine Science for hosting the fascinating discussion and I sincerely hope that even a fraction of the research identified gets realised. We need to know how our marine systems will respond – the possibilities are indeed frightening. Ignorance will leave us ill-prepared.

CJA Bradshaw

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Conservation Scholars: Stuart Pimm

5 01 2009

This series on ConservationBytes.com takes a page out of our book Tropical Conservation Biology (Sodhi, Brook & Bradshaw) – therein we produced a series of ‘Spotlights’ describing the contributions of great thinkers to conservation science. Each highlight of a Conservation Scholar includes a small biography, a list of major scientific publications and a Q & A on the person’s particular area of expertise.

Our ninth Conservation Scholar is Stuart Pimm

Biography

I am the Doris Duke Professor of Conservation Ecology at the School of the Environment at Duke University and have a secondary appointment of Extraordinary Professor at the Conservation Ecology Research Unit at the University of Pretoria, South Africa. My interests are endangered species conservation, biodiversity, species extinction, and habitat loss. I’m the author of over 200 scientific publications, many of them in Nature and Science, and have written four books, the most recent being the critically acclaimed World According to Pimm: a Scientist Audits the Earth. In 2006, Prince Willem-Alexander presented me the Dr. A.H. Heineken Prize for Environmental Sciences on behalf of the Royal Netherlands Academy of Arts and Sciences. How did all this happen?

Like many peers, I started out as a naturalist during my adolescence, read zoology at university, and then did a PhD in ecology. Unlike others, I worked in Hawai’i soon afterwards where I was deeply shaken by the total absence of many of the birds I expected to see – they were either extinct or close to it. I was curious about why some species succumbed while other survived. Importantly, these losses were an outrage. Scientists, I realized, could help prevent extinctions. Vitally, they had an obligation to do so. Thereafter, my research group has sought out the species and ecosystems that are in most urgent need of protection. That work takes us to the Everglades, the Amazon and the coastal forests of Brazil, to southern Africa, and to Madagascar. We work with local organisations and governments to provide the best possible advice to solving conservation problems. We’re problem driven and that means we develop whatever skills are needed to their solution. We’ve always had good quantitative skills, but in addition, my group members all use geographic information system and analyses of satellite imagery – skills we developed only in the last decade. And yes, some of the solutions come from sharing our knowledge with politicians and advising on policy issues.

Major Publications

Questions and Answers

1. The current biodiversity crisis has been termed the “sixth extinction”; an allusion to the five largest mass die-offs in Earth’s past. Is this comparison justified?

In the previous five die-offs – the last killed off the dinosaurs – more than half the variety of life disappeared. It took roughly ten million years to recover the former numbers of species. Human actions in the last thousand years have probably wiped out about 10 % of species, while actions in the last century have threatened at least 10 % of the remainder. By threatened, I mean that expert opinion judges that these species will become extinct in the next few decades if we do nothing to protect them. It gets worse. Tropical forests hold perhaps two-thirds of all species on land and tropical oceans, especially coral reefs, the great majority of marine species. If current trends continue, human actions will so massively reduce these ecosystems that a third or more of the remaining species will be on a path to extinction within a few decades.

2. How reliable are biogeographic proxies such as the species-area relationship for inferring extinction rates?

Our ability to predict future trends on land comes from the species-area relationship. It’s one of the great ecological laws – that is, a commonly observed pattern across different species groups in different areas. An oceanic island, half the size of larger island, will have about 15 % fewer species according to this law. Imagine we convert what was once a continuous forest – say, eastern North America – into islands of about half the forest cover. There are about 30 species of bird endemic to the forests of the region, so we’d expect to lose 4.5 species. And, indeed, four species of bird became extinct as eastern North America lost its forests in the four centuries since European colonisation – and another species in threatened with extinction! Detailed calculations like this one have now been done on many areas of tropical forest, which often contain hundreds of endemic species. The numbers of species the model predicts to go extinct and those that have done so are very similar (or are presently in danger of doing so, for extinctions take time to happen.). These excellent calibrations of the law mean that we can predict how many species will go extinct if we reduce tropical forests further.

3. How can scientists most effectively engage the often pseudo-scientific arguments posed by environmental ‘sceptics’, who claim global hazards, such as the large-scale death of species and climate change, are illusory or inconsequential?

The most effective strategy is not to engage the sceptics. I’m for honest scientific debate – it’s what I do every day. The evidence for global change and massive loss of species is unassailable, however. Sceptics ignore the evidence, usually in my experience, because they are paid to do so. There is nothing honest in the debate, indeed, it usually isn’t a debate. Would you debate someone who thought the world was flat? If you were so foolish as to do so, what would happen? You’d present all the familiar observations -Earth’s shadow on the Moon, for example, – and demolish your opponent. Would he continue with his foolish ideas? You bet! He would loudly trumpet that he’d debated a competent, thoughtful scientist at the University of Somewhere. To outsiders, his pathetically ignorant ideas would gain credibility and his sponsors would continue to pay him. Lots of good people work hard to address ways to reverse global change and reduce species loss. Get on with solving problems and don’t waste time with fools.

4. What is the future of tropical biodiversity… ‘according to Pimm’?

The important message is that we can stem the loss of tropical biodiversity – its future is not yet written. We can slow the rate of deforestation and we know enough about the patterns of where the most vulnerable species live to make their protection a priority.

CJA Bradshaw

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(with thanks to Navjot Sodhi, Barry Brook, Ward Cooper, Wiley-Blackwell and Stuart Pimm for permission to reproduce the text – buy your copy of Tropical Conservation Biology here)








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