Tag Archives: biodiversity

Why We Cannot Forget about Weeds

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Weeds are one of world’s most significant ecological problems. As such it is surprising that the word “weeds” does not appear at all in Sutherland et al. (2013), and only once in Sutherland et al. (2006). (Perhaps there are no weeds in the UK.) Weeds affect plant and animal communities in national parks and nature reserves as well as in agricultural landscapes and cities. We have taken a benign neglect attitude toward weeds, perhaps because they are everywhere, but ecologists may also wish to avoid the word ‘weed’ because it is not a useful aggregate term about which we can draw some ecological generalizations. How should we respond to weeds?

I consider ‘weeds’ as a collective term for what might be the worst global example of serious ecological problems (Strayer 2012). But is this collective term a very useful one? At the first step when we deal only with plants, we get confused with native plants and exotic plants. A utilitarian perspective looks at all plants to see if they are useful or harmful for humans. So some conservation biologists want to get rid of all exotic plants outside of gardens and crops, and others wish to limit all harmful plants, whether native or exotic, and call them ‘weeds’. So the rose in your front yard is indeed an exotic species but a good one. Farmers want to get rid of at least some weeds to maximize production but at the same time to tolerate other exotic species that increase production. Weeds might be thought of as a convenient grouping to simplify ecological generalizations. But alas it has not been so.

The War against Weeds is in general not going well for conservation biologists (Downey et al. 2010). While biological control is very useful for some weeds, it does not at present seem to work for most weeds of national concern. So it does not seem to be a universal solution. Herbicides work for a time and then natural selection intervenes. The problem is that weed problems are very much a local problem in being species-specific and environment-specific, so that there is no overall weed strategy that works everywhere (Vilà et al. 2011). If one is interested in community productivity, weeds may increase plant biomass which might be considered a good result for the ecosystem. Graziers may encourage weeds that plant ecologists would consider destructive to natural communities. Ecosystem ecologists might welcome weeds that increase plant cover if they reduce soil erosion and nutrient leakage into water bodies.

This conflict of interest comes home to us in quarantine restrictions on weeds. In Australia government research scientists work to increase the tolerance of exotic pasture grassess to cold and drought, even though the species in question is a weed of national significance, and improving it genetically will make it more invasive in natural communities (Driscoll et al. 2014). The problem comes back to who wants what kind of an ecological world. Generalist grazing mammals may care little about the exact species composition of the grasslands they inhabit, or alternately they may be poisoned by specific weeds that are toxic to farm animals. The devil rests in the details, so the general message is that we cannot forget species names and attributes in the War on Weeds.

As a minimum, we ought to encourage our governments to place quarantine restrictions on all plant species listed as global weeds of significance. For the present time the best predictor of whether or not an introduced plant will become a destructive weed is: what happened to that plant in other countries to which it was introduced? That you can still buy at your local plant store the seeds of an array of weeds of national significance shouts to ecologists that quarantine systems needs to be strengthened. The War on Weeds is greatly under-financed like many long term problems in ecology, and we should put more effort into developing tactics to deal with destructive weeds rather than ignoring them.

Downey, P.O. et al. 2010. Managing alien plants for biodiversity outcomes—the need for triage. Invasive Plant Science and Management 3(1): 1-11. doi:10.1614/ipsm-09-042.1.

Driscoll, D.A. et al. 2014. New pasture plants intensify invasive species risk. Proceedings of the National Academy of Sciences USA 111(46): 16622-16627. doi:10.1073/pnas.1409347111.

Strayer, D.L. 2012. Eight questions about invasions and ecosystem functioning. Ecology Letters 15(10): 1199-1210. doi:10.1111/j.1461-0248.2012.01817.x.

Sutherland, W.J. et al. 2006. The identification of 100 ecological questions of high policy relevance in the UK. Journal of Applied Ecology 43(4): 617-627. doi:10.1111/j.1365-2664.2006.01188.x.

Sutherland, W.J. et al. 2013. Identification of 100 fundamental ecological questions. Journal of Ecology 101(1): 58-67. doi:10.1111/1365-2745.12025.

Vilà, M., et al. 2011. Ecological impacts of invasive alien plants: a meta-analysis of their effects on species, communities and ecosystems. Ecology Letters 14(7): 702-708. doi:10.1111/j.1461-0248.2011.01628.x.

Ecosystem Science to the Rescue

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What can ecologists do to become useful in the mess that is currently the 21st Century? In Australia we have a set of guidelines now available as “Foundations for the Future: A Long Term Plan for Australian Ecosystem Science” (http://www.ecosystemscienceplan.org.au ) It is a useful overall plan in many respects and the only question I wish to discuss here is how we ecologists come to such plans and whether or not they are realistic.

We should begin by treating this plan as an excellent example of political ecology – a well presented, glossy brochure, with punch lines carved out and highlighted so that newspaper reporters and sympathetic politicians can present sound bites on air or in Parliament. One example: “Healthy ecosystems are the cornerstone of our social and economic wellbeing”. No arguments there.

Six key directions are indicated:

  1. Delivering maximum impact for Australia: Enhancing relationships between scientists and end-users
  2. Supporting long-term research
  3. Enabling ecosystem surveillance
  4. Making the most of data resources
  5. Inspiring a generation: Empowering the public with knowledge and opportunities
  6. Facilitating coordination, collaboration and leadership

Most ecologists would agree with all 6 key directions, but perhaps only 2 and 3 are scientific goals that are key to research planning. Everyone supports 2, but how do we achieve this without adequate funding? Similarly 3 is an admirable direction but how is it to be accomplished? Could we argue that most ecologists have been trying to achieve these 6 goals for 75 years, and particularly goals 2 and 3 for at least 35 years?

As a snapshot of the importance of ecosystem science, the example of the Great Barrier Reef is presented, and in particular understanding reef condition and its changes over time.

“Australia’s Great Barrier Reef is one of the seven wonders of the natural world, an Australian icon that makes an economic contribution of over $5 billion annually. Ongoing monitoring of the reef and its condition by ecosystem scientists plays a vital role in understanding pressures and informing the development of management strategies. Annual surveys to measure coral cover across the Great Barrier Reef since 1985 have built the world’s most extensive time series data on reef condition across 214 reefs. Researchers have used this long-term data to assess patterns of change and to determine the causes of change.”

The paper they cite (De’ath et al. 2012) shows a coral cover decline on the Great Barrier Reef of 50% over 27 years, with three main causes: cyclones (48% of total), crown-of-thorns starfish (43%) and coral bleaching (10%). From a management perspective, controlling the starfish would help recovery but only on the assumption that the climate is held stable lest cyclones and bleaching increase in future. It is not clear at all to me how ecosystem science can assist reef recovery, and we have in this case another good example of excellent ecological understanding with near-zero ability to rectify the main causes of reef degradation – climate change and water pollution.

The long-term plan presented in this report suggests many useful activities by which ecosystem studies could be more integrated. Exactly which ecosystem studies should be considered high priority are left for future considerations, as is the critical question of who will do these studies. Given that many of the originators of this ecosystem plan are from universities, one worries whether universities have the resources or the time frame or the mandate to accomplish all these goals which are essentially government services. With many governments backing out of serious ecosystem research because of budget cuts, the immediate future does not look good. Nearly 10 years ago Sutherland et al. (2006) gathered together a list of 100 ecological questions of high policy relevance for the United Kingdom. We should now go back to see if these became a blueprint for success or not.

De’ath, G., Fabricius, K.E., Sweatman, H., and Puotinen, M. (2012). The 27–year decline of coral cover on the Great Barrier Reef and its causes. Proceedings of the National Academy of Sciences 109(44): 17995-17999. doi:10.1073/pnas.1208909109.

Sutherland, W.J., et al. (2006). The identification of 100 ecological questions of high policy relevance in the UK. Journal of Applied Ecology 43(4): 617-627. doi: 10.1111/j.1365-2664.2006.01188.x

 

Are Birds of Any Consequence?

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We all love birds. They are colourful, interesting creatures and they entice many people to a love of nature and then hopefully the conservation of biodiversity. Thus we do not want to get rid of them. A great deal of effort goes into censusing birds and they are often thought of as indicator species of ecosystem health. No one is in favour of ‘Silent Spring’. But let us do a thought experiment.

The question I wish to ask is somewhat different than the important issue of bird conservation: are birds of any consequence to the operational integrity of communities and ecosystems? In the simplest case what would happen, say, to the eastern deciduous forest or the tall grass prairie or the arctic tundra if all the birds in those ecosystems went extinct? Predators that specialize on birds would clearly disappear but I do not know how many bird specialist predators exist. At the same time the parasites of these birds would be gone. But what about the integrity of existing ecosystems?

Can we dismiss the oceans because birds have a negligible effect on oceanic food webs and energy flow? I do not know the answer to this. In forests birds are often thought to keep insect pests of trees under control, but this seems to be unlikely in many systems in which defoliating insects damage trees of many sorts. Perhaps insect outbreaks would increase in frequency if there were no birds. I come away with the image that birds are for the most part of little consequence for terrestrial ecosystems because they are consumers operating at a very low quantitative level. An exception might be tropical forests in which birds are essential pollinators and seed dispersers, but again I am not sure how often they are necessary pollinators or seed dispersers.

All of this speculation is pretty useless, one might argue, because birds are not going to disappear. They may well be reduced in abundance if habitat is lost and habitat loss seems to be a global problem. But there are two aspects of current ecological research that these idle speculations touch on. First, are birds very good model systems for conservation biology? The answer the ecological world seems to have decided is that they are and very much research must be done on birds for this reason. If research time and money is limited, more research on birds means less on other aspects of community and ecosystem dynamics. Should we be concerned about this? Bird research is convenient and sexy, at least in university settings, but is it more of “Nero fiddling while Rome is burning”? One might in fact argue that many birds are the worst possible model system for understanding conservation problems except for those specific to birds. When I was producing a textbook section on population dynamics I tried to find a good solid example of a supposed decline in bird abundance for any species in which the mechanisms of decline were understood. While there are many data on declines, and much hand wringing, there were virtually no examples with hard data on mechanisms except for the vague idea of habitat loss. Maybe mechanisms are unimportant in conservation biology but it seems unlikely that they are superfluous to understanding the larger issues of population dynamics.

The second general question is the converse one of what kinds of organisms should ecologists be concentrating on if we are to make convincing arguments about biodiversity conservation? If changes in community and ecosystem dynamics are looming, so that the future will not look like the past, where should we put our energies to prevent ecosystem collapse? Are insects and invertebrates in general of greater importance that birds or mammals?

Hurlbert (1971, 1997) raised the question of how to determine the general functional importance of a species to a community, and he concluded that the only measure that has been put forward is ‘the sum over all species, of the changes in productivity which would occur on removal of the particular species from the community’. He pointed out that this definition of importance is clear and specific but could never be measured for even a single species in a community for practical reasons. Hurlbert (1997) also recognized that ‘importance’ had now morphed into ‘keystone’ for much of ecology (e.g. Daily et al. 1993), with all the problems associated with the keystone idea. He suggested, as did Walker (1992) that most species are redundant and of little consequence to ecosystem functioning. Much discussion has occurred since these papers and some has morphed into discussions of ‘functional groups’ instead of species. But plant ecologists have in general not addressed the challenges that Hurlbert (1999) asked, and we are far from being able to answer even the hypothetical question in the title of this blog.

Daily, G.C., Ehrlich, P.R., and Haddad, N.M. 1993. Double keystone bird in a keystone species complex. Proceedings of the National Academy of Sciences USA 90(2): 592-594. doi:10.2307/2361101.

Hurlbert, S.H. 1971. The non-concept of species diversity: a critique and alternative parameters. Ecology 52: 577-586.

Hurlbert, S.H. 1997. Functional importance vs. keystoneness: Reformulating some questions in theoretical biocenology. Australian Journal of Ecology 22(4): 369-382.

Walker, B.H. 1992. Biodiversity and ecological redundancy. Conservation Biology 6: 18-23.

On Political Ecology

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When I give a general lecture now, I typically have to inform the audience that I am talking about scientific ecology not political ecology. What is the difference? Scientific ecology is classical boring science, stating hypotheses, doing experiments or observations to gather the data, testing the idea, and accepting or rejecting it, outlined clearly in many papers (Platt 1963, Wolff and Krebs (2008), and illustrated in this diagram:

Scientific ecology is clearly out-of-date, and no longer ‘cool’ when compared to the new political ecology.

Political ecology is a curious mix of traditional ecology added to the advocacy issue of protecting biodiversity. Political ecology is aimed at convincing society in general and politicians in particular to protect the Earth’s biodiversity. This is a noble cause, and my complaint is only that when we advocate and use scientific ecology in pursuit of a political agenda we should be scientifically rigorous. Yet much of biodiversity science is a mix of belief and evidence, with unsuitable evidence used in support of what is a noble belief. If we believe that the end justifies the means, we would be happy with this. But I am not.

One example will illustrate my frustration with political ecology. Dirzo et al. (2014) in a recent Science paper give an illustration of the effects of removing large animals from an ecosystem. In their Figure 4, page 404, a set of 4 graphs purport to show experimentally what happens when you remove large wildlife species in Kenya, the Kenya Long-term Exclosure Experiment (Young et al. 1997). But this experiment is hopelessly flawed in being carried out on a set of plots of 4 ha, a postage stamp of habitat relative to large mammal movements and ecosystem processes. But the fact that this particular experiment was not properly designed for the questions it is now being used to address is not a problem if this is political ecology rather than scientific ecology. The overall goal of the Dirzo et al. (2014) paper is admirable, but it is achieved by quoting a whole series of questionable extrapolations given in other papers. The counter-argument in conservation biology has always been that we do not have time to do proper research and we must act now. The consequence is the elevation of expert opinion in conservation science to the realm of truth without going through the proper scientific process.

We are left with this prediction from Dirzo et al. (2014):

“Cumulatively, systematic defaunation clearly threatens to fundamentally alter basic ecological functions and is contributing to push us toward global-scale “tipping points” from which we may not be able to return ……. If unchecked, Anthropocene defaunation will become not only a characteristic of the planet’s sixth mass extinction, but also a driver of fundamental global transformations in ecosystem functioning.”

I fear that statements like this are more akin to something like a religion of conservation fundamentalism, while we proclaim to be scientists.

Dirzo, R., Young, H.S., Galetti, M., Ceballos, G., Isaac, N.J.B. & Collen, B. (2014) Defaunation in the Anthropocene. Science, 345, 401-406.

Platt, J.R. (1964) Strong inference. Science, 146, 347-353.

Wolff, J.O. & Krebs, C.J. (2008) Hypothesis testing and the scientific method revisited. Acta Zoologica Sinica, 54, 383-386.

Young, T.P., Okello, B.D., Kinyua, D. & Palmer, T.M. (1997) KLEE: A long‐term multi‐species herbivore exclusion experiment in Laikipia, Kenya. African Journal of Range & Forage Science, 14, 94-102.

Identifying the Most Critical Problems in Environmental Science

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A common perception of government policy makers is that ecologists fritter around doing interesting tidbits that produce nice 7 second sound-bites for radio or TV, but they never address the most serious environmental problems that the government faces in environmental science. So the question we need to address for any developed nation is this – what are the most critical environmental problems that ecologists could help to address? Since most critical environmental problems are long-term, one constraint would be that goals have to be achieved in the short term so that people could see progress. There would be funding constraints but let us assume that if we hit the right buttons, funding would be plentiful (think military).

There is no question that not all countries would have the same detailed list of critical environmental problems. But there ought to be communalities so we ought to cast a wide, general net to define problems. Start with some clear ecological principles: there is only one Earth and we ought to take care of it with a time frame that follows the First Nations principle of ‘seven generations’, about 300 years, as our time horizon. We know the solution to some environmental problems but new ones are continually a challenge. We need in every country the equivalent of an Environmental Army monitoring environmental problems.

1. Food security. All populations need food yet modern agriculture violates many simple ecological rules. Is the system sustainable in the long term? Probably not so the first major problem is how might we move modern agriculture toward sustainability. Subheadings here abound – pest control and alternatives to poisons, biological control of insect pests, cultural pest control, soil fertility decline, quarantine control, the list goes on. Implicit in all this is a regulatory framework that prevents the introduction of new miracle agricultural practices without adequate ecological background checks. The neonicotinoids-and-bees problem immediately comes to mind. We must get away from the attitude of ‘do it now’ and ‘clean up the mess later’ when we find problems.

2. Pollution effects. This is the hard one because it is climate change in the long term which must be emphasized. But in the shorter term detailed measurements of air quality and harmful effects of smoke and diesel fumes among other things on human and animal health could give an immediacy to such a detailed research program. The same principle applies here – do not put something new out in the environment and ask questions later. Fracking for natural gas and oil comes to mind, as well as the whole recycling system. Electricity generation is a key driver and mining for carbon-based energy ought to be eliminated gradually.

3. Conservation. Could our country be the first on Earth to have a complete inventory of species in all the taxonomic groups? It is a scandal that we do not have a list of life on Earth, and we need to get this message across with clever advertising. Taxonomists ought to be more important than bankers and be paid accordingly. Again many subheadings here – endangered species problems, pest management interactions with agriculture, disease ecology (always a hot button), monitoring, monitoring interacting with citizen science where possible.

4. The Oceans. We ought to be responsible for the health of at least our near-shore ecosystems, and monitoring protocols should be established so that we have ecosystem health scores presented as frequently as stock market reports. As global citizens we should be contributing to studying global problems of the high seas, the Antarctic Continent, and acting together with other nations to solve global issues.

The advantage of all these 4 topics with respect to convincing a politician to fund them is that they are interdisciplinary and consequently can be addressed only by carefully selected teams of ecologists, physicians, molecular biologists, geologists, chemists, and social scientists. A call for research proposals in these areas would soon build teams of scientists to address the major issues of our time. Money can help glue together scientific teams.

All of this will cost a lot of money and our current political philosophy seems to be that environmental costs are the lowest priority, and taxes for protecting the environment should be as near zero as possible. This must change soon lest the Earth become a garbage can unfit for human habitation.

Dicks, L. et al. (2013). What do we need to know to enhance the environmental sustainability of agricultural production? A prioritisation of knowledge needs for the UK food system. Sustainability 5, 3095-3115.

Sutherland, W.J.,et al. (2010) The identification of priority policy options for UK nature conservation. Journal of Applied Ecology 47(5): 955-965.

Does Forestry in British Columbia Make Money?

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While driving around British Columbia, one cannot help but notice the forestry industry – bare clear-cuts on the hills, logging trucks on the road. This simple observation leads me to this question: is the forest industry that now exists in BC profitable when one does a full-scale life-cycle analysis of its environmental impacts?

The answer to this question is obvious to most people – forestry is a good renewable-resource industry that provides many jobs and promotes economic growth. There is much literature from the government and the forest industry about how BC utilizes sustainable forestry. Most people accept this positive view of the forest industry. But I am concerned that we might find a different answer if we look behind the smoke screen of advertising and the government’s rosy view that all resource extraction industries are valuable for BC. Why might this be? I cannot analyse the economics of the forestry industry because I am not an economist, so in some sense all I would like to do here is ask some questions that others who are more qualified might help to answer.

The first question is what to include in such an analysis. If forestry is considered only trees, rather than the whole ecosystem with all its biodiversity, you would get one answer. If you worry about biodiversity you might get another answer (e.g. Drever 2000). If you worry about climate change and carbon dioxide dynamics, you can view forests as carbon stores that might be valuable if there is a price on carbon in the future. If you value the forests of BC as ecosystems that ought to be left as a legacy to our grandchildren, you might again take a different perspective. Do you include in your balance sheet the costs of fire-fighting and the government departments that manage the industry? What external costs are left out of a broad overview of forestry in BC?

At present it would appear to me that forest harvesting is not sustainable in BC, even if you take the narrow view that only trees matter in the calculations. If it were a sustainable industry, there would be no need to harvest old growth forests. But you could be certain that if any government actually said ‘no more cutting of old growth’, there would be an outcry. But if we continue as we are, we will cut our way to the North Pole, as long as we can find trees. The Yukon is next, if not now then for our grandchildren. But trees grow back again, so all will be well. Restoration ecology to the rescue. If you take a biodiversity perspective, you might find that what grows back is a pale imitation of what was there before. And if the ecosystem does restore, the time frame may be very long, looping back to the question of what sustainability means. If the forest ecosystem restores itself in 300 years, is that sustainable? How about 500 years?

If we treat forestry like any other agricultural enterprise, we might allocate some fraction of land to this activity and use the rest for recreation, tourism, and truly sustainable activities like berry picking. Suppose we planned that by 2020 forest companies could not cut anymore on crown land, and by that date land would be allocated to companies to purchase like any farmer would buy a farm. I can hear the howls of protest to such a suggestion. Is it correct that forestry then is really a mining industry operating on non-renewable resources – crown land that has old growth that belongs in theory to the people of BC in perpetuity? There are reports of how some forest companies are short-changing the government in their cutting practices because of the failure of inspection of the amount of wood taken off an area (e.g. see Parfitt, 2007) Short-changing the government is short-changing the people of the province and the people of the future who would live here.

But it seems to me that a much larger issue is that much of the planning for forestry in BC ignores the biodiversity issue. To be sure an iconic bird or plant might have some small areas saved for it, if it is included on the threatened species list. But as any ecologist might suggest, these protected areas are postage stamps that are in the long-term insufficient for the conservation of the species of concern. The major conservation issues of our day are those where economic growth produced by harvesting trees, natural gas, oil or coal collides directly with protecting our ecosystems for future generations. By any measure, the economic agenda wins the day, and the biodiversity agenda is peppered with good advertising telling us that all will be well.

It is fortunate that the First Nations of BC are rapidly awakening to these issues, and progress has been made in giving them more authority over their traditional lands. This is a bright side of the global issue of conservation in Canada.

The political issue that flows from this discussion is to ask how much subsidy our BC government provides to aid the exploitation of our natural resources, resources that ought to be managed for the future of the people of BC. Are we subsidizing environmental destruction with our tax dollars and all the while being told that even more economic growth is necessary? There must be another way, and for an ecologist concerned with biodiversity and the protection of the natural resources of our province, the current policies look like a Ponzi scheme.

Drever, R. 2000. A Cut Above: Ecological principles for sustainable forestry on BC’s coast. David Suzuki Foundation, Vancouver, B.C. ISBN 1-55054-689-9, Available at http://www.davidsuzuki.org/publications/reports/2000/a-cut-above-ecological-principles-for-sustainable-forestry-on-bcs-coast/

Parfitt, B. 2007. Over-cutting and Waste in B.C.’s Interior: A Call to Rethink B.C.’s Pine Beetle Logging Strategy. Canadian Centre for Policy Alternatives, Vancouver, BC. ISBN: 978-0-88627-533-4, available at www.policyalternatives.ca/BC f

The Conservative Agenda for Ecology

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Many politicians that are conservative are true conservatives in the traditional meaning of the term. Many business people are conservative in the same way, and that is a good thing. But there exist in the world a set of conservatives that have a particularly destructive agenda based on a general belief that evidence, particularly scientific evidence, is not any more important as a basis for action than personal beliefs. Climate change is the example of the day, but there are many others from the utility of vaccinations for children, to items more to an ecologist’s interest like the value of biodiversity. In a sense this is a philosophical divide that is currently producing problems for ecologists in the countries I know most about, Canada and Australia, but possibly also in the USA and Britain.

The conservative political textbook says cut taxes and all will be well, especially for the rich and those in business, and then say ‘we have no money for ‘<fill in the blank here> ‘so we must cut funding to hospitals, schools, universities, and scientists’. The latest example I want to discuss is from the dismemberment of the Commonwealth Scientific and Industrial Research Organization (CSIRO) in Australia by the current conservative government.

CSIRO was sent up in the 1950s to do research for the betterment of the people of Australia. Throughout the 1960s, 1970s and 1980s it was one of the world premier research organizations. If you do not believe this you can look at how many important papers, awards, and the occasional Nobel Prize came out of this organization. It had at this time perhaps 8500 employees in more than 25 Divisions. Divisions varied in size but in general they would have about 200-300 scientists and technicians. Divisions were run by a Chief who was a scientist and who decided the important directions for research in his or her area, whether it be horticulture, wildlife, energy technology, animal science, or mathematics and statistics. CSIRO itself was led by eminent scientists who provided some guidance to the Divisions but left the directions of science to the Chiefs and their scientists. It was a golden development for Australian science and a model for science that was appreciated all around the world.

This of course is dreamland in today’s world. So by the late 1980s the Australian federal government began determining scientific priorities for CSIRO. We know what science is important, the new leaders said, so do this. This would work well if it was not guided by politicians and MBAs who had no scientific training and knew nothing about science past or present. Piled on this were two neo-conservative philosophies. First, science is important only if it generates money for the economy. Coal mining triumphs wildlife research. Second, science in the public interest is not to be encouraged but cut. The public interest does not generate money. Why this change happened can be declared a mystery but it seemed to happen all around the western world in the same time frame. Perhaps it had something to do with scientific research that had the obvious message that one ought to do something about climate change or protecting biodiversity, things that would cost money and might curtail business practices.

Now with the current 2014 budget in Australia we have a clear statement of this approach to ecological science. The word from on high has come down within CSIRO that, because of cuts to their budget, one goal is as follows: “Reduce terrestrial biodiversity research (“reduced investment in terrestrial biodiversity with a particular focus on rationalising work currently conducted across the “Managing Species and Natural Ecosystems in a Changing Climate” theme and the “Building Resilient Australian Biodiversity Assets” theme in these Divisions”).Translated, this means about 20% of the staff involved in biodiversity research will be retrenched and work will continue in some areas at a reduced level. At a time when rapid climate change is starting, it boggles the mind that some people at some high levels think that supporting the coal and iron ore industry with government-funded research is more important than studies on biodiversity. (If you appreciate irony, this decision comes in a week when it is discovered that the largest coal company in Australia, mining coal on crown land, had profits of $16 billion last year and paid not one cent of tax.)

So perhaps all this illustrates that ecological research and all public interest research is rather low on the radar of importance in the political arena in comparison with subsidizing business. I should note that at the same time as these cuts are being implemented, CSIRO is also cutting agricultural research in Australia so biodiversity is not the only target. One could obtain similar statistics for the Canadian scene.

There is little any ecologist can do about this philosophy. If the public in general is getting more concerned about climate change, the simplest way to deal with this concern for a politician is to cut research in climate change so that no data are reported on the topic. The same can be said about biodiversity issues. There is too much bad news that the environmental sciences report, and the less information that is available to the public the better. This approach to the biosphere is not very encouraging for our grandchildren.

Perhaps our best approach is to infiltrate at the grass roots level in teaching, tweeting, voting, writing letters, and attending political meetings that permit some discussion of issues. Someday our political masters will realize that the quality of life is more important than the GDP, and we can being to worry more about the future of biodiversity in particular and science in general.

 

Krebs, C.J. 2013. “What good is a CSIRO division of wildlife research anyway?” In Science under Siege: Zoology under Threat, edited by Peter Banks, Daniel Lunney and Chris Dickman, pp. 5-8. Mosman, N.S.W.: Royal Zoological Society of New South Wales.

Oreskes, Naomi, and Erik M.M. Conway. 2010. Merchants of Doubt: How a Handful of Scientists Obscured the Truth on Issues from Tobacco Smoke to Global Warming. New York: Bloomsbury Press. 355 pp. ISBN 978-1-59691-610-4

Shaw, Christopher. 2013. “Choosing a dangerous limit for climate change: Public representations of the decision making process.” Global Environmental Change 23 (2):563-571. doi: 10.1016/j.gloenvcha.2012.12.012.

Wilkinson, Todd. 1998. Science Under Siege: The Politicians’ War on Nature and Truth. Boulder, Colorado: Johnson Books. 364 pp. ISBN 1-55566-211-0

 

Wildlife Management Dilemmas

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The science of wildlife management has moved from the good old days of worrying only about deer and ducks to the broader issues of conservation management of all species. But it operates in an impossible squeeze between human activities and wildlife responses. One key problem is the incremental creep of land use decisions. If we log half of the forest surely there is plenty left there for the wildlife to thrive, or so many people believe. So a central dilemma is habitat loss. The simple approach using ‘cow arithmetic’ says that if you have a farm one-third the size of what you have now, you will be able to have only one-third the number of cows. So habitat loss is critical but there seems to be no way of stopping it as long as the human population continues to expand.

To solve this problem we set up parks and reserves. That will please most of the botanists because if you have a plant species you are concerned about, you need set aside only a few hectares of land to keep it safe. This approach is at the core of wildlife management’s dilemma. You keep the plant species but lose the ecosystem. Certainly you can keep many of the small insects in a few hectares, so you protect not only the plant species but more of the biota. But you will lose all the birds and the larger species that need much larger areas of habitat. One of the defining moments in wildlife management and conservation ecology occurred when several ecologists recognized that even large national parks were not large enough for the charismatic megafauna.

Maybe we can rescue it all with metapopulations, islands of good habitat close enough to each other to permit dispersal. That will work in some cases and is a useful addition to the management arsenal of tools. But then we have to cope with additional problems – introduced pests and diseases that we may or may not be able to control, and global problems of air and water pollution that respect no neat geographic boundaries.

We cannot control species interactions so if we tinker with one aspect of the ecosystem, we find unintended consequences in another aspect of the ecosystem that we did not expect. We brought rabbits to Australia and to many islands with dire consequences no one seemed to anticipate. We also brought rats and pigs to island inadvertently with many well documented problems for bird and plants. We take predators away from ecosystems and then complain to the government that there are too may deer or Canada geese.

So part of the dilemma of wildlife management in the 21st century is that we do XYZ and then only later ask ecologists whether it was a good idea or not to do XYZ. Decisions are made by governments, companies, farmers, or city dwellers to change some element of the ecosystem without anyone asking a wildlife manager or an ecologist what the consequences might be. We love cats so we pass laws that prohibit managers from culling wild cats and only allow them to sterilize and release them. We love horses so we do the same. So wildlife management decisions are driven not by ecological studies and recommendations but by public demands and weak politicians. Wildlife management is thus a social science, with all the dilemmas generated when one part of society wishes to harvest seals and one part demands protection for seals.

Wildlife management has always been handicapped by the hunters and fishers who know everything about what management should be practiced. There is no need to have any professional training to decide management goals, management actions, and funding preferences for many of these people. I suppose we should at least be grateful that the same approach is not applied in medical science.

Wildlife management has always been a low priority activity, underfunded and moved more by political whims than by science. This is not at all the fault of all the excellent wildlife and fishery scientists who try their best to protect and manage our ecosystems. It is a victim of the constraints of making decisions on the spot about long term issues without the time or money to investigate the science necessary for knowledge of the consequences of our actions. The world changes slowly and if our memory is on the time span of 1-3 years, we are not on ecosystem time.

Much action must be spent on trying to restore ecosystems damaged by human activities. Restoration ecology recognizes that it is really partial restoration ecology because we cannot get back to the starting point. None of this is terribly new to ecologists or wildlife managers but it is good to keep it in mind as we get lost in the details of our daily chores.

Humans are destroying the earth in their quest for wealth, and simultaneously producing the problems of poverty and obesity. Led by politicians who do not lead and who do not seem to know what the problems of the Earth are, we keep a positive view of the scientific progress we generate, enjoy the existing beauty of biodiversity, and hope that the future will somehow cope with the changes we have set in motion.

“Humans, including ecologists, have a peculiar fascination with attempting to correct one ecological mistake with another, rather than removing the source of the problem”.   (Schindler 1997, p. 4)

 

Estes, J.A. et al. 2011. Trophic downgrading of Planet Earth. Science 333:301-306.

Likens, G.E. 2010. The role of science in decision making: does evidence-based science drive environmental policy? Frontiers in Ecology and the Environment 8:e1-e9.

Newmark, W.D. 1985. Legal and biotic boundaries of Western North American National Parks: A problem of congruence. Biological Conservation 33:197-208.

Pauly, D. 1995. Anecdotes and the shifting baseline syndrome of fisheries. Trends in Ecology and Evolution 10:430.

Schindler, D. W. 1997. Liming to restore acidified lakes and streams: a typical approach to restoring damaged ecosystems? Restoration Ecology 5:1-6.

 

Two Visions of Ecological Research

6 Replies

Let us assume for the moment that the goal of scientific ecology is to understand the reasons for changes in the distribution and abundance of animals, plants, and microbes. If you do not think this is our main agenda, perhaps you should not read further.

The conventional, old paradigm to achieve this goal is to obtain a good description of the natural history of the organisms of interest in a population or community, define the food web they operate within, and then determine by observations or manipulations the parameters that limit its distribution and abundance. This can be difficult to achieve in rich food webs with many species, and in systems in which the species are not yet taxonomically described, and particularly in microbe communities. Consequently a prerequisite of this paradigm is to have good taxonomy and to be able to recognize species X versus species Y. A whole variety of techniques can be used for this taxonomy, including morphology (the traditional approach) and genetics. Using this approach ecologists over the past 90 years have made much progress in deriving some tentative explanations for the changes that occur in populations and communities. If there has been a problem with this approach, it is largely because of disagreements about what data are sufficient to test hypothesis X, and whether the results of manipulation Y are convincing. A great deal of the accumulated data obtained with this approach has been useful to fisheries management, wildlife management, pest control, and agricultural production.

The new metagenomics paradigm, to use one label, suggests that this old approach is not getting us anywhere fast enough for microbial communities, and we need to forget most of this nonsense and get into sequencing, particularly for microbial communities. New improvements in the speed of doing this work makes it feasible. The question I wish to address here is not the validity or the great improvements in genetic analysis, but rather whether or not this approach can replace the conventional old paradigm. I appreciate that if we grab a sample of mud, water, or the bugs in an insect trap and grind it all up, and run it through these amazing sequencing machines, we get a very great amount of data. We then might try to associate some of these kinds of data with particular ‘species’ and this may well work in groups for which the morphological species are well described. But what do we do about the undescribed sequences? We know that microbial diversity is much higher than what we can currently culture in the laboratory. We can make rules about what to call unknown unit A, unknown unit B, and so on. That is fine, but now what? We are in some sense back where Linnaeus was in 1753 in giving names to plants.

Now comes the difficult bit. Do we just take the metagenomics approach and tack it on to the conventional approach, using unknown A, unknown B, etc. instead of Pseudomonas flavescens or Bacillus licheniformis? We cannot get very far this way because the first thing we need to decide is does unknown A a primary producer or unknown B a decomposer of complex organic molecules? So perhaps this leads us to invent a whole new taxonomy to replace the old one. But perhaps we will go another way to say we will answer questions with the new system like is this pond ecosystem changing in response to global warming or nutrient additions? We can describe many system shifts in DNA-terminology but will we have any knowledge of what they mean or how management might change these trends? We could work all this out in the long term I presume. So I guess my confusion is largely exactly which set of hypotheses are you going to test with the new metagenomics paradigm? I can see a great deal of alpha-descriptive information being captured but I am not sure where to go from there. My challenge to the developers of the new paradigm is to list a set of problems in the Earth’s ecosystems for which this new paradigm could provide better answers more quickly than the old approach.

Microbial ecology is certainly much more difficult to carry out than traditional ecology on macroscopic animals and plants. As such it should be able to use new technology that can improve understanding of the structure and function of microbe communities. All new advances in technology are helpful for solving some ecological problems and should be so used. The suggestion that the conventional approach is out of date should certainly be entertained but in the last 70 years the development of air photos, of radio telemetry, of satellite imagery, of electrophoresis, of simplified chemical analyses, of automated weather stations, and the new possibilities of genetic analysis have been most valuable to solving ecological questions for many of our larger species. But in every case, at every step we should be more careful to ask exactly what questions the new technology can answer. Piling up terabytes of data is not science and could in fact hinder science. We do not wish to validate the Rutherford prediction that our ecological science is “stamp collecting”.

Why I am Bored with Biodiversity and Ecosystem Services

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Ecosystem services have become the flavour of the month and already it seems tired and bland.  “Biodiversity must be preserved for its ecosystem services” but making the tie between diversity and services has been elusive and will continue to be so. A body of literature has accumulated on the results of small-scale experiments in which plant diversity is manipulated and some service, let’s say productivity, is monitored. In some cases a relationship is found − more species more productivity; but not always. A rancher who wants to increase the productivity of her rangeland would be more inclined to plant to a monoculture of a highly productive grass. For example the introduced species, Crested Wheat Grass (Agropyron cristatum), was widely used in British Columbia in the early 20th century. Cheat grass (Bromus tectorum), another exotic species (if we are talking about North America) is expanding into rangeland and while it might increase the diversity, it reduces the productivity for forage.

Recently Mark Vellend (TREE 29(3): 138, March 2014) reviewed a book by Donald Maier, “What’s so Good about Biodiversity? A Call for Better Reasoning about Nature’s Value. “(Springer 2012). The take home message of this book is that the biodiversity−ecosystem services rationale for protecting biodiversity does not always hold and more species does not necessarily translate into more food or less disease.  It is time to get rid of platitudes and to confront our biases in a critical manner when it comes to biodiversity.

Further to this topic, in December 2013 the first meeting was held of the budding International Panel on Biodiversity and Ecosystem Services. It will focus on the following topics:

1) Task force on capacity building
2) Task force on indigenous and local knowledge systems
3) Task force on knowledge and data
4) Development of a guide to the production and integration of assessments from and across all levels
5) Assessment on pollination and pollinators associated with food production
6) Methodological assessment on scenario analysis and modeling of biodiversity and ecosystem services
7)  Methodological assessment on the conceptualization of values of biodiversity and nature’s benefits to people
8) Development of a catalogue of policy support tools and methodologies and providing guidance on how further development of such tools and methodologies could be promoted and catalyzed

Given the involvement of 115 countries it will be interesting to track the success of this panel.  Note that pollination and pollinators are identified as a specific ecosystem service. Critical experimental ecologists should be involved if this panel is to be productive in a meaningful way and, if not on the panel, they should track its progress and comment accordingly. Stay tuned for further updates.